LocationSample Name
Sample Date
Sample Depth
Metals (mg/kg) GPL DTSC TTLC
Antimony 7.84 ‐ 500
Arsenic 24.3 0.36/82 500
Barium 43000 ‐ 10,000
Beryllium ‐ 6,900 75
Cadmium 970 4,000 100Chromium 660 ‐ 2,500
Chromium VI (Hexavalent) 30 6.2 500
Cobalt ‐‐ 8,000
Copper 5600 ‐ 2,500
Lead 232 320 1,000Mercury 2.1 4.4 20Molybdenum ‐‐ 3,500 Nickel 3400 64,000 2,000Selenium ‐‐ 100Silver ‐‐ 500Thallium ‐‐ 700Vanadium ‐‐ 2,400 Zinc ‐‐ 5,000
‐
PCBs (mg/kg)
Aroclor‐1016 (PCB‐1016) ‐ 17 ‐
Aroclor‐1221 (PCB‐1221) ‐ 0.53 ‐
Aroclor‐1232 (PCB‐1232) ‐ 0.49 ‐
Aroclor‐1242 (PCB‐1242) ‐ 0.58 ‐
Aroclor‐1248 (PCB‐1248) ‐ 0.58 ‐
Aroclor‐1254 (PCB‐1254) ‐ 0.59 ‐
Aroclor‐1260 (PCB‐1260) ‐ 0.6 ‐
Aroclor‐1262 (PCB‐1262) ‐‐‐
Aroclor‐1268 (PCB‐1268) ‐‐‐
Total PCBs 130 0.58 50
‐
PEST (mg/kg)
4,4'‐DDD ‐ 6.2 1.0
4,4'‐DDE ‐ 9.3 1.04,4'‐DDT ‐ 7.1 1.0
Aldrin ‐ 0.18 1.4
alpha‐BHC ‐ 0.24 ‐
beta‐BHC ‐ 0.82 ‐
Chlordane ‐ 6.1 2.5
delta‐BHC ‐‐‐
Dieldrin ‐ 0.093 8.0
Endosulfan I ‐ 6,000 ‐
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) < 0.773 < 0.765 < 0.754 < 0.732 < 0.765 < 0.765 < 0.761 < 0.732 < 0.718 0.43 J
3.85 1.95 3.25 1.38 5.58 1.77 6.75 2.06 2.77 2.44
94.5 62.3 72.6 69.5 79.4 74.9 92.9 83.4 99.5 76.8
0.366 0.323 0.239 J 0.309 0.242 J 0.318 0.282 0.326 0.305 0.377
0.513 J 0.415 J 0.407 J 0.335 J 0.451 J 0.881 0.432 J 0.51 0.881 0.432 J
17.3 15 12.8 16.3 17.5 17 14.3 16.9 15.6 18
‐‐‐‐‐‐‐‐‐‐
8.75 9.65 4.42 9.81 3.74 9.32 4.55 9.24 8.13 11.2
13.9 12 7.64 10 10.9 23.5 13.6 20.4 21.3 12.8
13.9 6.82 9.76 4.17 17.6 22.7 14.5 14.9 32.5 8.08
0.0152 J 0.0174 J 0.00945 J 0.0215 J 0.0239 J 0.0234 J 0.0218 J 0.0235 J 0.0194 J 0.0182 J
0.269 < 0.255 0.425 < 0.244 0.863 0.147 J 0.884 < 0.244 0.401 < 0.251
8.26 6.8 5.91 7.24 5.92 8.92 7.5 7.51 8.96 8.38
2.12 < 0.765 0.903 0.368 J < 0.765 0.467 J 1.16 < 0.732 < 0.718 < 0.754 < 0.258 < 0.255 < 0.251 < 0.244 0.185 J < 0.255 < 0.254 < 0.244 < 0.239 < 0.251
0.769 J 0.425 J 0.252 J < 0.732 0.47 J 0.181 J 0.734 J 0.223 J 0.192 J < 0.754
47.3 48 29.6 51.5 23.9 49.6 27.2 49.8 41.2 58
51.1 B 28.5 B 33 24.8 48.2 55.5 56.9 43.6 70 34.7
< 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 0.12 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05
0.033 J < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05
0.033 < 0.05 0.12 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ 0.0024 J ‐‐‐
‐‐ 0.0048 J ‐‐‐ 0.0041 J ‐‐‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.01 ‐ ‐ ‐ < 0.01 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.05 ‐ ‐ ‐ 0.033 J ‐‐‐
‐‐ < 0.01 ‐ ‐ ‐ < 0.01 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PEST (mg/kg) ‐
Endosulfan II ‐ 6,000 ‐
Endosulfan sulfate ‐ 11,000 ‐
Endrin ‐ 160 0.2
Endrin aldehyde ‐‐‐
Endrin ketone ‐‐‐
gamma‐BHC (Lindane) ‐ 2 4.0
Heptachlor ‐ 0.63 4.7
Heptachlor epoxide ‐ 0.33 ‐
Methoxychlor ‐ 2600 100
Toxaphene ‐ 1.2 5
‐
SVOCs (mg/kg)
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,3‐Dichlorobenzene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
1‐Methylnaphthalene ‐ 30 ‐
2,2'‐oxybis(2‐Chloropropane) ‐‐‐
2,4,5‐Trichlorophenol ‐ 53,000 ‐
2,4,6‐Trichlorophenol ‐ 21 ‐
2,4‐Dichlorophenol ‐ 1,600 ‐
2,4‐Dimethylphenol ‐ 11,000 ‐
2,4‐Dinitrophenol ‐ 1,100 ‐
2,4‐Dinitrotoluene ‐‐‐
2,6‐Dichlorophenol ‐ 4.7 ‐
2,6‐Dinitrotoluene ‐ 0.99 ‐
2‐Chloronaphthalene ‐ 27,000 ‐
2‐Chlorophenol ‐ 3,900 ‐
2‐Methylnaphthalene ‐ 1,300 ‐
2‐Methylphenol (o‐Cresol) ‐ 26,000 ‐
2‐Nitroaniline ‐ 5,200 ‐
2‐Nitrophenol ‐‐‐3,3'‐Dichlorobenzidine ‐ 0.93 ‐
3‐Nitroaniline ‐‐‐
4,6‐Dinitro‐2‐methylphenol ‐ 42 ‐
4‐Bromophenyl phenyl ether ‐‐‐
4‐Chloro‐3‐methylphenol ‐ 53,000 ‐
4‐Chloroaniline ‐ 7.4 ‐
4‐Chlorophenyl phenyl ether ‐‐‐
4‐Nitroaniline ‐ 74 ‐
4‐Nitrophenol ‐‐‐
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) ‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.01 ‐ ‐ ‐ < 0.01 ‐ ‐ ‐
‐‐ < 0.005 ‐ ‐ ‐ < 0.005 ‐ ‐ ‐
‐‐ < 0.1 ‐ ‐ ‐ < 0.1 ‐ ‐ ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
SVOCs (mg/kg) ‐
Acenaphthene ‐ 23,000 ‐
Acenaphthylene ‐‐‐Aniline ‐ 260 ‐
Anthracene ‐ 130,000 ‐
Azobenzene ‐‐‐Benzidine ‐ 0.003 ‐
Benzo(a)anthracene ‐ 12 ‐
Benzo(a)pyrene 14 1.3 ‐Benzo(b)fluoranthene ‐ 13 ‐
Benzo(g,h,i)perylene ‐‐‐Benzo(k)fluoranthene ‐ 210,000 ‐ Benzoic acid ‐ 2,100,000 ‐
Benzyl Alcohol ‐ 53,000 ‐
bis(2‐Chloroethoxy)methane ‐ 1,600 ‐
bis(2‐Chloroethyl)ether ‐ 0.47 ‐
bis(2‐Ethylhexyl)phthalate 57 110 ‐
Butyl benzylphthalate ‐ 780 ‐
Chrysene ‐ 1,300 ‐
Dibenz(a,h)anthracene ‐ 0.31 ‐
Dibenzofuran ‐ 650 ‐
Diethyl phthalate ‐ 420,000 ‐Dimethyl phthalate ‐‐‐
Di‐n‐butylphthalate ‐ 53,000 ‐
Di‐n‐octyl phthalate ‐ 5,300 ‐Fluoranthene ‐ 18,000 ‐
Fluorene ‐ 17,000 ‐
Hexachlorobenzene ‐ 0.86 ‐
Hexachlorobutadiene ‐ 5.3 ‐
Hexachlorocyclopentadiene ‐‐‐Hexachloroethane ‐‐‐Indeno(1,2,3‐cd)pyrene ‐ 13 ‐ Isophorone ‐ 1,600 ‐
m,p‐Cresols ‐‐‐
Naphthalene ‐ 6.5 ‐
Nitrobenzene ‐‐‐N‐Nitrosodimethylamine ‐ 0.53 ‐
N‐Nitrosodi‐n‐propylamine ‐ 0.21 ‐
N‐Nitrosodiphenylamine ‐ 300 ‐
Pentachlorophenol 0.0717 2 ‐Phenanthrene ‐‐‐Phenol ‐ 160,000 ‐ Pyrene ‐ 13,000 ‐
Pyridine ‐ 530 ‐
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) < 0.015 ‐ ‐ ‐ < 0.015 ‐ ‐ ‐ < 0.015 ‐
< 0.03 ‐ ‐ ‐ < 0.03 ‐ ‐ ‐ < 0.03 ‐
‐‐‐‐‐‐‐‐‐‐
< 0.0099 ‐ ‐ ‐ 0.0082 J ‐‐‐ < 0.01 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
0.0063 J ‐‐‐ 0.0055 J ‐‐‐ 0.0092 J ‐
0.012 ‐‐‐ 0.019 ‐‐‐ 0.0084 J ‐
0.016 ‐‐‐ 0.021 ‐‐‐ 0.01 ‐
0.026 ‐‐‐ 0.028 ‐‐‐ 0.014 ‐
0.0078 J ‐‐‐ 0.047 ‐‐‐ 0.015 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
0.0084 J ‐‐‐ 0.02 ‐‐‐ 0.013 ‐
0.054 ‐‐‐ 0.06 ‐‐‐ < 0.01 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
0.02 ‐‐‐ 0.054 ‐‐‐ 0.03 ‐
< 0.0099 ‐ ‐ ‐ < 0.01 ‐ ‐ ‐ < 0.01 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
0.1 ‐‐‐ 0.11 ‐‐‐ 0.0049 J ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.015 ‐ ‐ ‐ < 0.015 ‐ ‐ ‐ < 0.015 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
0.012 ‐‐‐ 0.023 ‐‐‐ 0.019 ‐
‐‐‐‐‐‐‐‐‐‐
0.039 ‐‐‐ 0.032 ‐‐‐ 0.058 ‐
‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
TPH (mg/kg)
PHC as Gasoline 5,400 97 ‐
Total Petroleum Hydrocarbons (C6) ‐‐‐
Total Petroleum Hydrocarbons (C7) ‐‐‐
Total Petroleum Hydrocarbons (C8) ‐‐‐
Total Petroleum Hydrocarbons (C9‐C10) ‐‐‐
Total Petroleum Hydrocarbons (C11‐C12) ‐‐‐
Total Petroleum Hydrocarbons (C13‐C14) ‐‐‐
Total Petroleum Hydrocarbons (C15‐C16) ‐‐‐
Total Petroleum Hydrocarbons (C17‐C18) ‐‐‐
Total Petroleum Hydrocarbons (C19‐C20) ‐‐‐
Total Petroleum Hydrocarbons (C21‐C22) ‐‐‐
Total Petroleum Hydrocarbons (C23‐C24) ‐‐‐
Total Petroleum Hydrocarbons (C25‐C28) ‐‐‐
Total Petroleum Hydrocarbons (C29‐C32) ‐‐‐
Total Petroleum Hydrocarbons (C33‐C36) ‐‐‐
Total Petroleum Hydrocarbons (C37‐C40) ‐‐‐
Total Petroleum Hydrocarbons (C41‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C6‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) Diesel ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) DRO ‐‐‐
Total Petroleum Hydrocarbons (>C28‐C44) ‐‐‐
Gasoline C6‐C8 (calculated) 2,900 ‐‐
Diesel C9‐C16 (calculated) 5,400 97 ‐
Oil C17‐C32 (calculated) 7,300 2,400 ‐
‐
VOCs (mg/kg)
1,1,1,2‐Tetrachloroethane ‐ 8.8 ‐
1,1,1‐Trichloroethane 1.7 7,200 ‐
1,1,2,2‐Tetrachloroethane ‐ 2.7 ‐
1,1,2‐Trichloroethane 0.04 ‐‐
1,1‐Dichloroethane 0.56 16 ‐
1,1‐Dichloroethene 0.071 350 ‐
1,1‐Dichloropropene ‐‐‐
1,2,3‐Trichlorobenzene ‐ 300 ‐
1,2,3‐Trichloropropane ‐ 0.021 ‐
1,2,3‐Trimethylbenzene ‐‐‐
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2,4‐Trimethylbenzene ‐‐‐
1,2‐Dibromo‐3‐chloropropane (DBCP) ‐ 0.057 ‐
1,2‐Dibromoethane (Ethylene Dibromide) ‐ 0.16 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,2‐Dichloroethane 0.0028 ‐‐
1,2‐Dichloropropane ‐‐‐
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) ‐‐‐‐‐‐‐‐‐‐
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5 < 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 2.9 J < 5 < 25 < 5.1 < 50 < 4.9 2.6 J < 5
22 J < 4.9 13 < 5 32 < 5.1 57 < 4.9 12 < 5
29 < 4.9 19 < 5 35 < 5.1 66 < 4.9 16 < 5
28 < 4.9 4.3 J < 5 29 < 5.1 42 J < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 29 J < 4.9 < 4.9 < 5
79 < 5 39 < 5 97 < 5 190 < 5 31 < 5
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
< 25 < 4.9 < 4.9 < 5 < 25 < 5.1 < 50 < 4.9 < 4.9 < 5
22 < 4.9 15.9 < 5 32 < 5.1 57 < 4.9 14.6 < 5
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0098 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0098 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
1,3,5‐Trimethylbenzene ‐‐‐
1,3‐Dichlorobenzene ‐‐‐
1,3‐Dichloropropane ‐ 2,200 ‐
1,4‐Dichloro‐2‐butene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
2,2‐Dichloropropane ‐‐‐
2‐Butanone (Methyl Ethyl Ketone) ‐‐‐
2‐Chlorotoluene ‐ 2,500 ‐
2‐Hexanone ‐‐‐2‐Phenylbutane (sec‐Butylbenzene) ‐ 12,000 ‐ 4‐Chlorotoluene ‐ 2,300 ‐
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) ‐‐‐
Acetone ‐‐‐Acrylonitrile ‐‐‐Allyl chloride ‐‐‐
Benzene 0.019 1.4 ‐Bromobenzene ‐‐‐Bromodichloromethane ‐ 1.3 ‐ Bromoform ‐ 86 ‐
Bromomethane (Methyl Bromide) ‐‐‐
Carbon disulfide ‐‐‐
Carbon tetrachloride ‐ 2.9 ‐
Chlorobenzene 2 ‐‐Chlorobromomethane ‐ 4.1 ‐
Chloroethane ‐‐‐Chloroform (Trichloromethane) ‐‐‐
Chloromethane (Methyl Chloride) ‐‐‐
cis‐1,2‐Dichloroethene 4.9 84 ‐
cis‐1,3‐Dichloropropene ‐‐‐
cis‐1,4‐Dichloro‐2‐butene ‐‐‐Cymene (p‐Isopropyltoluene) ‐ 1,600 ‐ Dibromochloromethane ‐‐‐Dibromomethane ‐‐‐Dichlorodifluoromethane (CFC‐12) ‐‐‐ Diisopropyl ether (DIPE) ‐‐‐
Ethylbenzene 7.7 ‐‐Hexachlorobutadiene ‐ 5.3 ‐
Isopropylbenzene (Cumene) ‐‐‐
m,p‐Xylenes 6 ‐‐
Methyl Tert Butyl Ether ‐‐‐
Methylene chloride 0.019 26 ‐
Naphthalene ‐ 6.5 ‐
n‐Butylbenzene ‐‐‐
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.13 < 0.12 < 0.13 < 0.13 < 0.12 < 0.12 < 0.13 < 0.13 < 0.13 < 0.13 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.026 < 0.025 < 0.026 < 0.025 < 0.025 < 0.025 < 0.026 < 0.026 < 0.026 < 0.025 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.026 < 0.025 < 0.026 < 0.025 < 0.025 < 0.025 < 0.026 < 0.026 < 0.026 < 0.025 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 0.0023 J < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
n‐Propylbenzene ‐‐‐
o‐Xylene 6 ‐‐
PHC as Gasoline 5,400 97 ‐
Styrene ‐ 32,000 ‐
Tert‐Amyl Methyl Ether (TAME) ‐‐‐
Tert‐Butyl Alcohol (tert‐Butanol) ‐‐‐
Tert‐Butyl Ethyl Ether (ETBE) ‐‐‐tert‐Butylbenzene ‐‐‐
Tetrachloroethene 2.1 2.7 ‐
Toluene 0.44 5,300 ‐trans‐1,2‐Dichloroethene 0.17 600 ‐ trans‐1,3‐Dichloropropene ‐‐‐
Trichloroethene 27 63 2,040
Trichlorofluoromethane (CFC‐11) ‐ 5,400 ‐
Trifluorotrichloroethane (Freon 113) 6.4 ‐‐
Vinyl acetate ‐‐‐
Vinyl chloride 13 0.15 ‐
Xylene (total) 6 ‐‐
Notes and Abbreviations:
BOLD = concentration detected at or above
reported detection limit.
No COPC in soil exceeded its Total Threshold Limit Concentration (TTLC). < = analyte not detected above the indicated
reporting limit.B = compound detected in the associated blank J = estimated concentration.‐ = not analyzed or not applicable. mg/kg = milligrams per kilogram.
bgs = below ground surface.
GPL: Groundwater Protection Level (Haley & Aldrich 2014a, 2014b) TTLC: Total Threshold Limit Concentration, CCR Title 22 Section 66261.24 1 Cancer Endpoint. If there is no Cancer Endpoint, the Noncancer Endpoint is noted.2 Site background3 U.S. EPA Region 9 Remediation Screening Level DTSC‐SL: Commercial/Industrial Department of Toxic Substances Control‐Screening Level, HHRA Note 3, June 2020.
BB‐16 BB‐16 BB‐17 BB‐17 BB‐18 BB‐18 BB‐19 BB‐19 BB‐20 BB‐20 BB‐16‐01 BB‐16‐03 BB‐17‐01 BB‐17‐04 BB‐18‐01 BB‐18‐04 BB‐19‐01 BB‐19‐03 BB‐20‐01 BB‐20‐03 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 3.5 ‐ 4 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.051 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.052 < 0.052 < 0.051 < 0.0051 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0052 < 0.0052 < 0.0051 ‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
Metals (mg/kg) GPL DTSC TTLC
Antimony 7.84 ‐ 500
Arsenic 24.3 0.36/82 500
Barium 43000 ‐ 10,000
Beryllium ‐ 6,900 75
Cadmium 970 4,000 100Chromium 660 ‐ 2,500
Chromium VI (Hexavalent) 30 6.2 500
Cobalt ‐‐ 8,000
Copper 5600 ‐ 2,500
Lead 232 320 1,000Mercury 2.1 4.4 20Molybdenum ‐‐ 3,500 Nickel 3400 64,000 2,000Selenium ‐‐ 100Silver ‐‐ 500Thallium ‐‐ 700Vanadium ‐‐ 2,400 Zinc ‐‐ 5,000
‐
PCBs (mg/kg)
Aroclor‐1016 (PCB‐1016) ‐ 17 ‐
Aroclor‐1221 (PCB‐1221) ‐ 0.53 ‐
Aroclor‐1232 (PCB‐1232) ‐ 0.49 ‐
Aroclor‐1242 (PCB‐1242) ‐ 0.58 ‐
Aroclor‐1248 (PCB‐1248) ‐ 0.58 ‐
Aroclor‐1254 (PCB‐1254) ‐ 0.59 ‐
Aroclor‐1260 (PCB‐1260) ‐ 0.6 ‐
Aroclor‐1262 (PCB‐1262) ‐‐‐
Aroclor‐1268 (PCB‐1268) ‐‐‐
Total PCBs 130 0.58 50
‐
PEST (mg/kg)
4,4'‐DDD ‐ 6.2 1.0
4,4'‐DDE ‐ 9.3 1.04,4'‐DDT ‐ 7.1 1.0
Aldrin ‐ 0.18 1.4
alpha‐BHC ‐ 0.24 ‐
beta‐BHC ‐ 0.82 ‐
Chlordane ‐ 6.1 2.5
delta‐BHC ‐‐‐
Dieldrin ‐ 0.093 8.0
Endosulfan I ‐ 6,000 ‐
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) < 0.773 < 0.735 < 0.739 < 0.721 < 0.721 < 0.789 < 0.758 < 0.777 < 3.2 < 3.1
4.41 2.06 3.04 2.17 2.27 1.39 4.17 1.57 2.6 1.9
82.5 84.9 57.8 77.9 73.1 74.7 72.4 78.3 68 64
1.38 0.254 0.271 0.333 0.273 0.381 0.226 J 0.286 < 0.54 < 0.51
1.35 0.498 1.18 0.45 J 0.866 0.353 J 0.473 J 0.548 < 0.54 < 0.51
12.3 13.1 14.1 17.2 15.1 19 9.67 15.3 16 17
‐‐‐‐‐‐‐‐ ‐‐
6.19 7.62 6.11 9.93 8.36 11.2 5.57 9.51 6.6 7.7
11.2 16.2 8.59 20.2 28.8 9.91 12.4 28.4 4.8 17
9.18 22.1 7.31 13.6 42.6 4.48 17.3 19 2.9 15
0.0177 J 0.0192 J < 0.082 0.0184 J 0.106 0.007 J 0.019 J 0.0258 J < 0.14 < 0.13
1.04 0.152 J < 0.246 0.243 < 0.24 < 0.263 0.429 0.229 J < 1.1 < 1
6.68 6.41 6.44 7.59 7.57 8.45 5.04 9.37 6.1 8.6
0.857 0.531 J < 0.739 0.421 J < 0.721 < 0.789 < 0.758 < 0.777 < 3.2 < 3.1 < 0.258 < 0.245 < 0.246 < 0.24 < 0.24 < 0.263 < 0.253 < 0.259 < 0.54 0.52
0.929 < 0.735 < 0.739 0.156 J < 0.721 < 0.789 < 0.758 < 0.777 < 3.2 < 3.1
28.9 39.6 34.7 51.5 42.9 63.6 29 47.6 59 47
40.6 65.7 42.9 40.3 78.3 31.6 59.7 59 38 46
< 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05
0.033 J < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05
0.033 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 ‐ ‐ ‐ 0.0099 ‐ < 0.005 ‐ ‐‐
0.0074 ‐‐‐ 1 ‐ 0.015 ‐ ‐‐
< 0.005 ‐ ‐ ‐ 0.23 ‐ 0.016 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.01 ‐ ‐ ‐ < 0.0099 ‐ < 0.01 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
0.03 J ‐‐‐ < 0.05 ‐ < 0.05 ‐ ‐‐
< 0.01 ‐ ‐ ‐ < 0.0099 ‐ < 0.01 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PEST (mg/kg) ‐
Endosulfan II ‐ 6,000 ‐
Endosulfan sulfate ‐ 11,000 ‐
Endrin ‐ 160 0.2
Endrin aldehyde ‐‐‐
Endrin ketone ‐‐‐
gamma‐BHC (Lindane) ‐ 2 4.0
Heptachlor ‐ 0.63 4.7
Heptachlor epoxide ‐ 0.33 ‐
Methoxychlor ‐ 2600 100
Toxaphene ‐ 1.2 5
‐
SVOCs (mg/kg)
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,3‐Dichlorobenzene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
1‐Methylnaphthalene ‐ 30 ‐
2,2'‐oxybis(2‐Chloropropane) ‐‐‐
2,4,5‐Trichlorophenol ‐ 53,000 ‐
2,4,6‐Trichlorophenol ‐ 21 ‐
2,4‐Dichlorophenol ‐ 1,600 ‐
2,4‐Dimethylphenol ‐ 11,000 ‐
2,4‐Dinitrophenol ‐ 1,100 ‐
2,4‐Dinitrotoluene ‐‐‐
2,6‐Dichlorophenol ‐ 4.7 ‐
2,6‐Dinitrotoluene ‐ 0.99 ‐
2‐Chloronaphthalene ‐ 27,000 ‐
2‐Chlorophenol ‐ 3,900 ‐
2‐Methylnaphthalene ‐ 1,300 ‐
2‐Methylphenol (o‐Cresol) ‐ 26,000 ‐
2‐Nitroaniline ‐ 5,200 ‐
2‐Nitrophenol ‐‐‐3,3'‐Dichlorobenzidine ‐ 0.93 ‐
3‐Nitroaniline ‐‐‐
4,6‐Dinitro‐2‐methylphenol ‐ 42 ‐
4‐Bromophenyl phenyl ether ‐‐‐
4‐Chloro‐3‐methylphenol ‐ 53,000 ‐
4‐Chloroaniline ‐ 7.4 ‐
4‐Chlorophenyl phenyl ether ‐‐‐
4‐Nitroaniline ‐ 74 ‐
4‐Nitrophenol ‐‐‐
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) < 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.01 ‐ ‐ ‐ < 0.0099 ‐ < 0.01 ‐ ‐‐
< 0.005 ‐ ‐ ‐ < 0.005 ‐ < 0.005 ‐ ‐‐
< 0.1 ‐ ‐ ‐ < 0.099 ‐ < 0.1 ‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
SVOCs (mg/kg) ‐
Acenaphthene ‐ 23,000 ‐
Acenaphthylene ‐‐‐Aniline ‐ 260 ‐
Anthracene ‐ 130,000 ‐
Azobenzene ‐‐‐Benzidine ‐ 0.003 ‐
Benzo(a)anthracene ‐ 12 ‐
Benzo(a)pyrene 14 1.3 ‐Benzo(b)fluoranthene ‐ 13 ‐
Benzo(g,h,i)perylene ‐‐‐Benzo(k)fluoranthene ‐ 210,000 ‐ Benzoic acid ‐ 2,100,000 ‐
Benzyl Alcohol ‐ 53,000 ‐
bis(2‐Chloroethoxy)methane ‐ 1,600 ‐
bis(2‐Chloroethyl)ether ‐ 0.47 ‐
bis(2‐Ethylhexyl)phthalate 57 110 ‐
Butyl benzylphthalate ‐ 780 ‐
Chrysene ‐ 1,300 ‐
Dibenz(a,h)anthracene ‐ 0.31 ‐
Dibenzofuran ‐ 650 ‐
Diethyl phthalate ‐ 420,000 ‐Dimethyl phthalate ‐‐‐
Di‐n‐butylphthalate ‐ 53,000 ‐
Di‐n‐octyl phthalate ‐ 5,300 ‐Fluoranthene ‐ 18,000 ‐
Fluorene ‐ 17,000 ‐
Hexachlorobenzene ‐ 0.86 ‐
Hexachlorobutadiene ‐ 5.3 ‐
Hexachlorocyclopentadiene ‐‐‐Hexachloroethane ‐‐‐Indeno(1,2,3‐cd)pyrene ‐ 13 ‐ Isophorone ‐ 1,600 ‐
m,p‐Cresols ‐‐‐
Naphthalene ‐ 6.5 ‐
Nitrobenzene ‐‐‐N‐Nitrosodimethylamine ‐ 0.53 ‐
N‐Nitrosodi‐n‐propylamine ‐ 0.21 ‐
N‐Nitrosodiphenylamine ‐ 300 ‐
Pentachlorophenol 0.0717 2 ‐Phenanthrene ‐‐‐Phenol ‐ 160,000 ‐ Pyrene ‐ 13,000 ‐
Pyridine ‐ 530 ‐
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) ‐‐ 0.0061 J ‐ < 0.015 ‐ ‐ ‐ ‐‐
‐‐ < 0.03 ‐ 0.011 J ‐‐‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.01 ‐ < 0.0099 ‐ ‐ ‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ 0.0031 J ‐ 0.0072 J ‐‐‐ ‐‐
‐‐ 0.0029 J ‐ 0.018 ‐‐‐ ‐‐
‐‐ 0.0054 J ‐ 0.0085 J ‐‐‐ ‐‐
‐‐ 0.0048 J ‐ 0.0035 J ‐‐‐ ‐‐
‐‐ < 0.01 ‐ 0.0085 J ‐‐‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.01 ‐ 0.0067 J ‐‐‐ ‐‐ ‐‐ < 0.01 ‐ < 0.0099 ‐ ‐ ‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.01 ‐ 0.021 ‐‐‐ ‐‐ ‐‐ 0.0038 J ‐ < 0.0099 ‐ ‐ ‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.01 ‐ 0.0046 J ‐‐‐ ‐‐ ‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.015 ‐ < 0.015 ‐ ‐ ‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐ < 0.01 ‐ 0.0062 J ‐‐‐ ‐‐ ‐‐‐‐‐‐‐‐ ‐‐‐‐ 0.0072 J ‐ 0.031 ‐‐‐ ‐‐
‐‐‐‐‐‐‐‐ ‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
TPH (mg/kg)
PHC as Gasoline 5,400 97 ‐
Total Petroleum Hydrocarbons (C6) ‐‐‐
Total Petroleum Hydrocarbons (C7) ‐‐‐
Total Petroleum Hydrocarbons (C8) ‐‐‐
Total Petroleum Hydrocarbons (C9‐C10) ‐‐‐
Total Petroleum Hydrocarbons (C11‐C12) ‐‐‐
Total Petroleum Hydrocarbons (C13‐C14) ‐‐‐
Total Petroleum Hydrocarbons (C15‐C16) ‐‐‐
Total Petroleum Hydrocarbons (C17‐C18) ‐‐‐
Total Petroleum Hydrocarbons (C19‐C20) ‐‐‐
Total Petroleum Hydrocarbons (C21‐C22) ‐‐‐
Total Petroleum Hydrocarbons (C23‐C24) ‐‐‐
Total Petroleum Hydrocarbons (C25‐C28) ‐‐‐
Total Petroleum Hydrocarbons (C29‐C32) ‐‐‐
Total Petroleum Hydrocarbons (C33‐C36) ‐‐‐
Total Petroleum Hydrocarbons (C37‐C40) ‐‐‐
Total Petroleum Hydrocarbons (C41‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C6‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) Diesel ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) DRO ‐‐‐
Total Petroleum Hydrocarbons (>C28‐C44) ‐‐‐
Gasoline C6‐C8 (calculated) 2,900 ‐‐
Diesel C9‐C16 (calculated) 5,400 97 ‐
Oil C17‐C32 (calculated) 7,300 2,400 ‐
‐
VOCs (mg/kg)
1,1,1,2‐Tetrachloroethane ‐ 8.8 ‐
1,1,1‐Trichloroethane 1.7 7,200 ‐
1,1,2,2‐Tetrachloroethane ‐ 2.7 ‐
1,1,2‐Trichloroethane 0.04 ‐‐
1,1‐Dichloroethane 0.56 16 ‐
1,1‐Dichloroethene 0.071 350 ‐
1,1‐Dichloropropene ‐‐‐
1,2,3‐Trichlorobenzene ‐ 300 ‐
1,2,3‐Trichloropropane ‐ 0.021 ‐
1,2,3‐Trimethylbenzene ‐‐‐
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2,4‐Trimethylbenzene ‐‐‐
1,2‐Dibromo‐3‐chloropropane (DBCP) ‐ 0.057 ‐
1,2‐Dibromoethane (Ethylene Dibromide) ‐ 0.16 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,2‐Dichloroethane 0.0028 ‐‐
1,2‐Dichloropropane ‐‐‐
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) ‐‐‐‐‐‐‐‐ < 3.8 < 2.8
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 1.3 J ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 2.6 J ‐‐
< 5 37 < 5 < 4.9 < 5 < 5 < 25 4 J ‐‐
2.2 J 1.9 J < 5 < 4.9 < 5 < 5 < 25 8.9 ‐‐
17 5 4.3 J < 4.9 < 5 < 5 62 13 ‐‐
18 2.4 J 7.1 < 4.9 < 5 < 5 45 9.2 ‐‐
9.7 < 4.9 < 5 < 4.9 < 5 < 5 48 5 J ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
47 46 11 < 5 < 5 < 5 150 44 ‐‐
‐‐‐‐‐‐‐‐ < 10 < 10
‐‐‐‐‐‐‐‐ < 10 < 10
‐‐‐‐‐‐‐‐ < 20 < 20
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
< 5 < 4.9 < 5 < 4.9 < 5 < 5 < 25 < 5 ‐‐
19.2 43.9 4.3 < 4.9 < 5 < 5 62 29.8 ‐‐
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.01 < 0.0099 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0098 < 0.01 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ ‐‐
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.01 < 0.0099 < 0.01 < 0.01 < 0.01 < 0.01 < 0.0098 < 0.01 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
1,3,5‐Trimethylbenzene ‐‐‐
1,3‐Dichlorobenzene ‐‐‐
1,3‐Dichloropropane ‐ 2,200 ‐
1,4‐Dichloro‐2‐butene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
2,2‐Dichloropropane ‐‐‐
2‐Butanone (Methyl Ethyl Ketone) ‐‐‐
2‐Chlorotoluene ‐ 2,500 ‐
2‐Hexanone ‐‐‐2‐Phenylbutane (sec‐Butylbenzene) ‐ 12,000 ‐ 4‐Chlorotoluene ‐ 2,300 ‐
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) ‐‐‐
Acetone ‐‐‐Acrylonitrile ‐‐‐Allyl chloride ‐‐‐
Benzene 0.019 1.4 ‐Bromobenzene ‐‐‐Bromodichloromethane ‐ 1.3 ‐ Bromoform ‐ 86 ‐
Bromomethane (Methyl Bromide) ‐‐‐
Carbon disulfide ‐‐‐
Carbon tetrachloride ‐ 2.9 ‐
Chlorobenzene 2 ‐‐Chlorobromomethane ‐ 4.1 ‐
Chloroethane ‐‐‐Chloroform (Trichloromethane) ‐‐‐
Chloromethane (Methyl Chloride) ‐‐‐
cis‐1,2‐Dichloroethene 4.9 84 ‐
cis‐1,3‐Dichloropropene ‐‐‐
cis‐1,4‐Dichloro‐2‐butene ‐‐‐Cymene (p‐Isopropyltoluene) ‐ 1,600 ‐ Dibromochloromethane ‐‐‐Dibromomethane ‐‐‐Dichlorodifluoromethane (CFC‐12) ‐‐‐ Diisopropyl ether (DIPE) ‐‐‐
Ethylbenzene 7.7 ‐‐Hexachlorobutadiene ‐ 5.3 ‐
Isopropylbenzene (Cumene) ‐‐‐
m,p‐Xylenes 6 ‐‐
Methyl Tert Butyl Ether ‐‐‐
Methylene chloride 0.019 26 ‐
Naphthalene ‐ 6.5 ‐
n‐Butylbenzene ‐‐‐
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045
0.022 J < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.094 < 0.091 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 ‐‐ < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.0047 < 0.0045
0.076 J < 0.12 < 0.13 < 0.13 < 0.13 < 0.13 < 0.12 < 0.13 < 0.094 < 0.091 ‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.025 < 0.025 < 0.025 < 0.026 < 0.025 < 0.025 < 0.025 < 0.026 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 ‐‐ < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.025 < 0.025 < 0.025 < 0.026 < 0.025 < 0.025 < 0.025 < 0.026 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
0.029 0.00073 J < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0094 < 0.0091 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
n‐Propylbenzene ‐‐‐
o‐Xylene 6 ‐‐
PHC as Gasoline 5,400 97 ‐
Styrene ‐ 32,000 ‐
Tert‐Amyl Methyl Ether (TAME) ‐‐‐
Tert‐Butyl Alcohol (tert‐Butanol) ‐‐‐
Tert‐Butyl Ethyl Ether (ETBE) ‐‐‐tert‐Butylbenzene ‐‐‐
Tetrachloroethene 2.1 2.7 ‐
Toluene 0.44 5,300 ‐trans‐1,2‐Dichloroethene 0.17 600 ‐ trans‐1,3‐Dichloropropene ‐‐‐
Trichloroethene 27 63 2,040
Trichlorofluoromethane (CFC‐11) ‐ 5,400 ‐
Trifluorotrichloroethane (Freon 113) 6.4 ‐‐
Vinyl acetate ‐‐‐
Vinyl chloride 13 0.15 ‐
Xylene (total) 6 ‐‐
Notes and Abbreviations:
BOLD = concentration detected at or above
reported detection limit.
No COPC in soil exceeded its Total Threshold Limit Concentration (TTLC). < = analyte not detected above the indicated
reporting limit.B = compound detected in the associated blank J = estimated concentration.‐ = not analyzed or not applicable. mg/kg = milligrams per kilogram.
bgs = below ground surface.
GPL: Groundwater Protection Level (Haley & Aldrich 2014a, 2014b) TTLC: Total Threshold Limit Concentration, CCR Title 22 Section 66261.24 1 Cancer Endpoint. If there is no Cancer Endpoint, the Noncancer Endpoint is noted.2 Site background3 U.S. EPA Region 9 Remediation Screening Level DTSC‐SL: Commercial/Industrial Department of Toxic Substances Control‐Screening Level, HHRA Note 3, June 2020.
BB‐21 BB‐21 BB‐22 BB‐22 BB‐23 BB‐23 BB‐24 BB‐24 PW‐01A PW‐01B BB‐21‐01 BB‐21‐03 BB‐22‐01 BB‐22‐03 BB‐23‐01 BB‐23‐03 BB‐24‐01 BB‐24‐03 PW01A‐1.5 PW01B‐1.5
6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 6/28/2016 07/29/2020 07/29/2020
0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 0.5 ‐ 1 (ft) 2.5 ‐ 3 (ft) 1.5 (ft) 1.5 (ft) < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.094 < 0.091
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
‐‐‐‐‐‐‐‐ < 0.0094 < 0.0091
‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
< 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 < 0.0047 < 0.0045 < 0.05 < 0.049 < 0.05 < 0.051 < 0.05 < 0.05 < 0.049 < 0.052 ‐‐ < 0.005 < 0.0049 < 0.005 < 0.0051 < 0.005 < 0.005 < 0.0049 < 0.0052 < 0.0047 < 0.0045 ‐‐‐‐‐‐‐‐ < 0.0047 < 0.0045
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
Metals (mg/kg) GPL DTSC TTLC
Antimony 7.84 ‐ 500
Arsenic 24.3 0.36/82 500
Barium 43000 ‐ 10,000
Beryllium ‐ 6,900 75
Cadmium 970 4,000 100Chromium 660 ‐ 2,500
Chromium VI (Hexavalent) 30 6.2 500
Cobalt ‐‐ 8,000
Copper 5600 ‐ 2,500
Lead 232 320 1,000Mercury 2.1 4.4 20Molybdenum ‐‐ 3,500 Nickel 3400 64,000 2,000Selenium ‐‐ 100Silver ‐‐ 500Thallium ‐‐ 700Vanadium ‐‐ 2,400 Zinc ‐‐ 5,000
‐
PCBs (mg/kg)
Aroclor‐1016 (PCB‐1016) ‐ 17 ‐
Aroclor‐1221 (PCB‐1221) ‐ 0.53 ‐
Aroclor‐1232 (PCB‐1232) ‐ 0.49 ‐
Aroclor‐1242 (PCB‐1242) ‐ 0.58 ‐
Aroclor‐1248 (PCB‐1248) ‐ 0.58 ‐
Aroclor‐1254 (PCB‐1254) ‐ 0.59 ‐
Aroclor‐1260 (PCB‐1260) ‐ 0.6 ‐
Aroclor‐1262 (PCB‐1262) ‐‐‐
Aroclor‐1268 (PCB‐1268) ‐‐‐
Total PCBs 130 0.58 50
‐
PEST (mg/kg)
4,4'‐DDD ‐ 6.2 1.0
4,4'‐DDE ‐ 9.3 1.04,4'‐DDT ‐ 7.1 1.0
Aldrin ‐ 0.18 1.4
alpha‐BHC ‐ 0.24 ‐
beta‐BHC ‐ 0.82 ‐
Chlordane ‐ 6.1 2.5
delta‐BHC ‐‐‐
Dieldrin ‐ 0.093 8.0
Endosulfan I ‐ 6,000 ‐
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) < 3.2 < 3.3 < 3< 3.2 < 2.8 < 3.2 < 2.7 < 0.75 < 0.75 < 0.75
2.1 < 1.1 2.2 5.7 5 4.5 2.8 2.74 7.81 8.71
49 89 59 51 31 54 54 74.3 100 91.4
< 0.53 < 0.55 < 0.5 < 0.53 < 0.47 < 0.54 < 0.45 0.26 0.39 0.287 < 0.53 < 0.55 < 0.5 0.96 < 0.47 < 0.54 < 0.45 0.927 5.32 2.42 19 20 21 13 8.5 14 15 15.1 23.9 20.4
‐‐‐ ‐‐ 0.095 J
6.8 7.8 11 5.7 4.5 5.6 5.6 7.46 12.7 9.69
11 12 13 41 14 12 5 15 65.4 46.9
4.8 2.1 4.6 26 11 10 1.6 12.7 85.2 112
< 0.14 < 0.14 < 0.14 < 0.13 < 0.13 < 0.13 < 0.14 ‐‐ < 0.0835 < 1.1 < 1.1 < 0.99 < 1.1 < 0.94 < 1.1 < 0.91 0.843 7.96 0.642
8.4 8.7 9.8 8.7 4.6 7 5 6.3 14 13.6
< 3.2 < 3.3 < 3< 3.2 < 2.8 < 3.2 < 2.7 < 0.75 < 0.75 < 0.75 < 0.53 0.55 0.81 < 0.53 < 0.47 < 0.54 < 0.45 < 0.25 < 0.25 < 0.25 < 3.2 < 3.3 < 3< 3.2 < 2.8 < 3.2 < 2.7 < 0.75 < 0.75 < 0.75 50 63 59 33 19 37 51 44.3 52.1 41.9
32 38 33 51 19 45 34 45 153 243
< 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 0.77 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 0.18 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.049 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐‐‐
< 0.05 < 0.049 < 0.05 < 0.05 0.18 < 0.05 < 0.05 < 0.05 0.77 < 0.05 ‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PEST (mg/kg) ‐
Endosulfan II ‐ 6,000 ‐
Endosulfan sulfate ‐ 11,000 ‐
Endrin ‐ 160 0.2
Endrin aldehyde ‐‐‐
Endrin ketone ‐‐‐
gamma‐BHC (Lindane) ‐ 2 4.0
Heptachlor ‐ 0.63 4.7
Heptachlor epoxide ‐ 0.33 ‐
Methoxychlor ‐ 2600 100
Toxaphene ‐ 1.2 5
‐
SVOCs (mg/kg)
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,3‐Dichlorobenzene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
1‐Methylnaphthalene ‐ 30 ‐
2,2'‐oxybis(2‐Chloropropane) ‐‐‐
2,4,5‐Trichlorophenol ‐ 53,000 ‐
2,4,6‐Trichlorophenol ‐ 21 ‐
2,4‐Dichlorophenol ‐ 1,600 ‐
2,4‐Dimethylphenol ‐ 11,000 ‐
2,4‐Dinitrophenol ‐ 1,100 ‐
2,4‐Dinitrotoluene ‐‐‐
2,6‐Dichlorophenol ‐ 4.7 ‐
2,6‐Dinitrotoluene ‐ 0.99 ‐
2‐Chloronaphthalene ‐ 27,000 ‐
2‐Chlorophenol ‐ 3,900 ‐
2‐Methylnaphthalene ‐ 1,300 ‐
2‐Methylphenol (o‐Cresol) ‐ 26,000 ‐
2‐Nitroaniline ‐ 5,200 ‐
2‐Nitrophenol ‐‐‐3,3'‐Dichlorobenzidine ‐ 0.93 ‐
3‐Nitroaniline ‐‐‐
4,6‐Dinitro‐2‐methylphenol ‐ 42 ‐
4‐Bromophenyl phenyl ether ‐‐‐
4‐Chloro‐3‐methylphenol ‐ 53,000 ‐
4‐Chloroaniline ‐ 7.4 ‐
4‐Chlorophenyl phenyl ether ‐‐‐
4‐Nitroaniline ‐ 74 ‐
4‐Nitrophenol ‐‐‐
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) ‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
SVOCs (mg/kg) ‐
Acenaphthene ‐ 23,000 ‐
Acenaphthylene ‐‐‐Aniline ‐ 260 ‐
Anthracene ‐ 130,000 ‐
Azobenzene ‐‐‐Benzidine ‐ 0.003 ‐
Benzo(a)anthracene ‐ 12 ‐
Benzo(a)pyrene 14 1.3 ‐Benzo(b)fluoranthene ‐ 13 ‐
Benzo(g,h,i)perylene ‐‐‐Benzo(k)fluoranthene ‐ 210,000 ‐ Benzoic acid ‐ 2,100,000 ‐
Benzyl Alcohol ‐ 53,000 ‐
bis(2‐Chloroethoxy)methane ‐ 1,600 ‐
bis(2‐Chloroethyl)ether ‐ 0.47 ‐
bis(2‐Ethylhexyl)phthalate 57 110 ‐
Butyl benzylphthalate ‐ 780 ‐
Chrysene ‐ 1,300 ‐
Dibenz(a,h)anthracene ‐ 0.31 ‐
Dibenzofuran ‐ 650 ‐
Diethyl phthalate ‐ 420,000 ‐Dimethyl phthalate ‐‐‐
Di‐n‐butylphthalate ‐ 53,000 ‐
Di‐n‐octyl phthalate ‐ 5,300 ‐Fluoranthene ‐ 18,000 ‐
Fluorene ‐ 17,000 ‐
Hexachlorobenzene ‐ 0.86 ‐
Hexachlorobutadiene ‐ 5.3 ‐
Hexachlorocyclopentadiene ‐‐‐Hexachloroethane ‐‐‐Indeno(1,2,3‐cd)pyrene ‐ 13 ‐ Isophorone ‐ 1,600 ‐
m,p‐Cresols ‐‐‐
Naphthalene ‐ 6.5 ‐
Nitrobenzene ‐‐‐N‐Nitrosodimethylamine ‐ 0.53 ‐
N‐Nitrosodi‐n‐propylamine ‐ 0.21 ‐
N‐Nitrosodiphenylamine ‐ 300 ‐
Pentachlorophenol 0.0717 2 ‐Phenanthrene ‐‐‐Phenol ‐ 160,000 ‐ Pyrene ‐ 13,000 ‐
Pyridine ‐ 530 ‐
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) ‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐‐‐‐‐‐‐‐ ‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
TPH (mg/kg)
PHC as Gasoline 5,400 97 ‐
Total Petroleum Hydrocarbons (C6) ‐‐‐
Total Petroleum Hydrocarbons (C7) ‐‐‐
Total Petroleum Hydrocarbons (C8) ‐‐‐
Total Petroleum Hydrocarbons (C9‐C10) ‐‐‐
Total Petroleum Hydrocarbons (C11‐C12) ‐‐‐
Total Petroleum Hydrocarbons (C13‐C14) ‐‐‐
Total Petroleum Hydrocarbons (C15‐C16) ‐‐‐
Total Petroleum Hydrocarbons (C17‐C18) ‐‐‐
Total Petroleum Hydrocarbons (C19‐C20) ‐‐‐
Total Petroleum Hydrocarbons (C21‐C22) ‐‐‐
Total Petroleum Hydrocarbons (C23‐C24) ‐‐‐
Total Petroleum Hydrocarbons (C25‐C28) ‐‐‐
Total Petroleum Hydrocarbons (C29‐C32) ‐‐‐
Total Petroleum Hydrocarbons (C33‐C36) ‐‐‐
Total Petroleum Hydrocarbons (C37‐C40) ‐‐‐
Total Petroleum Hydrocarbons (C41‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C6‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) Diesel ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) DRO ‐‐‐
Total Petroleum Hydrocarbons (>C28‐C44) ‐‐‐
Gasoline C6‐C8 (calculated) 2,900 ‐‐
Diesel C9‐C16 (calculated) 5,400 97 ‐
Oil C17‐C32 (calculated) 7,300 2,400 ‐
‐
VOCs (mg/kg)
1,1,1,2‐Tetrachloroethane ‐ 8.8 ‐
1,1,1‐Trichloroethane 1.7 7,200 ‐
1,1,2,2‐Tetrachloroethane ‐ 2.7 ‐
1,1,2‐Trichloroethane 0.04 ‐‐
1,1‐Dichloroethane 0.56 16 ‐
1,1‐Dichloroethene 0.071 350 ‐
1,1‐Dichloropropene ‐‐‐
1,2,3‐Trichlorobenzene ‐ 300 ‐
1,2,3‐Trichloropropane ‐ 0.021 ‐
1,2,3‐Trimethylbenzene ‐‐‐
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2,4‐Trimethylbenzene ‐‐‐
1,2‐Dibromo‐3‐chloropropane (DBCP) ‐ 0.057 ‐
1,2‐Dibromoethane (Ethylene Dibromide) ‐ 0.16 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,2‐Dichloroethane 0.0028 ‐‐
1,2‐Dichloropropane ‐‐‐
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) < 2.2 ‐ < 2.8 < 3.3 < 3.1 < 2.9 ‐ ‐‐‐
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 26
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 26
‐‐‐‐‐‐‐ 5.6 5.6 42
‐‐‐‐‐‐‐ < 5 < 5 32
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ 13 13 < 25
‐‐‐‐‐‐‐ 38 38 170
< 10 ‐ < 10 ‐‐‐‐‐‐‐
< 10 ‐ < 10 610 53 < 100 ‐‐‐‐
< 20 ‐ < 20 1200 240 < 200 ‐ ‐‐‐
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ < 5 < 5 < 25
‐‐‐‐‐‐‐ 5.6 5.6 94
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.01 < 0.01 < 0.01 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐ ‐‐‐
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.01 < 0.01 < 0.01 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
1,3,5‐Trimethylbenzene ‐‐‐
1,3‐Dichlorobenzene ‐‐‐
1,3‐Dichloropropane ‐ 2,200 ‐
1,4‐Dichloro‐2‐butene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
2,2‐Dichloropropane ‐‐‐
2‐Butanone (Methyl Ethyl Ketone) ‐‐‐
2‐Chlorotoluene ‐ 2,500 ‐
2‐Hexanone ‐‐‐2‐Phenylbutane (sec‐Butylbenzene) ‐ 12,000 ‐ 4‐Chlorotoluene ‐ 2,300 ‐
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) ‐‐‐
Acetone ‐‐‐Acrylonitrile ‐‐‐Allyl chloride ‐‐‐
Benzene 0.019 1.4 ‐Bromobenzene ‐‐‐Bromodichloromethane ‐ 1.3 ‐ Bromoform ‐ 86 ‐
Bromomethane (Methyl Bromide) ‐‐‐
Carbon disulfide ‐‐‐
Carbon tetrachloride ‐ 2.9 ‐
Chlorobenzene 2 ‐‐Chlorobromomethane ‐ 4.1 ‐
Chloroethane ‐‐‐Chloroform (Trichloromethane) ‐‐‐
Chloromethane (Methyl Chloride) ‐‐‐
cis‐1,2‐Dichloroethene 4.9 84 ‐
cis‐1,3‐Dichloropropene ‐‐‐
cis‐1,4‐Dichloro‐2‐butene ‐‐‐Cymene (p‐Isopropyltoluene) ‐ 1,600 ‐ Dibromochloromethane ‐‐‐Dibromomethane ‐‐‐Dichlorodifluoromethane (CFC‐12) ‐‐‐ Diisopropyl ether (DIPE) ‐‐‐
Ethylbenzene 7.7 ‐‐Hexachlorobutadiene ‐ 5.3 ‐
Isopropylbenzene (Cumene) ‐‐‐
m,p‐Xylenes 6 ‐‐
Methyl Tert Butyl Ether ‐‐‐
Methylene chloride 0.019 26 ‐
Naphthalene ‐ 6.5 ‐
n‐Butylbenzene ‐‐‐
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.096 < 0.13 < 0.074 < 0.11 < 0.14 < 0.085 ‐ < 0.05 < 0.05 < 0.05 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐ < 0.05 < 0.05 < 0.05
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.05 < 0.05 < 0.05 < 0.096 < 0.13 < 0.074 0.15 0.21 0.15 ‐ < 0.12 < 0.12 < 0.12 ‐‐‐‐‐‐‐ ‐‐‐
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.025 < 0.025 < 0.025 ‐‐‐‐‐‐‐ < 0.05 < 0.05 < 0.05
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.025 < 0.025 < 0.025 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0096 < 0.013 < 0.0074 < 0.011 < 0.014 < 0.0085 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.05 < 0.05 < 0.05 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.05 < 0.05 < 0.05 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
n‐Propylbenzene ‐‐‐
o‐Xylene 6 ‐‐
PHC as Gasoline 5,400 97 ‐
Styrene ‐ 32,000 ‐
Tert‐Amyl Methyl Ether (TAME) ‐‐‐
Tert‐Butyl Alcohol (tert‐Butanol) ‐‐‐
Tert‐Butyl Ethyl Ether (ETBE) ‐‐‐tert‐Butylbenzene ‐‐‐
Tetrachloroethene 2.1 2.7 ‐
Toluene 0.44 5,300 ‐trans‐1,2‐Dichloroethene 0.17 600 ‐ trans‐1,3‐Dichloropropene ‐‐‐
Trichloroethene 27 63 2,040
Trichlorofluoromethane (CFC‐11) ‐ 5,400 ‐
Trifluorotrichloroethane (Freon 113) 6.4 ‐‐
Vinyl acetate ‐‐‐
Vinyl chloride 13 0.15 ‐
Xylene (total) 6 ‐‐
Notes and Abbreviations:
BOLD = concentration detected at or above
reported detection limit.
No COPC in soil exceeded its Total Threshold Limit Concentration (TTLC). < = analyte not detected above the indicated
reporting limit.B = compound detected in the associated blank J = estimated concentration.‐ = not analyzed or not applicable. mg/kg = milligrams per kilogram.
bgs = below ground surface.
GPL: Groundwater Protection Level (Haley & Aldrich 2014a, 2014b) TTLC: Total Threshold Limit Concentration, CCR Title 22 Section 66261.24 1 Cancer Endpoint. If there is no Cancer Endpoint, the Noncancer Endpoint is noted.2 Site background3 U.S. EPA Region 9 Remediation Screening Level DTSC‐SL: Commercial/Industrial Department of Toxic Substances Control‐Screening Level, HHRA Note 3, June 2020.
PW‐02 PW‐03 PW‐06 PW‐07 PW‐11 PW‐12 PW‐15 UT‐02 UT‐02 UT‐03 PW02‐2 PW03‐5.5 PW06‐3
PW07‐1.5 PW11‐1.5 PW12‐1.5 PW15‐1 SSS00279 (UT‐02‐
05)
SSS00278 (UT‐02‐
01)
SSS00280 (UT‐03‐
01)
07/29/2020 07/29/2020 07/29/2020 7/28/2020 7/28/2020 7/28/2020 7/28/2020 4/22/2013 4/22/2013 4/22/2013 2 (ft) 5.5 (ft) 3 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 1.5 ‐ 1.5 (ft) 5 (ft) 1 (ft) 1 (ft) < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005
0.16 ‐ < 0.074 ‐‐‐‐‐‐‐
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0096 < 0.013 < 0.0074 < 0.011 < 0.014 < 0.0085 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 0.0047 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005
0.14 0.011 0.02 0.023 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.05 < 0.05 < 0.05 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.05 < 0.05 < 0.05 ‐‐‐‐‐‐‐ < 0.05 < 0.05 < 0.05
< 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ < 0.005 < 0.005 < 0.005 < 0.0048 < 0.0064 < 0.0037 < 0.0057 < 0.0071 < 0.0042 ‐ ‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
Metals (mg/kg) GPL DTSC TTLC
Antimony 7.84 ‐ 500
Arsenic 24.3 0.36/82 500
Barium 43000 ‐ 10,000
Beryllium ‐ 6,900 75
Cadmium 970 4,000 100Chromium 660 ‐ 2,500
Chromium VI (Hexavalent) 30 6.2 500
Cobalt ‐‐ 8,000
Copper 5600 ‐ 2,500
Lead 232 320 1,000Mercury 2.1 4.4 20Molybdenum ‐‐ 3,500 Nickel 3400 64,000 2,000Selenium ‐‐ 100Silver ‐‐ 500Thallium ‐‐ 700Vanadium ‐‐ 2,400 Zinc ‐‐ 5,000
‐
PCBs (mg/kg)
Aroclor‐1016 (PCB‐1016) ‐ 17 ‐
Aroclor‐1221 (PCB‐1221) ‐ 0.53 ‐
Aroclor‐1232 (PCB‐1232) ‐ 0.49 ‐
Aroclor‐1242 (PCB‐1242) ‐ 0.58 ‐
Aroclor‐1248 (PCB‐1248) ‐ 0.58 ‐
Aroclor‐1254 (PCB‐1254) ‐ 0.59 ‐
Aroclor‐1260 (PCB‐1260) ‐ 0.6 ‐
Aroclor‐1262 (PCB‐1262) ‐‐‐
Aroclor‐1268 (PCB‐1268) ‐‐‐
Total PCBs 130 0.58 50
‐
PEST (mg/kg)
4,4'‐DDD ‐ 6.2 1.0
4,4'‐DDE ‐ 9.3 1.04,4'‐DDT ‐ 7.1 1.0
Aldrin ‐ 0.18 1.4
alpha‐BHC ‐ 0.24 ‐
beta‐BHC ‐ 0.82 ‐
Chlordane ‐ 6.1 2.5
delta‐BHC ‐‐‐
Dieldrin ‐ 0.093 8.0
Endosulfan I ‐ 6,000 ‐
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 ‐
1.93 4.84 1.53 2.72 2.65 3.37 2.5 2.52 2.19 ‐
74 116 82.3 150 99.9 158 61.6 133 50.7 ‐
0.265 0.26 < 0.25 < 0.25 0.429 < 0.25 0.377 < 0.25 0.267 ‐ < 0.5 1.31 < 0.5 0.654 < 0.5 0.837 0.671 0.786 < 0.5 ‐
13 19.1 9.02 4.95 12 6.42 16 8.35 10.1 ‐
0.057 J ‐‐‐‐‐‐ 0.058 J < 0.4 ‐
7.14 6.5 8.93 6.13 7.85 6.97 9.69 4.63 6.9 ‐
9.09 45.6 5.32 7.37 6.26 6.72 10.6 13.4 4.46 ‐
3.16 112 3.5 7.65 4.64 14.3 4.11 46.1 3.75 ‐
< 0.0835 < 0.0835 < 0.0835 < 0.0835 < 0.0835 < 0.0835 < 0.0835 < 0.0835 < 0.0835 ‐ < 0.25 1.52 < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 0.403 < 0.25 ‐
5.48 20.6 5.57 1.96 6.98 3.1 7.61 5.23 5.98 ‐
< 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 ‐ < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 < 0.25 ‐ < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 < 0.75 ‐
47.1 26.4 32.8 25.4 30.9 29.5 41.8 18.4 32.6 ‐
29.7 371 19.2 81.5 27.2 89.8 35 88.2 17.4 ‐
< 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 0.23 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ ‐‐‐‐‐‐‐‐‐‐
< 0.05 0.23 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PEST (mg/kg) ‐
Endosulfan II ‐ 6,000 ‐
Endosulfan sulfate ‐ 11,000 ‐
Endrin ‐ 160 0.2
Endrin aldehyde ‐‐‐
Endrin ketone ‐‐‐
gamma‐BHC (Lindane) ‐ 2 4.0
Heptachlor ‐ 0.63 4.7
Heptachlor epoxide ‐ 0.33 ‐
Methoxychlor ‐ 2600 100
Toxaphene ‐ 1.2 5
‐
SVOCs (mg/kg)
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,3‐Dichlorobenzene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
1‐Methylnaphthalene ‐ 30 ‐
2,2'‐oxybis(2‐Chloropropane) ‐‐‐
2,4,5‐Trichlorophenol ‐ 53,000 ‐
2,4,6‐Trichlorophenol ‐ 21 ‐
2,4‐Dichlorophenol ‐ 1,600 ‐
2,4‐Dimethylphenol ‐ 11,000 ‐
2,4‐Dinitrophenol ‐ 1,100 ‐
2,4‐Dinitrotoluene ‐‐‐
2,6‐Dichlorophenol ‐ 4.7 ‐
2,6‐Dinitrotoluene ‐ 0.99 ‐
2‐Chloronaphthalene ‐ 27,000 ‐
2‐Chlorophenol ‐ 3,900 ‐
2‐Methylnaphthalene ‐ 1,300 ‐
2‐Methylphenol (o‐Cresol) ‐ 26,000 ‐
2‐Nitroaniline ‐ 5,200 ‐
2‐Nitrophenol ‐‐‐3,3'‐Dichlorobenzidine ‐ 0.93 ‐
3‐Nitroaniline ‐‐‐
4,6‐Dinitro‐2‐methylphenol ‐ 42 ‐
4‐Bromophenyl phenyl ether ‐‐‐
4‐Chloro‐3‐methylphenol ‐ 53,000 ‐
4‐Chloroaniline ‐ 7.4 ‐
4‐Chlorophenyl phenyl ether ‐‐‐
4‐Nitroaniline ‐ 74 ‐
4‐Nitrophenol ‐‐‐
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
SVOCs (mg/kg) ‐
Acenaphthene ‐ 23,000 ‐
Acenaphthylene ‐‐‐Aniline ‐ 260 ‐
Anthracene ‐ 130,000 ‐
Azobenzene ‐‐‐Benzidine ‐ 0.003 ‐
Benzo(a)anthracene ‐ 12 ‐
Benzo(a)pyrene 14 1.3 ‐Benzo(b)fluoranthene ‐ 13 ‐
Benzo(g,h,i)perylene ‐‐‐Benzo(k)fluoranthene ‐ 210,000 ‐ Benzoic acid ‐ 2,100,000 ‐
Benzyl Alcohol ‐ 53,000 ‐
bis(2‐Chloroethoxy)methane ‐ 1,600 ‐
bis(2‐Chloroethyl)ether ‐ 0.47 ‐
bis(2‐Ethylhexyl)phthalate 57 110 ‐
Butyl benzylphthalate ‐ 780 ‐
Chrysene ‐ 1,300 ‐
Dibenz(a,h)anthracene ‐ 0.31 ‐
Dibenzofuran ‐ 650 ‐
Diethyl phthalate ‐ 420,000 ‐Dimethyl phthalate ‐‐‐
Di‐n‐butylphthalate ‐ 53,000 ‐
Di‐n‐octyl phthalate ‐ 5,300 ‐Fluoranthene ‐ 18,000 ‐
Fluorene ‐ 17,000 ‐
Hexachlorobenzene ‐ 0.86 ‐
Hexachlorobutadiene ‐ 5.3 ‐
Hexachlorocyclopentadiene ‐‐‐Hexachloroethane ‐‐‐Indeno(1,2,3‐cd)pyrene ‐ 13 ‐ Isophorone ‐ 1,600 ‐
m,p‐Cresols ‐‐‐
Naphthalene ‐ 6.5 ‐
Nitrobenzene ‐‐‐N‐Nitrosodimethylamine ‐ 0.53 ‐
N‐Nitrosodi‐n‐propylamine ‐ 0.21 ‐
N‐Nitrosodiphenylamine ‐ 300 ‐
Pentachlorophenol 0.0717 2 ‐Phenanthrene ‐‐‐Phenol ‐ 160,000 ‐ Pyrene ‐ 13,000 ‐
Pyridine ‐ 530 ‐
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) ‐ 0.38 < 0.015 < 0.015 < 0.015 < 0.015 0.029 0.039 < 0.015 ‐ ‐ 3.5 < 0.03 < 0.03 < 0.03 0.085 < 0.03 2 < 0.03 ‐
‐‐‐‐‐‐‐‐‐‐‐ 0.28 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 0.21 < 0.01 ‐ ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 4.9 < 0.01 0.058 < 0.01 0.12 < 0.01 2.5 < 0.01 ‐ ‐ 7.2 0.014 0.084 < 0.01 0.3 < 0.01 3.6 < 0.01 ‐
‐ 4.4 < 0.01 0.11 < 0.01 0.21 < 0.01 2.9 < 0.01 ‐
‐ 4.5 0.011 0.094 < 0.01 0.25 < 0.01 2.4 < 0.01 ‐
‐ 3.2 < 0.01 0.13 < 0.01 0.18 < 0.01 1.7 0.012 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 9 0.016 0.19 < 0.01 0.31 < 0.01 5.4 0.025 ‐ ‐ 1.9 < 0.01 0.051 < 0.01 0.27 < 0.01 1.6 < 0.01 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 7.1 < 0.01 0.066 < 0.01 0.24 < 0.01 5.3 < 0.01 ‐ ‐ 0.5 < 0.01 < 0.01 < 0.01 0.04 0.013 0.86 < 0.01 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 3.9 < 0.01 0.11 < 0.01 0.19 < 0.01 2.1 0.012 ‐ ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 1.1 < 0.015 < 0.015 < 0.015 0.058 0.12 0.69 < 0.015 ‐ ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 3.1 < 0.01 0.02 < 0.01 0.11 < 0.01 4.6 < 0.01 ‐ ‐‐‐‐‐‐‐‐‐‐‐ 16 0.02 0.18 < 0.01 0.55 < 0.01 11 0.011 ‐
‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
TPH (mg/kg)
PHC as Gasoline 5,400 97 ‐
Total Petroleum Hydrocarbons (C6) ‐‐‐
Total Petroleum Hydrocarbons (C7) ‐‐‐
Total Petroleum Hydrocarbons (C8) ‐‐‐
Total Petroleum Hydrocarbons (C9‐C10) ‐‐‐
Total Petroleum Hydrocarbons (C11‐C12) ‐‐‐
Total Petroleum Hydrocarbons (C13‐C14) ‐‐‐
Total Petroleum Hydrocarbons (C15‐C16) ‐‐‐
Total Petroleum Hydrocarbons (C17‐C18) ‐‐‐
Total Petroleum Hydrocarbons (C19‐C20) ‐‐‐
Total Petroleum Hydrocarbons (C21‐C22) ‐‐‐
Total Petroleum Hydrocarbons (C23‐C24) ‐‐‐
Total Petroleum Hydrocarbons (C25‐C28) ‐‐‐
Total Petroleum Hydrocarbons (C29‐C32) ‐‐‐
Total Petroleum Hydrocarbons (C33‐C36) ‐‐‐
Total Petroleum Hydrocarbons (C37‐C40) ‐‐‐
Total Petroleum Hydrocarbons (C41‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C6‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) Diesel ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) DRO ‐‐‐
Total Petroleum Hydrocarbons (>C28‐C44) ‐‐‐
Gasoline C6‐C8 (calculated) 2,900 ‐‐
Diesel C9‐C16 (calculated) 5,400 97 ‐
Oil C17‐C32 (calculated) 7,300 2,400 ‐
‐
VOCs (mg/kg)
1,1,1,2‐Tetrachloroethane ‐ 8.8 ‐
1,1,1‐Trichloroethane 1.7 7,200 ‐
1,1,2,2‐Tetrachloroethane ‐ 2.7 ‐
1,1,2‐Trichloroethane 0.04 ‐‐
1,1‐Dichloroethane 0.56 16 ‐
1,1‐Dichloroethene 0.071 350 ‐
1,1‐Dichloropropene ‐‐‐
1,2,3‐Trichlorobenzene ‐ 300 ‐
1,2,3‐Trichloropropane ‐ 0.021 ‐
1,2,3‐Trimethylbenzene ‐‐‐
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2,4‐Trimethylbenzene ‐‐‐
1,2‐Dibromo‐3‐chloropropane (DBCP) ‐ 0.057 ‐
1,2‐Dibromoethane (Ethylene Dibromide) ‐ 0.16 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,2‐Dichloroethane 0.0028 ‐‐
1,2‐Dichloropropane ‐‐‐
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) ‐‐‐‐‐‐‐‐‐‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 22 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 35 < 5 ‐
< 5 < 250 < 5 < 5 < 5 6 < 5 64 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 45 < 5 ‐
< 5 < 250 < 5 < 5 < 5 7.2 < 5 47 < 5 ‐
< 5 290 < 5 < 5 < 5 12 < 5 66 < 5 ‐
< 5 380 < 5 < 5 < 5 13 < 5 47 < 5 ‐
< 5 < 250 < 5 < 5 < 5 7.2 < 5 33 < 5 ‐
< 5 < 250 < 5 < 5 < 5 8.1 < 5 25 < 5 ‐
< 5 1300 < 5 13 6.8 64 < 5 400 < 5 ‐
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 < 250 < 5 < 5 < 5 < 5 < 5 < 10 < 5 ‐
< 5 290 < 5 < 5 < 5 25.2 < 5 279 < 5 ‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
1,3,5‐Trimethylbenzene ‐‐‐
1,3‐Dichlorobenzene ‐‐‐
1,3‐Dichloropropane ‐ 2,200 ‐
1,4‐Dichloro‐2‐butene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
2,2‐Dichloropropane ‐‐‐
2‐Butanone (Methyl Ethyl Ketone) ‐‐‐
2‐Chlorotoluene ‐ 2,500 ‐
2‐Hexanone ‐‐‐2‐Phenylbutane (sec‐Butylbenzene) ‐ 12,000 ‐ 4‐Chlorotoluene ‐ 2,300 ‐
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) ‐‐‐
Acetone ‐‐‐Acrylonitrile ‐‐‐Allyl chloride ‐‐‐
Benzene 0.019 1.4 ‐Bromobenzene ‐‐‐Bromodichloromethane ‐ 1.3 ‐ Bromoform ‐ 86 ‐
Bromomethane (Methyl Bromide) ‐‐‐
Carbon disulfide ‐‐‐
Carbon tetrachloride ‐ 2.9 ‐
Chlorobenzene 2 ‐‐Chlorobromomethane ‐ 4.1 ‐
Chloroethane ‐‐‐Chloroform (Trichloromethane) ‐‐‐
Chloromethane (Methyl Chloride) ‐‐‐
cis‐1,2‐Dichloroethene 4.9 84 ‐
cis‐1,3‐Dichloropropene ‐‐‐
cis‐1,4‐Dichloro‐2‐butene ‐‐‐Cymene (p‐Isopropyltoluene) ‐ 1,600 ‐ Dibromochloromethane ‐‐‐Dibromomethane ‐‐‐Dichlorodifluoromethane (CFC‐12) ‐‐‐ Diisopropyl ether (DIPE) ‐‐‐
Ethylbenzene 7.7 ‐‐Hexachlorobutadiene ‐ 5.3 ‐
Isopropylbenzene (Cumene) ‐‐‐
m,p‐Xylenes 6 ‐‐
Methyl Tert Butyl Ether ‐‐‐
Methylene chloride 0.019 26 ‐
Naphthalene ‐ 6.5 ‐
n‐Butylbenzene ‐‐‐
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005< 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
n‐Propylbenzene ‐‐‐
o‐Xylene 6 ‐‐
PHC as Gasoline 5,400 97 ‐
Styrene ‐ 32,000 ‐
Tert‐Amyl Methyl Ether (TAME) ‐‐‐
Tert‐Butyl Alcohol (tert‐Butanol) ‐‐‐
Tert‐Butyl Ethyl Ether (ETBE) ‐‐‐tert‐Butylbenzene ‐‐‐
Tetrachloroethene 2.1 2.7 ‐
Toluene 0.44 5,300 ‐trans‐1,2‐Dichloroethene 0.17 600 ‐ trans‐1,3‐Dichloropropene ‐‐‐
Trichloroethene 27 63 2,040
Trichlorofluoromethane (CFC‐11) ‐ 5,400 ‐
Trifluorotrichloroethane (Freon 113) 6.4 ‐‐
Vinyl acetate ‐‐‐
Vinyl chloride 13 0.15 ‐
Xylene (total) 6 ‐‐
Notes and Abbreviations:
BOLD = concentration detected at or above
reported detection limit.
No COPC in soil exceeded its Total Threshold Limit Concentration (TTLC). < = analyte not detected above the indicated
reporting limit.B = compound detected in the associated blank J = estimated concentration.‐ = not analyzed or not applicable. mg/kg = milligrams per kilogram.
bgs = below ground surface.
GPL: Groundwater Protection Level (Haley & Aldrich 2014a, 2014b) TTLC: Total Threshold Limit Concentration, CCR Title 22 Section 66261.24 1 Cancer Endpoint. If there is no Cancer Endpoint, the Noncancer Endpoint is noted.2 Site background3 U.S. EPA Region 9 Remediation Screening Level DTSC‐SL: Commercial/Industrial Department of Toxic Substances Control‐Screening Level, HHRA Note 3, June 2020.
UT‐03 UT‐18 UT‐18 UT‐19 UT‐19 UT‐20 UT‐20 UT‐21 UT‐21 UT‐22 SSS00281 (UT‐03‐
05)
SSS00310 (UT‐18‐
01)
SSS00311 (UT‐18‐
05)
SSS00312 (UT‐19‐
01)
SSS00313 (UT‐19‐
05)
SSS00314 (UT‐20‐
01)
SSS00315 (UT‐20‐
05)
SSS00316 (UT‐21‐
01)
SSS00317 (UT‐21‐
05)
SSS00320 (UT‐22‐
01)
4/22/2013 4/22/2013 4/22/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
Metals (mg/kg) GPL DTSC TTLC
Antimony 7.84 ‐ 500
Arsenic 24.3 0.36/82 500
Barium 43000 ‐ 10,000
Beryllium ‐ 6,900 75
Cadmium 970 4,000 100Chromium 660 ‐ 2,500
Chromium VI (Hexavalent) 30 6.2 500
Cobalt ‐‐ 8,000
Copper 5600 ‐ 2,500
Lead 232 320 1,000Mercury 2.1 4.4 20Molybdenum ‐‐ 3,500 Nickel 3400 64,000 2,000Selenium ‐‐ 100Silver ‐‐ 500Thallium ‐‐ 700Vanadium ‐‐ 2,400 Zinc ‐‐ 5,000
‐
PCBs (mg/kg)
Aroclor‐1016 (PCB‐1016) ‐ 17 ‐
Aroclor‐1221 (PCB‐1221) ‐ 0.53 ‐
Aroclor‐1232 (PCB‐1232) ‐ 0.49 ‐
Aroclor‐1242 (PCB‐1242) ‐ 0.58 ‐
Aroclor‐1248 (PCB‐1248) ‐ 0.58 ‐
Aroclor‐1254 (PCB‐1254) ‐ 0.59 ‐
Aroclor‐1260 (PCB‐1260) ‐ 0.6 ‐
Aroclor‐1262 (PCB‐1262) ‐‐‐
Aroclor‐1268 (PCB‐1268) ‐‐‐
Total PCBs 130 0.58 50
‐
PEST (mg/kg)
4,4'‐DDD ‐ 6.2 1.0
4,4'‐DDE ‐ 9.3 1.04,4'‐DDT ‐ 7.1 1.0
Aldrin ‐ 0.18 1.4
alpha‐BHC ‐ 0.24 ‐
beta‐BHC ‐ 0.82 ‐
Chlordane ‐ 6.1 2.5
delta‐BHC ‐‐‐
Dieldrin ‐ 0.093 8.0
Endosulfan I ‐ 6,000 ‐
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) ‐‐‐‐‐‐‐‐ < 0.75 < 0.75
‐‐‐‐‐‐‐‐ 5.66 2.25
‐‐‐‐‐‐‐‐ 79.2 75.8
‐‐‐‐‐‐‐‐ 0.318 0.382
‐‐‐‐‐‐‐‐ 0.915 < 0.5
‐‐‐‐‐‐‐‐ 13.6 12.5
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 8.48 5.87
‐‐‐‐‐‐‐‐ 34.7 6.05
‐‐‐‐‐‐‐‐ 31.5 4.3
‐‐‐‐‐‐‐‐ < 0.0835 < 0.0835
‐‐‐‐‐‐‐‐ < 0.25 < 0.25
‐‐‐‐‐‐‐‐ 7.29 5.8‐‐‐‐‐‐‐‐ < 0.75 < 0.75
‐‐‐‐‐‐‐‐ < 0.25 < 0.25
‐‐‐‐‐‐‐‐ < 0.75 < 0.75
‐‐‐‐‐‐‐‐ 36.2 30.5
‐‐‐‐‐‐‐‐ 148 25.7
‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐‐‐‐‐‐‐‐‐‐‐ < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
PEST (mg/kg) ‐
Endosulfan II ‐ 6,000 ‐
Endosulfan sulfate ‐ 11,000 ‐
Endrin ‐ 160 0.2
Endrin aldehyde ‐‐‐
Endrin ketone ‐‐‐
gamma‐BHC (Lindane) ‐ 2 4.0
Heptachlor ‐ 0.63 4.7
Heptachlor epoxide ‐ 0.33 ‐
Methoxychlor ‐ 2600 100
Toxaphene ‐ 1.2 5
‐
SVOCs (mg/kg)
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,3‐Dichlorobenzene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
1‐Methylnaphthalene ‐ 30 ‐
2,2'‐oxybis(2‐Chloropropane) ‐‐‐
2,4,5‐Trichlorophenol ‐ 53,000 ‐
2,4,6‐Trichlorophenol ‐ 21 ‐
2,4‐Dichlorophenol ‐ 1,600 ‐
2,4‐Dimethylphenol ‐ 11,000 ‐
2,4‐Dinitrophenol ‐ 1,100 ‐
2,4‐Dinitrotoluene ‐‐‐
2,6‐Dichlorophenol ‐ 4.7 ‐
2,6‐Dinitrotoluene ‐ 0.99 ‐
2‐Chloronaphthalene ‐ 27,000 ‐
2‐Chlorophenol ‐ 3,900 ‐
2‐Methylnaphthalene ‐ 1,300 ‐
2‐Methylphenol (o‐Cresol) ‐ 26,000 ‐
2‐Nitroaniline ‐ 5,200 ‐
2‐Nitrophenol ‐‐‐3,3'‐Dichlorobenzidine ‐ 0.93 ‐
3‐Nitroaniline ‐‐‐
4,6‐Dinitro‐2‐methylphenol ‐ 42 ‐
4‐Bromophenyl phenyl ether ‐‐‐
4‐Chloro‐3‐methylphenol ‐ 53,000 ‐
4‐Chloroaniline ‐ 7.4 ‐
4‐Chlorophenyl phenyl ether ‐‐‐
4‐Nitroaniline ‐ 74 ‐
4‐Nitrophenol ‐‐‐
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
SVOCs (mg/kg) ‐
Acenaphthene ‐ 23,000 ‐
Acenaphthylene ‐‐‐Aniline ‐ 260 ‐
Anthracene ‐ 130,000 ‐
Azobenzene ‐‐‐Benzidine ‐ 0.003 ‐
Benzo(a)anthracene ‐ 12 ‐
Benzo(a)pyrene 14 1.3 ‐Benzo(b)fluoranthene ‐ 13 ‐
Benzo(g,h,i)perylene ‐‐‐Benzo(k)fluoranthene ‐ 210,000 ‐ Benzoic acid ‐ 2,100,000 ‐
Benzyl Alcohol ‐ 53,000 ‐
bis(2‐Chloroethoxy)methane ‐ 1,600 ‐
bis(2‐Chloroethyl)ether ‐ 0.47 ‐
bis(2‐Ethylhexyl)phthalate 57 110 ‐
Butyl benzylphthalate ‐ 780 ‐
Chrysene ‐ 1,300 ‐
Dibenz(a,h)anthracene ‐ 0.31 ‐
Dibenzofuran ‐ 650 ‐
Diethyl phthalate ‐ 420,000 ‐Dimethyl phthalate ‐‐‐
Di‐n‐butylphthalate ‐ 53,000 ‐
Di‐n‐octyl phthalate ‐ 5,300 ‐Fluoranthene ‐ 18,000 ‐
Fluorene ‐ 17,000 ‐
Hexachlorobenzene ‐ 0.86 ‐
Hexachlorobutadiene ‐ 5.3 ‐
Hexachlorocyclopentadiene ‐‐‐Hexachloroethane ‐‐‐Indeno(1,2,3‐cd)pyrene ‐ 13 ‐ Isophorone ‐ 1,600 ‐
m,p‐Cresols ‐‐‐
Naphthalene ‐ 6.5 ‐
Nitrobenzene ‐‐‐N‐Nitrosodimethylamine ‐ 0.53 ‐
N‐Nitrosodi‐n‐propylamine ‐ 0.21 ‐
N‐Nitrosodiphenylamine ‐ 300 ‐
Pentachlorophenol 0.0717 2 ‐Phenanthrene ‐‐‐Phenol ‐ 160,000 ‐ Pyrene ‐ 13,000 ‐
Pyridine ‐ 530 ‐
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) ‐‐‐‐‐‐‐‐ < 0.015 < 0.015
‐‐‐‐‐‐‐‐ 1.2 < 0.03
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 0.048 < 0.01
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 0.75 < 0.01
‐‐‐‐‐‐‐‐ 1.3 < 0.01
‐‐‐‐‐‐‐‐ 0.85 < 0.01
‐‐‐‐‐‐‐‐ 0.8 < 0.01
‐‐‐‐‐‐‐‐ 0.54 < 0.01
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 1.6 < 0.01 ‐‐‐‐‐‐‐‐ 0.59 < 0.01
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 2 < 0.01 ‐‐‐‐‐‐‐‐ 0.24 < 0.01
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 0.7 < 0.01 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 0.79 < 0.015
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 1.4 < 0.01 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ 3.8 < 0.01‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
TPH (mg/kg)
PHC as Gasoline 5,400 97 ‐
Total Petroleum Hydrocarbons (C6) ‐‐‐
Total Petroleum Hydrocarbons (C7) ‐‐‐
Total Petroleum Hydrocarbons (C8) ‐‐‐
Total Petroleum Hydrocarbons (C9‐C10) ‐‐‐
Total Petroleum Hydrocarbons (C11‐C12) ‐‐‐
Total Petroleum Hydrocarbons (C13‐C14) ‐‐‐
Total Petroleum Hydrocarbons (C15‐C16) ‐‐‐
Total Petroleum Hydrocarbons (C17‐C18) ‐‐‐
Total Petroleum Hydrocarbons (C19‐C20) ‐‐‐
Total Petroleum Hydrocarbons (C21‐C22) ‐‐‐
Total Petroleum Hydrocarbons (C23‐C24) ‐‐‐
Total Petroleum Hydrocarbons (C25‐C28) ‐‐‐
Total Petroleum Hydrocarbons (C29‐C32) ‐‐‐
Total Petroleum Hydrocarbons (C33‐C36) ‐‐‐
Total Petroleum Hydrocarbons (C37‐C40) ‐‐‐
Total Petroleum Hydrocarbons (C41‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C6‐C44) ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) Diesel ‐‐‐
Total Petroleum Hydrocarbons (C10‐C28) DRO ‐‐‐
Total Petroleum Hydrocarbons (>C28‐C44) ‐‐‐
Gasoline C6‐C8 (calculated) 2,900 ‐‐
Diesel C9‐C16 (calculated) 5,400 97 ‐
Oil C17‐C32 (calculated) 7,300 2,400 ‐
‐
VOCs (mg/kg)
1,1,1,2‐Tetrachloroethane ‐ 8.8 ‐
1,1,1‐Trichloroethane 1.7 7,200 ‐
1,1,2,2‐Tetrachloroethane ‐ 2.7 ‐
1,1,2‐Trichloroethane 0.04 ‐‐
1,1‐Dichloroethane 0.56 16 ‐
1,1‐Dichloroethene 0.071 350 ‐
1,1‐Dichloropropene ‐‐‐
1,2,3‐Trichlorobenzene ‐ 300 ‐
1,2,3‐Trichloropropane ‐ 0.021 ‐
1,2,3‐Trimethylbenzene ‐‐‐
1,2,4‐Trichlorobenzene 0.818 35 ‐
1,2,4‐Trimethylbenzene ‐‐‐
1,2‐Dibromo‐3‐chloropropane (DBCP) ‐ 0.057 ‐
1,2‐Dibromoethane (Ethylene Dibromide) ‐ 0.16 ‐
1,2‐Dichlorobenzene 28 ‐‐
1,2‐Dichloroethane 0.0028 ‐‐
1,2‐Dichloropropane ‐‐‐
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) ‐‐‐‐‐‐‐‐‐‐‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 5.3 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 6.6 < 5 < 5 6.8 < 5
‐ < 5 < 5 < 5 < 5 6.8 < 5 < 5 5.6 < 5
‐ < 5 < 5 < 5 < 5 5.1 < 5 < 5 9.8 < 5
‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 23 < 5 < 5 42 < 5
‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 ‐ < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5 < 5
‐ < 5 < 5 < 5 < 5 6.6 < 5 < 5 12.1 < 5
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
1,3,5‐Trimethylbenzene ‐‐‐
1,3‐Dichlorobenzene ‐‐‐
1,3‐Dichloropropane ‐ 2,200 ‐
1,4‐Dichloro‐2‐butene ‐‐‐
1,4‐Dichlorobenzene 0.23 ‐‐
2,2‐Dichloropropane ‐‐‐
2‐Butanone (Methyl Ethyl Ketone) ‐‐‐
2‐Chlorotoluene ‐ 2,500 ‐
2‐Hexanone ‐‐‐2‐Phenylbutane (sec‐Butylbenzene) ‐ 12,000 ‐ 4‐Chlorotoluene ‐ 2,300 ‐
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) ‐‐‐
Acetone ‐‐‐Acrylonitrile ‐‐‐Allyl chloride ‐‐‐
Benzene 0.019 1.4 ‐Bromobenzene ‐‐‐Bromodichloromethane ‐ 1.3 ‐ Bromoform ‐ 86 ‐
Bromomethane (Methyl Bromide) ‐‐‐
Carbon disulfide ‐‐‐
Carbon tetrachloride ‐ 2.9 ‐
Chlorobenzene 2 ‐‐Chlorobromomethane ‐ 4.1 ‐
Chloroethane ‐‐‐Chloroform (Trichloromethane) ‐‐‐
Chloromethane (Methyl Chloride) ‐‐‐
cis‐1,2‐Dichloroethene 4.9 84 ‐
cis‐1,3‐Dichloropropene ‐‐‐
cis‐1,4‐Dichloro‐2‐butene ‐‐‐Cymene (p‐Isopropyltoluene) ‐ 1,600 ‐ Dibromochloromethane ‐‐‐Dibromomethane ‐‐‐Dichlorodifluoromethane (CFC‐12) ‐‐‐ Diisopropyl ether (DIPE) ‐‐‐
Ethylbenzene 7.7 ‐‐Hexachlorobutadiene ‐ 5.3 ‐
Isopropylbenzene (Cumene) ‐‐‐
m,p‐Xylenes 6 ‐‐
Methyl Tert Butyl Ether ‐‐‐
Methylene chloride 0.019 26 ‐
Naphthalene ‐ 6.5 ‐
n‐Butylbenzene ‐‐‐
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 < 0.12 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005< 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.025 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 2
SUMMARY OF VADOSE ZONE SOIL DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Name
Sample Date
Sample Depth
GPL
(mg/kg)
Comm/Ind
DTSC‐
SL1(mg/kg)
TTLC
(mg/kg)
VOCs (mg/kg) ‐
n‐Propylbenzene ‐‐‐
o‐Xylene 6 ‐‐
PHC as Gasoline 5,400 97 ‐
Styrene ‐ 32,000 ‐
Tert‐Amyl Methyl Ether (TAME) ‐‐‐
Tert‐Butyl Alcohol (tert‐Butanol) ‐‐‐
Tert‐Butyl Ethyl Ether (ETBE) ‐‐‐tert‐Butylbenzene ‐‐‐
Tetrachloroethene 2.1 2.7 ‐
Toluene 0.44 5,300 ‐trans‐1,2‐Dichloroethene 0.17 600 ‐ trans‐1,3‐Dichloropropene ‐‐‐
Trichloroethene 27 63 2,040
Trichlorofluoromethane (CFC‐11) ‐ 5,400 ‐
Trifluorotrichloroethane (Freon 113) 6.4 ‐‐
Vinyl acetate ‐‐‐
Vinyl chloride 13 0.15 ‐
Xylene (total) 6 ‐‐
Notes and Abbreviations:
BOLD = concentration detected at or above
reported detection limit.
No COPC in soil exceeded its Total Threshold Limit Concentration (TTLC). < = analyte not detected above the indicated
reporting limit.B = compound detected in the associated blank J = estimated concentration.‐ = not analyzed or not applicable. mg/kg = milligrams per kilogram.
bgs = below ground surface.
GPL: Groundwater Protection Level (Haley & Aldrich 2014a, 2014b) TTLC: Total Threshold Limit Concentration, CCR Title 22 Section 66261.24 1 Cancer Endpoint. If there is no Cancer Endpoint, the Noncancer Endpoint is noted.2 Site background3 U.S. EPA Region 9 Remediation Screening Level DTSC‐SL: Commercial/Industrial Department of Toxic Substances Control‐Screening Level, HHRA Note 3, June 2020.
UT‐22 UT‐23 UT‐23 UT‐24 UT‐24 UT‐25 UT‐25 UT‐25 UT‐66 UT‐66 SSS00321 (UT‐22‐
05)
SSS00322 (UT‐23‐
01)
SSS00323 (UT‐23‐
05)
SSS00324 (UT‐24‐
01)
SSS00325 (UT‐24‐
05)
SSS00420 (UT‐25‐
01A)
SSS00326 (UT‐25‐
01)
SSS00327 (UT‐25‐
05)
SSS00318 (UT‐66‐
01)
SSS00319 (UT‐66‐
05)
4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/23/2013 4/29/2013 4/29/2013 4/23/2013 4/23/2013 5 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) 1 (ft) 1 (ft) 5 (ft) 1 (ft) 5 (ft) < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐‐
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 0.059 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.05 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 ‐‐‐‐‐‐‐‐‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 2_Soil Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location B29‐V03 B29‐V04 B29‐V05 B29‐V06 B29‐V07 B29‐V08 B29‐V09 B29‐V10 Sample Name B29‐SV03‐1' B29‐SV04‐1' B29‐V05‐1' B29‐SV06‐1' B29‐SV07‐1' B29‐SV08‐1' B29‐V09‐1' B29‐V10‐1' Sample Date 5/23/2018 5/23/2018 5/22/2018 5/23/2018 5/23/2018 5/24/2018 5/22/2018 5/22/2018 Sample Depth 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55 < 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70 1,1,1‐Trichloroethane < 28 < 28 46 < 28 < 28 < 28 110 < 28 1,1,2,2‐Tetrachloroethane 7 < 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70 1,1,2‐Trichloroethane 26 < 55 < 55 < 55 < 55 < 55 < 55 < 55 < 55 1,1‐Dichloroethane 260 < 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41 1,1‐Dichloroethene < 20 < 20 < 20 < 20 < 20 < 20 < 20 < 20 1,1‐Difluoroethane < 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27 1,2,4‐Trichlorobenzene < 75 < 75 < 75 < 75 < 75 < 75 < 75 < 75 1,2,4‐Trimethylbenzene < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 1,2‐Dibromoethane (Ethylene Dibromide) 0.68 < 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39 1,2‐Dichlorobenzene < 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61 1,2‐Dichloroethane 16 < 21 < 21 < 21 < 21 < 21 < 21 < 21 < 211,2‐Dichloropropane 41 < 47 < 47 < 47 < 47 < 47 < 47 < 47 < 47 1,2‐Dichlorotetrafluoroethane (CFC 114) < 71 < 71 < 71 < 71 < 71 < 71 < 71 < 71 1,3,5‐Trimethylbenzene < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 1,3‐Dichlorobenzene < 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61 1,4‐Dichlorobenzene 37 < 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61 2‐Butanone (Methyl Ethyl Ketone) < 60 < 60 < 60 < 60 < 60 < 60 < 60 < 60 2‐Hexanone < 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
4‐Ethyl toluene < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) < 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41 Benzene 14 49 < 16 27 < 16 < 16 < 16 < 16 < 16
Bromodichloromethane 11 < 68 < 68 < 68 < 68 < 68 < 68 < 68 < 68 Bromoform 370 < 100 < 100 < 100 < 100 < 100 < 100 < 100 < 100 Bromomethane (Methyl Bromide) < 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39 Carbon disulfide < 32 < 32 < 32 < 32 < 32 < 32 < 32 < 32 Carbon tetrachloride 68 < 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13 Chlorobenzene < 23 < 23 < 23 < 23 < 23 < 23 < 23 < 23
Chloroethane < 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27
Chloroform (Trichloromethane) 18 12000 < 25 < 25 < 25 240 < 25 170 < 25 Chloromethane (Methyl Chloride) < 21 < 21 < 21 < 21 < 21 < 21 < 21 < 21cis‐1,2‐Dichloroethene 250 < 40 < 40 < 40 < 40 < 40 < 40 < 40 cis‐1,3‐Dichloropropene < 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46 Dibromochloromethane < 86 < 86 < 86 < 86 < 86 < 86 < 86 < 86 Dichlorodifluoromethane (CFC‐12) < 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50 Ethylbenzene 160 < 22 < 22 47 < 22 < 22 < 22 < 22 < 22
Vapor ESL:
Commercial/
Industrial Cancer
Risk
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location B29‐V03 B29‐V04 B29‐V05 B29‐V06 B29‐V07 B29‐V08 B29‐V09 B29‐V10 Sample Name B29‐SV03‐1' B29‐SV04‐1' B29‐V05‐1' B29‐SV06‐1' B29‐SV07‐1' B29‐SV08‐1' B29‐V09‐1' B29‐V10‐1' Sample Date 5/23/2018 5/23/2018 5/22/2018 5/23/2018 5/23/2018 5/24/2018 5/22/2018 5/22/2018 Sample Depth 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) VOCs (µg/m3)
Vapor ESL:
Commercial/
Industrial Cancer
Risk
Hexachlorobutadiene 19 < 110 < 110 < 110 < 110 < 110 < 110 < 110 < 110 m,p‐Xylenes < 44 < 44 190 < 44 88 < 44 < 44 < 44
Methylene chloride 410 < 35 < 35 < 35 < 35 < 35 < 35 < 35 < 35 o‐Xylene < 22 < 22 53 < 22 31 < 22 < 22 < 22
Styrene < 43 < 43 < 43 110 < 43 52 52 92
Tetrachloroethene 67 150 210 220 < 34 2200 80 < 34 < 34 Toluene < 38 < 38 180 44 46 < 38 < 38 < 38
trans‐1,2‐Dichloroethene 82 < 40 < 40 < 40 < 40 < 40 < 40 < 40 trans‐1,3‐Dichloropropene < 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46 Trichloroethene 100 920000 7500 < 27 < 27 7800 130 11000 120 Trichlorofluoromethane (CFC‐11) < 56 < 56 < 56 < 56 < 56 < 56 < 56 < 56 Trifluorotrichloroethane (Freon 113) < 77 < 77 < 77 < 77 < 77 < 77 < 77 < 77 Vinyl chloride 5.2 < 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13 Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55
1,1,1‐Trichloroethane
1,1,2,2‐Tetrachloroethane 7
1,1,2‐Trichloroethane 26
1,1‐Dichloroethane 260
1,1‐Dichloroethene
1,1‐Difluoroethane
1,2,4‐Trichlorobenzene
1,2,4‐Trimethylbenzene
1,2‐Dibromoethane (Ethylene Dibromide) 0.68
1,2‐Dichlorobenzene
1,2‐Dichloroethane 16
1,2‐Dichloropropane 41
1,2‐Dichlorotetrafluoroethane (CFC 114)
1,3,5‐Trimethylbenzene
1,3‐Dichlorobenzene
1,4‐Dichlorobenzene 37
2‐Butanone (Methyl Ethyl Ketone)
2‐Hexanone4‐Ethyl toluene
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone)
Benzene 14Bromodichloromethane 11Bromoform 370Bromomethane (Methyl Bromide) Carbon disulfide
Carbon tetrachloride 68
Chlorobenzene
ChloroethaneChloroform (Trichloromethane) 18Chloromethane (Methyl Chloride) cis‐1,2‐Dichloroethene
cis‐1,3‐Dichloropropene
DibromochloromethaneDichlorodifluoromethane (CFC‐12)
Ethylbenzene 160
Vapor ESL:
Commercial/
Industrial Cancer
Risk
B29‐V11 B29‐V12 B29‐V13 B29‐V14 B29‐V15 B29‐V16 B29‐V17 B29‐V18 B29‐V11‐1' B29‐V12‐1' B29‐V13‐1' B29‐V14‐1' B29‐V15‐1' B29‐V16‐1' B29‐V17‐1' B29‐V18‐1' Rep 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) < 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70
< 28 < 28 < 28 46 < 28 790 < 28 < 28
< 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70
< 55 < 55 < 55 < 55 < 55 < 55 < 55 < 55
< 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
< 20 < 20 < 20 < 20 < 20 < 20 < 20 < 20
< 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27
< 75 < 75 < 75 < 75 < 75 < 75 < 75 < 75
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 21 < 21 < 21 < 21 < 21 < 21 < 21 < 21
< 47 < 47 < 47 < 47 < 47 < 47 < 47 < 47
< 71 < 71 < 71 < 71 < 71 < 71 < 71 < 71
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 60 < 60 < 60 < 60 < 60 < 60 < 60 < 60
< 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
< 16 < 16 < 16 < 16 < 16 < 16 < 16 < 16
< 68 < 68 < 68 < 68 < 68 < 68 < 68 < 68
< 100 < 100 < 100 < 100 < 100 < 100 < 100 < 100
< 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39
< 32 < 32 < 32 < 32 < 32 < 32 < 32 < 32
< 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13
< 23 < 23 < 23 < 23 < 23 < 23 < 23 < 23
< 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27
< 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25
< 21 < 21 < 21 < 21 < 21 < 21 < 21 < 21
< 40 < 40 < 40 < 40 < 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46
< 86 < 86 < 86 < 86 < 86 < 86 < 86 < 86
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 22 < 22 < 22 < 22 < 22 < 22 < 22 < 22
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
Vapor ESL:
Commercial/
Industrial Cancer
Risk
Hexachlorobutadiene 19m,p‐XylenesMethylene chloride 410o‐XyleneStyreneTetrachloroethene 67Toluenetrans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene
Trichloroethene 100Trichlorofluoromethane (CFC‐11)
Trifluorotrichloroethane (Freon 113)
Vinyl chloride 5.2
Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
B29‐V11 B29‐V12 B29‐V13 B29‐V14 B29‐V15 B29‐V16 B29‐V17 B29‐V18 B29‐V11‐1' B29‐V12‐1' B29‐V13‐1' B29‐V14‐1' B29‐V15‐1' B29‐V16‐1' B29‐V17‐1' B29‐V18‐1' Rep 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 5/22/2018 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) < 110 < 110 < 110 < 110 < 110 < 110 < 110 < 110
< 44 < 44 < 44 < 44 < 44 < 44 < 44 < 44
< 35 < 35 < 35 < 35 < 35 < 35 < 35 < 35
< 22 < 22 < 22 < 22 < 22 < 22 < 22 < 22
66 53 74 65 64 < 43 110 62
< 34 < 34 < 34 < 34 < 34 340 < 34 54< 38 < 38 < 38 < 38 < 38 < 38 < 38 < 38 < 40 < 40 < 40 < 40 < 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46
< 27 < 27 < 27 < 27 < 27 16000 43 < 27
< 56 < 56 < 56 < 56 60 < 56 < 56 < 56
< 77 < 77 < 77 < 77 < 77 320 < 77 < 77
< 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55
1,1,1‐Trichloroethane
1,1,2,2‐Tetrachloroethane 7
1,1,2‐Trichloroethane 26
1,1‐Dichloroethane 260
1,1‐Dichloroethene
1,1‐Difluoroethane
1,2,4‐Trichlorobenzene
1,2,4‐Trimethylbenzene
1,2‐Dibromoethane (Ethylene Dibromide) 0.68
1,2‐Dichlorobenzene
1,2‐Dichloroethane 16
1,2‐Dichloropropane 41
1,2‐Dichlorotetrafluoroethane (CFC 114)
1,3,5‐Trimethylbenzene
1,3‐Dichlorobenzene
1,4‐Dichlorobenzene 37
2‐Butanone (Methyl Ethyl Ketone)
2‐Hexanone4‐Ethyl toluene
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone)
Benzene 14Bromodichloromethane 11Bromoform 370Bromomethane (Methyl Bromide) Carbon disulfide
Carbon tetrachloride 68
Chlorobenzene
ChloroethaneChloroform (Trichloromethane) 18Chloromethane (Methyl Chloride) cis‐1,2‐Dichloroethene
cis‐1,3‐Dichloropropene
DibromochloromethaneDichlorodifluoromethane (CFC‐12)
Ethylbenzene 160
Vapor ESL:
Commercial/
Industrial Cancer
Risk
B29‐V18 B29‐V19 B99‐V01 B99‐V02 B99‐V03 B99‐V04 B99‐V05 B99‐V06 B29‐V18‐1' B29‐V19‐1' B99‐SV01‐1' B99‐SV02‐1' B99‐SV03‐1' B99‐SV04‐1' B99‐SV05‐1' B99‐SV06‐1' 5/22/2018 5/22/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) < 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70
< 28 480 < 28 < 28 < 28 < 28 < 28 < 28
< 70 < 70 < 70 < 70 < 70 < 70 < 70 < 70
< 55 < 55 < 55 < 55 < 55 < 55 < 55 < 55
< 41 53 < 41 < 41 < 41 < 41 < 41 < 41
< 20 < 20 < 20 < 20 < 20 < 20 < 20 < 20
< 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27
< 75 < 75 < 75 < 75 < 75 < 75 < 75 < 75
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 21 < 21 < 21 < 21 < 21 < 21 < 21 < 21
< 47 < 47 < 47 < 47 < 47 < 47 < 47 < 47
< 71 < 71 < 71 < 71 < 71 < 71 < 71 < 71
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 61 < 61 < 61 < 61 < 61 < 61 < 61 < 61
< 60 < 60 < 60 < 60 < 60 < 60 < 60 < 60
< 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 41 < 41 < 41 < 41 < 41 < 41 < 41 < 41
< 16 < 16 < 16 < 16 < 16 < 16 < 16 < 16
< 68 < 68 < 68 < 68 < 68 < 68 < 68 < 68
< 100 < 100 < 100 < 100 < 100 < 100 < 100 < 100
< 39 < 39 < 39 < 39 < 39 < 39 < 39 < 39
< 32 < 32 < 32 < 32 < 32 < 32 < 32 < 32
< 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13
< 23 < 23 < 23 < 23 < 23 < 23 < 23 < 23
< 27 < 27 < 27 < 27 < 27 < 27 < 27 < 27
< 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25
< 21 < 21 < 21 < 21 < 21 < 21 < 21 < 21
< 40 1300 < 40 < 40 < 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46
< 86 < 86 < 86 < 86 < 86 < 86 < 86 < 86
< 50 < 50 < 50 < 50 < 50 < 50 < 50 < 50
< 22 < 22 < 22 < 22 < 22 < 22 < 22 < 22
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
Vapor ESL:
Commercial/
Industrial Cancer
Risk
Hexachlorobutadiene 19m,p‐XylenesMethylene chloride 410o‐XyleneStyreneTetrachloroethene 67Toluenetrans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene
Trichloroethene 100Trichlorofluoromethane (CFC‐11)
Trifluorotrichloroethane (Freon 113)
Vinyl chloride 5.2
Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
B29‐V18 B29‐V19 B99‐V01 B99‐V02 B99‐V03 B99‐V04 B99‐V05 B99‐V06 B29‐V18‐1' B29‐V19‐1' B99‐SV01‐1' B99‐SV02‐1' B99‐SV03‐1' B99‐SV04‐1' B99‐SV05‐1' B99‐SV06‐1' 5/22/2018 5/22/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 5/25/2018 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) 1 (ft) < 110 < 110 < 110 < 110 < 110 < 110 < 110 < 110
< 44 < 44 < 44 < 44 < 44 < 44 < 44 < 44
< 35 < 35 < 35 < 35 < 35 < 35 < 35 < 35
< 22 < 22 < 22 < 22 < 22 < 22 < 22 < 22
48 99 80 61 64 < 43 82 63
57 < 34 < 34 < 34 < 34 < 34 < 34 < 34
< 38 < 38 < 38 < 38 < 38 < 38 < 38 < 38
< 40 150 < 40 < 40 < 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46 < 46 < 46 < 46 < 46
42 9800 < 27 < 27 < 27 < 27 32 < 27
< 56 < 56 < 56 < 56 < 56 < 56 < 56 < 56
< 77 1900 < 77 < 77 < 77 < 77 < 77 < 77
< 13 < 13 < 13 < 13 < 13 < 13 < 13 < 13
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55
1,1,1‐Trichloroethane
1,1,2,2‐Tetrachloroethane 7
1,1,2‐Trichloroethane 26
1,1‐Dichloroethane 260
1,1‐Dichloroethene
1,1‐Difluoroethane
1,2,4‐Trichlorobenzene
1,2,4‐Trimethylbenzene
1,2‐Dibromoethane (Ethylene Dibromide) 0.68
1,2‐Dichlorobenzene
1,2‐Dichloroethane 16
1,2‐Dichloropropane 41
1,2‐Dichlorotetrafluoroethane (CFC 114)
1,3,5‐Trimethylbenzene
1,3‐Dichlorobenzene
1,4‐Dichlorobenzene 37
2‐Butanone (Methyl Ethyl Ketone)
2‐Hexanone4‐Ethyl toluene
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone)
Benzene 14Bromodichloromethane 11Bromoform 370Bromomethane (Methyl Bromide) Carbon disulfide
Carbon tetrachloride 68
Chlorobenzene
ChloroethaneChloroform (Trichloromethane) 18Chloromethane (Methyl Chloride) cis‐1,2‐Dichloroethene
cis‐1,3‐Dichloropropene
DibromochloromethaneDichlorodifluoromethane (CFC‐12)
Ethylbenzene 160
Vapor ESL:
Commercial/
Industrial Cancer
Risk
B100‐V01 B100‐V02 B100‐V03 B100‐V03
B100‐SV01‐1' B100‐SV02‐1' B100‐SV03‐1' Rep B100‐SV03‐1' 5/25/2018 5/25/2018 5/25/2018 5/25/2018
1 (ft) 1 (ft) 1 (ft) 1 (ft)
< 70 < 70 < 70 < 70
< 28 < 28 < 28 < 28
< 70 < 70 < 70 < 70
< 55 < 55 < 55 < 55
< 41 < 41 < 41 < 41
< 20 < 20 < 20 < 20
< 27 < 27 < 27 < 27
< 75 < 75 < 75 < 75
< 50 < 50 < 50 < 50
< 39 < 39 < 39 < 39
< 61 < 61 < 61 < 61
< 21 < 21 < 21 < 21
< 47 < 47 < 47 < 47
< 71 < 71 < 71 < 71
< 50 < 50 < 50 < 50
< 61 < 61 < 61 < 61
< 61 < 61 < 61 < 61
< 60 < 60 < 60 < 60
< 41 < 41 < 41 < 41
< 50 < 50 < 50 < 50
< 41 < 41 < 41 < 41
< 16 < 16 < 16 < 16
< 68 < 68 < 68 < 68
< 100 < 100 < 100 < 100
< 39 < 39 < 39 < 39
< 32 < 32 < 32 < 32
< 13 < 13 < 13 < 13
< 23 < 23 < 23 < 23
< 27 < 27 < 27 < 27
< 25 < 25 < 25 < 25
< 21 < 21 < 21 < 21
< 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46
< 86 < 86 < 86 < 86
< 50 < 50 < 50 < 50
< 22 < 22 < 22 < 22
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 3
SUMMARY OF SUB‐SLAB SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample NameSample DateSample Depth
VOCs (µg/m3)
Vapor ESL:
Commercial/
Industrial Cancer
Risk
Hexachlorobutadiene 19m,p‐XylenesMethylene chloride 410o‐XyleneStyreneTetrachloroethene 67Toluenetrans‐1,2‐Dichloroethene trans‐1,3‐Dichloropropene
Trichloroethene 100Trichlorofluoromethane (CFC‐11)
Trifluorotrichloroethane (Freon 113)
Vinyl chloride 5.2
Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
B100‐V01 B100‐V02 B100‐V03 B100‐V03
B100‐SV01‐1' B100‐SV02‐1' B100‐SV03‐1' Rep B100‐SV03‐1' 5/25/2018 5/25/2018 5/25/2018 5/25/2018
1 (ft) 1 (ft) 1 (ft) 1 (ft)
< 110 < 110 < 110 < 110
< 44 < 44 < 44 < 44
< 35 < 35 < 35 < 35
< 22 < 22 < 22 < 22
< 43 69 < 43 < 43
< 34 < 34 < 34 < 34
< 38 < 38 < 38 < 38
< 40 < 40 < 40 < 40
< 46 < 46 < 46 < 46
30 < 27 < 27 < 27
< 56 < 56 < 56 < 56
< 77 < 77 < 77 < 77
< 13 < 13 < 13 < 13
HALEY & ALDRICH, INC.
2021_04_HAI_Table 3_Subslab Summary_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location B29‐V01 B29‐V01 B29‐V01 B29‐V02 B29‐V02 B29‐V03 B29‐V04 B29‐V05 B29‐V05 B29‐V06 B29‐V06 B29‐V07 Sample Name B29‐SV01‐5' B29‐SV01‐5' Rep B29‐SV01‐10' B29‐SV02‐5' B29‐SV02‐10' B29‐SV03‐5' B29‐SV04‐5' B29‐SV05‐5' B29‐SV05‐10' B29‐SV06‐5' B29‐SV06‐5' Rep B29‐SV07‐5' start depth 5 5 10 5 10 5 5 5 10 5 5 5
Sample Date 5/24/2018 5/24/2018 5/25/2018 5/24/2018 5/24/2018 5/24/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 Sample Depth 5 (ft) 5 (ft) 10 (ft) 5 (ft) 10 (ft) 5 (ft) 5 (ft) 5 (ft) 10 (ft) 5 (ft) 5 (ft) 5 (ft) VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55 < 70 < 70 < 70 < 700 < 70 < 17000 < 700 < 70 < 70 < 70 < 70 < 70 1,1,1‐Trichloroethane 45 40 < 28 280 < 28 < 6900 < 280 59 37 69 50 140 1,1,2,2‐Tetrachloroethane 7 < 70 < 70 < 70 < 700 < 70 < 17000 < 700 < 70 < 70 < 70 < 70 < 70 1,1,2‐Trichloroethane 26 < 55 < 55 < 55 < 550 < 55 < 14000 < 550 < 55 < 55 < 55 < 55 < 55 1,1‐Dichloroethane 260 < 41 < 41 < 41 < 410 < 41 < 10000 < 410 < 41 < 41 < 41 < 41 < 41 1,1‐Dichloroethene < 20 < 20 < 20 < 200 < 20 < 5000 < 200 < 20 < 20 < 20 < 20 < 20 1,1‐Difluoroethane < 27 < 27 < 27 < 270 < 27 < 6800 < 270 < 27 < 27 < 27 < 27 < 27 1,2,3‐Trichloropropane ‐‐‐‐‐‐‐‐‐‐‐‐
1,2,4‐Trichlorobenzene < 75 < 75 < 75 < 750 < 75 < 19000 < 750 < 75 < 75 < 75 < 75 < 75 1,2,4‐Trimethylbenzene 110 77 < 50 < 500 < 50 < 12000 < 500 < 50 < 50 < 50 < 50 < 50 1,2‐Dibromoethane (Ethylene Dibromide) 0.68 < 39 < 39 < 39 < 390 < 39 < 9700 < 390 < 39 < 39 < 39 < 39 < 39 1,2‐Dichlorobenzene < 61 < 61 < 61 < 610 < 61 < 15000 < 610 < 61 < 61 < 61 < 61 < 61 1,2‐Dichloroethane 16 < 21 < 21 < 21 < 210 < 21 < 5100 < 210 < 21 < 21 < 21 < 21 < 21 1,2‐Dichloropropane 41 < 47 < 47 < 47 < 470 < 47 < 12000 < 470 < 47 < 47 < 47 < 47 < 47 1,2‐Dichlorotetrafluoroethane (CFC 114) < 71 < 71 < 71 < 710 < 71 < 18000 < 710 < 71 < 71 < 71 < 71 < 71 1,3,5‐Trimethylbenzene < 50 < 50 < 50 < 500 < 50 < 12000 < 500 < 50 < 50 < 50 < 50 < 50 1,3‐Butadiene ‐‐‐‐‐‐‐‐‐‐‐‐
1,3‐Dichlorobenzene < 61 < 61 < 61 < 610 < 61 < 15000 < 610 < 61 < 61 < 61 < 61 < 61 1,4‐Dichlorobenzene 37 < 61 < 61 < 61 < 610 < 61 < 15000 < 610 < 61 < 61 < 61 < 61 < 61 1,4‐Dioxane 53 ‐‐‐‐‐‐‐‐‐‐‐‐
2,2,4‐Trimethylpentane ‐‐‐‐‐‐‐‐‐‐‐‐
2‐Butanone (Methyl Ethyl Ketone) 77 < 60 < 60 < 600 79 < 15000 < 600 < 60 < 60 < 60 < 60 < 60 2‐Hexanone < 41 < 41 < 41 < 410 < 41 < 10000 < 410 < 41 < 41 < 41 < 41 < 41 2‐Phenylbutane (sec‐Butylbenzene) ‐‐‐‐‐‐‐‐‐‐‐‐
4‐Ethyl toluene 100 < 50 < 50 < 500 < 50 < 12000 < 500 < 50 < 50 < 50 < 50 < 50 4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone) < 41 < 41 < 41 < 410 < 41 < 10000 < 410 < 41 < 41 < 41 < 41 < 41 Acetone ‐‐‐‐‐‐‐‐‐‐‐‐Allyl chloride ‐‐‐‐‐‐‐‐‐‐‐‐
Benzene 14 130 140 < 16 950 41 < 4000 < 160 78 31 34 29 69 Benzyl Chloride ‐‐‐‐‐‐‐‐‐‐‐‐Bromodichloromethane 11 < 68 < 68 < 68 < 680 < 68 < 17000 < 680 < 68 < 68 < 68 < 68 < 68 Bromoform 370 < 100 < 100 < 100 < 1000 < 100 < 26000 < 1000 < 100 < 100 < 100 < 100 < 100 Bromomethane (Methyl Bromide) < 39 < 39 < 39 < 390 < 39 < 9900 < 390 < 39 < 39 < 39 < 39 < 39 Carbon disulfide 130 140 < 32 1300 < 32 < 7900 < 320 < 32 < 32 < 32 < 32 < 32 Carbon tetrachloride 68 < 13 < 13 < 13 < 130 < 13 < 3200 < 130 < 13 < 13 < 13 < 13 < 13 Chlorobenzene < 23 < 23 < 23 < 230 < 23 < 5900 < 230 < 23 < 23 < 23 < 23 < 23 Chloroethane < 27 < 27 < 27 < 270 < 27 < 6700 < 270 < 27 < 27 < 27 < 27 < 27 Chloroform (Trichloromethane) 18 56 48 56 < 250 < 25 39000 < 250 < 25 < 25 < 25 < 25 1500 Chloromethane (Methyl Chloride) < 21 < 21 < 21 < 210 < 21 < 5200 < 210 < 21 < 21 < 21 < 21 < 21 cis‐1,2‐Dichloroethene < 40 < 40 < 40 < 400 < 40 < 10000 < 400 < 40 < 40 < 40 < 40 < 40 Vapor ESL:
Commercial/
Industrial Cancer Risk
HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location B29‐V01 B29‐V01 B29‐V01 B29‐V02 B29‐V02 B29‐V03 B29‐V04 B29‐V05 B29‐V05 B29‐V06 B29‐V06 B29‐V07 Sample Name B29‐SV01‐5' B29‐SV01‐5' Rep B29‐SV01‐10' B29‐SV02‐5' B29‐SV02‐10' B29‐SV03‐5' B29‐SV04‐5' B29‐SV05‐5' B29‐SV05‐10' B29‐SV06‐5' B29‐SV06‐5' Rep B29‐SV07‐5' start depth 5 5 10 5 10 5 5 5 10 5 5 5
Sample Date 5/24/2018 5/24/2018 5/25/2018 5/24/2018 5/24/2018 5/24/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 5/23/2018 Sample Depth 5 (ft) 5 (ft) 10 (ft) 5 (ft) 10 (ft) 5 (ft) 5 (ft) 5 (ft) 10 (ft) 5 (ft) 5 (ft) 5 (ft) Vapor ESL:
Commercial/
Industrial Cancer Risk
VOCs (µg/m3)
cis‐1,3‐Dichloropropene < 46 < 46 < 46 < 460 < 46 < 12000 < 460 < 46 < 46 < 46 < 46 < 46 Cyclohexane ‐‐‐‐‐‐‐‐‐‐‐‐Cymene (p‐Isopropyltoluene) ‐‐‐‐‐‐‐‐‐‐‐‐ Dibromochloromethane < 86 < 86 < 86 < 860 < 86 < 22000 < 860 < 86 < 86 < 86 < 86 < 86 Dichlorodifluoromethane (CFC‐12) < 50 < 50 < 50 < 500 < 50 < 13000 < 500 < 50 < 50 < 50 < 50 < 50 Ethyl acetate ‐‐‐‐‐‐‐‐‐‐‐‐
Ethylbenzene 160 160 120 25 780 37 < 5500 < 220 41 < 22 < 22 23 < 22 Hexachlorobutadiene 19 < 110 < 110 < 110 < 1100 < 110 < 27000 < 1100 < 110 < 110 < 110 < 110 < 110 Hexane ‐‐‐‐‐‐‐‐‐‐‐‐
Isobutane ‐‐‐‐‐‐‐‐‐‐‐‐Isopropyl Alcohol (2‐Propanol) ‐‐‐‐‐‐‐‐‐‐‐‐ Isopropylbenzene (Cumene) ‐‐‐‐‐‐‐‐‐‐‐‐
m,p‐Xylenes 550 410 61 1900 74 < 11000 < 440 140 < 44 < 44 < 44 64 Methyl Tert Butyl Ether 1600 ‐‐‐‐‐‐‐‐‐‐‐‐
Methylene chloride 410 < 35 < 35 < 35 < 350 < 35 < 8800 < 350 < 35 < 35 < 35 < 35 < 35 Naphthalene 12 ‐‐‐‐‐‐‐‐‐‐‐‐N‐Heptane ‐‐‐‐‐‐‐‐‐‐‐‐
n‐Propylbenzene ‐‐‐‐‐‐‐‐‐‐‐‐
o‐Xylene 140 110 27 640 28 < 5500 < 220 38 < 22 < 22 < 22 < 22 Propylene (Propene) ‐‐‐‐‐‐‐‐‐‐‐‐
Styrene 200 230 78 2100 110 < 11000 < 430 < 43 110 120 100 < 43 Tetrachloroethene 67 83 61 36 780 84 < 8600 430 160 180 < 34 < 34 11000 Tetrahydrofuran ‐‐‐‐‐‐‐‐‐‐‐‐Toluene 700 590 100 3900 170 < 9500 < 380 280 84 98 81 230trans‐1,2‐Dichloroethene < 40 < 40 < 40 < 400 < 40 < 10000 < 400 < 40 < 40 < 40 < 40 < 40 trans‐1,3‐Dichloropropene < 46 < 46 < 46 < 460 < 46 < 12000 < 460 < 46 < 46 < 46 < 46 < 46 Trichloroethene 100 450 450 3400 1500 64 3000000 27000 < 27 < 27 120 100 51000 Trichlorofluoromethane (CFC‐11) < 56 < 56 < 56 < 560 < 56 < 14000 < 560 < 56 < 56 < 56 < 56 < 56 Trifluorotrichloroethane (Freon 113) < 77 < 77 < 77 < 770 < 77 < 19000 < 770 < 77 < 77 < 77 < 77 < 77 Vinyl acetate ‐‐‐‐‐‐‐‐‐‐‐‐
Vinyl Bromide (Bromoethene) ‐‐‐‐‐‐‐‐‐‐‐‐
Vinyl chloride 5.2 < 13 < 13 < 13 < 130 < 13 < 3200 < 130 < 13 < 13 < 13 < 13 < 13 Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Namestart depth
Sample DateSample Depth
VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55
1,1,1‐Trichloroethane1,1,2,2‐Tetrachloroethane 7
1,1,2‐Trichloroethane 26
1,1‐Dichloroethane 260
1,1‐Dichloroethene
1,1‐Difluoroethane
1,2,3‐Trichloropropane
1,2,4‐Trichlorobenzene1,2,4‐Trimethylbenzene1,2‐Dibromoethane (Ethylene Dibromide) 0.68 1,2‐Dichlorobenzene
1,2‐Dichloroethane 16
1,2‐Dichloropropane 41
1,2‐Dichlorotetrafluoroethane (CFC 114)
1,3,5‐Trimethylbenzene
1,3‐Butadiene
1,3‐Dichlorobenzene
1,4‐Dichlorobenzene 37
1,4‐Dioxane 53
2,2,4‐Trimethylpentane
2‐Butanone (Methyl Ethyl Ketone)
2‐Hexanone2‐Phenylbutane (sec‐Butylbenzene)
4‐Ethyl toluene
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone)
AcetoneAllyl chlorideBenzene 14Benzyl ChlorideBromodichloromethane 11Bromoform 370Bromomethane (Methyl Bromide)Carbon disulfide Carbon tetrachloride 68
ChlorobenzeneChloroethaneChloroform (Trichloromethane) 18Chloromethane (Methyl Chloride) cis‐1,2‐Dichloroethene
Vapor ESL:
Commercial/
Industrial Cancer Risk
B29‐V08 B29‐V08 PW‐01B PW‐02 PW‐03 PW‐03 PW‐04 PW‐05 PW‐06 PW‐07 PW‐08 PW‐09 B29‐SV08‐5' B29‐SV08‐10' PW01B‐SV‐5 PW02‐SV‐5 PW03‐SV‐5 PW03‐SV‐5DUP PW04‐SV‐5 PW05‐SV‐4 PW06‐SV‐3.5 PW07‐SV‐4 PW08‐SV‐5 PW09‐SV‐4.5 5 10 5 5 5 5 5 4 3.5 4 5 4.5
5/24/2018 5/24/2018 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/30/2020 5 (ft) 10 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 4 ‐ 4 (ft) 3.5 ‐ 3.5 (ft) 4 ‐ 4 (ft) 5 ‐ 5 (ft) 4.5 ‐ 4.5 (ft) < 1400 < 1400 ‐‐‐‐‐‐‐‐‐‐
< 550 < 550 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 38 < 16 120 < 1400 < 1400 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1100 < 1100 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 820 < 820 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 400 < 400 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 550 < 550 ‐‐‐‐‐‐‐‐‐‐
‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1500 < 1500 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1000 < 1000 610 < 2400 < 2400 < 2400 110 < 2400 600 120 530 140 < 780 < 780 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1200 < 1200 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 410 < 410 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 940 < 940 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1400 < 1400 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1000 < 1000 220 < 2400 < 2400 < 2400 48 < 2400 < 400 48 270 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1200 < 1200 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1200 < 1200 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1200 < 1200 < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 < 830 < 830 < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1000 < 1000 130 < 2400 < 2400 < 2400 26 < 2400 < 400 22 160 < 80 < 830 < 830 < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 ‐‐ < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 320 < 320 < 16 < 2400 < 2400 < 2400 38 < 2400 < 400 < 16 75 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1400 < 1400 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 140 < 2100 < 2100 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 790 < 790 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 630 < 630 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 260 < 260 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 470 < 470 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 540 < 540 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 490 < 490 < 16 18000 6800 7100 52 16000 1600 160 32 410 < 410 < 410 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 800 < 800 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Namestart depth
Sample DateSample Depth
Vapor ESL:
Commercial/
Industrial Cancer Risk
VOCs (µg/m3)
cis‐1,3‐Dichloropropene
CyclohexaneCymene (p‐Isopropyltoluene)
DibromochloromethaneDichlorodifluoromethane (CFC‐12)
Ethyl acetate
Ethylbenzene 160Hexachlorobutadiene 19HexaneIsobutaneIsopropyl Alcohol (2‐Propanol)Isopropylbenzene (Cumene) m,p‐Xylenes
Methyl Tert Butyl Ether 1600
Methylene chloride 410Naphthalene 12N‐Heptane
n‐Propylbenzeneo‐XylenePropylene (Propene)
StyreneTetrachloroethene 67TetrahydrofuranToluenetrans‐1,2‐Dichloroethenetrans‐1,3‐DichloropropeneTrichloroethene 100Trichlorofluoromethane (CFC‐11) Trifluorotrichloroethane (Freon 113)
Vinyl acetateVinyl Bromide (Bromoethene)
Vinyl chloride 5.2
Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
B29‐V08 B29‐V08 PW‐01B PW‐02 PW‐03 PW‐03 PW‐04 PW‐05 PW‐06 PW‐07 PW‐08 PW‐09 B29‐SV08‐5' B29‐SV08‐10' PW01B‐SV‐5 PW02‐SV‐5 PW03‐SV‐5 PW03‐SV‐5DUP PW04‐SV‐5 PW05‐SV‐4 PW06‐SV‐3.5 PW07‐SV‐4 PW08‐SV‐5 PW09‐SV‐4.5 5 10 5 5 5 5 5 4 3.5 4 5 4.5
5/24/2018 5/24/2018 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/31/2020 7/30/2020 5 (ft) 10 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 5 ‐ 5 (ft) 4 ‐ 4 (ft) 3.5 ‐ 3.5 (ft) 4 ‐ 4 (ft) 5 ‐ 5 (ft) 4.5 ‐ 4.5 (ft) < 920 < 920 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ 79 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 80 < 80 < 1700 < 1700 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1000 < 1000 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 440 < 440 150 < 2400 < 2400 < 2400 78 < 2400 < 400 28 340 < 80 < 2100 < 2100 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 33 < 80 < 880 < 880 670 < 2400 < 2400 < 2400 320 < 2400 1100 130 1300 200 ‐‐ < 40 < 6000 < 6000 < 6000 < 40 < 6000 < 1000 < 40 < 40 < 200 < 710 < 710 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ 80 < 2400 < 2400 < 2400 20 < 2400 < 400 < 16 120 < 80 < 440 < 440 240 < 2400 < 2400 < 2400 82 < 2400 < 400 40 360 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 860 < 860 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 2200 1600 < 16 < 2400 < 2400 < 2400 47 5800 < 400 330 96 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 760 < 760 230 < 2400 < 2400 < 2400 260 < 2400 510 51 670 150 < 800 < 800 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 920 < 920 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 2100 1500 140 2900000 1100000 1100000 1400 2400000 160000 7600 54 14000 < 1100 < 1100 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 1500 < 1500 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 ‐‐ < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 < 260 < 260 < 16 < 2400 < 2400 < 2400 < 16 < 2400 < 400 < 16 < 16 < 80 HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Namestart depth
Sample DateSample Depth
VOCs (µg/m3)
1,1,1,2‐Tetrachloroethane 55
1,1,1‐Trichloroethane1,1,2,2‐Tetrachloroethane 7
1,1,2‐Trichloroethane 26
1,1‐Dichloroethane 260
1,1‐Dichloroethene
1,1‐Difluoroethane
1,2,3‐Trichloropropane
1,2,4‐Trichlorobenzene1,2,4‐Trimethylbenzene1,2‐Dibromoethane (Ethylene Dibromide) 0.68 1,2‐Dichlorobenzene
1,2‐Dichloroethane 16
1,2‐Dichloropropane 41
1,2‐Dichlorotetrafluoroethane (CFC 114)
1,3,5‐Trimethylbenzene
1,3‐Butadiene
1,3‐Dichlorobenzene
1,4‐Dichlorobenzene 37
1,4‐Dioxane 53
2,2,4‐Trimethylpentane
2‐Butanone (Methyl Ethyl Ketone)
2‐Hexanone2‐Phenylbutane (sec‐Butylbenzene)
4‐Ethyl toluene
4‐Methyl‐2‐Pentanone (Methyl Isobutyl Ketone)
AcetoneAllyl chlorideBenzene 14Benzyl ChlorideBromodichloromethane 11Bromoform 370Bromomethane (Methyl Bromide)Carbon disulfide Carbon tetrachloride 68
ChlorobenzeneChloroethaneChloroform (Trichloromethane) 18Chloromethane (Methyl Chloride) cis‐1,2‐Dichloroethene
Vapor ESL:
Commercial/
Industrial Cancer Risk
PW‐11 PW‐12 PW‐13 PW‐14 PW‐14 PW‐15 PW‐16
PW11‐SV‐3 PW12‐SV‐3 PW13‐SV‐4 PW14‐SV‐4 PW14‐SV‐4DUP PW15‐SV‐4.5 PW16‐SV‐5 3 3 4 4 4 4.5 5
7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 3 ‐ 3 (ft) 3 ‐ 3 (ft) 4 ‐ 4 (ft) 4 ‐ 4 (ft) 4 ‐ 4 (ft) 4.5 ‐ 4.5 (ft) 5 ‐ 5 (ft) ‐‐‐‐‐‐‐
< 2< 2 12 < 800 < 1600 1100 35
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
‐‐‐‐‐‐‐
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
110 400 500 < 800 < 1600 < 200 490
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
67 180 180 < 800 < 1600 < 200 180
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2 12 3.9 < 800 < 1600 < 200 < 2
< 5< 5< 5< 2000 < 4000 < 500 < 5
< 5< 5< 5< 2000 < 4000 < 500 < 5
< 2 8.1 < 2< 800 < 1600 < 200 4.5
29 110 94 < 800 < 1600 < 200 55
< 5< 5< 5< 2000 < 4000 < 500 < 5
51 59 43 < 2000 < 4000 < 500 < 5
< 2< 2< 2< 800 < 1600 < 200 < 2
10 36 8 < 800 < 1600 < 200 7.6
< 2< 2 9.8 < 800 < 1600 < 200 < 2
16 17 < 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
14 20 26 < 800 < 1600 < 200 5.8
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2 3.8 4300 4400 < 200 < 2
HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 4
SUMMARY OF DEEPER SOIL VAPOR DATA
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
LocationSample Namestart depth
Sample DateSample Depth
Vapor ESL:
Commercial/
Industrial Cancer Risk
VOCs (µg/m3)
cis‐1,3‐Dichloropropene
CyclohexaneCymene (p‐Isopropyltoluene)
DibromochloromethaneDichlorodifluoromethane (CFC‐12)
Ethyl acetate
Ethylbenzene 160Hexachlorobutadiene 19HexaneIsobutaneIsopropyl Alcohol (2‐Propanol)Isopropylbenzene (Cumene) m,p‐Xylenes
Methyl Tert Butyl Ether 1600
Methylene chloride 410Naphthalene 12N‐Heptane
n‐Propylbenzeneo‐XylenePropylene (Propene)
StyreneTetrachloroethene 67TetrahydrofuranToluenetrans‐1,2‐Dichloroethenetrans‐1,3‐DichloropropeneTrichloroethene 100Trichlorofluoromethane (CFC‐11) Trifluorotrichloroethane (Freon 113)
Vinyl acetateVinyl Bromide (Bromoethene)
Vinyl chloride 5.2
Notes:
Volatile Organic Compounds (VOCs) analyzed by EPA Method TO‐15.
BOLD = concentration detected at or above reported detection limit, 2019 San Francisco Bay Regional Water Quality Control Board Vapor ESLs Cells shaded gray = concentration detected at or above the Vapor ESL Abbreviations:
< = analyte not detected above the indicated reporting limit. ‐ = not analyzed or not applicable.
ESL = Environmental Screening Level
µg/m3 = micrograms per cubic meter.
PW‐11 PW‐12 PW‐13 PW‐14 PW‐14 PW‐15 PW‐16
PW11‐SV‐3 PW12‐SV‐3 PW13‐SV‐4 PW14‐SV‐4 PW14‐SV‐4DUP PW15‐SV‐4.5 PW16‐SV‐5 3 3 4 4 4 4.5 5
7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 7/30/2020 3 ‐ 3 (ft) 3 ‐ 3 (ft) 4 ‐ 4 (ft) 4 ‐ 4 (ft) 4 ‐ 4 (ft) 4.5 ‐ 4.5 (ft) 5 ‐ 5 (ft) < 2< 2< 2< 800 < 1600 < 200 < 2
< 2 3.6 < 2< 800 < 1600 < 200 < 2
8.8 63 53 < 800 < 1600 < 200 27
12 9.5 < 2< 800 < 1600 < 200 < 2
< 2< 2 17 < 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
50 150 81 < 800 < 1600 < 200 61
< 2< 2< 2< 800 < 1600 < 200 < 2
5.9 11 3.6 < 800 < 1600 < 200 < 25.1 < 2< 2< 800 < 1600 < 200 < 2 < 5< 5< 5< 2000 < 4000 < 500 < 5
5.9 20 11 < 800 < 1600 < 200 7.7
160 710 400 < 800 < 1600 < 200 310
< 5< 5< 5< 2000 < 4000 < 500 < 5
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 6.3
4.9 12 4.2 < 800 < 1600 < 200 < 2
19 87 59 < 800 < 1600 < 200 36
70 200 140 < 800 < 1600 < 200 99
7.5 30 < 2< 800 < 1600 < 200 < 2
14 19 < 2< 800 < 1600 < 200 10
16 1500 4.7 < 800 < 1600 < 200 16
< 2< 2< 2< 800 < 1600 < 200 < 2
89 350 98 < 800 < 1600 < 200 120
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
5.9 35 91 64000 64000 13000 25
< 2< 2 94 < 800 < 1600 < 200 6.7
5.6 < 2< 2< 800 < 1600 740 72
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
< 2< 2< 2< 800 < 1600 < 200 < 2
HALEY & ALDRICH, INC.
2021_04_HAI_Table 4_Analytical_SV_F.xlsx APRIL 2021
TABLE 5
INDOOR AIR SCREENING RESULTS ‐ BREATHING ZONE IN BUILDING 29 ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Screening
Location Location Description TVOC1 (ppbv) TCE2 (µg/m3) TVOC1 (ppbv) TCE2 (µg/m3) Comments V03 Occupied northern portion of building, Column 18/19 50‐500 114 50‐500 4.2 Utility trench nearby, adjacent to crack in slab
(sealed prior to February), flammables storage
cabinets nearby, organic odors, vaulted floor
along northern wall. Rollup door open in
September and closed in February. In February,
TCE was remeasured two days later (121 µg/m3).
V03‐020 Occupied northern portion of building, Column 18/19 500‐5,000 ‐‐ 50‐500 ‐‐ Crack next to flammables cabinet V03‐021 Dock, Column 19 10‐50 ‐‐ 50‐500 ‐‐
V04 Occupied northern portion of building, Column 18/19 50‐500 40 50‐500 5.5 Utility trench nearby, wall fans operating, vaulted
floor along northern wall. Rollup door open in
September and closed in February. In February,
TCE was remeasured two days later (31 µg/m3).
NDT1 Occupied northern portion of building, Column 16/17 50‐500 4.7 50‐500 0.16 Passive roof wind turbine, flammables storage cabinet nearby.
V05‐027 Machine Shop, Column 17 50‐500 ‐‐ 50‐500 ‐‐
V05‐028
Outside hallway to women's
restroom, Column 15 50‐500 ‐‐ 50‐500 ‐‐
V05‐029 Hallway outside men's
restroom, Column 15 500‐5,000 2.8 500‐5,000 0.25
Stuffy, drop ceiling, slight organic odor. Exhaust
fans on in men's restroom. Near metallurgy lab
and utility room.
February 2019 September 2018
HALEY & ALDRICH, INC.
2021_04_HAI_Table 5 & 6_Bldg 29_Indoor_Air_Screening_F.xlsx APRIL 2021 TABLE 5
INDOOR AIR SCREENING RESULTS ‐ BREATHING ZONE IN BUILDING 29 ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Screening
Location Location Description TVOC1 (ppbv) TCE2 (µg/m3) TVOC1 (ppbv) TCE2 (µg/m3) Comments February 2019 September 2018
V06‐025 Machine Shop, Column 16 50‐500 ‐‐ 50‐500 ‐‐
V07 Occupied northern portion of building, Column 17 50‐500 5.2 50‐500 1.4 Organic odors, rollup door open in September and closed in February.
V08‐018
Detail Fab Shop spray booth
area, Column 16 50‐500 8.6 50‐500 1.8
Rollup door open in September and closed in
February. Sample collected from breathing zone
above metal plate labeled "drain." Hole was
welded shut prior to February sampling. In
February, TCE was remeasured two days later
(6.2 µg/m3).
V09M Vacant, Column 16 50‐500 5.3 50‐500 0.023 Rollup door closed, passive roof ventilation only. 14‐29‐20 Vacant, Column 15 50‐500 6.7 50‐500 <0.54
Rollup door closed, passive roof ventilation only.
In February, hydraulic oil drum storage near
sampling location.
V10‐015 NDT Lab, Column 16/17 50‐500 ‐‐ 50‐500 ‐‐
V11‐012 Vacant, Column 12 10‐50 ‐‐ 50‐500 ‐‐ Above expansion joint V12‐008 Mezzanine A, Column 1/2 <10 ‐‐ 50‐500 ‐‐
V13 Vacant, Column 12 10‐50 5.9 50‐500 0.024 Rollup door closed, passive roof ventilation only.
V14 Vacant, Column 8/9 10‐50 1.8 50‐500 0.024 Rollup door closed, passive roof ventilation only.
V15‐009 Vacant, Column 7 10‐50 ‐‐ 50‐500 ‐‐
V16 Vacant, Column 4/5 <10 1.6 50‐500 0.019 Rollup door closed, passive roof ventilation only.
V17‐003 Vacant, Column 4 10‐50 ‐‐ 50‐500 ‐‐
V17‐004 Vacant, Column 4 10‐50 ‐‐ 50‐500 ‐‐
HALEY & ALDRICH, INC.
2021_04_HAI_Table 5 & 6_Bldg 29_Indoor_Air_Screening_F.xlsx APRIL 2021 TABLE 5
INDOOR AIR SCREENING RESULTS ‐ BREATHING ZONE IN BUILDING 29 ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Screening
Location Location Description TVOC1 (ppbv) TCE2 (µg/m3) TVOC1 (ppbv) TCE2 (µg/m3) Comments February 2019 September 2018
V17‐006 Mezzanine A, Column 1/2 <10 ‐‐ 50‐500 ‐‐
V17‐007 Mezzanine A, Column 1 <10 ‐‐ 50‐500 ‐‐
F3/UV Storage/Vacant, Column 2/3 <10 1.6 50‐500 0.016 Indoor fans operating in September but off in February.
V18‐001 Column B/C‐2/3 10‐50 ‐‐ 50‐500 ‐‐
V19 Vacant, Column 3 10‐50 1.5 50‐500 0.012
Rollup door intermittently opened in September
but closed in February. Organic odors noted in
February.
B29‐052 Metallurgy lab, fume hood
area, Column B/C‐16 50‐500 2.2 >5,000 2.0 Fume hood fan operating.
B29‐053 Metallurgy lab, tile walkway, Column C‐16 50‐500 2.0 >5,000 ‐‐ B29‐054 Occupied northern portion of building, Column G/H‐17 50‐500 9.5 ‐‐ ‐‐ Rollup door closed B29‐055 Occupied northern portion of building, Column I/J‐18 50‐500 37 ‐‐ ‐‐ Rollup door closed B29‐056 Occupied northern portion of building, Near Door 29‐B 50‐500 19 ‐‐ ‐‐ Rollup door closed B29‐057 Occupied northern portion of building, Column E‐18 50‐500 4.8 ‐‐ ‐‐ Rollup door closed HALEY & ALDRICH, INC.
2021_04_HAI_Table 5 & 6_Bldg 29_Indoor_Air_Screening_F.xlsx APRIL 2021 TABLE 5
INDOOR AIR SCREENING RESULTS ‐ BREATHING ZONE IN BUILDING 29 ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Screening
Location Location Description TVOC1 (ppbv) TCE2 (µg/m3) TVOC1 (ppbv) TCE2 (µg/m3) Comments February 2019 September 2018
B29‐OUT01
Ambient outdoor air,
near Door 29‐15
<10 0.75 <10 0.031
B29‐OUT02
Ambient outdoor air,
near Door 29‐21
<10 0.23 <10 0.35
B29‐OUT02
Ambient outdoor air,
near Door 29‐21
10‐50 1.2 <10 0.19
B29‐OUT02
Ambient outdoor air,
near Door 29‐21
‐‐ ‐‐ <10 1.1
B29‐OUT03
Ambient outdoor air,
near Door 29‐19
50‐500 0.50 ‐‐ ‐‐
Notes:µg/m3 = micrograms per cubic meter
ppbv = parts per billion by volume
1TVOC = total volatile organic compounds measured using ppbRAE Photoionization Detector2TCE = trichloroethene measured using HAPSITE Mass Spectrometer/Gas Chromatograph Bold and gray shading indicates that the TCE concentration is greater than or equal to the US EPA Region 9 Interim TCE Indoor Air Response Level
TCE concentrations less than 0.54 µg/m3 or greater than 107 µg/m3 are outside the instrument's calibration range and should be considered estimated.
Ambient Outdoor Air
HALEY & ALDRICH, INC.
2021_04_HAI_Table 5 & 6_Bldg 29_Indoor_Air_Screening_F.xlsx APRIL 2021 TABLE 6
INDOOR AIR SCREENING RESULTS ‐ PREFERENTIAL PATHWAYS IN BUILDING 29 ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Screening
Location Location Description TVOC1 (ppbv) TCE2 (µg/m3) TVOC1 (ppbv) TCE2 (µg/m3) Comments V03‐019 Occupied northern portion of building, Column 18/19 >5,000 121 500‐5,000 599 Sample collected inside crack in slab. Crack was sealed prior to February sampling. Rollup door closed in February. In February, TCE was remeasured two days later (72 µg/m3).
V03‐022 Dock, Column 19 10‐50 ‐‐ 50‐500 ‐‐
V03‐023 Dock, Column 19 10‐50 ‐‐ 50‐500 ‐‐
V03‐024 Dock, Column 19 10‐50 ‐‐ 50‐500 ‐‐
V06‐026 Machine Shop, Column 16 50‐500 ‐‐ 50‐500 ‐‐ Floor drainV08‐017 Detail Fab Shop spray booth
area, Column 16 50‐500 9.6 500‐5,000 352
Sample collected inside hole in metal plate labeled "drain." Hole was welded closed prior to February 2019 sampling. Rollup door closed. In February, TCE was remeasured two days later (6.0 µg/m3).
V10‐016 NDT Lab, Column 16 50‐500 ‐‐ 50‐500 ‐‐ Along base of wall V11‐013 Vacant, Column 12 10‐50 ‐‐ 50‐500 ‐‐ Floor utility box V11‐014 Vacant, Column 15/16 50‐500 ‐‐ 50‐500 ‐‐ Floor trench V12‐010 Vacant, Column 9 10‐50 ‐‐ 50‐500 ‐‐ Floor drain V12‐011 Vacant, Column 9 10‐50 ‐‐ 50‐500 ‐‐ Expansion joint V17‐005 Vacant, Column 4 10‐50 ‐‐ 50‐500 ‐‐ Expansion joint V18‐002 Column C/D‐3 10‐50 ‐‐ 50‐500 ‐‐
B29‐051 Metallurgy lab, fume hood sink drain, Column B/C‐16 50‐500 2.2 >5,000 1.6 Fume hood fan operating Notes:µg/m3 = micrograms per cubic meter
ppbv = parts per billion by volume
1TVOC = total volatile organic compounds measured using ppbRAE Photoionization Detector2TCE = trichloroethene measured using HAPSITE Mass Spectrometer/Gas Chromatograph TCE concentrations less than 0.54 µg/m3 or greater than 107 µg/m3 are outside the instrument's calibration range and should be considered estimated.
February 2019 September 2018
HALEY & ALDRICH, INC.
2021_04_HAI_Table 5 & 6_Bldg 29_Indoor_Air_Screening_F.xlsx APRIL 2021 TABLE 7
SUMMARY OF VADOSE SOIL SCREENING CRITERIA EXCEEDANCES
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
GPL DTSC‐SL Commercial/Industrial1 TTLC
B29‐02 As
B29‐03 As
B29‐03A As
B29‐03B As
B29‐05 PCBs
B29‐07 As
B29‐07A As
B29‐07B As
B29‐12 DahA
B29‐23 TCE TCE
B29‐24 TCE
BB‐23 DDE
UT‐02* PCBs
UT‐03* As
UT‐18* BaP, DahA
UT‐21* BaP, DahA
UT‐66* BaP, DahA
Total No. of Locations Above
Screening Criterion 2 15 1
Notes:
No other VOCs, SVOCs, OCPs, or metals were above their respective screening criteria.
GPL = Groundwater Protection Level
DTSC‐SL = Department of Toxic Substances Control Screening Level TTLC = Total Threshold Limit Concentration
BaP = Benzo(a)pyrene
DahA = Dibenz(a,h)anthracene
DDE = 4,4'‐DDE
TCE = Trichloroethene
1 Arsenic is compared to background established for the Former South Campus (8 mg/kg).
COPC Concentration Above Screening Criterion
PCBs = Total Polychorinated Biphenyls
Boring ID
As = Arsenic
* Boring not located on Rohr property (adjacent railroad right‐of‐way).
HALEY & ALDRICH, INC.
2021_04_HAI_Table 7_Summary COPCs Soil_F.xlsx APRIL 2021 TABLE 8
SUMMARY OF SUB‐SLAB/SOIL VAPOR ESL EXCEEDANCES
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location TCE PCE Chloroform Benzene BDCM Ethylbenzene
B29‐V03 ●● ● ●
B29‐V04 ●●
B29‐V05 ●●
B29‐V07 ●● ●
B29‐V08 ●●
B29‐V09 ●● ●
B29‐V10 ●
B29‐V16 ●●
B29‐V19 ●
Total No. of Sub‐Slab
Above Vapor ESL 87 3 20 0
B29‐V01 ●● ● ●
B29‐V02 ●● ●
B29‐V03 ●●
B29‐V04 ●
B29‐V05 ●
B29‐V06 ●●
B29‐V07 ●● ● ●
B29‐V08 ●●
Sub‐Slab Soil Vapor:
Deeper Soil Vapor:
HALEY & ALDRICH, INC.
2021_04_HAI_Table 8_Summary COPCs Soil_F.xlsx APRIL 2021 TABLE 8
SUMMARY OF SUB‐SLAB/SOIL VAPOR ESL EXCEEDANCES
ROHR, INC. ‐ PARCEL A
CHULA VISTA, CALIFORNIA
Location TCE PCE Chloroform Benzene BDCM Ethylbenzene
PW‐01B ●
PW‐02 ●●
PW‐03 ●●
PW‐04 ● ●●
PW‐05 ●● ●
PW‐06 ●●
PW‐07 ●● ●
PW‐08 ●●
PW‐09 ● ●●
PW‐11 ●●
PW‐12 ● ● ●●
PW‐14 ●
PW‐15 ●
Total No. of Deeper
Vapor Above Vapor ESL 15 8 12 8 3 1
Notes:TCE = TrichloroethenePCE = Tetrachlorethene
BDCM = BromodichloromethaneVapor ESL: San Francisco Bay Regional Water Quality Control Board’s commercial/industrial sub‐slab/soil gas Vapor Environmental Screening Level, 2019 (Rev. 2)
Deeper Soil Vapor:
HALEY & ALDRICH, INC.
2021_04_HAI_Table 8_Summary COPCs Soil_F.xlsx APRIL 2021
FIGURES
ROHR, INC., A COLLINS AEROSPACE COMPANY
NORTH CAMPUS - PARCEL A
CHULA VISTA, CALIFORNIA
SITE LOCUS
APPROXIMATE SCALE: 1 IN = 2,000 FT
MARCH 2021 FIGURE 1
\\haleyaldrich.com\share\sdg_common\43559_North Campus\000_Global\GIS\Maps\2021_03\127827_023_0001_SITE_LOCUS.mxd SITE
MAP SOURCE: ESRI
USGS QUAD: NATIONAL CITY, IMPERIAL BEACH
SITE COORDINATES: 32°38'03.8"N, 117°05'56.9"W
SAN DIEGO PUMPS
& COMPRESSOR
SUPPLY
368 BAY
FORMER SHALLOW SWALE (1948)
161 161
3-09596 3-09596
148 148147 147146 146
145 145
161 161
301 301
300 300
JACKSON'S
IMPORT AUTO
350-360 BAY
SAN DIEGO PUMP
& COMPRESSOR SUPPLY
364-368 BAY
MAINTENANCE
DEPARTMENT
FORMER
FORMER TRUCK
ENGINE REPAIR
100
99 29
G
S
T
REET
INTERSTATE 5
BAY BOULEVARD
FORMER
LUMBER YARD
(1948)
FORMER
AGRICULTURE - CITRUS
(1948)
VAULT (4 FEET BGS)
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
304A
304C 304C
304B
304D
204 204
200 200
226 226
202 202 201 201
203 203
56702233
56701007
56702217
56702228
57133030
57133024
56702230
56702231
57133016
57133003
57133029
56702216
ROHR, INC., A COLLINS AEROSPACE COMPANY
NORTH CAMPUS - PARCEL A
CHULA VISTA, CALIFORNIA
FIGURE 2 SCALE: AS SHOWN
APRIL 2021
0 125 250
SCALE IN FEET
GIS FILE PATH: G:\43559_North Campus\000_Global\GIS\Maps\2021_03\127827_023_0002_HISTORICAL_FEATURES_LOCATIONS.mxd - USER: dfm - LAST SAVED: 4/29/2021 3:11:04 PM LEGEND
FORMER MILLS/LATHES
FORMER VESSELS AND VAULTS
UST (UNDERGROUND STORAGE TANK)
BASED ON DEH EVALUATION OF CCR
TITLE 23. CLOSED THROUGH REMOVAL OR
FILLING.
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND STORAGE TANK)
PAINT BOOTH
DEGREASER
STORM WATER CONVEYANCE SYSTEM
VAULT (4 FEET BGS, INSTALLED IN 2000)
ASSESSOR'S PARCEL BOUNDARY AND
NUMBER
FORMER EXCAVATION AREA
! ! ! ! ! !
! ! ! ! ! !
! ! ! ! ! !
SHALLOW SWALE (1948)
SUBJECT SITE
NOTES
1. ALL LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. SOURCES: ABC 1998, URS 2013, ROHR MILLS AND LATHES - EQUIPMENT MANUAL
3. THE LOCATIONS OF FORMER VESSELS AND VAULTS FROM ABC 1998 AND URS 2013.
SOME LOCATIONS HAVE BEEN ADJUSTED BASED ON SITE RECONNAISSANCE.
4. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, MARCH 2017
HISTORICAL ENVIRONMENTAL
SITE FEATURES
BUILDING NUMBER
56701029
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A@DA@ A@DA@D
A@
AD
@DA@
A@D
A@D A@D
A@D
B29-18
B29-17
B29-13
B29-15
B29-14
B29-11
B29-10
B29-08
B29-06
B29-04
B99-04
B99-02
B99-03
B29-03 B29-07
B29-05
B29-12
B29-19
B29-20
B29-09
B99-01
B29-02
B29-01
B29-16
B29-21
UT-24
B29-V05
B29-V07
B29-V01 B29-V02
B29-V09
B29-V10
B29-V13
B29-V11 B29-V15
B29-V16
B29-V17
B29-V19
B29-V18
B29-V12
B29-V08
B29-V04
B29-V03
B29-V06
B99-V01
B99-V02
B99-V05
B99-V06
B100-V02
B100-V03
B99-V03
B99-V04
B100-V01 B29-V14
B11
B12
B29-02B
B29-02C B29-02A
B29-25 B29-34C
B29-34A
B29-34B
B29-30
B29-03B
B29-03A
B29-07B
B29-07A
B29-24
B29-22
B29-27
B29-31
B29-29
B29-26
B29-28
B29-23
B29-35B
B29-35C
B29-35A
B29-05B
B29-05C
B29-05A
B29-32B
B29-32C
B29-32A
B29-33A
B29-33B
B29-33C
PW-16
PW-15
PW-12 PW-11
PW-07 PW-05 PW-02
PW-03
PW-06
PW-01B
PW-14
PW-13
PW-10
PW-08
PW-04
PW-09
PW-01A
UT-23 UT-25 UT-22
UT-19 UT-20
UT-18 UT-66
UT-03 UT-21
B15
DB-4
OW-4
OW-3
OW-1
OW-2
DB-5
DB-2
100
99 29
BB-15
BB-18
BB-21
BB-14 BB-17 BB-20 BB-23
BB-16 BB-19 BB-22 BB-24
56702233
56701007
56702217
56702228
57133030
57133024
56702230
56702231
57133016
57133003
57133029
56702216
G
S
T
REET
INTERSTATE 5
BAY BOULEVARD
MW-A
MW-B
MW-C
MW-D
ROHR, INC., A COLLINS AEROSPACE COMPANY
NORTH CAMPUS - PARCEL A
CHULA VISTA, CALIFORNIA
FIGURE 3 SCALE: AS SHOWN
APRIL 2021
0 125 250
SCALE IN FEET
GIS FILE PATH: G:\43559_North Campus\000_Global\GIS\Maps\2021_03\127827_023_0003_SAMPLE_LOCATION_MAP.mxd - USER: dfm - LAST SAVED: 3/24/2021 10:29:15 AM LEGEND
A@ EXISTING MONITORING WELL
A@D DESTROYED MONITORING
WELL/TRANSDUCER
@ 2020 BORING LOCATION
2016 BORING LOCATION
?!" 2013 BORING LOCATION
?!" OTHER HISTORICAL BORING LOCATION
2018 SOIL VAPOR PROBE
GSI 2020 SOIL VAPOR PROBE AND/OR SOIL
BORING
CROSS SECTION LINE
VAULT (4 FEET BGS, INSTALLED IN 2000)
ASSESSOR'S PARCEL BOUNDARY AND
NUMBER
SUBJECT SITE
NOTES
1. ALL LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, MARCH 2017
SAMPLE LOCATION MAP
A A'
BUILDING NUMBER
56701029
B
B'
29 A@D
A@D
A@A@
A@DA@DA@D
A@D
A@D
A@D
A@D
THERMO KING
340 BAY
JACKSON'S
IMPORT AUTO
350-360 BAY
SAN DIEGO PUMP
& COMPRESSOR
SUPPLY
364-368 BAY
BB-11
BB-12
BB-13
BB-14
BB-15
BB-16
BB-17
BB-18
BB-19
BB-20
BB-21
BB-22
BB-23
BB-24
UT-02
MW-2B
MW-1B
MW-3B
MW-B
DB-4
OW-4
OW-3
OW-1
DB-2
OW-2
DB-5
FORMER
AGRICULTURE - CITRUS
(1948)
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
GIS FILE PATH: C:\Projects\127827_North_campus\GIS\Maps\2021_01\127827_023_0004_DETAIL_EXPLORATION_LOCATIONS.mxd - USER: DFM - LAST SAVED: 3/29/2021 5:10:57 PM 0 40 80
SCALE IN FEET
ROHR, INC, A COLLINS AEROSPACE COMPANY
NORTH CAMPUS SITEWIDE CONCEPTUAL MODEL
CHULA VISTA, CALIFORNIA
DETAIL HISTORICAL ENVIRONMENTAL
FEATURES AND SAMPLE LOCATION
MAP - 350, 360, 364, AND 368 BAY
BOULEVARD
FIGURE 4A SCALE: AS SHOWN
APRIL 2021
LEGEND
BORING
CPT
&( HYDROPUNCH
SOIL VAPOR
A@ MONITORING WELL ZONE A A@D DESTROYED MONITORING
WELL/TRANSDUCER
FORMER MILLS/LATHES
STORM WATER CONVEYANCE
SYSTEM
CURRENT
FORMER (PRE-1998)
ASSESSOR'S PARCEL
BOUNDARY AND NUMBER
FORMER VESSELS AND VAULTS
UST (UNDERGROUND
STORAGE TANK)
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND
STORAGE TANK)
PAINT BOOTH
DEGREASER
VAULT LOCATION
FORMER EXCAVATION AREA
SITE BOUNDARY
NOTES
1. LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. FORMER VESSELS AND VAULTS SIZE ARE FOR
PRESENTATION PURPOSE ONLY. ACTUAL SIZE MAY VARY.
3. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, 2017
SITE PLAN AND DETAIL AREA 1 " = 1,500 ' H STREET
MARINA PARKWAY
F STREET
G STREET
LAGOON AVE
PARCEL H-3
FUTURE PARK DEVELOPMENT
29 BUILDING NUMBER
A@D
A@D
A@D
A@D
A@D
A@A@
A@DA@DA@D
A@D
O PUMP
ESSOR
LY
BAY
200
148
147
146
145
BB-23
BB-24
B100-V01
B100-V02
B100-V03
B99-01
B99-02
B99-03
B99-04
B99-V01
B99-V02
B99-V03
B99-V04
B99-V05
B99-V06
UT-03
PW-01B
PW-01A
100
99 MW-A
MW-B MW-C
MW-D
DB-4
OW-4
OW-3
OW-1
DB-2
OW-2
DB-5
FORMER
AGRICULTURE - CITRUS
(1948)
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
FORMER TRUCK
ENGINE REPAIR
G STREET
GIS FILE PATH: C:\Projects\127827_North_campus\GIS\Maps\2021_01\127827_023_0004_DETAIL_EXPLORATION_LOCATIONS.mxd - USER: DFM - LAST SAVED: 3/29/2021 5:10:57 PM 0 40 80
SCALE IN FEET
ROHR, INC, A COLLINS AEROSPACE COMPANY
NORTH CAMPUS SITEWIDE CONCEPTUAL MODEL
CHULA VISTA, CALIFORNIA
DETAIL HISTORICAL ENVIRONMENTAL
FEATURES AND SAMPLE LOCATION
MAP - BUILDINGS 99 AND 100
FIGURE 4B SCALE: AS SHOWN
APRIL 2021
LEGEND
BORING
CPT
&( HYDROPUNCH
SOIL VAPOR
A@ MONITORING WELL ZONE A A@D DESTROYED MONITORING
WELL/TRANSDUCER
FORMER MILLS/LATHES
STORM WATER CONVEYANCE
SYSTEM
CURRENT
FORMER (PRE-1998)
ASSESSOR'S PARCEL
BOUNDARY AND NUMBER
FORMER VESSELS AND VAULTS
UST (UNDERGROUND
STORAGE TANK)
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND
STORAGE TANK)
PAINT BOOTH
DEGREASER
VAULT LOCATION
FORMER EXCAVATION AREA
SITE BOUNDARY
NOTES
1. LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. FORMER VESSELS AND VAULTS SIZE ARE FOR
PRESENTATION PURPOSE ONLY. ACTUAL SIZE MAY VARY.
3. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, 2017
SITE PLAN AND DETAIL AREA 1 " = 1,500 ' H STREET
MARINA PARKWAY
F STREET
G STREET
LAGOON AVE
PARCEL H-3
FUTURE PARK DEVELOPMENT
29 BUILDING NUMBER
202
201
203
300
304A
B11
B15
B29-01
B29-02
B29-02A
B29-02B
B29-02C
B29-03
B29-03A B29-03B
B29-04
B29-05
B29-05A
B29-05B
B29-05C
B29-06
B29-07
B29-07A
B29-07B
B29-09
B29-22
B29-23
B29-24
B29-25
B29-26
B29-27
B29-28
B29-29
B29-30
B29-31
B29-32A
B29-32B
B29-32C
B29-V01 B29-V02
B29-V03
B29-V04
B29-V05
B29-V06
B29-V07
B29-V08
B29-V09
B29-V10
UT-23 UT-24
UT-18
UT-19
UT-66
PW-02
PW-03
PW-04
PW-05
PW-06
PW-07
PW-08
PW-09
PW-10
B1
FORMER SHALLOW
SWALE (1948)
FORMER
LUMBER YARD
(1948)
FORMER
AGRICULTURE - CITRUS
(1948)
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
MAINTENANCE
DEPARTMENT
FORMER
G STREET
GIS FILE PATH: C:\Projects\127827_North_campus\GIS\Maps\2021_01\127827_023_0004_DETAIL_EXPLORATION_LOCATIONS.mxd - USER: DFM - LAST SAVED: 3/29/2021 5:10:57 PM 0 40 80
SCALE IN FEET
ROHR, INC, A COLLINS AEROSPACE COMPANY
NORTH CAMPUS SITEWIDE CONCEPTUAL MODEL
CHULA VISTA, CALIFORNIA
DETAIL HISTORICAL ENVIRONMENTAL
FEATURES AND SAMPLE LOCATION
MAP - BUILDING 29 NORTH
FIGURE 4C SCALE: AS SHOWN
APRIL 2021
LEGEND
BORING
CPT
&( HYDROPUNCH
SOIL VAPOR
A@ MONITORING WELL ZONE A A@D DESTROYED MONITORING
WELL/TRANSDUCER
FORMER MILLS/LATHES
STORM WATER CONVEYANCE
SYSTEM
CURRENT
FORMER (PRE-1998)
ASSESSOR'S PARCEL
BOUNDARY AND NUMBER
FORMER VESSELS AND VAULTS
UST (UNDERGROUND
STORAGE TANK)
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND
STORAGE TANK)
PAINT BOOTH
DEGREASER
VAULT LOCATION
FORMER EXCAVATION AREA
SITE BOUNDARY
NOTES
1. LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. FORMER VESSELS AND VAULTS SIZE ARE FOR
PRESENTATION PURPOSE ONLY. ACTUAL SIZE MAY VARY.
3. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, 2017
SITE PLAN AND DETAIL AREA 1 " = 1,500 ' H STREET
MARINA PARKWAY
F STREET
G STREET
LAGOON AVE
PARCEL H-3
FUTURE PARK DEVELOPMENT
29 BUILDING NUMBER
161
3-09596
161
304C
304B
B29-08
B29-10
B29-11
B29-12
B29-13
B29-14
B29-15
B29-16
B29-21
B29-33A
B29-33C
B29-34A
B29-34C
B29-V11
B29-V12
B29-V13
B29-V14
B29-V15
B29-V16
B29-V17
UT-25
UT-20
PW-11 PW-12
PW-13
PW-14
PW-10
29 BAY BOULEVARD
FORMER
LUMBER YARD
(1948)
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
GIS FILE PATH: C:\Projects\127827_North_campus\GIS\Maps\2021_01\127827_023_0004_DETAIL_EXPLORATION_LOCATIONS.mxd - USER: DFM - LAST SAVED: 3/29/2021 5:10:57 PM 0 40 80
SCALE IN FEET
ROHR, INC, A COLLINS AEROSPACE COMPANY
NORTH CAMPUS SITEWIDE CONCEPTUAL MODEL
CHULA VISTA, CALIFORNIA
DETAIL HISTORICAL ENVIRONMENTAL
FEATURES AND SAMPLE LOCATION
MAP - BUILDING 29 CENTRAL
FIGURE 4D SCALE: AS SHOWN
APRIL 2021
LEGEND
BORING
CPT
&( HYDROPUNCH
SOIL VAPOR
A@ MONITORING WELL ZONE A A@D DESTROYED MONITORING
WELL/TRANSDUCER
FORMER MILLS/LATHES
STORM WATER CONVEYANCE
SYSTEM
CURRENT
FORMER (PRE-1998)
ASSESSOR'S PARCEL
BOUNDARY AND NUMBER
FORMER VESSELS AND VAULTS
UST (UNDERGROUND
STORAGE TANK)
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND
STORAGE TANK)
PAINT BOOTH
DEGREASER
VAULT LOCATION
FORMER EXCAVATION AREA
SITE BOUNDARY
NOTES
1. LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. FORMER VESSELS AND VAULTS SIZE ARE FOR
PRESENTATION PURPOSE ONLY. ACTUAL SIZE MAY VARY.
3. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, 2017
SITE PLAN AND DETAIL AREA 1 " = 1,500 ' H STREET
MARINA PARKWAY
F STREET
G STREET
LAGOON AVE
PARCEL H-3
FUTURE PARK DEVELOPMENT
29 BUILDING NUMBER
204
226
3-09596
301
304C
304B
304D
B12
B29-16
B29-17
B29-18
B29-19
B29-20
B29-33A
B29-33B
B29-33C
B29-34A B29-34B
B29-34C
B29-35A
B29-35B
B29-35C
B29-V17
B29-V18
B29-V19
UT-22
UT-21
PW-14
PW-15
PW-16
BAY BOULEVARD
WESTERN DRAINAGE SWALE
SAN DIEGO & ARIZONA EASTERN RAIL ROAD
H STREET
GIS FILE PATH: C:\Projects\127827_North_campus\GIS\Maps\2021_01\127827_023_0004_DETAIL_EXPLORATION_LOCATIONS.mxd - USER: DFM - LAST SAVED: 3/29/2021 5:10:57 PM 0 40 80
SCALE IN FEET
ROHR, INC, A COLLINS AEROSPACE COMPANY
NORTH CAMPUS SITEWIDE CONCEPTUAL MODEL
CHULA VISTA, CALIFORNIA
DETAIL HISTORICAL ENVIRONMENTAL
FEATURES AND SAMPLE LOCATION
MAP - BUILDING 29 SOUTH
FIGURE 4E SCALE: AS SHOWN
APRIL 2021
LEGEND
BORING
CPT
&( HYDROPUNCH
SOIL VAPOR
A@ MONITORING WELL ZONE A A@D DESTROYED MONITORING
WELL/TRANSDUCER
FORMER MILLS/LATHES
STORM WATER CONVEYANCE
SYSTEM
CURRENT
FORMER (PRE-1998)
ASSESSOR'S PARCEL
BOUNDARY AND NUMBER
FORMER VESSELS AND VAULTS
UST (UNDERGROUND
STORAGE TANK)
UV (UNDERGROUND VESSEL)
AST (ABOVEGROUND
STORAGE TANK)
PAINT BOOTH
DEGREASER
VAULT LOCATION
FORMER EXCAVATION AREA
SITE BOUNDARY
NOTES
1. LOCATIONS AND DIMENSIONS ARE APPROXIMATE.
2. FORMER VESSELS AND VAULTS SIZE ARE FOR
PRESENTATION PURPOSE ONLY. ACTUAL SIZE MAY VARY.
3. AERIAL IMAGERY SOURCE: SAN DIEGO COUNTY, 2017
SITE PLAN AND DETAIL AREA 1 " = 1,500 ' H STREET
MARINA PARKWAY
F STREET
G STREET
LAGOON AVE
PARCEL H-3
FUTURE PARK DEVELOPMENT
29 BUILDING NUMBER
-10-505101520
ELEVATION IN FEET ABOVE MEAN LOW LEVEL WATER (MLLW) -20 -15 NORTH A -10 -505101520 ELEVATION IN FEET ABOVE MEAN LOW LEVEL WATER (MLLW) -20 -15 SOUTH A' B29-20
B29-23/B29-V03
B29-05/PW-07
B29-30/B29-V09
B29-10/B29-V13
B29-12
B29-15/B29-V16
B29-35C/B29-V19
B99-01
B100-V01 < 0.50 < 27 17 5.36 < 0.50 8 0.67 2.7 30 BUILDING 100 G STREET BUILDING 29 VAULT SILTY SAND SILTY SAND SILT/CLAY SILT/CLAY < 5.0 < 5.1 5.53 < 1.0 < 1.0 22.9 50.2 < 4.9 < 4.8 1.8 J < 4.9 < 5.0 < 5.2 < 5.0 < 5.2 1415 ? ? ? ? ? ? ? ? ? ? 37,800 1,280 1,490
920,000 3,000,000
11,000 16,000 9,800
PW-02
PW-05
B29-V08
PW-11
PW-12
PW-14
PW-15
PW-01B 140 2,900,00 2,400,000 130 2,100 1,500 5.9 35/1,500* 64,000 7,600 13,000 LEGEND FILL SILT/CLAY SILTY SAND LITHOLOGY CONTACT (INFERRED) NOTES 1. ALL LOCATIONS AND DIMENSIONS ARE APPROXIMATE. 2. < 0.50 = NOT DETECTED ABOVE LABORATORY REPORTING LIMIT G:\43559_NORTH CAMPUS\000_GLOBAL\CAD\127827_019_0005_06_CROSS_SECTION.DWG DFM X-SEC A-A' 3/24/2021 11:47 AM Sheet: Printed: FIGURE 5 ROHR, INC., A COLLINS AEROSPACE COMPANY NORTH CAMPUS - PARCEL A CHULA VISTA, CALIFORNIA GEOLOGIC CROSS SECTION A-A' SCALE: AS SHOWN APRIL 2021 00 SCALE IN FEET HORIZ. VERT. 120 240 12 24 B27 EXPLORATION DESIGNATION EXPLORATION LEGEND SAMPLE LOCATION SURFACE GROUNDWATER ELEVATION AT TIME OF DRILLING < 0.50 30< 5.0 TRICHLOROETHENE CONCENTRATION SOIL (ug/kg) SOIL GAS (ug/m^3) GROUNDWATER (ug/L) * TETRACHLOROETHENE CONCENTRATION -10-505101520
ELEVATION IN FEET ABOVE MEAN LOW LEVEL WATER (MLLW) -20 -15 WEST B B29-03/B29-V01
B29-22/PW-02*
B29-23/B29-V03
B29-27 -10 -505101520
ELEVATION IN FEET ABOVE MEAN LOW LEVEL WATER (MLLW) -20 -15 EAST B' SILTY SAND SILT/CLAY SILT/CLAY BUILDING 29 LOADING DOCK 6" CONCRETE 50.2 37,800 1,280 1,490 920,000 3,000,000 < 5.2 0.64 1,330 47.4 7,830 92.5 272 2.73 450/450 3,400 7,500 27,000 737 18.6 ? ? 1,600 B29-26/B29-V04/
PW-06*
160,000
B29-24/PW-03*
1,100,000
2,900,000
PW-04
2,500,000 LEGEND FILL : SILTY FINE SAND WITH ASPHALT SILT/CLAY SILTY SAND LITHOLOGY CONTACT (INFERRED) NOTES 1. ALL LOCATIONS AND DIMENSIONS ARE APPROXIMATE. 2. < 0.50 = NOT DETECTED ABOVE LABORATORY REPORTING LIMIT G:\43559_NORTH CAMPUS\000_GLOBAL\CAD\127827_019_0005_06_CROSS_SECTION.DWG DFM X-SEC B-B' 3/24/2021 11:46 AM Sheet: Printed: FIGURE 6 ROHR, INC., A COLLINS AEROSPACE COMPANY NORTH CAMPUS - PARCEL A CHULA VISTA, CALIFORNIA GEOLOGIC CROSS SECTION B-B' SCALE: AS SHOWN APRIL 2021 00 SCALE IN FEET HORIZ. VERT. 120 240 12 24 B27 EXPLORATION DESIGNATION EXPLORATION LEGEND SAMPLE LOCATION SURFACE GROUNDWATER ELEVATION AT TIME OF DRILLING < 0.50 30< 5.0 TRICHLOROETHENE CONCENTRATION SOIL (ug/kg) SOIL GAS (ug/m^3) GROUNDWATER (ug/L) * PROBE LOCATED IN VAULT (APPROX. 4 FEET BGS) G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
B29-23
TCE(AB): 37.8
B29-24
TCE(B): 7.83
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7A
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007A_ V OC_ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/19/202112:38:20PM LEGEND
NOT ANALY Z ED FOR V OCs IN SOIL
ANALY Z ED FOR V OCs IN SOIL
V OCs EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017 V OCs IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7B
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007B_ TPH_ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/24/202111:03:36AM LEGEND
NOT ANALY Z ED FOR TPH IN SOIL
ANALY Z ED FOR TPH IN SOIL
TPH EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017
TPH IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
B29-12
D(a,h)A(B): 0.63
UT-18
B(a)P(B): 7.2
D(a,h)A(B): 1.9
UT-21
B(a)P(B): 3.6
D(a,h)A(B): 1.6
UT-66
B(a)P(B): 1.3
D(a,h)A(B): 0.59
G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7C
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007C_ SV OCs _ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/19/20211:00:48PM LEGEND
NOT ANALY Z ED FOR SV OCs IN SOIL
ANALY Z ED FOR SV OCs IN SOIL
SV OCs EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017 SV OCs IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
B29-05
PCB-1260/TOTAL(B): 1.3
UT-02
PCB-1254/TOTAL(B): 0.77
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7D
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007D_ PCBs _ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/19/20211:08:03PM LEGEND
NOT ANALY Z ED FOR PCBs IN SOIL
ANALY Z ED FOR PCBs IN SOIL
PCBs EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017 PCBs IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
BB-23
4,4-DDE(C): 1
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7E
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007E_ PESTICIDE_ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/19/20211:10:40PM LEGEND
NOT ANALY Z ED FOR PECTICIDES IN SOIL
ANALY Z ED FOR PECTICIDES IN SOIL
PECTICIDES EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017
PECTICIDES IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
B29-02
As(B): 23.3
B29-03
As(B): 19.6
B29-03A
As(B): 20.4
B29-03B
As(B): 21.9
B29-07
As(B): 21.8
B29-07A
As(A): 24.6
B29-07B
As(B): 22
UT-03
As(B): 8.71
G
S
T
REET
INTERSTATE5
BAY BOU LEV ARD
100
99 29
ROHR, INC., A COLLINS AEROSPACE COM PANY
NORTH CAM PU S - PARCEL A
CHU LA V ISTA, CALIFORNIA
APRIL 2021
SCALE: AS SHOWN FIGU RE 7F
0 125 250
SCALE IN FEET
GISFILEPATH:G:\43559_ North Cam pus \000_ Global\GIS\M aps \2021_ 03\127827_ 023_ 0007F_ M ETALS_ SOIL_ SAM PLE_ EXCEEDING_ CRITERIA.m xd ― U SER:dfm ― LASTSAV ED:3/24/202111:12:05AM LEGEND
NOT ANALY Z ED FOR M ETALS IN SOIL
ANALY Z ED FOR M ETALS IN SOIL
M ETALS EXCEEDING SCREENING CRITERIA
GPL
COM M ERCIAL/INDU STRIAL DTSC-SL
TTLC
FORM ER M ILLS/LATHES
FORM ER V ESSELS AND V AU LTS
U ST (U NDERGROU ND STORAGE TANK)
BASED ON DEH EV ALU ATION OF CCR TITLE
23. CLOSED THROU GH REM OV AL OR
FILLING.
U V (U NDERGROU ND V ESSEL)
AST (ABOV EGROU ND STORAGE TANK)
PAINT BOOTH
DEGREASER
V AU LT (4 FEET BGS, INSTALLED IN 2000)
SU BJECT SITE
NOTES
1. ALL LOCATIONS AND DIM ENSIONS ARE APPROXIM ATE.
2. SOU RCES: ABC 1998, U RS 2013, ROHR M ILLS AND LATHES - EQU IPM ENT M ANU AL
3. THE LOCATIONS OF FORM ER V ESSELS AND V AU LTS FROM ABC 1998 AND U RS 2013.
SOM E LOCATIONS HAV E BEEN ADJU STED BASED ON SITE RECONNAISSANCE.
4. SEE REPORT FOR ABBREV IATION ACRONY M S
5. POSTSCRIPT KEY :
(A) = EXCEEDS GPL
(B) = EXCEEDS COM M ERCIAL/INDU STRIAL DTSC-SL
(C) = EXCEEDS TTLC
6. AERIAL IM AGERY SOU RCE: SAN DIEGO COU NTY , M ARCH 2017 TITLE 22 M ETALS AND HEXAV ALENT
CHROM IU M IN V ADOSE Z ONE SOIL
EXCEEDING SCREENING CRITERIA
29 BU ILDING NU M BER
B11
2.5' : < 0.005
B12
2.5' : < 0.005
B15
5.0' : < 0.005
B29-01
0.5' : < 0.00031
1.5' : < 0.0003
B29-02
0.5' : < 0.0003
1.5' : < 0.00031
B29-03
0.5' : < 0.00031
2.5' : 0.00064
B29-04
0.5' : < 0.0003
4.5' : < 0.0003
B29-05
1.5' : 0.015
4.5' : 0.014
B29-06
0.5' : < 0.00031
4.5' : < 0.00029
B29-07
0.5' : < 0.00031
2.5' : < 0.00031
B29-08
0.5' : < 0.0003
4.5' : < 0.00032
B29-09
0.5' : < 0.0003
4.5' : < 0.0003
B29-10
0.5' : < 0.00031
4.5' : < 0.0003
B29-11
0.5' : < 0.0003
4.5' : < 0.00031
B29-12
0.5' : < 0.00031
4.5' : < 0.0003
B29-13
3.5' : < 0.00031
4.5' : < 0.00031
B29-14
1.0' : 0.0042
2.5' : 0.002
B29-15
0.5' : < 0.0003
2.5' : 0.0018
B29-16
0.5' : < 0.00031
2.5' : < 0.00029
B29-17
0.5' : < 0.0003
2.5' : < 0.00031
B29-18
1.0' : < 0.00029
2.5' : < 0.0003
B29-19
1.5' : < 0.00031
4.5' : < 0.00031
B29-20
0.5' : < 0.00029
1.5' : < 0.0003
B29-21
0.5' : 0.00079
B29-22
0.5' : 1.33
4.5' : 0.0474
B29-23
0.5' : 37.8
4.5' : 0.0502
B29-24
0.5' : 7.83
4.5' : 0.0925
B29-25
0.5' : < 0.0004
4.5' : < 0.000404
B29-26
0.5' : 0.737
4.5' : 0.0186
B29-27
0.5' : 0.275
4.5' : 0.00273
B29-28
0.5' : 1.43
4.5' : 0.00228
B29-29
0.5' : 0.0779
4.5' : 0.00313
B29-30
0.5' : 0.0229
4.5' : < 0.0004
B29-31
0.5' : 0.0011
4.5' : < 0.0004
B29-32A
0.5' : < 0.0004
4.5' : < 0.0004
B29-32B
0.5' : < 0.0004
4.5' : < 0.0004
B29-32C
0.5' : < 0.0004
4.5' : < 0.0004
B29-33A
0.5' : < 0.0004
4.5' : 0.00725
B29-33B
0.5' : < 0.0004
1.5' : 0.323
B29-33C
0.5' : 0.000925
4.5' : < 0.0004
B29-34A
0.5' : < 0.0004
4.5' : < 0.0004
B29-34B
0.5' : < 0.0004
4.5' : < 0.0004
B29-34C
0.5' : < 0.0004
4.5' : < 0.0004
B29-35A
0.5' : < 0.0004
4.5' : < 0.0004
B29-35B
0.5' : < 0.0004
4.5' : < 0.0004
B29-35C
0.5' : < 0.0004
4.5' : 0.00553 B99-01
0.5' : < 0.0003
4.5' : < 0.0003
B99-02
0.5' : < 0.0003
3.5' : < 0.00031
B99-03
0.5' : < 0.00031
3.5' : < 0.0003
B99-04
0.5' : < 0.00031
2.5' : < 0.0003
PW-07
1.5' : 0.023
PW-11
1.5' : < 0.0071
PW-12
1.5' : < 0.0042
UT-22
1.0' : < 0.0003
5.0' : < 0.0003
UT-23
1.0' : < 0.0003
5.0' : 0.059 UT-24
1.0' : < 0.0003
5.0' : < 0.0003
UT-25
1.0' : < 0.0003
5.0' : < 0.0003
BB-14
0.5' : < 0.0049
4.5' : < 0.0052
BB-15
0.5' : < 0.0051
2.5' : < 0.005
BB-16
0.5' : < 0.0051
2.5' : < 0.005
BB-17
0.5' : < 0.0051
3.5' : < 0.005
BB-17
0.5' : < 0.005
3.5' : < 0.0049
BB-19
0.5' : < 0.0052
2.5' : < 0.0052
BB-20
0.5' : < 0.0052
2.5' : < 0.0051
BB-21
0.5' : < 0.005
2.5' : < 0.0049
BB-22
0.5' : < 0.005
2.5' : < 0.0051
BB-23
0.5' : < 0.005
2.5' : < 0.005
BB-24
0.5' : < 0.0049
2.5' : < 0.0052
UT-02
1.0' : < 0.005
5.0' : < 0.005
PW_01B
1.5' : < 0.0045
PW_01A
1.5' : < 0.0047
UT-03
1.0' : < 0.005
5.0' : < 0.005
UT-18
1.0' : < 0.005
5.0' : < 0.005
UT-66
1.0' : < 0.005
5.0' : < 0.005
UT-10
1.0' : < 0.005
5.0' : < 0.005 UT-20
1.0' : < 0.005
5.0' : < 0.005
UT-21
1.0' : < 0.005
5.0' : < 0.005
PW-07
2.0' : 0.14
PW-03
5.5' : 0.011
PW-06
3.0' : 0.02
1 0.01
10 0.1
0.01 0.1
0.01 100
99 29
INT ERST AT E5
NOTES
1. ALL LOCAT IONS AND DIMENSIONS ARE APPROX IMAT E.
2. ALL CONCENT RAT IONS ARE IN MILLIGRAMS PER K ILOGRAM (m g/kg)
3. < = LESS T HAN LABORAT ORY DET ECT ION LIMIT S ARE SHOWN
4. T CE = T RICHLOROET HENE
5. AERIAL IMAGERY SOU RCE: SAN DIEGO COU NT Y , MARCH 2017 ROHR, INC., A COLLINS AEROSPACE COMPANY
NORT H CAMPU S - PARCEL A
CHU LA VIST A, CALIFORNIA
EX T ENT OF T CE IN SOIL
0-2 FEET BELOW GROU ND SU RFACE
FIGU RE 8 SCALE: AS SHOWN
APRIL 2021
LEGEND
SOIL SAMPLE LOCAT ION WHERE T CE DET ECT ED
SOIL SAMPLE LOCAT ION WHERE T CE NOT
DET ECT ED
T RICHLOROET HENE (T CE) CONT OU R IN SOIL 0-2
FEET BGS (m g/kg)
FORMER MILLS/LAT HES
FORMER VESSELS AND VAU LT S
U ST (U NDERGROU ND ST ORAGE T ANK ) BASED ON
DEH EVALU AT ION OF CCR T IT LE 23. CLOSED
T HROU GH REMOVAL OR FILLING.
U V (U NDERGROU ND VESSEL)
AST (ABOVEGROU ND ST ORAGE T ANK )
PAINT BOOT H
DEGREASER
VAU LT (4 FEET BGS, INST ALLED IN 2000)
SU BJECT SIT E
GISFILEPAT H:G:\43559_ North Cam p us\000_ Global\GIS\Map s\2021_ 03\127827_ 023_ 0008_ EX T ENT _ OF_ T CE_ IN_ SOIL.m xd ― U SER:dfm ― LAST SAVED:3/24/202111:15:32AM 0 130 260
SCALE IN FEET
29 BU ILDING NU MBER
B
CF
PCE
T CE
05/24/2018
5 130/140
48/56
83 450/450
05/25/2018
10 -
56 -
3,400
B29-V 01
B
E
PCE
T CE
05/24/2018
5 950
780
780
1,500
05/24/2018
10 41
-
84 -
B29-V 02
B
CF
PCE
T CE
05/23/2018
1 49
12,000
150
920,000
05/24/2018
5 -
39,000
-
3,000,000
B29-V 03
PCE
T CE
05/23/2018
1 210
7,500
05/23/2018
5 430
27,000
B29-V 04
B
PCE
05/22/2018
1 27
220
05/23/2018
5 78
160
05/23/2018
10 31
180
B29-V 05
B
T CE
05/23/2018
5 34/29
120/100
B29-V 06
B
CF
PCE
T CE
05/23/2018
1 -
240
2,200
7,800
05/23/2018
5 69
1,500
11,000
51,000
B29-V 07
PCE
T CE
05/24/2018
1 80
130
05/24/2018
5 2,200
2,100
05/24/2018
10 1,600
1,500
B29-V 08
CF
T CE
05/22/2018
1 170
11,000
B29-V 09
T CE
05/22/2018
1 120
B29-V 10
PCE
T CE
05/22/2018
1 340
16,000
B29-V 16
T CE
05/22/2018
1 9,800
B29-V 19
CF
T CE
07/31/2020
5 18,000
2,900,000
PW-02
CF
T CE
07/31/2020
5 6,800/7,100
1,100,000/1,100,000
PW-03
B
CF
T CE
07/31/2020
5 38
52 1,400
PW-04
CF
PCE
T CE
07/31/2020
4 16,000
5,800
2,400,000
PW-05
CF
T CE
07/31/2020
3.5 1,600
160,000
PW-06
CF
PCE
T CE
07/31/2020
4 160
330
7,600
PW-07
B
CF
E
PCE
07/31/2020
5 75
32 340
96 PW-08
BDCM
CF
T CE
07/30/2020
4.5 140
410
14,000
PW-09
BDCM
07/30/2020
3 16
PW-11
B
BDCM
CF
PCE
07/30/2020
3 36
17 20
1,500
PW-12
CF
07/30/2020
4 26
PW-13
T CE
07/30/2020
4 64,000/64,000
PW-14
T CE
07/30/2020
4.5 13,000
PW-15
T CE
07/31/2020
5 140
PW-01B
B29-V05
B29-V07
B29-V01 B29-V02
B29-V09
B29-V10
B29-V13
B29-V11 B29-V15
B29-V16
B29-V17
B29-V19
B29-V18
B29-V08
B29-V04
B29-V03*
B29-V06
B99-V01
B99-V02
B99-V05
B99-V06
B100-V02
B100-V03
B99-V03
B99-V04
B100-V01 B29-V14
B29-V12
PW-16
PW-15
PW-12 PW-11
PW-05* PW-07
PW-02*
PW-03*
PW-06
PW-01B
PW-14
PW-13
PW-10
PW-08
PW-04*
PW-09
99 29
100
INT ERST AT E5
ROHR, INC., A COL L INS AEROSPACE COMPANY
NORT H CAMPU S - PARCEL A
CHU L A V IST A, CAL IFORNIA
APRIL 2021
SCAL E: AS SHOWN FIGU RE 9
0 125 250
SCAL E IN FEET
GISFIL EPAT H:G:\43559_North Cam pus\000_Global\GIS\Maps\2021_03\127827_023_0009_SOIL _V APOR_COPCs_EX CEED_SCREEN.m xd ― U SER:dfm ― L AST SAV ED:3/24/20213:55:28PM LEGEND
SOIL V APOR PROBE
FORMER MIL L S/L AT HES
FORMER V ESSEL S AND V AU L T S
U ST (U NDERGROU ND ST ORAGE T ANK)
BASED ON DEH EV AL U AT ION OF CCR
T IT L E 23. CL OSED T HROU GH REMOV AL OR
FIL L ING.
U V (U NDERGROU ND V ESSEL )
AST (ABOV EGROU ND ST ORAGE T ANK)
PAINT BOOT H
DEGREASER
V AU L T (4 FEET BGS, INST AL L ED IN 2000)
SU BJECT SIT E
NOTES
1. AL L L OCAT IONS AND DIMENSIONS ARE APPROX IMAT E.
2. SOU RCES: ABC 1998, U RS 2013, ROHR MIL L S AND
L AT HES - EQU IPMENT MANU AL
3. T HE L OCAT IONS OF FORMER V ESSEL S AND V AU L T S
FROM ABC 1998 AND U RS 2013. SOME L OCAT IONS HAV E
BEEN ADJU ST ED BASED ON SIT E RECONNAISSANCE.
4. * = T HESE SAMPL E L OCAT IONS WERE NOT EV AL U AT ED
SINCE T HEY ARE L OCAT ED IN T HE PORT ION OF T HE
BU IL DING T HAT IS T O BE DEMOL ISHED.
5. AERIAL IMAGERY SOU RCE: SAN DIEGO COU NT Y ,
MARCH 2017
SOIL V APOR COPCs
EX CEEDING SCREENING CRIT ERIA
BU IL DING NU MBER
B
CF
PCE
T CE
05/24/2018
5 130/140
48/56
83 450/450
05/25/2018
10 -
56 -
3,400
B29-V 01
CF
PCE
T CE
PW-05
LOCATION ID
SAMPLE DEPTH BELOW
GROUND SURFACE IN FEET
CHEMICAL
NAME
SAMPLING DATE
CONCENTRATIONS
IN μg/L
ABBREV IAT IONS:
X X X B = BENZ ENE
X X X CF = CHL OROFORM
X X X BDCM = BROMODICHL OROMET HANE
X X X E = ET HY L BENZ ENE
X X X PCE = T ET RACHL OROET HENE
X X X T CE = T RICHL OROET HENE
29 1
T CE
05/25/2018
30 B100-V01
1 T CE
05/25/2018
< 27
B100-V02
1 T CE
05/25/2018
< 27/< 27
B100-V03
5 10
T CE
05/24/2018
450/450
-
T CE
05/25/2018
-
3,400
B29-V01
5 10
T CE
05/24/2018
1,500
64 B29-V02
1 5
T CE
05/23/2018
920,000
-
T CE
05/24/2018
-
3,000,000
B29-V03
1 5
T CE
05/23/2018
7,500
27,000
B29-V04
1 5
10 T CE
05/22/2018
< 27
-
-
T CE
05/23/2018
-
< 27
< 27
B29-V05
1 5
T CE
05/23/2018
< 27
100/120
B29-V06
1 5
T CE
05/23/2018
7,800
51,000
B29-V07
1 5
10 T CE
05/24/2018
130
2,100
1,500
B29-V08
1 T CE
05/22/2018
11,000
B29-V09
1 T CE
05/22/2018
120
B29-V10
1 T CE
05/22/2018
< 27
B29-V11
1 T CE
05/22/2018
< 27
B29-V12
1 T CE
05/22/2018
< 27
B29-V13
1 T CE
05/22/2018
< 27
B29-V14
1 T CE
05/22/2018
< 27
B29-V15
1 T CE
05/22/2018
16,000
B29-V16
1 T CE
05/22/2018
43 B29-V17
1 T CE
05/22/2018
42/< 27
B29-V18
1 T CE
05/22/2018
9,800
B29-V19
1 T CE
05/25/2018
< 27
B99-V01
1 T CE
05/25/2018
< 27
B99-V02
1 T CE
05/25/2018
< 27
B99-V03
1 T CE
05/25/2018
< 27
B99-V04
1 T CE
05/25/2018
32 B99-V05
1 T CE
05/25/2018
< 27
B99-V06
5 T CE
07/31/2020
140
PW-01B
5 T CE
07/31/2020
2,900,000
PW-02
5 T CE
07/31/2020
1,100,000/1,100,000
PW-03
5 T CE
07/31/2020
1400
PW-04
4 T CE
07/31/2020
2,400,000
PW-05
3.5 T CE
07/31/2020
160,000
PW-06
4 T CE
07/31/2020
7,600
PW-07
5 T CE
07/31/2020
54 PW-08
4.5 T CE
07/30/2020
14,000
PW-09
3 T CE
07/30/2020
5.9 PW-11
3 T CE
07/30/2020
35 PW-12
4 T CE
07/30/2020
91 PW-13
4 T CE
07/30/2020
64,000/64,000
PW-14
4.5 T CE
07/30/2020
13,000
PW-15
5 T CE
07/30/2020
25 PW-16
B29-V05
B29-V07
B29-V01
B29-V09
B29-V10
B29-V13
B29-V11
B29-V14
B29-V15
B29-V16
B29-V17
B29-V19
B29-V18
B29-V12
B29-V08
B29-V04
B29-V03
B29-V06
B99-V01
B99-V02
B99-V05
B99-V06
B100-V02
B100-V03
B99-V03
B99-V04
B100-V01
B29-V02
100
99 29
100,000
1,000
1,000,000
10,000
100
1000
100
10000
100
100
INT ERST AT E5
NOTES
1. ALL LOCAT IONS AND DIMENSIONS ARE APPROX IMAT E.
2. ALL CONCENT RAT IONS ARE IN MICROGRAMS PER CU BIC MET ER (μg/m 3
)
3. < = LESS T HAN LABORAT ORY DET ECT ION LIMIT S ARE SHOWN
4. T CE = T RICHLOROET HENE
5. AERIAL IMAGERY SOU RCE: SAN DIEGO COU NT Y , MARCH 2017 ROHR, INC., A COLLINS AEROSPACE COMPANY
NORT H CAMPU S - PARCEL A
CHU LA VIST A, CALIFORNIA
EX T ENT OF T CE IN SOIL VAPOR
FIGU RE 10 SCALE: AS SHOWN
APRIL 2021
LEGEND
HIST ORICAL VAPOR SAMPLE LOCAT ION
GSI SOIL VAPOR SAMPLE LOCAT ION
FORMER MILLS/LAT HES
FORMER VESSELS AND VAU LT S
U ST (U NDERGROU ND ST ORAGE T ANK ) BASED ON
DEH EVALU AT ION OF CCR T IT LE 23. CLOSED
T HROU GH REMOVAL OR FILLING.
U V (U NDERGROU ND VESSEL)
AST (ABOVEGROU ND ST ORAGE T ANK )
PAINT BOOT H
DEGREASER
T RICHLOROET HENE (T CE) CONT OU R IN SOIL VAPOR
(IN μg/m 3)
VAU LT (4 FEET BGS, INST ALLED IN 2000)
SU BJECT SIT E
GISFILEPAT H:G:\43559_ North Cam pus\000_ Global\GIS\Maps\2021_ 03\127827_ 023_ 0010_ EX T ENT _ OF_ T CE_ IN_ SOIL_ VAPOR.m xd ― U SER:dfm ― LAST SAVED:3/24/202111:26:00AM 0 130 260
SCALE IN FEET
1 5
10 T CE
05/24/2018
130
2,100
1,500
B29-V08
1 B29-V09
BU ILDING NU MBER
LOCATION ID
SAMPLE DEPTH BELOW
GROUND SURFACE IN FEET
SAMPLING DATE
CONCENTRATIONS
IN μg/m3
29 LB : < ND
1000
100
10 10
10 100
B15:3.3
B12:< 1
B11:< 1
UT-25:< 1
UT-22:42
UT-23:520 UT-24:4.7
UT-18:< 1 UT-19:< 1
UT-20:< 1
UT-21:< 1
UT-66:< 1
B29-32C:< 1.00 B29-28:63.8
B29-23:1280
B29-30:5.36
B29-33C:1.52*
B29-35C:17*
B29-34C:< 1*
B99-01: < 0.5* B29-20:< 0.5*
B29-15:2.7*
B29-16:< 1*
B29-12:0.67*
B29-04: 0.79*
B29-05: 7.9*
B29-03:750*
B29-07:21
BB-23: < 0.5*
BB-17: < 0.5* 100
99 29
INT ERS T AT E5
BAY BOU LEVARD
NOTES
1. ALL LOCAT IONS AND DIMENS IONS ARE APPROX IMAT E.
2. ALL CONCENT RAT IONS ARE IN MICROGRAMS PER LIT ER (μg/L)
3. * = U PPER Z ONE B DAT A
4. < = LES S T HAN LABORAT ORY DET ECT ION LIMIT S ARE S HOW N
5. T CE = T RICHLOROET HENE
6. AERIAL IMAGERY S OU RCE: S AN DIEGO COU NT Y , MARCH 2017 ROHR, INC., A COLLINS AEROS PACE COMPANY
NORT H CAMPU S - PARCEL A
CHU LA VIS T A, CALIFORNIA
EX T ENT OF T CE
IN Z ONE A GROU NDW AT ER
FIGU RE 11 S CALE: AS S HOW N
APRIL 2021
LEGEND
GROU NDW AT ER S AMPLE LOCAT ION
FORMER MILLS /LAT HES
FORMER VES S ELS AND VAU LT S
U S T (U NDERGROU ND S T ORAGE T ANK) BAS ED ON DEH
EVALU AT ION OF CCR T IT LE 23. CLOS ED T HROU GH REMOVAL OR FILLING.
U V (U NDERGROU ND VES S EL)
AS T (ABOVEGROU ND S T ORAGE T ANK)
PAINT BOOT H
DEGREAS ER
T RICHLOROET HENE (T CE) CONT OU R IN Z ONE A
GROU NDW AT ER (ug/L)
VAU LT (4 FEET BGS , INS T ALLED IN 2000)
S U BJ ECT S IT E
GIS FILEPAT H:G:\43559_No rth Cam pus\000_Glo bal\GIS \Maps\2021_03\127827_023_0011_EX T ENT _OF_T CE_IN_GROU NDW AT ER.m xd ― U S ER:dfm ― LAS T S AVED:3/24/202111:28:47AM 0 130 260
S CALE IN FEET
29 BU ILDING NU MBER
#
#
)
)
#
#
#
#
#
# #
# #
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
)
)
)
)
)
) )
) )
)
)
)
)
)
)
) )
)
)
)
)
)
)
)
)
)
)
)
#
#
#
#
#
#
#
#
#
#
#
#
#
#
# )
)
)
)
)
)
)
)
)
)
)
) )
)
)
29 VAU L T (4FEET BGS)
V03-019
599
B29-051A
1.6 V08-017
352
V18-002
V12-010
V12-011
V11-013
V11-014
V06-026
V03-022
V03-023
V03-024
V10-016
V12-010
B29-053
F3/UV
0.016
V19
0.012
V16
0.019
V14
0.024
V13
0.024
14-29-20
<0.54
V04
5.5 V03-020
4.2 V07
1.4 NTD1
0.16 V09M
0.023
B29-052
2.0 V05-029
0.25 V08-018
1.8 B29-OUT01
0.031 B29-OUT02
B29-OUT03 0.35
0.19 B29-OUT04
1.1 V17-005
V17-004
V17-003 V17-006
V17-008
V12-008
V18-001
V15-009
V11-012 V06-025
V03-020
V03-021
V05-027
V10-015
V05-028
NOTES
1. AL L L OCAT IONS AND DIMENSIONS ARE APPROX IMAT E.
2. SOU RCES: ABC 1998, U RS 2013, ROHR MIL L S AND L AT HES - EQU IPMENT MANU AL
3. T HE L OCAT IONS OF CU RRENT AND FORMER VESSEL S AND VAU L T S FROM ABC 1998 AND U RS 2013. SOME L OCAT IONS HAVE BEEN ADJU ST ED BASED ON SIT E RECONNAISSANCE.
4. T OT AL VOL AT IL E ORGANIC COMPOU ND (T VOC) CONCENT RAT IONS IN PART S PER BIL L ION BY VOL U ME (PPBV) AND MEASU RED U SING PPBRAE. T RICHL OROET HENE (T CE) CONCENT RAT IONS IN MICROGRAMS PER CU BIC MET ER (ug/m 3 ) AND MEASU RED U SING
HAPSIT E.
5. AL L T CE MEASU REMENT S COL L ECT ED IN BREAT HING Z ONE U NL ESS OT HERWISE SPECIFIED. T VOC MEASU REMENT S COL L ECT ED IN BREAT HING Z ONE AND POT ENT IAL PREFERENT IAL PAT HWAY S.
6. MEASU REMENT S COL L ECT ED ON SEPT EMBER 11-12, 2018.
7. DU PL ICAT E T VOC MEASU REMENT S COL L ECT ED AT SOME L OCAT IONS. T HE MAX IMU M T VOC CONCENT RAT ION IS SHOWN.
8. NO SAMPL E L OCAT IONS EX CEEDED EPA REGION 9 INT ERIM T CE INDOOR AIR ACCEL ERAT ED RESPONSE ACT ION OF 8 μg/m 3
9. AERIAL IMAGERY SOU RCE: SAN DIEGO COU NT Y , MARCH 2017 ROHR, INC., A COL L INS AEROSPACE COMPANY
NORT H CAMPU S - PARCEL A
CHU L A VIST A, CAL IFORNIA
INDOOR AIR SCREENING RESU L T S
SEPT EMBER 2018
FIGU RE 12 SCAL E: AS SHOWN
APRIL 2021
LEGEND
SAMPL E T Y PE
)
# BREAT HING Z ONE/OU T DOOR SAMPL E
#) PREFERENT IAL PAT HWAY
INDOOR AIR SCREENING L OCAT ION T CE FIEL D
MEASU REMENT (μg/m 3)
T VOC (p p bv)
)
# <10
)
# 10 - 50
)
# >50 - 500
)
# >500 - 5,000
)
# >5,000
ST ORM WAT ER CONVEY ANCE SY ST EM
FORMER MIL L S/L AT HES
FORMER VESSEL S AND VAU L T S
U ST (U NDERGROU ND ST ORAGE T ANK) BASED ON
DEH EVAL U AT ION OF CCR T IT L E 23. CL OSED
T HROU GH REMOVAL OR FIL L ING.
U V (U NDERGROU ND VESSEL )
AST (ABOVEGROU ND ST ORAGE T ANK)
PAINT BOOT H
DEGREASER
VAU L T (4 FEET BGS, INST AL L ED IN 2000)
BU IL DING BOU NDARY
GISFIL EPAT H:G:\43559_North Cam p us\000_Global\GIS\Map s\2021_03\127827_023_0012_INDOOR_AIR_SCREENING_L OCAT IONS_SEP_2018.m xd ― U SER:dfm ― L AST SAVED:3/24/202111:40:36AM 0 60 120
SCAL E IN FEET
V14
0.024
AIR SAMPLING
LOCATION ID
TCE CONCENTRATION
MICROGRAMS PER CUBIC METER (μg/m3)
LABEL KEY
#
#
#
#
#
# #
# #
#
#
#
#
#
#
#
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
#
)
) )
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
)
#
#
#
#
#
#
#
)
)
)
)
)
)
)
#
#
#
#
#
#
)
)
)
)
) )
29 VAU L T (4FEET BGS)
V03-019
121
B29-051
2.2 V08-017
9.6 V18-002
V12-010
V12-011
V11-013
V11-014
V06-026
V03-022
V03-023
V03-024
V10-016
F3/UV
1.6 V19
1.5 V16
1.6 V14
1.8 V13
5.9 14-29-20
6.7 V04
40.4 V07
5.2 NDT1
4.7 V09M
5.3 B29-052
2.2 V05-029
2.8 V08-018
8.6 B29-053
2.0 B29-OUT01
B29-OUT02 0.75
0.23/1.2
B29-052
2.2 B29-057
4.8 B29-056
19 B29-054
9.5 B29-055
37 B29-OUT03
0.50 V03
114
V17-005
V17-004
V17-003 V17-006
V17-008
V12-008
V18-001
V15-009
V11-012 V06-025
V03-020
V03-021
V05-027
V10-015
V05-028
NOTES
1. AL L L OCAT IONS AND DIMENSIONS ARE APPROX IMAT E.
2. SOU RCES: ABC 1998, U RS 2013, ROHR MIL L S AND L AT HES - EQU IPMENT MANU AL
3. T HE L OCAT IONS OF CU RRENT AND FORMER VESSEL S AND VAU L T S FROM ABC 1998 AND U RS 2013. SOME L OCAT IONS HAVE BEEN ADJU ST ED BASED ON SIT E RECONNAISSANCE.
4. T OT AL VOL AT IL E ORGANIC COMPOU ND (T VOC) CONCENT RAT IONS IN PART S PER BIL L ION BY VOL U ME (PPBV) AND MEASU RED U SING PPBRAE. T RICHL OROET HENE (T CE) CONCENT RAT IONS IN MICROGRAMS PER CU BIC MET ER (ug/m 3 ) AND MEASU RED U SING
HAPSIT E.
5. AL L T CE MEASU REMENT S COL L ECT ED IN BREAT HING Z ONE U NL ESS OT HERWISE SPECIFIED. T VOC MEASU REMENT S COL L ECT ED IN BREAT HING Z ONE AND POT ENT IAL PREFERENT IAL PAT HWAY S.
6. MEASU REMENT S COL L ECT ED ON FEBRU ARY 26-28, 2019.
7. DU PL ICAT E T VOC MEASU REMENT S COL L ECT ED AT SOME L OCAT IONS. T HE MAX IMU M T VOC CONCENT RAT ION IS SHOWN.
8. NS INDICAT ES NO MEASU REMENT WAS COL L ECT ED.
9. EPA REGION 9 INT ERIM T CE INDOOR AIR ACCEL ERAT ED RESPONSE ACT ION IS 8 μg/m 3
10. AERIAL IMAGERY SOU RCE: SAN DIEGO COU NT Y , MARCH 2017 ROHR, INC., A COL L INS AEROSPACE COMPANY
NORT H CAMPU S - PARCEL A
CHU L A VIST A, CAL IFORNIA
INDOOR AIR SCREENING RESU L T S
FEBRU ARY 2019
FIGU RE 13 SCAL E: AS SHOWN
APRIL 2021
LEGEND
SAMPL E T Y PE
)
# BREAT HING Z ONE/OU T DOOR SAMPL E
#) PREFERENT IAL PAT HWAY
INDOOR AIR SCREENING L OCAT ION T CE FIEL D
MEASU REMENT (μg/m 3)
T VOC (p p bv)
)
# NOT SAMPL ED (NS)
)
# <10
)
# 10 - 50
)
# >50 - 500
)
# >500 - 5,000
)
# >5,000
SAMPL E L OCAT ION EX CEEDS EPA REGION 9 INT ERIM T CE
INDOOR AIR ACCEL ERAT ED RESPONSE ACT ION L EVEL
ST ORM WAT ER CONVEY ANCE SY ST EM
FORMER MIL L S/L AT HES
FORMER VESSEL S AND VAU L T S
U ST (U NDERGROU ND ST ORAGE T ANK) BASED ON DEH
EVAL U AT ION OF CCR T IT L E 23. CL OSED T HROU GH REMOVAL OR FIL L ING.
U V (U NDERGROU ND VESSEL )
AST (ABOVEGROU ND ST ORAGE T ANK)
PAINT BOOT H
DEGREASER
VAU L T (4 FEET BGS, INST AL L ED IN 2000)
BU IL DING BOU NDARY
GISFIL EPAT H:G:\43559_North Cam p us\000_Global\GIS\Map s\2021_03\127827_023_0013_INDOOR_AIR_SCREENING_L OCAT IONS_FEB_2019.m xd ― U SER:dfm ― L AST SAVED:3/24/202111:40:33AM 0 60 120
SCAL E IN FEET
V14
0.024
AIR SAMPLING
LOCATION ID
TCE CONCENTRATION
MICROGRAMS PER CUBIC METER (μg/m3)
LABEL KEY
GROUNDWATER FLOW
FORMATION
EROSION
BAYPOINT
AST
ACCIDENTAL SPILLS /
LEAKS / DISCHARGES
STORM DRAIN
INFILTRATION /
LEACHING
BUILDING 99
MONITORING
WELL
PARKING RAILROAD
TRACKS
USTs / SUMPS / VAULTS
UTILITY CONDUITS / CORRIDORS
(ABOVE WATER TABLE)
VAPOR DEGREASERS
FUGITIVE DUST
PAINT BOOTH
BUILDING 29
PARKING VAPOR
TCE PLUME
FLOW
J:\GRAPHICS\127827\127827-023 CSM NORTH CAMPUS - AREA A 2020-1116.DWG Saved by: TAM Printed:11/17/2020 2:53 PM Sheet: PRES
FIGURE 14
ROHR, INC. A COLLINS AEROSPACE COMPANY NORTH CAMPUS - PARCEL A CHULA VISTA, CALIFORNIA
CONCEPTUAL SITE MODEL
NOT TO SCALE
APRIL 2021
ROHR, INC., A
COLLINS AEROSPACE COMPANY
NORTH CAMPUS - PARCEL A
CHULA VISTA, CALIFORNIA
EXPOSURE PATHWAYS
APRIL 2021 FIGURE 15
LEGEND
\\haleyaldrich.com\share\sdg_common\127827_North Campus\023_Parcel A Conceptual Site Model\Deliverables\Figures
APPENDIX A
Boring Logs
Ill
Ill
........ --
)
•
·-_.:))
L&G£rJD
f-----·------- )
MARINA PARKWAY
..._
t;:;
w
c:::
1-
C/l
Project: BFGoodrich
Project Location: Chula Vista, GA
Project Number: 98530678-0100
Key to Log
Sheet 1 of 2
• 0.
>
,_
-" •
E
0 z
0 ,g
•
0 aJ
COLUMN DESCRIPTIONS
Elevation:
Sample Type:
Sample Number:
Sample Blows/foot:
Grephic log:
MATERIAL DESCRIPTION
Medium dense, moist, brown, silty SAND (SM)
[solid line denotes observed contact between strata]
[dashed line denotes inferred contact between strata
or gradational change in soil type]
Samples obtained by using a wire-line core sampler
Distance lin feet) below the ground surface.
11-
Q E 0.0.
• 0. -uI a.
Approximate elevation {in feet) referenced from the ground surface. •
REMARKS
Type of soil sample collected at depth interval depicted; symbols explained above.
Semple identification number.
Number of blows required to advance driven sampler 1 foot, or distance indicated, using a 1 40-lb hammer (or as otherwise indicetcd) with a 30-inch drop. "•" indicates blow count for initial 6-inch seating interval of sempling only.
Graphic depiction of subsurface materiel encountered; symbology explained on Sheet 2 of Key.
Material Description: Description of subsurface materiel encountered, including USCS soil designation.
Well Completion log: Graphic depiction of well construction; symbology explained on Sheet 2 of Key.
He&dspace:
Remarks:
GENERAL NOTES
Photoionization detector (PIDl field headspece reeding (in parts per million).
NO indicates that no organic vapors were detected.
Comments or observations regarding drilling/sampling mad" by driller or Woodward-Clyde's field personnel
1. Soil clessifications ere baaed on the Unified Soil Clessificetion System (USCS) or recorded end include consistency/relative density (where standerd blow count correlation is possible). moisture, end color.
2. Descriptions on these boring logs apply only to the specific boring locations et the time the borings were advenced. They are not werrented to be representative of subsurface conditions et other Jocetions or for other times.
ATD = At time of drilling
NO = Organic vapors not detected
NR = Negligible to no recovery
.. Based on availeble topographic plen
Greiner Woodward Clyde ____ _ _j
Project: . BFGoodrich Key to Log
Project Location: Chula Vista, CA
Sheet 2 of 2 Project Number: 98530678-0100
SAMPLES
c 0 c
·- 0 0
.c' ·;; ' ,g MATERIAL DESCRIPTION ·;; E
- "' • ] • 0.0.
c.- >- .c • a. • 0. REMARKS
"" "" • E 3 0. =1j ., - o.e w-
-OJ 0. • C>
" :> 0 ' 0
• 0
>-- z "' (!)__, :S:u J:O..
UNIAEO SOIL CLASSIACATION SYSTEM
SYMBOL AND ROCK TYPE NAME VERSUS
CORRESPONDING GRAPHIC LOG
Sand
Clay
Silt
Silt/Sand
Sand/Clay
Gravel
Sand with cobbles·
SYMBOlS USED IN WE:U
COMPlETION tOG
Casing in cement grout
Casing in bentonite grout
Casing in Lones tar # 1/20 aand I\ I}
··'··'
Casing in Lonestar #3 sand
'ii
f:
! Slotted casing in fitter pack t::
c•. B-1
,,.,.,,_;,;o'-<•• URS Greiner Woodward G e
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 98530678-0100
og of Boring DB-1
Sheet 1 of '9
Date(s)
Drilled 1 1/2/98 through 1 1/1 2/98 Logged
By KS, VW, RKS Checked By RKS
Drilling
Method Mud Rotary
Drill Rig
Type CME 75, Canterra 550
Groundwater 3
levef (feet)
Location: South of BuiJding 61
._.
C:UJ 0
£ . g:2 ,g "' >.; .0 • "" "" • E 3 o.e _.,
w- a.
> 0 ,_ z 1ii
0 5
5 0
J NR
15 -10
20 -15
I
25 Drill Bit 94-mm wireline core.
SizefType 5 7/8" tricone
Total Depth
Drilled (feet) 30Z.O
Drilled
By
Date
Measured
Tri-County Drilling
1 1/2/98
Hammer Weight/
Drop (lbs/in.) ••
Approx. Surface
Elevation (feet, MSLJ 5.0
Borehole
Backfill Bentonite grout
MATERIAL DESCRIPTION
and other remarks
Asphalt over rock base and silt
olive brown, silty CLAY (Cl)
.- Becomes wet, dark gray to black, clay
,r-- Becomes reddish brown, silty CLAY {Cl) with trace send Wet, olive brown, clayey SILT {Ml)
- CLAY "(CU.- Wfth-
·-'t.io·t: ·a,JVe ·brown: ·siLt- ·y,;ith ·some ·cfa·v ·------·-· · ·-------- -- ·ci.Av· iCU--------------------------
-- W"e·t: .... s·AND-iSMi .. -
· V../o·t: tin;,· SAND ·,spr,· · ·--·---· ·-· ·-·---· ·--·- ...,_._ With trace of sand at 26.5 feet
·-wet·.· Oiive; browr;.-;fit¥ -tine; SAf..fD · fSMf sencf at·-- ·. 27.6' ·ciA y· iC:Lr---------------.----------.------------. .... u
0. c ·c .... : -. :o-" ·- 0>
- c >'- • 0 -. :!:u o:!:
Other Tests/
Comments
2'
ents at
end
GM
Project: SF Goodrich of Boring DB-1
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 2 of 9
_ __,
C:(f)
-5 .g:2
"'
>..;
"'""
o.!!' """"
_,
UJ30T -25
35 -30
40 -35
-40
50 -45
60 65 -60
D -" •
E "-> 0
>- z
MATERIAL DESCRIPTION
and other remarks
,r- Becomes silty at 33'
Wet, olive brown, Sll T (Mll
.. SAND -(SMY
·- 37.5-38.5' 1-.._-+--¥<8'<'+ ·,wet.- b·ro·wn.· Sf1tV ·cl.A'l tcu ·,;. .-itli- ·tine· · OiiV_e_ SAND- (SMi------------.----------------. -. i.i.fc·t: tO SAr'lD "iSWC
shells
.. iS Pi ·.;.:ith
shells
-- -iS Pi .. -----.... -------.--------.
-- SAND. iSCf--------------------------------
---r-+--biZit: ,-- "SAND- (SMi "CiA 'l (Ci..i.------
-.
'',With coarse szmd, shells and cley lenses from 52'-52.8' , ·to SiltY. c·LA Y 1CU .. -...... -........... . -Vl,;t: ·g;ayfsh ·to mediUn;-SAND ·,gpj ..... -......... -.. -- W"e·t: "s"iitY- iSM)
- t;ra·wr;,· sar;dy ·cLAY. tO "SANti iC-LtSCi--------
..,.
c
-·-
". c • 0
0 "- .<::: - Other c-
>"ii Comments
iB
, GS
,GM
Greiner Woodward Clyde ___
Project: BFGoodrich of Boring DB-1
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 3 of 9
MATERIAL DESCRIPTION *
c ' . and other remarks -·-c • 0 $:u
-_J
ccn
.<::
.,., .,.,
"' - o2 -Q)
I
1 I
70+ -65
T
75 -70
85 -80 - SANti (SM)-------------------------------
NR
95 -- S1i-f -fMU----------------------------
100 - -(5\M- -s-ilt-----------
0 a. ·'§ ...: Other
:J-li, Comments ·o
a$:
Project: BFGoodrich of Boring DB-1
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 4 of 9
-..J
C:.CJ)
.!::
-a.- "'
>.;
o2 "" ""
_,
wSAMPLES
0 • ,g .Q • c. • E ,. , 0
f- 2: a;
.<;
c.
""' 0 '-!l...J
MATERIAL DESCRIPTION
and other remarks
f · · ·ciA y· · ;{rt · · · · ·· · · · · · · · · · · · · ·- 1 05
TI _, 00
· · -,.; ·s.ANo· · · · --=
. .. . · · s".A.i·io · isF>i · · .. · · · ·---
I '.--J-'n"'-R·-.Lj-'--l::<<r
, J '" 1 : '""
_ .. "SiLT "{MiY With-
---.. --------------.---
· i.fiie·t: ·bray;.;: -tin;,-t·o ·me·dilim· s·ANo · fSPi ·with ·some ·silt- an·d · · · · · · ·- clay 1-·············································--···········-·········- Wet, olive brown, silty ClAY to c/4yey SILT (CL/MU ····························-·-········-···-·····-·················- Wet, reddish brown, fine silty SAND (SM}. with cll!y, micaceous
Becomes coarser grained
1.. /{ ·cLA•iiSC·,cu · · · · ·--· -·-
1'-+c=+--J · · ;;,<fd';;.t.· b·,;,;,v;;: · si\J\io ·.,:;;iti ·g;o,;;,r · · · --··································--····-·······-··················- Wet, brown, clayey SILT (Mll. with trace of very fine sand and gravel at 133' ·
r- - Becomes more clayey
............ -....................................................... - Wet, grayish brown, silty, fine to medium SAND (SM) SOIL !TIES
-·-c • 0
su
·'§ Other Tests/
:o-" ·if Comments
as
ITDs, GM
IP, GS
and
Greiner Woodward Figure B-2 Clyde ___
Project: BFGoodrich g of Boring DB-1
Project Location: Chula Vista. CA
Project Number: 98530678-0100 Sheet 5 of 9
150 -145
NR
155 -150
160
NR
65 -160
170 -165
MATERIAL DESCRIPTION
and other remarks
Becomes olive brown
Becomes dark gray with orange mottling
.. W""e·t: ·g;,;y: CLA-Y -tCLI-
. mottling ---------------.-----------....
With silt
;:_w;,-, cf.A-v -!CIT-------------------------------------- ,. Becomes silty
-W""e·t: C:L.A Y -(CLJ- SAf,fD (SMi
minor sm811 shells
-·vi,;t: "d8fk ·g;,;y: Cieyey· SAN[) (SC">- Sf1t------------------------ a ark· grey: ·cLAv· fCi.i ·witti ·some ·arT;eli · · ·------· · · · With troco silt
;j1
c
.
--. - c • 0
$u
0 0.
·c Other
:;:,-"
>'Iii "'Comments
as
is very
L,-,==,------URS Greiner Woodward Clyde ___
Project: BFGoodrich of Boring DB-1
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 6 of 9
_ _,
ccn .g:2
"' - "'"'
-<1>
w175+ -170
t
180 -175
185 -180 '.--J----,1-----1
MATERIAL DESCRIPTION
and other remarks
- ·dark ·brown: ·dayey-lftLT -<MLi: Wit-h sancJ an·d · · · -it.agments
__} With gravel
.._ With some silty fine sand
190 -1 8 5 .................................................................. . Wet, dark olive brown, ClAY {Cl) with trace silt -- W""e·t: -<SWf---.----------.--------
200 -195
<f.
c ' .
-·-c • 0 'i::u
0 "-
.. : Other T
=>-E.
>"C Comments
oi::
Project: BFGoodrich og of Boring DB-1
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 7 of 9
•...J
C(/J
-3::?:
"' - "'"
-Q)
210T -205
t
215+ -210 .-.1-+---i
T
I
225 -220
23o I -225
235 -230
240 -235
245 -240
u
Wet, gray.
MATERIAL DESCRIPTION
and other remarks
trace gravel
- -t-O -d·a,·k ·g;,;y .- san·dy-sicr· · · ·- dark gray, silty CLAY {ML-CL) with z:ones of iron staining ·wet·.-g;ay: ·to· san·dy "GR-AVEL"fGMI-------.----------.---- -- - "(SP) GRAVE-L---
(GPI
;!!
c
-·-'. c • 0 i:u
0 0.
·c....:
::>-" "'
oi:
Comments
at
with
bit.
by
Project: BFGoodrich
Project Location: . Chula Vista. CA
Project Number: 98530678-0100
260 -255
' •
J>
E ,.. , ,_ z
og of Boring DB-1
MATERIAL DESCRIPTION
and other remarks
Becomes sandy
Sheet 8 of 9
Comments
275 -270 . Wit: "biOWO "SAND -,s·pj------------------------------.---------- -275
Greiner Woodward Clyde ___
Project: BFGoodrich
Project Location:
Project Number:
_ _,
C:U)
£ "' "" ""
-Q) • w- "->
f-
-285
29 -290
3001-+-- -295
I 3Cl -l- -300
31 -305
31 -310
Chula Vista, CA
98530678-0100
0 • ,g ..0 •
E
, 0
z iii
u
.c
"-• "
0 "-'
J Clay
MATERIAL DESCRIPTION
and other remarks
Bottom of boring at 302 feet
Boring backfilled with bentonite grout
of Boring DB-1
Sheet 9 of 9
c " .
-·-c • 0 su
Other
Comments
Project: BFGoodrich
Project Location:
Project Number:
Chula Vista, CA
98530678-0100
Date(s)
Drilled 11/1 9/98 through 12/22/98 Logged
By K. Shirley
Drilling
Method
Drill Rig
Type
Mud Rotary
Failing F-8
Drill Bit 2" ID wireline core,
Size/Type 5" coring drag bit
Drilled
By THF Drilling
I Disturbed: NA i Undisturbed: NA Depth to Ground-1 Fi(st I Completion 1 Sampling 14 ! •• 1 14.14
Number
of Samples
Diameter of 12&S· 718 1 of 6 Hole {inches} ) Well {Jnches) Type of Lonestar #3 and 111/20
Fitter Pack.
Boring Location North of Building 99
c' 0 .Q .c <; ,g "' -" • "'" "'"' D E o2 -<> c. w- > 0
>-- z a;
0 20
5 15
10 10
15 5
20 0
Type of
Well Casing
Type of
Seal{sl
Schedule 80 PVC
Bentonite grout
MATERIAL DESCRIPTION
BAY POINT FORMATION
Asphalt over moist, brown, silty fine SAND (SM)
. ·sAND ·<s·p,· ·oi---.
silt
Moist, brown, silty SAND (SM) with trace of clay
.. b;o.;.,;n-.- SAND iSC-,-;,.it-h -siti -<Mli .•. --.
Becomes finer grained with trace of silt
Becomes coarser grained
.f= Becomes finer grained with trace of silt
,. Becomes coarser grained
Silt or clay? (confirm with E·log)
W---1----hd-·-·-······---------·-·-·········----·-------····-··-- wet, brown, fine SAND (SP) 25 wet: 01iV8 fine· to ·mediu,;.; s·AND iSMi-- · · ·--
of Well DB-2
Sheet 1 of 10
Checked
By R. Scott
Approx. Surface 22 0 Elevation (feet, MSL) •
Total Depth
Drilled (feet)
Sampler
Type
Screen
Perforation
• E c. c. .,_ • c.
:co..
380.0
Wire-line core barrel
0.020"
REMARKS
Greiner Woodward Clyde ___
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 98530678-0100
c
.c.· .Q
"' "" ""
-Q)
30l
-10
35 -1 5
40 -20
45 -25
50 -30
55 -35
60 -40
65 -46
70 •
0. >
>-
NR
NR
MATERIAL DESCRIPTION
Wet, brown, fine SAND (SP) with trace of medium sand
-b,-a·wn: SAND-(SM)----------.-- ------
With coarse sand and fine and medium gravel at 32'
_______________________ _
OiiVe- tine· to s·ANil ·(sM; With--·-
trace of clay
-t-O SAND- coarse sand (SW)
- "SilT -{Mli------------------
;eddiSh -,ittV ·cLAY ·<c·c,· ·o;
- s·,i. ;.· ·sA:No· cSPl
- SiltY ·cL.A·v ·(ci->----------------
Ci8Y8Y ·siLT {ML) With Oi _s_a_n_d--------
- -tO SA-Nti (SPi,-pc",Orl;;-.-.----
graded
of Well DB-2
Sheet 2 of 10
c
0 .,
•
0. =E
• 0
su
• E 0.0.
• 0. -oIO:
REMARKS
discarded
[b•,ca,usa it contained
mud.
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 98530678-0100
.c
-
a.-
""
70l
75 80
85 90
95 100
105
110
-50
-55
-60
-65
-70
-76
-80
-85
•
a.
>
,_
NA
u
:c
a.
""' 0
"'-'
MATERIAL DESCRIPTION
olive brown, silty fine SAND (SM)
.. iSP1- -t·race· Of -si1t--------
---------.----.----------------.---------------.------
Wet, brown to olive brown, silty fine SAND (SM) with
trace of clay
wer.· very -,inS to· SAND-(SPI.-With ;;ace ·or---·
sitt
Wet: S"ANO ·(sc,· .;..;iih
-Wet·; SA"Nfi iSP,- ----------------------.----.
+---- With some medium and coarse sand
Wet, olive brown, very fine SAND to silty SAND (SMJ
Greiner Woodward Clyde
of Well DB-2
Sheet 3 of 10
c
0 . .,
•
a. =E
• 0 su
• E a. a. • a. ., -
I"-
REMARKS
Hydropunch sample
DB-2-HP77 obtained
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 98530676-0100
£
"'"'
110l
115
120
125
130
135
140
145
c::
.g
"'
"" 0 -<I> a_
w- >
....
·90
·95
NR
·1 00
·1 05
·11 0
MATERIAL DESCRIPTION
-wer.: iS Pi·--------·-··---·······-----
·siity· SANO-(Srii>-----.-- ---.--------.-.-
r-- Becomes silty with shells
•
--------------------------------------·---------------- Wet, dark gray, silty SAND {SM) with shells
- cSV.i)- ·o;---
silt and fine gravel
of Well DB-2
Sheet 4 of 10
o_
E "-"- • a_ "-
o_ oo
I a.
REMARKS
IC obtained
Project: BFGoodrich g of Well DB-2 Project Location: Chula Vista, CA Project Number: 98530678-0100
.<::
a.-
o!
"""
150
155
160
165
170
175
180
185
c:-
0 0
·;; t ,g "' .0 • """"
_., •
0. E w- ,. 0 0
>- z a;
.130 I NR
:.-.1---+---
. 1 3 5 ,Ll.,__-:c::c-+---1 NR
MATERIAL DESCRIPTION
1'-+---:-::::--f---l+S+lNA
. -.................. -......... -............. -........ . Wet, gray, silty tine SAND (SM) .r--- Becomes silty clay with light gray mudstone clasts -145
With light gray mudstone nodules, with iron staining
Viet: iii:,-ht Sil ;-· (-Mi.i
layers
-150
-155
- ;i;,:y SAND (SMf With
NR - ;iit·v· GRAVEL----
IGMJ
-160
NR
-165
--------------.--.----------------.-.-------.---------
Sheet 5 of 10
REMARKS
\ C<>btoleo at 1 80'
to obtain core
samples; drilling
bi-cone
181' to 210',
logged using drill
!cutti<lgo
Project: BFGoodrich og of Well DB-2
Project Location: Chula Vista, CA
Project Number: 98530678-0100
190
-170
195
-175
... ----.---------------------------------------------- Wet, brown, CLAY {CL), with silt 200
-180
205
-185
210
------------------------------------------------------- Wet, brown, silty fine SAND (SM)
215
------------------------------------------------------ -195 Wet, brown, fine to coarse SAND (SWJ 220 -wet; SftiY ·cLAY (Ci.i---------------.-.--
-200
225
.._ Becomes corarsar grained
--- G-RAVEL -<GCi---------------
NR
230
Sheet 6 of 10
REMARKS
Project: BFGoodrich Log of Well DB-2
Project Location: Chula Vista, CA
Project Number: 98530678-0100
2301
·210
235
·215
240.
·220
245
-225
250
·230
255
260
265
·246
a. •
>
....
NR
NR
MATERIAL DESCRIPTION
Dry to moist, brown, fine SAND (SP) with some silt and
trace gravels
tO SAND (SWi
lenses
Sheet 7 of 10
c
.Q
;;
c.
=E
• 0 :S:u
·-
lj E 0.0.
• 0. ., -
:I: a.
REMARKS
\Mate•ialvery dense;
unable to obtain core
barrel samples;
II with bi-cone bit
3to241'
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 98530678-0100
c
0 .c . .,
"'
o!:! """"
_.,
270
-250
275
-255
280
-260
285
-265
290
-270
295
-275
300
-280
305
-286
310
•
c.
>
>--
MATERIAL DESCRIPTION
--- .. ------.--.-----------.-------.------ ..... - Wet, olive brown, silty CLAY (CL) ·wee.· ·b,"c;;..n·. ·siitY-very ·sAi-iO ·wrt;,·
clay lenses
-ory ·ro morst: brown: (SPl v;ith· r·,ace· ot- · ·
'.sitt
-;;;.;;-i
GRAVEL (GW)
------------------------------------------------·····-
Moist, reddish brown, silty CLAY (Cl)
------------------------------------------------------- of Well DB-2
Sheet 8 of 10
• E c. c. • c. -,-
Iii:
REMARKS
I to obtain core
samples; drilling
bi-cone
295.5' to 306'
Project: BFGoodrich g of Well DB-2
Project Location: Chula Vista, CA
Project Number: 98530678-0100
J::
o.e ""
310
315
320
325
330
335
340
345
,:
0 ·;:;
"'
"" 0 -aJ o_ w- >
I-
-290
-295
-300
NR
-305 'r-.1-----t------1
-310
-315
-320
MATERIAL DESCRIPTION
Moist, reddish brown, silty fine SAND (SM)
gravel and silt
. w;t: ;;tty s·AND (SMi
- .. SAND-(SP)---------------------------
Sheet 9 of 10
c
-E
0 c_
=E
0 0 3:u
0 E o_o_
,_
oo_
•o
o_
J:O.
REMARKS
dense sand
to cor&);
!co•nellate with E-log
,,,JI"''i ..
Greiner Woodward Clyde
Project: BFGoodrich og of Well DB-2
Project Location: Chula Vista, CA
Project Number: 98530678-0100
<:AMPI <=<:
c:'
0 0 .c ·;:; ,g MATERIAL DESCRIPTION "' • 0
.c :c • w" "" • E c. -w ,..
c. 0 0 . "' "0
>- z "' "--' 350-
Wet, brown, SILT (Ml), with clay
f- -330
355-
--335
360-
f--340
-wet: brown.· SittY sAND -,sM5- ·------·--·-·-· · · ·--· · · · · · 365-
f--345
370-
f--350
375-
---355
380-
Bottom of boring at 380 feet
+·-360
385-
---385
390-
w"m_,c= .,.,-----URS Greiner Woodward Clyde
Sheet 10 of 10
c
0 . ., • E • c. c. c. • c. REMARKS -ES -o-
• 0
SU...J Io..
- ttttttt1
.
-1
-
Project: BFGoodrich of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 1 of 9
Date(s) 12/17/98 thmugh 12/22/98 I Logged L. Jacobs Checked R. Scott Drilled By By Drilling Mud Rotary, steel conductor Drill Bit 6'" core bit Total Depth 306.0 Method Sizeffype Drilled (feet) Drill Rig Ingersoll Rand TH-100 Drilled Beylik Drilling Hammer Weight/ NA Type By Drop {lbs(in.)
Groundwater 6 Date Surface
Level (feet) Measured Elevation (feet)
Location: Northeatct corner of former Building 56 Borehole Cement-bentonite grout BackfiJJ _ _, '<dMPt FS SOIL
ccn 0 ;j!. <:;
£ .g2 ,g 0.
Other Tests/ ' MATERIAL DESCRIPTION .'!:::: • "' • 0 c c- "' • :c -. :::>-§, "" "" • 0 0. and other remarks ·- Comments o2 -Q) 0. . "' w- - c >'4i > , 0 • 0 >- 2: "' - 0 S:u iSS:
0- "'-'
NR AN 11FICIAL FILL 1; 5 · with
0.2' asphalt over subangular sandy gravel
BAY POINT d d Moist, redd1sh brown, Wit me 1um to coarse san leasing to 1 5'
5- _,r-- Trace of gravel - ...................................................................... - ·Moist to wet, brown, clayey SAND (SC) - i••7ple
10- r- - ,..,Q 0 U010) I .......................................................... ............
Wet, dark brown, silty SAND to sandy SILT (SM/ML)
••
••••• 15- •• r- - •••••• coring .................................................................... - 5" Wet, brown, fine SAND (SP) with trace of silt
Nt<
20- -· .................................................................. ·- Wet, olive, CLAY {CH) with trace of silt
r· .................................................................... - Wet, olive, silty fine SAND (SM), with iron staining 25- I 1- -
.............................................................. ' .... - Wet, olive brown, fine SAND (SPl. with iron staining ,...- With trace of silt •
30-
URS Greiner Woodward Cl de Figure 8-4 2/19199 IGLGIO 5J051 Project: BFGoodrich og of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 2 of 9
30-
35-
40-
45-
50-
55-
60-
65-
•
0. >
>-
.0 •
E
,
z
NR
NR
0 l!h MATERIAL DESCRIPTION
and other remarks
,r- With trace of clay
--------------------------.--·--. -- ·---------------------------------- reddish brown, silty fine SAND (SM) with trace of clay !l@!l\l:l _] With trace of coarse sand from 37.5 to 39 feet k-----------·--------------.------------------.-------------------- Wet, reddish brown, clayey SILT (Ml). with trace of fine sand =:J- Silty SAND (SMI
ri,Y,t+--- fSMi ------------------------------.. ----- . - W'"e·t-. ·sAND -<SPf-------------.----------------------- NR
NR -------------------------------.------------------------ Wet, .. ----.... - brown, SILT (Ml)
I
I NR =:J- Light brown, silty sand layer
1'--'1-=NR+--l'rlll"'l is Mi ..
$Q DDt"" :s
# 'E Other Tests/
::I.e
iii § Comments
su os
'-7,;;;;,, , .,.,,""'oc••""''·"='·" • _____ URS Greiner Woodward Clyde ____ Project: BFGoodrich og of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 3 of 9
--J
CCI)
.c "'
>..;
"" ""'
-<u •
c.
>
,._
70 75
80 85
90 95
100
-" •
E
z
MATERIAL DESCRIPTION
and other remarks
Wet, brown, SILT (Mll
· ·siLT ·(Mii ·w-ith· · · · · ·
fine sand
Becomes finer grained and silty
- SANii iSC}---------------------------------
-- c·LA y·<c-LJ----------.----.-----------------
-- SAND ·<g·p;
......_ With some medium send
--- .......... -- ...... -... ··-.... ·----· ...... --.---------.... --- ... . Wet, light gray to brown, sandy CLAY (Cll :::J-.- ------.------------------.----.---------
*
c
-
.
-. -
c • 0 3:u
0 c.
·i§ -· Other
:>-§,
>"ii Comments
c;:;::
"--<===:;------URS Greiner Woodward Clyde ___
Project: BFGoodrich •
Log of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 4 of 9
•...I
""'
.c .g:E t >-' "' -" "" "" • E o.!'! -Q) c. w- >
f- z
105
1 10
1 15
120
125
130
135
0 ,g
0 0
a;
MATERIAL DESCRIPTION
and other remarks
Wet, olive brown to brown, fine SAND (SP} with iron staining -- SAND -(SPi
Light gray, fine to medium SAND (SW)
With clay
· g·rav·.-SiitY ·etA v· fCi.i ·iron·
· v .. grey: "tine· SAr'fD "fSPf With -t·race· Sltt · · · · · ·-------------· -- g;;y· SIL. f (Mlf--------------------------------------- - ·sAND-iSMi--.-----------------------------
With CLAY (Cll layers
"tfQht ·t·r;; "dtiV;, ·
With shelf fragments
With trace of coarse sand and more shell fragments
Becomes yellowish brown with trace of silt
c
-·-
". c • 0 $:u
Comments
Project: BFGoodrich Log of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 5 of 9
._J
CU)
.c "'
>..;
CJ-1: "" w-
-OJ ""
140-
145-
150-
155-
160-
165-
170-
• MATERIAL DESCRIPTION .Q
•
c. E >
f- z
and other remarks
- .- ·da;k SrLT -1MU ·v,;;th 'o"f ... --------------
162 1··------------------------------------------------------------------- f- Wet, d8rk brown, clayey coarse GRAVEL end cobbles {GC) _ V'1 with trace of sand · NR
-
l-l--+----fH"#---V..i,;t·. ·siLT -<M -<
-
--------------------------------- 1-1--+----f'ff"ft---W"e·t: "CiaVOV SA]\.iQ ·csci: ..... - end aome medium send NR
--------------------------------------------------------------------- Wet, brown, fine to medium SAND (SW) with trace of gravel SOIL !TIES
*- u
0. ·2..: Other Tests/
::J-" c >"C " Comments • 0 3:u a:::
fori/1 chatter
URS Greiner Woodward Clyde ___
Project: BFGoodrich Log of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 6 of 9
-5
""'
175-
180-
185-
190-
195-
200-
205-
210-
0 ,g
•
0 ii'i
,4-,-;;;---+----t f- NR
MATERIAL DESCRIPTION
and other remarks
-
With some clay and cobbles · --------.. --.----------. - - L--.l---1-_...j Wet, brown, SILT (MLI with of clay
-
(Coarse gravel and cobbles)
NR
-·· ........ .... ... ... ........
NR
.. ... ................. ........... ......... ...... Wet, brown, fine to medium AND (SPI SOIL
* 0 c.
C ·c:.; Other Tests/
:J.J: ... c; Comments
as
bit lost
in borehole
,,.,.,,= '"'",.,,=0.,-----URS Greiner Woodward Clyde
Project: BFGoodrich of Boring DB-3
Project Location: Chula Vista, CA
Project Number: 98530678-0100 Sheet 7 of 9
_ _,
C(J)
.c
>..: "'
a2 "" ""
-<>
w210
215
220
225
230
235.
240
245
' • .0
•
c. E
>
>-- z
0 ,g
•
0 a;
MATERIAL DESCRIPTION
and other remarks
· ·(s·w,- ·tine··-···--- .. gravel ·cLAY-fCU ---.--------- .... -----.---------.------. 1--1---+---ffLI"Tt--- "SiLY {rjfLI: ·.;;ith ·c,-aV fi'n·e ra-.;ers---.-.
Becomes coarser grained
=:J- With coarse sand and fine gnwel
.
Wet, brown, fine to coerse SAND (SW} with trece of silt ------------------------------------------------------------------- " ;:
-·-'. c • 0
;;:u
u
c. :'::: - c- ::>-"' " Comments
o;;:
Greiner Woodward Clyde ___
Project: SF Goodrich of Boring DB-3
Project Location: Chula Vista, CA
Sheet 8 of 9 Project Number: 98530678-0100
•...J
r:Ul
-5 "' - o2 ""' "'"
_,
250-
255-
260-
265-
270-
275-
280-
'" I O'C:
0 :; ,g .0 • E
0 0
z a;
'NR
0 :c
c.
""
"0 <!J..J
MATERIAL DESCRIPTION
and other remarks
--------................................ ·-.-.. ---.--- .. -.. -... -- .. -- .. - Wet, brown, fine to coarse SAND (SW) r -
- "tSP) -- ·--.---.----------.-------
l r--- Becomes coarser greined t-"'- Wet, -_-- --.-------------------------------.-----------------------.. - olive brown, CLAY (CL) ---------------------------------------------------------------------- '1- Wet, olive brown, silty SAND ISM) _
v: _. olive brown, SILT (ML)
Becomes reddish brown and clayey with trece sand
"' -
r- Becomes brown
Becomes 8<1!1ndier
11rl Wet, brown, SILT (Ml) with trace cl8y
---
Wet,
-- ---- ----- -------- ---- -- -. --- -- -. -- ----. ----- --------- ----. ---- --. brown to olive brown, silty fine to medium SAND (SM) r- S8od becomes co8rser gr8ined
SOIL riES
c -. -·-c • 0 S:u
u
·;§ Other Tests/
=>"'
Comments
as:
L,=, .. ,G,Gio,=.,o,,------URS Greiner Woodward Clyde
Project: BFGoodrich og of Boring DB-3
Project location: Chula Vista. CA
Project Number: 98530678-0100 Sheet 9 of 9
285-
••••
290-
295-
NR
305- . NR
310- -
315- -
MATERIAL DESCRIPTION
and other remarks
=::r Brown, silty clay
-- ·sANtY iSMi--- ·-
Becomes medium to coarse sand
Becomes silt
Sand becomes coarser grained
·························-
-
-
.................................................................... - Wet, olive brown, SILT (Ml) Become sandy
Becomes clayey
:=J-- Becomes silty sand
Bottom of boring at 306 feet
-
-
-
-
-
SOIL
c
.
-. - -
c 0 0 3:u
y
0. ·1§ _. f Other Tests/
::>"' Comments
o3:
. .""'?'P.i•. lcollccted dut
to
.. URS Greiner Woodward Clyde ___ ---=.F.:a.::.:.igurre::...:B=-- 4 :__.....J
"
-- 78
) 79 a
11 443
0 0
I 57
61 0 300 600
APPROXIMATE GRAPHIC SCALE
(FEET)
"
"
:r:
29 u
I
l5 kd.J..:j
"'
1 B
"' 00
55 ,., "' [
54 Q
-a
46 •'·
OULEVARo
t;j 1 E::::J cc::::::=:-,
WAIN! IT A\tfNtw:----' -- - - - -
"
3 4 5 ,....::.0__,23
L,c__ _ ___J sf 0,..
rn
"
849
=
42 w
0::
1-
(/)
851
" l
'I " L
t"67 I
u· ..
0 MARINA PARKWAY
___ __.!.:->
"
"
0 5
SITE FACILITY
BFGOODRICH - CHULA VISTA
VBAY BOULEVARD
LANDSCAPING LANDSCAPING
'
I I
BUILDING 99
PARKING LOT
BLDG. 100
' " " ., " .,
I I I I I I I I I I I I
I I I I I I I I I I
SAN DIEGO & ARIZONA EASTERN RAILROAD RIGHT -OF -WAY
LEGEND
¥B-4 ·APPROXIMATE LOCATION OF WELL
)( CHAIN-UNK FENCING
AQUIFER TESTING WELL LOCATION MAP
BFGOODRICH - CHULA VISTA
BY: I DATE: 1 a:.. 1-99 I ;1 NO: "'l57B.oo
I
I
" z
(/")
0 DRIVEWAY
v
I
I
I F1G. NO: 2
I
I
URS Greiner _,,vv
0 10'
20'
30:
40'
50'
60'
70'
80'
45.2'
54.3'
59.4'
BOTTOM OF BORING
AT 80 FEET
0 10'
20'
SCHEDULE 40
BLANK PVC CASING
30'
CEMENT
ENVIROPLUG
BENTONITE PELLETS
0.020" SLOTTED
PVC SCREEN
LONESTAR
#3 SAND
BOTTOM OF BORING
AT 30.7 FEET
OW-3 MATERIALS
CEMENT
SCHEDULE 40
BLANK PVC CASING
ENVIROPLUG
BENTONITE PELLETS
0.020" SLOTTED
PVC SCREEN
LONESTAR
#3 SAND
7 BAGS LONESTAR #3 SAND
2 BAGS ENVIROPLUG PELLETS
20' PVC 0.020" SCREEN PIPE
1 0' SCHEDULE 40 BLANK CASING
OW-4 MATERIALS
1 0 BAGS LON EST AR //3 SAND
4 BAGS ENVIROPLUG PELLETS
10 BAGS PORTLAND CEMENT II
1 BAG BENTONITE POWDER
20' PVC 0.020" SCREEN PIPE
60' SCHEDULE 40 BLANK CASING
Project: BFGoodrich Key to Log
Project Location: Chula Vista, CA
Sheet 1 of 2 Project Number: 58-98530676.00-00400
-5
CY
o-2:! "'"'
c:
0 ·;:;
"' >- "'"' _., • w_ "-> ,_
I
.c •
E
z "
MATERIAL DESCRIPTION
Medium dense, moist, brown, silty SAND (SM)
[solid line denotes observed contact between strata]
[dashed line denotes inferred contact between strata
or gradational change in soil type]
Wire-line core barrel sample
c
0 ...
•
= • 0 :S:u
• E "-"-
""-
., -
J:o..
REMARKS
COLUMN DESCRIPTIONS
[}]
0 IIJ
@]
[_[]
Elevation:
Sample Type:
Sample Number:
Sample Blows/foot:
Graphic Log:
Distance On feet) below the ground surface.
Approximate elevation (in feet) referenced from the ground surface.* Type of soil sample collected at depth interval depicted; symbols explained above.
Sample identification number.
Number of blows required to advance driven sampler 1 foot, or distance indicated, using a 140-lb hammer (or as otherwise indicated) with a 30-inch drop. " .... indicates blow count for initial 6-inch seating interval of sampling only.
Graphic depiction of subsurface material encountered; symbology explained on Sheet 2 of Key.
Material Description: Description of subsurface material encountered, including USCS soil designation.
Well Completion log: Graphic depiction of well construction; symbology explained on Sheet 2 of Key.
Headspace:
Remarks:
GENERAL NOTES
Photoionization detector (PI D) field headspace reading (in parts per million).
NO indicates that no organic vapors were detected.
Comments or observations regarding drilling/sampling made by driller or URSGWC's field personnel
1. Soil classifications are based on the Unified Soil Classification System (USCS) or recorded and include consistency/relative density (where standard blow count correlation is possible). moisture, and color.
2. Descriptions on these boring logs apply only to the specific boring locations at the time the borings were advanced. They are not warranted to be representative of subsurface conditions at other locations or for other times.
NR - No Recovery
•Based on available topographic plan
Figure A-1 .... ;;;-;wc,;cu;;;;;;-,:m;; "'"';;;;;;, • .,,,.,w"""".:--URS Greiner Woodward Clyde Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678-00-00400
c:
0 -= ·;::;
-
c.- "' >- .<> • "" "" 0 E o.e -Q) c. w- > , >- z
M
Sand
Clay
s;lt
MATERIAL DESCRIPTION
UNIAEO SOIL CLASSIACATION SYSTEM
SYMBOL AND ROCK TYPE NAME VERSUS
CORRESPONDING GRAPHIC LOG
Silt/Sand
Silt/Clay
SYMBOLS USED IN WELL
COMPLETION LOG
Casing in concrete
Casing in cement/bentonite grout
Casing in bentonite chips or pellets
Casing in bentonite/sand
Slotted casing in f1lter pack
to Log
Sheet 2 of 2
c
0 c.
= 0 0 ":.s
REMARKS
Project: BFGoodrich of Boring::::DB:-4::==
Project Location: Chula Vista, CA --- Project Number: 58-98530678.00-00400 Sheet 1 of 15 Oate(s) 6/16/99 thmugh 6/22/99 Logged A. Greene Checked R. Scott Drilled By By Drilling Mud Rotary Drill Bit 6.25"112.26" tricone Approx. Surface 22 0 Method Size!Type Elevation (feet, MSL) • Drill Rig T -3 lngersoi-Rand Drilled Beylik Drilling Total Depth 555.0 Type By Drilled (feet) Depth to Ground-i First i Completion ! Sampling Number I ! Undisturbed: ·- Sampler water (feet, bg3) i 14 ' I of Samples 1 Disturbed: -- Type Wire-line core barrel '
Diameter of 12.25 1 Diameter of 4 Type of Schedule 80 PVC Screen 0.020" Hole (inches} ! Well (inches) Well Casing Perforation Type of Lonestar #3 Type of Bentonite chips and cement/bentonite grout Filter Pack Seal(s) Boring Location North of Building 99
'"'DI FS
c: .; "- 0
.s::;" ·;; u MATERIAL DESCRIPTION g E
- "' :;: c. c. .,., c.- .,.,
>- .n •c. REMARKS • E c. -co2 -<ll c. me> >- 0 j 0 .... z "'-' I c.. ol '-' Ill i l POINT FORMATION
-w 2" asphalt parking lot over 3" base material over medium dense, moist, reddish brown, silty fine SAND (SM)
20 Becomes less dense
5- -
-
-15
",r- Becomes moist to wet, medium brown, fine to
medium SAND with silt (SM), micaceous
10- lliJIIt -
10 15-
jr Becomes wet
-
-
-5 J
20- .,.__ Interbedded clay layers -
I
1/
0 25- -
-5
30-
URS Greiner Woodward Cl de _l'i!!llre l/1 tl/00 1 WL 1 tiFGOO Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
" 0
.<:: .,
"' "" "" -QJ
w30l
·1 0
35 ·15
40 ·20
45 ·25
50 -30
55 -35
60 -40
' • -" • c. E
>
... z "
MATERIAL DESCRIPTION
Becomes wet, grayish brown,
(SP)
Becomes finer grained
to medium SAND
Dense, wet, grayish brown, silty to clayey fine SAND
ISM/SCI
Slight increase in grain size, fine to medium sand
Becomes poorly graded fine to medium SAND with
little silt (SP)
of Boring DB-4
Sheet 2 of 15
c
0 . .,
• c.
=E
• 0
!!:u
REMARKS
Project: BFGoodrich ..
Project Location:
Project Number:
.!:
.,.,
o2
75 80
85 90
95 100
105
110
·55
-60
-65
-70
-75
-80
-85
Chula Vista, CA
58-9853067B.00-00400
" .c
E
z
MATERIAL DESCRIPTION
r-Increasing reddish brown SILT (SM)
Dense, wet, medium brown, silty fine SAND (SM)
Becomes grayish brown, fine to very fine sand with
silt
of Boring DB-4
Sheet 3 of 15
c
0 "i
c.
=E
• 0
S:u
• E "-"-
.,_ me_
•o
Io..
·-
REMARKS
Project: BFGoodrich log of Boring DB-4
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400 Sheet 4 of 15
115
-95
120
-100
125
-105
130
-110
135
-115
140
-120
145
-125
150
c.
>
....
.c
E
z
MATERIAL DESCRIPTION
Becomes dark gray to olive, fine to very fine sand
with silt
Becomes olive gray, fine to medium SAND with
little silt (SP/SM) and coarse sand
Becomes clayey fine SAND (SC) with shell
fragments
c
0 ·;
Q_
=E oo :S:u
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
155
160
165
c:
0 ·;:;
"' "" -Q>
UJ-
-130
-135
-140
-145
not""
175
-155
180
-160
185
-165
• c.
• .D
E
z "
MATERIAL DESCRIPTION
&+····················································· Dense, wet, dark olive gray, silty to clayey fine SAND
with trace medium sand {SM/SC)
Increasing Sll T with little fine sand (ML)
Wet, grayish brown to gray, fine to coarse SAND
with subrounded gravels (SP/GP) 3/4" gravels
of Boring DB-4
Sheet 5 of 15
c
0 c.
=E
• 0 :S:u
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
c
0 ·;:;
"' >- "" _.,
w-
• c.
>
...
MATERIAL DESCRIPTION ..0
E
,
z
of Boring DB-4
Sheet 6 of 15
c
0 .,
• c.
=E
• 0 :?:u
REMARKS
1901 --------------------------
J -170
195
-175
200
-180
205
-185
210
-190
215
·195
220
-200
Decreasing gravels
Dense, wet, reddish to grayish brown, silty to clayey fine to medium SAND (SM/SC)
Gravel lanse
oen·s·e-,- ·siitV- SANDsand (SM)
225l
'-===;;;;--,.------URS Greiner Woodward Clyde
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
23 -210
235
I -215
240
-220
245
-225
250
-230
255
-235
260
-240
265
.0
E
z
0 ,g
0 0
ii5
MATERIAL DESCRIPTION
Dense, wet, reddish brown to brown, fine to medium
SAND with silt (SM)
of Boring DB-4
Sheet 7 of 15
·-E
.
"-"-"- -o-
•o
J:Q_
·-
REMARKS
Project: BFGoodrich
Project Location:
Project Number:
270
275
280
285
290
295
300
305
c:
0 ·;::;
..
Q)Ql G W2 g:
>-
-250
-255
-260
-265
-270
-275
-280
-285
Chula Vista, CA
58-9853067B.00-00400
0 0
"" • 3
0 iii
MATERIAL DESCRIPTION
Dense, wet, grayish brown, silty to clayey fine SAND
(SM/SC)
Light brown, poorly graded fine to medium SAND
with little silt (SP)
,r-Increasing gravels
of Boring DB-4
Sheet 8 of 15
·-E "-"-
""- -e- Go G_
:I: c.
REMARKS
Project: BFGoodrich Log of Boring DB-4
Project location: Chula Vista, CA
Project Number: 58-98530678.00-00400
,;
0 0
£ :;::; 0; 0
"' "' 0
.r. • :;: .,., .,., • E ;: Q.
o-2! -Ql w_ Q. me> > 0 0
>- z 10 "-' "1 ·290
·295
Run 2
320 Run 3
·300
325
330
·310
1 Run 8
335
·315
340
345
NR
350
MATERIAL DESCRIPTION
oen·s·e·,-We·t: gray· t-0 reddiSh ·very-fine· S&ndysiL T to silty fine SAND (SM/ML) ...__ Becomes dark gray, fine to medium sand with little ...- silt and coarse sand
, ____ ____________________ _
Dense, moist olive gray, silty fine SAND with little clay sand (SM)
Becomes reddish brown, lean CLAY with trace fine
sand (CL) -------------.-------------------------------------- ·.,Dense, wet, grayish brown, poorly graded fine to , .. ______________________ _ :
wet, dark brown, silty fine SAND with few thin
- _,.,.o,;;um sand lenses (SM), micaceous
_____ _ _______ . ___ . ______________ _ Dense, wet, reddish to olive brown, fine sandy SILT to silty fine SAND (SM/ML)
Olive brown SILT (ML)
Sand nodule concretion
,r-- Becomes dark brown, clayey fine SAND (SC) to fine
sandy CLAY ICL}, trace medium sand
,r-- Becomes brownish dark gray, clayey fine SAND
with interbedded fine to medium sand lenses (SC)
r-- Becomes dark gray. fine to medium SAND with silt
.,. ISP/SM)
Dense, wet, dark brown, silty fine SAND ISM)
Becomes dark brown to dark brownish gray
Dense, wet, dark yellowish brown, very fine sandy CLAY
(CLJ
Sheet 9 of 15
c
0 c.
=E
• 0 3:u
REMARKS
#1, 315'-324'
#2, 324.-333'
#3, 333'-345.5'
#4, 345.5'-357.5'
Project: SF Goodrich
Project location: Chula Vista, CA
Project Number: 58-98530678.00-00400
-5
.,.,
a.-
350
355
360
365
370
375
380
385
390
c
0 ·;:;
.,
.,.,
>-
-Ql
w-
-330
·345
·355
-360
• "->
fMATERIAL DESCRIPTION
Becomes dark yellowish brown, silty fine SAND to
fine sandy Sll T ISMIML)
Medium coarse sand lense
Dark grayish brown, fine SAND with silt and
medium sand {SM)
1--1--=-:-cc;o-+---fi"'r'TI-r- Becomes fine sandy silt
Run 24
NA
Grayish brown very fine sandy silt
Concretion
Very dense, wet, brown, fine to coarse SAND with silt
and few gravels (SP/SM), gravel 3/4 ..
-very wet: medfum· t-O (fa-,k-bro;.;n; S1it"Y very -t-ine---- to fine SAND (SM) Becomes brownish gray
Reddish brown, fine sandy SILT lanse (ML)
Interbedded fine to medium SAND with silt and
trace coarse sand (SM)
Reddish brown, fine sandy SILT lanse (ML)
Coarsens to fine to medium sand wtth little silt
Dense, wet, medium brown, silty fine SAND (SM)
Dense, wet, brownish gray, fine SAND with silt (SP/SM), micaceous
Dense, wet, grayish brown, fine to coarse SAND with
silt and few gravels (SM)
-
365 ·ro ve·ry-dense: OliVE;
Run 26 fine sandy SILT to CLAY (ML/CL)
Becomes more sandy (SC), concretion
Concretion
of Boring DB-4
Sheet 1 0 of 1 5
·-
E "-"- REMARKS
:ro..
#5, 357.7'·373.5'
#6, 373.5'·383'
#7. 383'-395'
Project: SF Goodrich
Project Location: Chula Vista, CA
of Boring DB-4
Sheet 11 of 1 5 Project Number: 58-98530678.00-00400
c·
0 .<: ·;:;
.,., .,., "'
o2 -Q) UJ390l
--370
395-
O:AOAPI 0:0:
0 ,g 0
.0 • 0 :c
• E c. c.
> . " " 0 0 .... z iii Cl...J
MATERIAL DESCRIPTION
Run 27
Run 28 I
w ........................................................
Dense, wet, olive brown, silty very fine SAND (SM),
micaceous
- Run 29
- reddis-h ve·ry-fine· sanay· SIL-T ·to- c·cAv----
(MUCL)
ljH: wet, dark brown, silty fine SAND (SM),
micaceous
Reddish brown, sandy SILT (ML) to CLAY (CL)
Redd1sh brown, sandy Sll T to CLAY (ML/CL) to
olive brown to dark brown, s1tty very fme SAND
(SM) to very f1ne sandy SILT (ML) ) ,r-- Becomes more dark brown and SILT (Mll ,r-- Becomes dense, olive brown, silty very fine SAND
(SM), micaceous
Concretion
-
-
.... ·; .................................................... . Hard, wet, reddish brown, fine sandy CLAY with medium coarse (CL) to clayey medium to fine SAND (SC)
,r-- Becomes more clayey (CUSC)
..,._ Concretion
,r-- Becomes greenish brown, silty very fine SAND (SM)
,r-- Dark olive gray, silty fine sand with gravels
- 2.5" gravel
1" gravel
-
-
m' ·········-··············································· c
0 . .,
0 c.
= E. 0 0
5:u-"
= = ::
c::
=
= =
REMARKS
Box #8,
Box #10, 414.25'-428'
!Box #11, 428'-442.25'
Greiner Woodward Clyde -------'-F=i 9UI"e:___-'
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
.s:::
15.-
o.e ""
440
445
450
455
460
465
·425
-430
-435
-440
-445
c -" •
E "-> " ,... z
Run 42
NR
Run 44
0 ,g
•
0 1D
MATERIAL DESCRIPTION
Dense, wet, olive gray, poorly graded fine
little silt (SP), contains trace gravels
Dense, wet, light brown, poorly graded fine SAND (SP),
NR
NR
Run 49
NR
Run 51
NR
Core 53
Run 56
_t_?_ !i!l!!. ____________________ _
Dense to hard, wet, medium brown, fine sandy CLAY to
silty fine SAND (interbedded) (SM/Cl)
Brown, lean CLAY (CL)
- -tine ·sAND ·..:...it-h ·--·- (SCI
Becomes more sandy (SP)
+---Cuttings are light brownish to greenish gray, poorly graded fine SAND with medium sand (SP)
-very· -,i9
-ht- to gray.-SitiY--
fine SAND (SM)
Sandstone concretion 2"x2"
---- Very dense, moist, reddish brown to olive brown, clayey fine to medium SAND with trace coarse sand (SC)
oer;se-.-,;.;o1st: t1ne- SAND (SMi.-----
Becomes brownish gray, fine sandy SILT (ML)
Becomes reddish brown, SILT to CLAY (MUCL)
Reddish brown, fine sandy silt to clay
Silty fine SAND with trace medium sand (SM)
Silty fine SAND with trace medium sand (SM),
coarsens with depth
Reddish brown, fine sandy SILT to fine sandy CLAY
(ML/CL) ----------------------------------------------------- Dense, moist, reddish brown, silty fine to medium SAND
(SM). with trace coarse grains
of Boring DB-4
Sheet 1 2 of 1 5
REMARKS
470
Greiner Woodward
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
r::
0 .r:: ·;;
-.,., c.- .,., "' >-
-Ill
LU470
-450
475
480
-460
485
-465
490
-470
495
-475
500
505
510
• c. • " E
>
... z
NR
NR
0 ,g
•
0 1ii
MATERIAL DESCRIPTION
-oen·s·e·.- ·gr'"a-viSh .. ;;,·,
SAND with gravels and trace silt (SP), angular gravels
- Gray, silty fine SAND lanse (SM)
·gr""a·v-. SAND---
with silt (SP/SM)
NR Very dense, wet, light brown, poorly graded fine to
Run 63
Run 66
NR
NR
Run 67
coarse SAND with few gravels (SP)
Becornes greenish gray, silty to clayey fine SAND
lense (SM/SC)
____ ________________ _ Hard, wet, dark greenish gray, very fine sandy Sll T (ML), iron staining
- Silt-y to tine- to---- coarse SAND (SM/SC)
Becomes grayish brown (mottled)
Coarsens to clayey fine to medium SAND (SC)
(concretion)
Reddish brown to very fine sandy SILT (Ml)
Coarsens
Becomes brown, fine to coarse SAND with little
clay (SP/SC)
DB-4
Sheet 1 3 of 1 5
REMARKS
#15,
Project: BFGoodrich of Boring DB-4
Sheet 14 of 1 5
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
§ 0 c Ill_
g E £ .iii <; ,g MATERIAL DESCRIPTION c. c. REMARKS ! ! 1.9 :.9 ••
NR silt .
I- -490 1 / j Concretions
515-
II "71: ....,__ Dark brown, silty to clayey fine SAND (SM/SC), • •u• • • .... r-interbedded
NR • Becomes fine sandy with trace silt
I.-J-R_u_n_7_6---J---_j•;;:')J .. · · · · · · · · · · · · · · · · ·-· · · · ·-· · ·-· · ·-· ·-· · · · · · · ·--·--·-· · · · .-:
Hard, wet, reddish brown, very fine sandy SILT (MLJ
r- Becomes interbedded, reddish to grayish brown,
· ci"Av· icCi · · · · ·
Very dense, wet, brownish to greenish gray, fine SAND
with little silt (SP/SM)
Dark brown, fine sandy CLAY tCL)
L I····-····-·-··-·-·-·-······--··--·---·--··-·--·-·----·--· Hard, wet, grayish brown, fine sandy SILT (ML),
us
I
-+ Becomes finer, medium brown, very fine sandy
CLAY (CL), micaceous
+ Becomes reddish brown to gray brown
+Strong reddish brown, fine sandy CLAY to clayey
1-....--- fine SAND with medium sand (SCICLI (very dense) I .; Mottled coloring
- -wet: bfOWciiS_h_ gray -to- Oiive-brown.-tine-sandy------ SILT to CLAY (ML/CL)
+ Grades to clayey fine to medium SAND (SCI
-H8-rd: -wet; -tirle -SflT tO-ELAY-fMUCij-
:J.- Brown, clayey fine SAND lense (SC)
+--- Cemented sandstone concretion
- -Qr8_y_iSh -tine -t-0 -sA-ND-With----
little clay(SP/SC)
..................................................................................
Hard, wet, grayish to reddish brown, very fine sandy
CLAY (CL)
+ Brown, silty fine SAND (SM)
Becomes grayish brown, poorly graded fine SAND iii irr- with trace silt (SP) i =:J- Reddish brown, silty fine SAND (SP)
t _ _v_e_r_y_ !i!_"l_e_ '!_ _________ "
Hard, wet, grayish brown, very fine sandy SILT (ML),
mottled coloring ... Concretion (cemented sandstone)
::'-,...-"
'-===::-------URS Greiner Woodward Clyde
Box #1 6, 526'-538'
I sox #17, 538"-555'
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
" 0
.<:: ·;:;
.,., .,., "' • o2 w-
-Ql a.
>
1-
550- I
c--530
555-
f-·535
560-
c--540
565-
--545
570-
-
--550
575-
c--555
580-
--560
585-
-
---565
-
-
590-
SAMPLES
0 • ,g .c • E
0 0
z iii
Run 90
NR
Run 91
NR
u
:;:
.
a. ., - 0 "-'
MATERIAL DESCRIPTION
___)- Reddish brown, very fine sandy CLAY (CL)
Grayish brown, silty very fine SAND (SM)
Concretion (cemented sandstone)
Hard, wet, olive gray, very fine sandy SILT {ML)
.------ Grayish brown, silty fine SAND (SM)
Bottom of boring at 555 feet
Log of Boring DB-4
Sheet 1 5 of 1 5
-
-
-
-
-
-
c
0 ...
• c.
>00
>U-'
REMARKS
-----URS Greiner Woodward Clyde ____ _..:.F..:.=ig:::..:u•.::..e --..J Project: BFGoodrich
Project Location:
Project Number:
Chula Vista, CA
58-98530678.00-00400
Date(s)
Drilled 7/6/99 through 7 n /99
Drilling
Method Mud Rotary
Drill Rig
Type T -3 lngersoi-Rand
Depth to Ground-' First J
1 completion II Sampling
water (feet, bgs) ; 14
Diameter of
Hole (inches) 14.75 ! Diameter of 6 I Well (inches)
Logged
By A. Greene
Bit Size/Type 6.25"/14.75" tricone
Drilled
By Beylik Drilling
Number
of Samples
Type of
Well Casing
I j Disturbed: l Undisturbed: -
Steel with wire wrap screen
of Boring:_QB=:5=::J
Sheet 1 of 6
Checked
By R. Scott
Approx. Surface 22 0 Elevation {feet, MSL) •
Total Depth 202 5 Drilled (feet) •
Sampler
Type
Screen
Perforation
Wire-line core barrel
0.075"
Type of
Filter Pack Lonestar Crs. Aquarium Type of
Seal(s) Bentonite chips and cement/bentonite grout
Boring Location
5 15
10 10
15 6
20 0
25 -5
North of Building 99
r-- Becomes moist to wet, medium brown, fine to medium SAND with silt (SM), micaceous Interbedded clay layers
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-9853067B.00-00400
30 -10
35 -1 5
40 -20
45 -25
50 -30
55 -35
60 -40
65 -45
70 MATERIAL DESCRIPTION
Becomes wet, grayish brown, fine to medium SAND
(SP)
Dense, wet, grayish brown, silty to clayey fine SAND
{SM/SC)
Slight increase in grain size, fine to medium sand
Becomes poorly graded fine to medium SAND with
little silt (SP)
of Boring DB-5
Sheet 2 of 6
c
0 ...
• c.
=E
• 0
;'i:u
• E c. c. •c. -c-
•o
:I:Il.
·-
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Log of Boring
Sheet 3 of 6 Project Number: 58-98530678.00-00400
r::
0 .c ·;:;
-C.1i) "' >1i)
0-"" w70
·50
75 ·55
80 ·60
85 ·65
30 ·70
95 ·75
100
·80
105
·85
110
0;
.D
c. • E >-
... z
0 0
"' w
0 a;
MATERIAL DESCRIPTION
,r-- Increasing reddish brown SILT (SM)
Dense, wet, medium brown, silty fine SAND (SM)
Becomes grayish brown, fine to very fine sand with
silt
DB-5
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
£
o.2: ""
110
1151
120
125
130
135
140
145
150-
·90
·95
·1 00
·1 05
·1 10
·115
·120
·125
.c
E
z "
0 ,g
• 3
0 iii
MATERIAL DESCRIPTION
Becomes dark gray to olive, fine to very fine sand
with silt
Becomes olive gray, fine to medium SAND with
little silt (SP/SMI end coarse sand
Becomes clayey fine SAND {SCI with shell
fragments
of Boring DB-5
Sheet 4 of 6
c
0 Q.
=E
• 0
S:u
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
.c
-.,., c.-
o2
150
155
160
165
170
175
180
185
., 30
·1 35
_, 40
_, 45
_,50
G
c.
>
...
.c
E
z "
Run 2
-155 Run3
MATERIAL DESCRIPTION
Dense, wet, dark olive gray, silty to clayey fine SAND
with trace medium sand (SM/SC)
'Wet; dark ·g;.;y; ;,it-y very -tine ·s.A:No·-
with interbedded very fine, sandy silt layers (SM/ML)
r- Becomes more sandy with trace gravels (SM/SPJ
Dark gray to brown, silty to clayey fine SAND
• (SCISM) '-------------------------------------------------- Dense, wet, yellowish brown, silty fine SAND with ·coarse sand and gravel (SM) , l-4l-=c:-;:-f-----1F H -,iQht poo·,ly ·---• -160 coarse SAND with grovels and cobblea (SPIGPJ, angular to rounded rock fragments
of Boring DB-5
Sheet 5 of 6
REMARKS
190 Greiner Woodward Clyde-
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
of Boring DB-5
Sheet 6 of 6
c .... 0 o ME
£ a; MATERIAL DESCRIPTION a. a.
1i) Q) E ! =- Ql i:::_a. REMARKS
w.& g: ::1 1..::; :_3
__
--170
205-
--185
210-
-f"" .< 15 J
-195
220-
--200
225-
f- -205
230-
1-1-=.,-,--f----lli' t- #
2 •
Run11 tRun 12
••••
Bottom of boring at 202.5 feet
I
b= t-
- I=
I=
I=
I= t:
I= r-
-
-
-
-
-
-
-
-
-
'-;-,="""'"'"w"'";o., ____ URS Greiner Woodward FigUIJr;;..;_e_-----' Project: BFGoodrich of Borina--uw ·•
Project Location: Chula Vista, CA - Project Number: 58-98530678.00-00400 Sheet 1 of 4 Oate(s) 7/1/99 to 7/2/99 Logged A. Greene Checked R.Scott Drilled By By Drilling Mud Rotary Drill Bit s· tricone Approx. Surface 22 0 Method Size/Type Elevation (feet, MSL) • Drill Rig T -3 lngeraoi-Rand Drilled Beylik Drilling Total Depth 160.0 Type By Drilled (feet) Depth to Ground-i First 1 Sampling Number ' Sampler l Disturbed: - j Undisturbed: -- NA w8ter (feet, bgs): 14 I of Samples ' Type Diameter of 8 ! Diameter of 2 Type of Schedule 40 PVC Screen 0.020" hole (inches) ) Well (inches) We/J Casing Perforation Type of Lonestar #8 Type of Bentonite pellets end cement/bentonite grout Filter Pack Seal(s) Boring Location North of Building 99
SAMPLES
c: 0 c ·- 0 0
.£ ., ,g MATERIAL DESCRIPTION ... g E
- "' • "-"- c.- >- -" 0 c. 0 "- REMARKS "" "" c E 3 1.3 =E "0- o2 -Q)
w- "-> 0 ooj ,_ z "' S:u_"" Ill. 0- I .
Claos II base ove< dense, mo;ot, ! bo,i;;;. log brown, fine to medium SAND (SM), OW·2 20 few
BAY POINT FORMATION
Dense, moist, reddish to medium brown, silty to clayey
fine SAND with medium sand and few gravels (SM/SC)
5- -
15 10- -
r-1o
Becomes wet
15- Becomes more sandy (SM/SP) -
1-5 .
.
20- -
r-o -
25-
11 i!i
-
C"-·5
30-
URS Greiner Woodward Cli r/e Figure 2/16/00 1 Wll C I)N.;OO Project: SF Goodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
35 40
45 50
55 60
65 70
_, 0
• 1 5
-20
-25
-30
-35
-40
-45
.c •
E
z "
0 :c
c.
""' 0
MATERIAL DESCRIPTION
Hard, wet, grayish to olive brown, fine sandy CLAY (CL) with few interbedded coarse sand layers
-o;,-n·s·e·.- ·grS-viSh ·to mec:tfum·
fine to medium SAND (SP) with few interbedded coarse
and lenses
Greiner Woodward Clyde
of Boring OW-1
Sheet 2 of 4
REMARKS
Project: BFGoodrich
Project location: Chula Vista, CA
Project Number: 58-98530678.00-00400
-60
75 -55
80 -60
85 -65
90 -70
95 -75
100
-80
105
.c
E
z
0 ,g
0 0
1ii
MATERIAL DESCRIPTION
Becomes more sandy
Dense, wet, brownish gray, poorly graded fine to
medium SAND with few coarse sands (SP)
l of Boring OW-1
Sheet 3 of 4
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
110
115
120
125
135
140
145
-90
-95
-100
-105
. 1 1 0
• 1 1 5
-120
·1 25
0 ..0
E
z
0 ,g
• ;;
0 iii
MATERIAl DESCRIPTION
Becomes finer grained
dense to hard, wet, dark brownish gray, fine fine
(SM) with interbedded CLAY layers (Cl)
Dense, wet, light grayish brown, poorly graded fine to
coarse SAND (SP) few gravels
gray, silty to clayey fine SAND (SM)
of Boring OW-1
Sheet 4 of 4
REMARKS
Project: BFGoodrich of B . on ' .. y- -uvv-£
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400 Sheet 1 of 5
Oate(s) 6/30/99 to 711/99 Logged A. Greene Checked R.Scott Drilled By By Drilling Mud Rotary Drill Bit 8'" trioone Approx. Surface 22 0 Method Size/Type Elevation (feet, MSL) • Drill Rig T -3 lngersoi-Rand Drilled Beylik Drilling Total Depth 168.5 Type By Drilled (feet) Depth to Ground-.! First /Completion / Sampling Number i Disturbed: -- Undisturbed: -- Sampler NA water (feet. bgs) i 14 ' . of Samples Type Diameter of 8 i Diameter of 2 Type of Schedule 40 PVC Screen 0.020" Hole (inches) ! Well (inches) Well Casing Perforation Type of lonestar #8 Type of Bentonite chips and cement/bentonite grout Filter Pack Seal(s) Boring Location North of Building 99
c:" '"" 0 0
.r:;" :;:; :?_ g MATERIAL DESCRIPTION "' c. c. ..c • h .,., .,., •c. REMARKS • E ..,_ o.!!! -Q) c. i.S w- > 0 ,... z Ol :to. 0- over Class II base over dense, moist,
20 1 r to medium SAND (SM),
.... medium brown, silty to clayey
fine SAND with medium sand and few gravels (SM/SC)
5- -
="'
1 5
10- - -
-
l-10
••••
'V
Becomes wet
15- Becomes more sandy (SM/SP) -
5 20-. -
\-0
25- -
l-·5
'
30-
2 '1 6/00 1 Wll C BFGOO URS Greiner Woodward Cl de
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-9853067B.00-00400
30 -10
35 -1 5
40 -20
45 -25
50 -30
55 -35
60 -40
65 t·45
7J
.c
E
z
MATERIAL DESCRIPTION
Hard, wet, grayish to olive brown, fine sandy CLAY (CL) with few interbedded coarse sand layers
Dense, wet, grayish to medium brown, poorly graded
fine to medium SAND (SP) with few interbedded coarse
and lenses
of Boring OW-2
Sheet 2 of 5
c
0 c_
=E e o ;i:u
e E 0.0.
-omo e_
::t:c.
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
75 -65
80 -60
85 -66
90 -r-70
95 -75
100
-80
105
-85
..c
E
z "
MATERIAL DESCRIPTION
Dense, wet, reddish brown, silty fine
clay (SM/SC)
Becomes more sa.ndy
Dense, wet, brownish gray, poorly graded fine to
medium SAND with few coarse sands (SP)
of Boring OW-2
Sheet 3 of 5
E "-"-
-cJ:o. ·-
REMARKS
Project: BFGoodrich
Project Location:
Project Number:
110
115
120
125
130
135
140
145
c:
0 ·;:;
"' >-
w.e "" . g:
,__
-90
-95
-100
-105
-110
·115
-120
-125
Chula Vista, CA
58-98530678.00-00400
..c • E
z "
MATERIAL DESCRIPTION
Very dense to hard, wet, dark brownish gray, fine fine
SAND (SM) with interbedded CLAY layers (Cl)
Dense, wet, light grayish brown, poorly graded fine to
coarse SAND (SP) few gravels
Very dense to hard, wet, brownish dark gray to olive
gray, silty to clayey fine SAND (SM)
of Boring OW-2
Sheet 4 of 5
REMARKS
Project: BFGoodrich
Project Location: Chula Vista, CA
Project Number: 58-98530678.00-00400
0::
0 0
.c: ,g 10 G
-" 0 .,., .,., G -Q) c. E
w- > 0
... z a;
MATERIAL DESCRIPTION
150
-130 lnterbeded CLAY lenses (CL)
155
t"'
1601
-140
165
-145
Bottom of boring at 1 68.5 feet
170
-150
175
t·155
I -16o
185
-1 66
L of Boring OW-2
Sheet 5 of 5
REMARKS
FILL
Dry, light brown silt
Becomes reddish brown
Bottom of boring at 5 feet
ND
ND
SSS00278
SSS00279
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/22/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured None encountered
Direct-push
Geoprobe 6620 DT LAR
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
17 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 5.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
5.0 feet
04/22/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6620 DT LAR
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
17 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
None encountered
0 5
10 15
20 25
15 10
5 0
-5
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-02 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-02 FILL
Moist, reddish brown silt
Trace clay
Becomes micaceous
Bottom of boring at 5 feet
ND
ND
SSS00280
SSS00281
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/22/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured None encountered
Direct-push
Geoprobe 6620 DT LAR
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
15 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 5.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
5.0 feet
04/22/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6620 DT LAR
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
15 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
None encountered
0 5
10 15
20 25
15 10
5 0
-5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-03 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-03 1" asphalt cover present at
surface
Groundwater sample
GWS00834
BAY POINT FORMATION
Moist, dark brown SILT (ML)
Becomes clayey silt
Bottom of boring at 15 feet
Temporary 3/4-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 5 to 15 feet.
ND
ND
SSS00310
SSS00311
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/22/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 15 feet at time of drilling
Direct-push
Geoprobe 6620 DT LAR
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
13 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/22/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6620 DT LAR
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
13 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
15 feet at time of drilling
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-18 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-18 Groundwater sample
GWS00835
FILL
1" asphalt over moist, dark brown sand with little medium to coarse-grained sand, asphalt shard, trace fine gravel
Moist, dark brown, clayey silt with trace medium-grained sand
BAY POINT FORMATION
Moist, dark reddish brown, silty CLAY (CL) with medium-grained sandy layers
Moist, olive gray, fine sandy SILT (ML), trace clay
Wet, olive gray, silty fine-grained SAND (SM)
Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
1.0 ND
SSS00310
SSS00311
See Site Plan
K. Foster
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 10 feet at time of drilling
Direct-push
Geoprobe 6600
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
13 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6600
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
13 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled K. Foster
Approximate
Surface Elevation
10 feet at time of drilling
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-19 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-19 Groundwater sample
GWS00836
FILL
~1" asphalt over moist, brown, fine to coarse-grained sandy silt, micaceous, trace asphalt shards
Moist, reddish brown silty clay, trace fine to medium-grained sand
BAY DEPOSITS
Moist, olive SILT (ML), trace clay
Becomes sandy silt
Becomes wet
BAY POINT FORMATION
Moist, dark reddish brown, silty CLAY (CL)
Wet, olive, sandy SILT (ML) with silty fine-grained sand Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
ND
ND
ND
ND
SSS00314
SSS00315
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 11.5 feet at time of drilling
Direct-push
Geoprobe 6620 DT LAR
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
12 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6620 DT LAR
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
12 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
11.5 feet at time of drilling
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-20 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-20 Groundwater sample
GWS00837
FILL
Moist, olive gray, fine to medium-grained sandy silt, trace fine gravel, micaceous
Moist, brown, silty clay, trace fine to medium-grained sand Becomes fine to medium-grained sandy clay
BAY DEPOSITS
Moist, olive, clayey SILT (ML), micaceous
BAY POINT FORMATION
Moist, dark brown, fat CLAY (CH)
Moist, olive, fine-grained sandy SILT (ML), little clay, micaceous Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
ND
ND
ND
SSS00316
SSS00317
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured NA
Direct-push
Geoprobe 6620 DT LAR
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
11 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6620 DT LAR
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
11 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
NA
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-21 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-21 Hand auger 0-2.5'
Groundwater sample
GWS00839
FILL
6.5" concrete over dry, brown, silty fine to medium-grained sand, trace gravel and cobble
BAY POINT FORMATION
Dry, dark brown CLAY (CL)
Decrease in sand content
Becomes moist
Becomes dry
Carbonate concretion
Trace silt
Bottom of boring at 20 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 20 feet.
ND
ND
ND
ND
ND
SSS00320
SSS00321
See Site Plan
K. Foster
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured NA
Direct-push
Geoprobe 6600
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
14 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 20.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
20.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6600
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
14 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled K. Foster
Approximate
Surface Elevation
NA
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-22 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-22 Hand auger 0-3'
Groundwater sample
GWS00840
FILL
6.5" concrete over moist, yellowish brown, silty fine-grained sand Becomes dark brown
BAY POINT FORMATION
Dry, reddish brown CLAY (CL), trace silt
Moist, brown SILT (ML) with fine-grained sand
Increase in sand content
Becomes wet
Becomes moist
Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
ND
3.5 4.2
6.3 5.9
SSS00322
SSS00323
See Site Plan
K. Foster
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 12.5 feet at time of drilling
Direct-push
Geoprobe 6600
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
15 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6600
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
15 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled K. Foster
Approximate
Surface Elevation
12.5 feet at time of drilling
0 5
10 15
20 25
15 10
5 0
-5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-23 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-23 Hand auger 0-3'
No recovery 3'-4'
Groundwater sample
GWS00841
FILL
6.5" concrete over moist, yellowish brown, silty fine-grained sand Trace gravel
Becomes moist
BAY POINT FORMATION
Dry, brown CLAY (CL)
Manganese staining
Trace mica
Becomes brown, increase in mica content
Moist to wet, brown SILT (ML) with fine-grained sand
Carbonate concretions
Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
ND
ND
ND
ND
ND
ND
SSS00324
SSS00325
See Site Plan
K. Foster
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 11 feet at time of drilling
Direct-push
Geoprobe 6600
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
13 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6600
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
13 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled K. Foster
Approximate
Surface Elevation
11 feet at time of drilling
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-24 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-24 Groundwater sample
GWS00838
FILL
1.5" asphalt over moist, dark reddish brown silt with clay, trace fine gravel
BAY POINT FORMATION
Moist, dark reddish brown, silty CLAY (CL)
Clayey fine sand zones, micaceous
Wet, brown, fine sandy SILT (ML), micaceous
Becomes moist, clayey silt
Bottom of boring at 15 feet
Temporary 1-inch diameter piezometer installed to collect groundwater sample.
Screen interval: 10 to 15 feet.
ND
ND
ND
ND
ND
SSS00318
SSS00319
See Site Plan
L. Woodbury
Drilling
Contractor Cascade Drilling
04/23/13
NA
Drill Bit
Size/Type
Groundwater Level
and Date Measured 10 feet at time of drilling
Direct-push
Geoprobe 6600
Granular bentonite, hydrated
Sampling
Method(s)
Drill Rig
Type
R. Scott
Location Borehole
Completion
2.25-inch diameter
Grab/Undisturbed/Acetate Sleeve
13 feet (MSL)
Date(s)
Drilled
Hammer
Data
Drilling
Method
Total Depth
of Borehole 15.0 feet
Logged
By
Approximate
Surface Elevation
Checked
By
Type Elevation feet Graphic Log
REMARKS AND
OTHER TESTS
HeadspacePID, ppm
Depth, feet
MATERIAL DESCRIPTION
SAMPLES Number
Total Depth
of Borehole
Hammer
Data
15.0 feet
04/23/13
NA
Checked
By
Drilling
Method
Drill Bit
Size/Type 2.25-inch diameter
Groundwater Level
and Date Measured
Direct-push
Geoprobe 6600
R. Scott
Drilling
Contractor
Drill Rig
Type
Sampling
Method(s)
Borehole
Completion
13 feet (MSL)
Logged
By
Granular bentonite, hydrated Location See Site Plan
Cascade Drilling
Date(s)
Drilled L. Woodbury
Approximate
Surface Elevation
10 feet at time of drilling
0 5
10 15
20 25
10 5
0 -5
-10
Project Location: 850 Lagoon Drive
Project Number: 27701511.01000 Sheet 1 of 1
Log of Boring UT-66 Project: Rohr North Campus
Report: ENV_S/W_SIMPLE_NO BLOWS; File: 27701311.GPJ; 4/29/2015 UT-66 60/60
BB-14-01
BB-14-05
60/60
BB-14-10
1 5
10 Yellowish gray silty SAND, dry
-FILLBrown silty fine SAND (SM), dry
-FILLReddish brown CLAY (CL), dry
-BAY POINT FORMATIONBrown fine sandy SILT (ML), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
SM
CL
ML
19 1
14 5
11 8
ND
0.7 0.5
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-14
Datum
Type
Barrel
--
Water
BB-14
Total Depth (ft)
3 10
19 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-15-01
BB-15-03
60/60
BB-15-10
1 3
10 Yellowish gray silty fine SAND, dry, trace gravel
becomes silty fine to medium SAND
-FILLReddish brown clayey SILT (ML), dry
-BAY POINT FORMATIONBrown silty fine SAND (SM), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
SM
19 2
13 8
ND
0.2 0.3
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-15
Datum
Type
Barrel
--
Water
BB-15
Total Depth (ft)
3 10
21 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-16-01
BB-16-03
60/60
BB-16-10
1 3
10 Yellowish gray silty fine SAND, dry
-FILLReddish brown clayey SILT (ML), dry
-BAY POINT FORMATIONOlive brown silty fine SAND (SM), dry Brown fine to medium SAND (SP), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
SM
SP
22 2
18 6
15 9
0.2 0.3
0.3 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-16
Datum
Type
Barrel
--
Water
BB-16
Total Depth (ft)
3 10
24 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-17-01
BB-17-04
60/60
BB-17-10
60/60
60/60
BB-17-
GW
1 4
10 25
Yellowish gray silty fine SAND, dry
-FILLReddish brown CLAY (CL), dry
-BAY POINT FORMATIONReddish brown SILT (ML), dry
Reddish brown CLAY (CL), dry
Yellowish brown fine to medium SAND (SP), moist
Olive brown fine to coarse SAND (SW), micaceous, wet
Note: Not logged.
BOTTOM OF EXPLORATION 25 FT
Note: Backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
CL
ML
CL
SP
SW
16 2
14 4
12 6
8 10
4 14
0.5 0.5
0.3 0.6
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 27, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 27, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-17
Datum
Type
Barrel
--
Water
BB-17
Total Depth (ft)
3 25
18 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
50/60
BB-18-01
BB-18-04
60/60
BB-18-10
1 4
10 Yellowish gray silty fine SAND, dry
-FILLbecomes tan with gravel
Reddish brown clayey SILT (ML), dry
-BAY POINT FORMATIONOlive brown silty fine SAND (SM), moist BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
SM
17 3
12 8
0.5 0.6
0.9 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-18
Datum
Type
Barrel
--
Water
BB-18
Total Depth (ft)
3 10
20 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
36/60
BB-19-01
BB-19-03
60/60
BB-19-10
1 3
10 Yellowish gray silty SAND, dry, concrete chunks
-FILLBrown SILT, dry
Reddish brown CLAY (CL), dry
-BAY POINT FORMATIONBrown fine sandy SILT (ML), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
CL
ML
23 1
22 2
18 5
1.3 1.2
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-19
Datum
Type
Barrel
--
Water
BB-19
Total Depth (ft)
3 10
23 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-20-01
BB-20-03
60/60
BB-20-10
1 3
10 Yellowish gray sandy SILT, dry
-FILLOlive brown SILT (ML), dry
-BAY POINT FORMATIONbecomes reddish brown
Brown fine SAND (SP), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
SP
15 2
10 7
0.5 0.9
1.0 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-20
Datum
Type
Barrel
--
Water
BB-20
Total Depth (ft)
3 10
17 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-21-01
BB-21-03
60/60
BB-21-10
1 3
10 Yellowish gray silty fine SAND, dry
-FILLReddish brown SILT (ML), dry
Olive brown lean CLAY (CL), dry
Brown silty fine SAND (SM), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
CL
SM
16 3
13 6
12 8
1.3 1.5
0.7 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-21
Datum
Type
Barrel
--
Water
BB-21
Total Depth (ft)
3 10
19 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
60/60
BB-22-01
BB-22-03
60/60
BB-22-10
1 3
10 Grayish brown silty SAND, dry
-FILLReddish brown SILT (ML), dry
-BAY POINT FORMATIONBrown fine sandy SILT (ML), dry
BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
ML
ML
23 1
16 7
0.9 0.6
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-22
Datum
Type
Barrel
--
Water
BB-22
Total Depth (ft)
3 10
23 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
48/60
BB-23-01
BB-23-03
60/60
BB-23-10
60/60
60/60
BB-23-
GW
1 3
10 25
Yellowish gray silty fine SAND, dry
-FILLReddish brown CLAY (CL), dry
-BAY POINT FORMATIONBrown silty fine SAND (SM), dry
Olive brown fine to medium SAND (SP), micaceous, wet
Note: Not logged.
BOTTOM OF EXPLORATION 25 FT
Note: Backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
CL
SM
SP
17 1
12 5
1 16
0.6 0.8
1.3 0.7
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 27, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 27, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-23
Datum
Type
Barrel
--
Water
BB-23
Total Depth (ft)
3 25
17 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
50/60
BB-24-01
BB-24-03
60/60
BB-24-10
1 3
10 Yellowish gray silty fine SAND, dry
-FILLReddish brown lean CLAY (CL), dry
-BAY POINT FORMATIONOlive brown fine sandy SILT (ML), dry BOTTOM OF EXPLORATION 10 FT
Note: Backfilled with hydrated bentonite.
CL
ML
20 2
16 6
0.7 1.0
0.8 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
G. Becker
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700 Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
BB-24
Datum
Type
Barrel
--
Water
BB-24
Total Depth (ft)
3 10
22 (est.)
T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
VACANT BAY BOULEVARD PROPERTIES, CHULA VISTA, CALIFORNIA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023_GP-BB SERIES-RAO.GPJ Jul 20, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B99-01-1
60/60
B99-01-5
50/60
B99-01-
10 60/60
60/60
1 5
10 15
3 in. ASPHALT over
Reddish brown silty CLAY (CL), moist
-BAY POINT FORMATIONBrown clayey SILT (ML), moist, micaceous Brown silty fine SAND (SM), moist, micaceous
Brown clayey SILT (ML), moist, micaceous
Brown silty SAND (SM), wet
Brown SILT (ML), moist
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Notes: Backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
CL
ML
SM
ML
SM
ML
9.5 7.5
6.5 10.5
4 13
1.5 15.5
-1.5
18.5 ND
ND
ND
ND
0.1 ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
27 June 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700
Sheet No.
G - Geoprobe
27 June 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B99-01
Datum
Type
Barrel
--
Water
B99-01
Total Depth (ft)
3 25
17 (est.)
K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 99, CHULA VISTA, CA
GEOPROBE REPORT H&A-GEOPROBE-09-SDG HA-LIB09-TAB.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-GP-B99 SERIES.GPJ 15 Jul 16 Depth (ft) 0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B99-02-1
60/60
B99-02-4
60/60
B99-02-
10 1
4 5
10 3 in. ASPHALT over
Reddish brown fine sandy SILT (ML), trace gravel, dry
-BAY POINT FORMATIONReddish brown silty CLAY (CL), moist Reddish brown SILT (ML), moist
Brown CLAY (CL), moist
Reddish brown to brown SILT (ML), moist, micaceous
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
ML
CL
ML
CL
ML
12 3
10 5
8 7
7 8
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
27 June 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700
Sheet No.
G - Geoprobe
27 June 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B99-02
Datum
Type
Barrel
--
Water
B99-02
Total Depth (ft)
3 10
15 (est.)
K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 99, CHULA VISTA, CA
GEOPROBE REPORT H&A-GEOPROBE-09-SDG HA-LIB09-TAB.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-GP-B99 SERIES.GPJ 15 Jul 16 Depth (ft) 0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B99-03-1
60/60
B99-03-4
60/60
B99-03-
10 1
4 5
10 3 in. ASPHALT over
Tan silty SAND (SM) with trace clay, moist
-FILLReddish brown sandy CLAY (CL), moist
-BAY POINT FORMATIONBrown SILT (ML), moist, micaceous
Brown CLAY (CL), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
SM
CL
ML
CL
17 3
15 5
11.5 8.5
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
27 June 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700
Sheet No.
G - Geoprobe
27 June 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B99-03
Datum
Type
Barrel
--
Water
B99-03
Total Depth (ft)
3 10
20 (est.)
K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 99, CHULA VISTA, CA
GEOPROBE REPORT H&A-GEOPROBE-09-SDG HA-LIB09-TAB.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-GP-B99 SERIES.GPJ 15 Jul 16 Depth (ft) 0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B99-04-1
60/60
B99-04-4
60/60
B99-04-
10 1
4 5
10 3 in. ASPHALT over
Reddish brown fine sandy SILT (ML), moist
-BAY POINT FORMATIONReddish brown CLAY (CL), moist
Brown SILT (ML), moist
Brown silty SAND (SM), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
ML
CL
ML
SM
15 2
12 5
8 9
ND
ND
0.1 ND
0.1 0.1
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
27 June 2016
H&A Rep.
Samples
Date Bottom
MiniRAE 3000
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe 7700
Sheet No.
G - Geoprobe
27 June 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B99-04
Datum
Type
Barrel
--
Water
B99-04
Total Depth (ft)
3 10
17 (est.)
K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 99, CHULA VISTA, CA
GEOPROBE REPORT H&A-GEOPROBE-09-SDG HA-LIB09-TAB.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-GP-B99 SERIES.GPJ 15 Jul 16 Depth (ft) 0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-01-1
60/60
B29-01-2
60/60
B29-01-
10 0
2 10
3.0 in. asphalt over yellow fine SAND with clay (SC)
-FILLReddish brown CLAY (CL), moist
-BAY POINT FORMATIONReddish brown SILT with clay (ML), micaceous, moist Becomes light brown, trace clay
Light brown silty fine SAND (SM), moist, micaceous
BOTTOM OF EXPLORATION 10.0 FT
Note: Boring backfilled with hydrated bentonite.
SC
CL
ML
SM
13 1
10 4
5 9
ND
ND
ND
0.3 0.4
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 27, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 27, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-01
Datum
Type
Barrel
--
Water
B29-01
Total Depth (ft)
3 10
14 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-02-1
60/60
B29-02-2
60/60
B29-02-
10 1
2 10
3.0 in. asphalt over tan silty SAND, dry
-FILLReddish brown CLAY (CL), moist
-BAY POINT FORMATIONReddish brown clayey SILT (ML), moist, trace fine sand Reddish brown CLAY (CL), moist
Brown SILT (ML), moist
Brown silty fine SAND (SM), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Boring backfilled with hydrated bentonite.
CL
ML
CL
ML
16 1
13 4
13 5
12 5
9 9
0.3 0.3
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 24, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 24, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-02
Datum
Type
Barrel
--
Water
B29-02
Total Depth (ft)
3 10
17 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-03-
01 60/60
B29-03-
03 60/60
B29-03-
10 60/60
60/60
B29-03-
GW
0 3
10 25
Asphalt, grayish brown medium SAND with gravel, dry
-FILLBrown sandy CLAY (CL), moist
-BAY POINT FORMATIONReddish brown silty fine SAND (SM), moist Olive brown fine SAND (SM), moist, some silt
Reddish brown sandy CLAY (CL), dry
Olive brown silty fine SAND (SM)
Brown sandy CLAY (CL), moist
Olive brown well graded SAND (SW), wet
Olive brown poorly graded SAND (SW), wet
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
CL
SM
SP
CL
SM
CL
SW
SP
9 3
8 4
7 5
6 6
5 7
0 12
-1
13 -5
17 -8
20 0.4
0.3 0.4
0.2 -
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-03
Datum
Type
Barrel
--
Water
B29-03
Total Depth (ft)
3 25
12 T. Burns
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-04-1
60/60
B29-04-5
60/60
B29-04-
10 60/60
60/60
B29-04-
GW
1 5
10 25
3.0 in. asphalt over reddish brown sandy clay (CL), moist -BAY POINTReddish brown clayey SILT (ML)
Reddish brown CLAY (CL), moist
Reddish brown SILT (ML), moist, trace clay
Reddish brown CLAY (CL), moist
Olive brown silty SAND (SM), moist, micaceous
Becomes wet
Olive brown fat CLAY (CH), moist
Olive brown silty SAND (SM), wet
Note: Note logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Bottom of exploration 25 ft. Groundwater sample collected at 25.0 ft.
ML
CL
ML
CL
SM
CH
SM
14 3
12 5
9 8
7 10
5 12
0 17
-1
18 -2
19 ND
ND
ND
0.2 ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 27, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 27, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-04
Datum
Type
Barrel
--
Water
B29-04
Total Depth (ft)
3 25
17 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-05-2
48/60
B29-05-5
60/60
B29-05-
10 60/60
60/60
B29-05-
GW
2 5
10 25
6.0 in. concrete over reddish brown silty CLAY (CL), dry -BAY POINT FORMATIONBecomes brown
Brown SILT (ML), moist
Brown silty SAND (SM), moist
Brown SILT (ML), moist
Brown silty SAND (SM), moist, carbonate concretions
Brown CLAY (CL), moist
Brown silty SAND (SM), wet
CLAY (CL)
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Boring backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
ML
SM
ML
SM
CL
SM
CL
5 8
0 13
-1
14 -2
15 -3
16 -6
19 -7
20 ND
0.3 0.4
0.2 ND
0.1 ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-05
Datum
Type
Barrel
--
Water
B29-05
Total Depth (ft)
3 25
13 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-06-1
60/60
B29-06-5
60/60
B29-06-
10 1
5 10
6.0 in. asphalt over reddish brown sandy CLAY (CL)
-BAY POINT FORMATIONSimilar to above
Similar to above
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
CL
5 10
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-06
Datum
Type
Barrel
--
Water
B29-06
Total Depth (ft)
3 25
15 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
60/60
B29-07-1
B29-07-3
60/60
60/60
B29-07-
10 B29-07-
GW-A
60/60
B29-07-
GW
1 3
10 12
25 6.0 in. asphalt over brown silty SAND with angular sub-base -FILLReddish brown CLAY (CL), dry, carbonate concretions -BAY POINT FORMATIONBecomes clay with sand
Becomes clay with trace silt, micaceous
Brown clayey SILT (ML), moist
Becomes wet and tan
Brown silty CLAY (CL), moist
Brown silty SAND (SM), wet
Brown CLAY (CL), moist
Brown silty SAND (SM), wet
Brown sandy SILT (ML), wet
Brown silty SAND (SM), wet
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Groundwater sample at 12 and 25 ft. Backfilled with hydrated bentonite.
CL
ML
CL
SM
CL
SM
ML
SM
13 1
8 6
4 10
2 12
0 14
-1
15 -3
17 -6
20 ND
ND
0.1 ND
0.2 0.4
0.5 ND
0.5 ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-07
Datum
Type
Barrel
--
Water
B29-07
Total Depth (ft)
3 25
14 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-08-1
60/60
B29-08-5
60/60
B29-08-
10 1
5 10
6.0 in. concrete over reddish brown to brown silty SAND (SM) -BAY POINT FORMATIONBrown CLAY (CL), moist
Tan SILT with some sand (ML), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
SM
CL
ML
11 3
5 9
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-08
Datum
Type
Barrel
--
Water
B29-08
Total Depth (ft)
3 10
14 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-09-1
60/60
B29-09-5
60/60
B29-9-10
1 5
10 6.0 in. concrete over reddish brown CLAY (CL), dry
-BAY POINT FORMATIONSame as above
Trace carbonate concretions
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
CL
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-09
Datum
Type
Barrel
--
Water
B29-09
Total Depth (ft)
3 10
15 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-10-1
60/60
B29-10-5
60/60
B29-10-
10 1
5 10
6.0 in. concrete over brown clayey SILT (ML)
-BAY POINT FORMATIONBrown silty SAND (SM), dry
Brown CLAY (CL), dry
Light brown fat CLAY (CH), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Boring backfilled with hydrated bentonite.
ML
SM
CL
CH
14 1
13 2
6 9
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-10
Datum
Type
Barrel
--
Water
B29-10
Total Depth (ft)
3 10
15 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-11-1
60/60
B29-11-5
60/60
B29-11-
10 1
5 10
6.0 in. concrete over dry reddish brown sandy SILT (ML) -BAY POINT FORMATIONBrown CLAY (CL), moist
Brown SILT (ML), moist
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
ML
CL
ML
11 4
7 8
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-11
Datum
Type
Barrel
--
Water
B29-11
Total Depth (ft)
3 10
15 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
B29-12-1
60/60
B29-12-5
60/60
B29-12-
10 60/60
60/60
B29-12-
GW
1 5
10 25
6.0 in. concrete over brown silt (ML), dry
-BAY POINT FORMATIONBrown CLAY (CL), dry
Brown SILT with clay (ML), micaceous, moist
Brown CLAY (CL), moist
Brown clayey SILT (ML), moist
Brown CLAY (CL), moist
Brown silty SAND (SM), wet
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Groundwater sample collected at 25.0 ft.
ML
CL
ML
CL
ML
CL
SM
13 2
8 7
7 8
3 12
1 14
-2
17 -5
20 ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-12
Datum
Type
Barrel
--
Water
B29-12
Total Depth (ft)
3 25
15 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
24/60
B29-13-4
B29-13-5
60/60
B29-13-
10 1
4 5
10 6.0 in. concrete
-FILLNo recovery
Tan silty SAND with gravel (SM), moist
Reddish brown CLAY (CL), moist
-BAY POINT FORMATIONBecomes silty clay
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
SM
CL
12 3
11 4
5 10
ND
ND
ND
ns
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 28, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 28, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-13
Datum
Type
Barrel
--
Water
B29-13
Total Depth (ft)
3 25
15 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-14-
1.5 60/60
B29-14-3
60/60
B29-14-
10 2
3 10
6.0 in. asphalt over light brown silty sand with clay
-FILLReddish brown CLAY (CL), moist
-BAY POINT FORMATIONBecomes brown
BOTTOM OF EXPLORATION 10.0 FT
Note: Boring backfilled with hydrated bentonite.
12 CL
2 4
10 ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-14
Datum
Type
Barrel
--
Water
B29-14
Total Depth (ft)
3 25
14 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-15-1
36/36
B29-15-3
60/60
B29-15-
10 60/60
60/60
B29-15-
GW
1 3
10 25
6.0 in. concrete over angular aggregale and silty sand fill, hydrocarbon odor -FILL6.0 in. concrete
Brown CLAY (CL), moist
-BAY POINT FORMATIONBecomes dark brown
Same as above
Brown silty SAND (SM), moist
CLAY (CL), moist
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Backfilled with hydrated bentonite. Groundwater sample collected at 25 ft.
CL
SM
CL
12 2
12 3
-3
17 -5
19 42
ND
ND
ND
ND
ND
0.1 ND
0.3 0.3
ND
ND
ND
0.3 ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-15
Datum
Type
Barrel
--
Water
B29-15
Total Depth (ft)
3 25
14 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-16-
1.5 60/60
B29-16-4
60/60
B29-16-
10 60/60
60/60
60/60
B29-16-
GW
2 4
10 25
6.0 in. concrete over tan silty sand, dry
-FILLReddish brown SILT with clay (ML), dry
-BAY POINT FORMATIONReddish brown CLAY (CL), dry
Becomes brown
Same as above
Same as above
Same as above
Same as above
Olive brown SILT (ML), wet
BOTTOM OF EXPLORATION 30.0 FT
Note: Groundwater sample at 30 ft. Backfilled with hydrated bentonite.
ML
CL
ML
13 2
10 5
-13
28 -15
30 ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-16
Datum
Type
Barrel
--
Water
B29-16
Total Depth (ft)
3 25
15 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-17-1
60/60
B29-17-3
60/60
B29-17-
10 1
3 10
6.0 in. concrete over light brown silty sandy, dry
-FILLBrown CLAY (CL), moist
-BAY POINT FORMATIONSame as above
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
13 CL
2 5
10 ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-17
Datum
Type
Barrel
--
Water
B29-17
Total Depth (ft)
3 25
15 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-18-
1.5 60/60
B29-18-3
60/60
B29-18-
10 2
3 10
6.0 ft asphalt over brown silty lauercaic with aggregrate, dry -FILLBrown CLAY (CL), dry
-BAY POINT FORMATIONSame as above
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
11 CL
2 2
10 ND
ND
ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-18
Datum
Type
Barrel
--
Water
B29-18
Total Depth (ft)
3 25
12 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
60/60
B29-19-2
B29-19-5
60/60
B29-19-
10 2
5 10
6.0 in. asphalt over silty sand
-FILLBrown CLAY (CL), moist
-BAY POINT FORMATIONCarbonate concretions
No carbonate concretions
BOTTOM OF EXPLORATION 10.0 FT
Note: Backfilled with hydrated bentonite.
10 CL
2 2
10 ND
ND
ND
ND
ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 29, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 29, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-19
Datum
Type
Barrel
--
Water
B29-19
Total Depth (ft)
3 25
12 K Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
B29-20-1
B29-20-2
60/60
60/60
B29-20-
10 60/60
60/60
B29-20-
GW
1 2
10 25
3.0 in. asphalt over light brown silty SAND (SM)
-FILLBrown CLAY with silt, moist
- BAY POINT FORMATIONCarbonate concretions
Same as above
Same as above
Becomes sandy CLAY (CL)
Becomes wet
Olive brown silty SAND (SM), moist
Note: Not logged.
BOTTOM OF EXPLORATION 25.0 FT
Note: Groundwater sample collected from 20 from 25 ft. Backfilled with hydrated bentonite.
SM
CL
SM
10 1
-7
18 -9
20 ND
0.1 0.1
0.1 ND
ND
-
of Casing
Boring No.
--
Elapsed
43559-023
†
Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Sampler
of
Inside Diameter (in.)
Hammer Fall (in.)
Finish
Drilling Equipment and Procedures
June 27, 2016
H&A Rep.
Samples
Date Bottom
See Plan
E. Jasso
Start
1 Bit Type:
Time Bottom
Water Level Data
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
S - Splitspoon Sample
O - Open End Rod
T - Thin Wall Tube
U - Undisturbed Sample
G Rig Make & Model: Geoprobe Truck
Sheet No.
G - Geoprobe
June 27, 2016
of Hole
Boring No.
Driller
Summary
1 Drill Mud:
Hammer Weight (lb) -
File No.
Elevation
Location
Time (hr.)
B29-20
Datum
Type
Barrel
--
Water
B29-20
Total Depth (ft)
3 25
11 K. Foster
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Depth (ft) to:
Field Tests:
Client
Contractor NATIONAL EWP
Project
ROHR, INC.
ROHR - BUILDING 29, CHULA VISTA, CA
GEOPROBE REPORT
H&A-GEOPROBE-09-SDG HA-LIB09-BOS.GLB HA-TB+CORE+WELL-09 W FENCE.GDT \\BOS\GINT\43559-023-TB-KOS.GPJ Jul 22, 16 Depth (ft)
0 5
10 15
20 25
Sample No.
& Rec. (in.)
Sample
Depth (ft)
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Color, GROUP NAME, max. particle size†, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
USCS Symbol Stratum Change Elev/Depth (ft)
PID Readings
(ppm)
PID: ND = non-detect
0.5 1.0
2.5 3.0
0.5 3.0
CL
6-in. ASPHALT
Reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-02A-010
36/36
B29-02A-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-02A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 18.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Truck: Geoprobe 6620
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-02A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 3.0
CL
6-in. ASPHALT
Reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-02B-010
36/36
B29-02B-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-02B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 18.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Truck: Geoprobe 6620
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-02B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 3.0
CL
6-in. ASPHALT
Reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-02C-010
36/36
B29-02C-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-02C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 18.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Truck: Geoprobe 6620
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-02C
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 0.8
3.0 SM
CL
6-in. ASPHALT
1-in. light brown fine SAND, no odor, moist
-FILLDark yellowish-brown to reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-03A-010
34/36
B29-03A-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-03A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 14.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-03A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 0.8
3.0 CL
6-in. ASPHALT
1-in. light brown fine SAND, no odor, moist
-FILLDark yellowish-brown to reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-03B-010
36/36
B29-03B-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-03B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 14.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-03B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
1.5 2.0
2.5 3.0
0.5 3.0
6-in. CONCRETE
1-in. light brown fine SAND at 0.5 ft
Moderate yellowish-brown to reddish-brown, silty fine SAND, no odor, moist with clay 1-in. degraded asphalt at 2.4 ft bgs with petroleum hydrocarbon odor -FILLBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-05A-020
36/36
B29-05A-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-05A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-05A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
1.5 2.0
2.5 3.0
0.5 3.0
6-in. CONCRETE
1-in. light brown fine SAND at 0.5 ft
Moderate yellowish-brown to reddish-brown, silty fine SAND, no odor, moist with clay 1-in. degraded asphalt at 2.4 ft bgs with petroleum hydrocarbon odor -FILLBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-05B-020
36/36
B29-05B-030
ND
0.7 -
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-05B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-05B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
1.5 2.0
2.5 3.0
0.5 3.0
6-in. CONCRETE
Moderate yellowish-brown to reddish-brown silty fine SAND, no odor, moist, with trace angular fine gravel 1-in. degraded asphalt at 1.0 ft bgs
-FILL1-in. degraded asphalt at 2.5 ft bgs
BOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-05C-020
36/36
B29-05C-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-05C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-05C
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 0.8
3.0 CL
6-in. ASPHALT
1-in. light brown fine SAND, no odor, moist
-FILLDark yellowish-brown to reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-07A-010
36/36
B29-07A-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-07A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 14.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-07A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
2.5 3.0
0.5 0.8
3.0 CL
6-in. ASPHALT
1-in. light brown fine SAND, no odor, moist
-FILLDark yellowish-brown to reddish-brown silty CLAY, no odor, moist, with trace fine sand -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 3.0 FT
Note:
-No groundwater encountered
B29-07B-010
36/36
B29-07B-030
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-07B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 14.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-07B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 11.5
0.5 2.5
6.0 7.5
11.5 13.5
SM
ML
CL
ML
SM
ML
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist, with angular fine gravel 3-in. degraded asphalt at 1.5 ft bgs
-FILLSoft reddish-brown clayey SILT, no odor, moist
-BAYPOINT FORMATIONWith trace fine sand at 4.5 ft bgs
Stiff reddish-brown to light yellowish-brown silty CLAY, no odor, moist Reddish-brown to light yellowish-brown clayey SILT, no odor, moist Becomes light yellowish-brown at 10.0 ft bgs
Becomes wet at 11.0 ft bgs
Loose light yellowish-brown silty fine SAND, no odor, wet Soft light yellowish-brown SILT, no odor, moist to wet, with trace fine sand B29-22-010
48/48
B29-22-050
48/48
48/48
B29-22-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-22
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-22
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 16.0
17.0 SM Loose moderate yellowish-brown silty fine SAND, no odor, saturated BOTTOM OF EXPLORATION 17.0 FT
Note:
-Groundwater encountered at 16.0 ft bgs
-During drilling, groundwater sample collected between 12.0 and 17.0 ft bgs 12/12
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-22
B29-22
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 2.5
5.5 12.5
14.0 SC
ML
SM
ML
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist 3-in. degraded asphalt at 1.5 ft bgs
-FILLMedium dense reddish-brown clayey SAND, no odor, moist -BAYPOINT FORMATIONStiff moderate yellowish-brown clayey SILT, no odor, moist Becomes soft and light yellowish-brown at 10.0 ft bgs
With trace fine sand at 11.0 ft bgs
Becomes wet at 12.0 ft bgs
Loose silty fine SAND, no odor, saturated
Clayey SILT, no odor, moist
B29-23-010
48/48
B29-23-050
48/48
48/48
B29-23-100
48/48
5.6 ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-23
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 10, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-23
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 10, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 20.0
24.0 28.0
16.0 22.0
28.0 29.8
30.0 SM
CL
SCSM
CL
With trace fine sand at 15.0 ft bgs
Loose silty fine SAND, no odor, saturated
Becomes silty medium sand at 16.5 ft bgs
Hard yellowish-gray CLAY, no odor, moist
Loose yellowish-gray clayey medium SAND, no odor, saturated Becomes yellowish-brown silty to clayey fine SAND at 29.5 ft bgs Soft yellowish-brown sandy CLAY, no odor, wet
BOTTOM OF EXPLORATION 30.0 FT
Note:
-Groundwater encountered at 12.5, 16.0, and 28.0 ft bgs during drilling -2 groundwater samples collected between 12.0 and 17.0 ft and 25.0 to 30.0 ft bgs 48/48
48/48
48/48
24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-23
B29-23
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
25 30
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 2.5
10.0 ML
ML
SM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist 3-in. degraded asphalt at 1.5 ft bgs
-FILLMedium dense reddish-brown silty fine SAND, no odor, moist -BAYPOINT FORMATIONModerate yellowish-brown clayey SILT, no odor, moist Becomes soft and light yellowish-brown at 8.5 ft bgs
With trace fine sand at 9.5 ft bgs
Loose light yellowish-brown silty fine SAND, no odor, moist to wet Becomes wet at 12.0 ft bgs
B29-24-010
48/48
B29-24-050
48/48
48/48
B29-24-100
48/48
4.9 0.4
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-24
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-24
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 17.0
Becomes saturated at 16.0 ft bgs
BOTTOM OF EXPLORATION 17.0 FT
Note:
-Groundwater encountered at 16.0 ft bgs during drilling -Groundwater samples collected between 12.0 and 17.0 ft bgs 12/12
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-24
B29-24
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 11.5
0.5 2.5
6.5 10.0
12.0 CL
ML
SM
ML
SM
6-in. CONCRETE
Stiff dark yellowish-brown to reddish-brown silty CLAY, no odor, moist -BAYPOINT FORMATIONSoft dark yellowish-brown to reddish-brown clayey SILT, no odor, moist Becomes moderate to light yellowish-brown with trace fine sand at 5.0 ft bgs Loose light yellowish-brown silty fine SAND, no odor, moist Becomes moderate yellowish-brown at 9.0 ft bgs
Soft moderate yellowish-brown clayey SILT, no odor, moist Becomes wet at 11.5 ft bgs
Loose moderate to light yellowish-brown silty fine to medium SAND, no odor, wet Becomes saturated at 14.5 ft bgs
B29-25-010
48/48
B29-25-050
48/48
48/48
B29-25-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-25
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 16.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Truck: Geoprobe 6620
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-25
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.5
19.0 ML Soft moderate yellowish-brown clayey SILT, no odor, moist to wet BOTTOM OF EXPLORATION 19.0 FT
Note:
-Groundwater encountered at 14.5 ft bgs during drilling -Groundwater samples collected between 14.0 and 19.0 ft bgs 36/36
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-25
B29-25
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 1.0
5.0 9.5
SM
ML
SM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist, with trace black angular fine gravel (asphalt) from 0.5 to 1.0 ft bgs
-FILLLoose to medium dense reddish-brown silty fine SAND, no odor, moist -BAYPOINT FORMATIONStiff moderate yellowish-brown clayey SILT, no odor, moist Becomes soft and light yellowish-brown at 7.5 ft bgs
With trace fine sand at 8.5 ft bgs
Becomes wet at 9.0 ft bgs
Loose light yellowish-brown silty fine to medium SAND, no odor, wet B29-26-010
48/48
B29-26-050
48/48
48/48
B29-26-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-26
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-26
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.0
Becomes saturated at 16.0 ft bgs
BOTTOM OF EXPLORATION 18.0 FT
Note:
-Groundwater encountered at 16.0 ft bgs during drilling -Groundwater samples collected between 13.0 and 18.0 ft bgs 24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-26
B29-26
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 2.5
5.0 9.0
SM
ML
SM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist -FILLLoose to medium dense reddish-brown silty fine SAND, no odor, moist -BAYPOINT FORMATIONModerate yellowish-brown clayey SILT, no odor, moist Becomes soft and light yellowish-brown at 7.5 ft bgs
With trace fine sand at 8.5 ft bgs
Becomes wet at 9.0 ft bgs
Loose light yellowish-brown silty fine to medium SAND, no odor, wet B29-27-010
48/48
B29-27-050
48/48
48/48
B29-27-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-27
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-27
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.0
Becomes saturated at 16.0 ft bgs
BOTTOM OF EXPLORATION 18.0 FT
Note:
-Groundwater encountered at 16.0 ft bgs during drilling -Groundwater samples collected between 13.0 and 18.0 ft bgs 24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-27
B29-27
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
9.5 10.0
12.0 0.5
2.5 5.0
9.0 ML
CL
SCSM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist -FILLSoft reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONBecomes clayey SILT at 4.0 ft bgs
Dark reddish-brown silty CLAY, no odor, moist, with trace fine sand Becomes moderate yellowish-brown at 6.0 ft bgs
Loose to medium dense moderate yellowish-brown clayey fine SAND, no odor, moist Becomes light yellowish-brown silty fine to medium sand at 11.0 ft bgs Becomes clayey fine sand at 12.0 ft bgs
Becomes silty fine to medium sand, wet at 13.0 ft bgs
Becomes saturated at 14.0 ft bgs
B29-28-010
48/48
B29-28-050
48/48
B29-28-100
48/48
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-28
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-28
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.0
BOTTOM OF EXPLORATION 18.0 FT
Note:
-Groundwater encountered at 14.0 ft bgs during drilling -Groundwater samples collected between 13.0 and 18.0 ft bgs 48/48
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-28
B29-28
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.5 9.5
10.0 12.0
0.5 2.5
5.0 9.0
ML
CL
SCSM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist -FILLSoft reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONBecomes clayey SILT at 4.0 ft bgs
Dark reddish-brown silty CLAY, no odor, moist, with trace fine sand Becomes moderate yellowish-brown at 6.0 ft bgs
Loose to medium dense moderate yellowish-brown clayey fine SAND, no odor, moist Becomes light yellowish-brown silty fine to medium sand at 11.0 ft bgs Becomes clayey fine sand at 12.0 ft bgs
Becomes silty fine to medium sand, wet at 13.0 ft bgs
Becomes saturated at 14.0 ft bgs
B29-29-010
48/48
B29-29-050
48/48
48/48
B29-29-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-29
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-29
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.0
BOTTOM OF EXPLORATION 18.0 FT
Note:
-Groundwater encountered at 14.0 ft bgs during drilling -Groundwater samples collected between 13.0 and 18.0 ft bgs 24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-29
B29-29
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
7.5 9.5
10.0 11.5
0.5 1.5
5.5 7.5
9.5 12.0
SM
CL
ML
SM
ML
6-in. CONCRETE
Soft dark yellowish-brown to reddish-brown fine sandy SILT, no odor, moist -FILLMedium dense dark yellowish-brown to reddish-brown clayey fine SAND, no odor, moist -BAYPOINT FORMATIONDark yellowish-brown to reddish-brown silty CLAY, no odor, moist Soft dark yellowish-brown to reddish-brown clayey SILT, no odor, moist Becomes moderate yellowish-brown with trace fine sand at 8.0 ft bgs Loose moderate yellowish-brown silty fine SAND, no odor, moist Becomes wet at 10.5 ft bgs
Soft moderate yellowish-brown clayey SILT, no odor, wet, micaceous B29-30-010
48/48
B29-30-050
48/48
48/48
B29-30-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-30
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-30
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 19.0
16.0 21.0
22.0 SM
ML
Loose moderate yellowish-brown clayey silty fine SAND, no odor, wet Becomes saturated at 17.0 ft bgs
Moderate yellowish-brown clayey SILT, no odor, moist to wet BOTTOM OF EXPLORATION 22.0 FT
Note:
-Groundwater encountered at 17.0 ft during drilling
-Groundwater sampler collected between 17.0 and 22.0 ft bgs 48/48
24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-30
B29-30
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 0.5
4.5 0.5
5.5 8.0
9.5 0.5
11.0 0.5
1.5 5.5
9.0 11.0
14.0 SC
CL
ML
SM
ML
6-in. CONCRETE
Soft dark yellowish-brown to reddish-brown fine sandy SILT, no odor, moist -FILLMedium dense dark yellowish-brown to reddish-brown clayey fine SAND, no odor, moist -BAYPOINT FORMATIONDark yellowish-brown to reddish-brown silty CLAY, no odor, moist Soft dark yellowish-brown to light yellowish-brown clayey SILT, no odor, moist Loose light yellowish-brown to light yellowish-gray silty fine SAND, no odor, moist Becomes wet at 11.5 ft bgs
Becomes saturated at 12.5 ft bgs
Soft reddish-brown clayey SILT, no odor, moist, with trace fine sand B29-31-010
48/48
B29-31-050
48/48
48/48
B29-31-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-31
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-31
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 19.5
16.0 22.0
23.0 SM
ML
Loose yellowish-brown to dark yellowish-brown silty fine SAND, no odor, wet, no odor, moist to wet Becomes saturated at 19.0 ft bgs
Yellowish-brown to reddish-brown clayey SILT, no odor, moist BOTTOM OF EXPLORATION 23.0 FT
Note:
-Groundwater encountered at 12.5 ft and 19.0 ft bgs during drilling -Groundwater sampler collected between 18.0 and 23.0 ft bgs 48/48
36/36
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-31
B29-31
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
9.5 10.0
0.5 1.0
10.0 ML
6-in. CONCRETE
Loose moderate yellowish-brown to reddish-brown silty fine SAND, no odor, moist, with trace black angular fine gravel from 0.5 to 1.0 ft bgs (asphalt)
-FILLSoft reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONBecomes clayey silt at 4.0 ft bgs
Becomes moderate yellowish-brown at 5.0 ft bgs
Becomes fine sandy silt at 6.0 ft bgs
Becomes wet at 8.0 ft bgs
BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-32A-010
48/48
B29-32A-050
48/48
B29-32A-100
24/24
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-32A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-32A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
9.5 10.0
0.5 1.0
10.0 ML
6-in. CONCRETE
Loose moderate yellowish-brown to reddish-brown silty fine SAND, no odor, moist, with trace black angular fine gravel from 0.5 to 1.0 ft bgs (asphalt)
-FILLSoft reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONBecomes clayey silt at 4.0 ft bgs
Becomes moderate yellowish-brown at 5.0 ft bgs
Becomes fine sandy silt at 6.0 ft bgs
Becomes wet at 8.0 ft bgs
BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-32B-010
48/48
B29-32B-050
48/48
B29-32B-100
24/24
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-32B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-32B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 2.5
5.0 9.0
SM
ML
CL
SCSM
6-in. CONCRETE
Loose dark yellowish-brown to reddish-brown silty fine SAND, no odor, moist 3-in. degraded asphalt at 1.5 ft bgs
-FILLSoft reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONBecomes clayey SILT at 4.0 ft bgs
Dark reddish-brown silty CLAY, no odor, moist, with trace fine sand Becomes moderate yellowish-brown at 6.0 ft bgs
Loose to medium dense moderate yellowish-brown clayey fine SAND, no odor, moist Becomes light yellowish-brown silty fine to medium sand at 11.0 ft bgs Becomes clayey fine sand at 12.0 ft bgs
Becomes silty fine to medium sand, wet at 13.0 ft bgs
Becomes saturated at 14.0 ft bgs
B29-32C-010
48/48
B29-32C-050
48/48
48/48
B29-32C-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-32C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 14, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-32C
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 14, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 18.0
BOTTOM OF EXPLORATION 18.0 FT
Note:
-Groundwater encountered at 14.0 ft bgs during drilling -Groundwater samples collected between 13.0 and 18.0 ft bgs 24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-32C
B29-32C
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
4.5 10.0
ML
6-in. CONCRETE
Loose yellowish-brown silty fine to medium SAND, no odor, moist -FILLReddish brown fine sandy SILT, with nails and broken glass fragments at 4.3 ft bgs Loose reddish to yellowish-brown silty fine SAND, no odor, moist, with clay and tracel shell fragments -BAYPOINT FORMATIONBecomes medium dense at 8.0 ft bgs
BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-33A-010
48/48
B29-33A-050
48/48
24/24
B29-33A-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-33A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-33A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
3.0 5.0
10.0 ML
CL
6-in. CONCRETE
Loose yellowish-brown silty fine to medium SAND, no odor, moist, with trace coarse sand and fine gravel -FILLSoft dark yellowish-brown to reddish-brown SILT, no odor, moist -BAYPOINT FORMATIONStiff dark yellowish-brown silty CLAY, no odor, moist With fine sand between 8.0 and 8.5 ft bgs
BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-33B-010
48/48
B29-33B-050
48/48
24/24
B29-33B-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-33B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-33B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 3.0
6.0 9.0
ML
SM
CL
6-in. CONCRETE
Loose yellowish-brown silty fine to medium SAND, no odor, moist, with trace coarse sand and fine gravel -FILLYellowish-brown to reddish-brown fine SILT, no odor, moist -BAYPOINT FORMATIONLoose to medium dense reddish-brown silty fine SAND, no odor, moist Yellowish-brown CLAY, no odor, moist
B29-33C-010
48/48
B29-33C-050
48/48
48/48
B29-33C-100
48/48
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-33C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 9, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-33C
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 9, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 19.0
22.0 24.0
SM
Becomes soft light yellowish-gray at 18.0 ft bgs
Becomes moderate yellowish-brown with trace fine sand at 19.5 ft bgs Loose yellowish-brown silty fine SAND, no odor, wet, micaceous Becomes saturated at 23.0 ft bgs
BOTTOM OF EXPLORATION 24.0 FT
Note:
-Groundwater encountered at 23.0 ft bgs during drilling -Groundwater sampler collected between 19.0 and 24.0 ft bgs 48/48
48/48
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-33C
B29-33C
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
2.0 4.0
10.0 ML
CL
6-in. CONCRETE
Loose dark yellowish-brown silty fine to medium SAND, no odor, moist, with trace coarse sand -FILLSoft dark reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONStiff dark reddish-brown to yellowish-brown silty CLAY, no odor, moist, with trace fine sand BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-34A-010
48/48
B29-34A-050
48/48
24/24
B29-34A-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-34A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-34A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
2.0 4.0
10.0 ML
CL
6-in. CONCRETE
Loose dark yellowish-brown silty fine to medium SAND, no odor, moist, with trace coarse sand -FILLSoft dark reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONStiff dark reddish-brown to yellowish-brown silty CLAY, no odor, moist, with trace fine sand BOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-34B-010
48/48
B29-34B-050
48/48
24/24
B29-34B-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-34B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-34B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 2.0
4.0 ML
CL
6-in. CONCRETE
Loose reddish to yellowish-brown silty fine SAND, no odor, moist, with trace angular fine gravel -FILL1.5-in. concrete fragments at 2.0 ft bgs
Soft dark reddish-brown SILT, no odor, moist
-BAYPOINT FORMATIONStiff dark reddish-brown to yellowish-brown silty CLAY, no odor, moist, with trace fine sand No silt at 12.0 ft bgs
B29-34C-010
48/48
B29-34C-050
48/48
48/48
B29-34C-100
24/24
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-34C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-34C
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 20.0
24.0 16.0
22.0 25.0
CL
ML
SM
Become dark yellowish-brown silty clay at 15.5 ft
Stiff light yellowish-brown clayey SILT, no odor, moist Becomes light yellowish-gray at 20.0 ft bgs
Loose yellowish-brown silty fine SAND, no odor, wet, micaceous Becomes saturated at 23.0 ft bgs
BOTTOM OF EXPLORATION 25.0 FT
Note:
-Groundwater encountered at 23.0 ft during drilling
-Groundwater sampler collected between 20.0 and 25.0 ft bgs 48/48
48/48
12/12
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-34C
B29-34C
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
25 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
4.0 10.0
CL
6-in. CONCRETE
Loose yellowish-brown silty fine to medium SAND, no odor, moist 2-in. dark brown silty medium SAND, with trace angular fine gravel and slight petroleum hydrocarbon odor -FILLVery stiff yellowish-brown to reddish-brown sandy CLAY, no odor, moist -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-35A-010
48/48
B29-35A-050
48/48
24/24
B29-35A-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-35A
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-35A
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 0.5
4.0 10.0
CL
6-in. CONCRETE
Loose yellowish-brown silty fine to medium SAND, no odor, moist 2-in. dark brown silty medium SAND, with trace angular fine gravel and slight petroleum hydrocarbon odor -FILLVery stiff yellowish-brown to reddish-brown sandy CLAY, no odor, moist -BAYPOINT FORMATIONBOTTOM OF EXPLORATION 10.0 FT
Note:
-No groundwater encountered
B29-35B-010
48/48
B29-35B-050
48/48
24/24
B29-35B-100
ND
ND
ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
1 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-35B
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-35B
Samples
Datum
Elevation
M. Juarez
H. Heggeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
0.5 1.0
4.5 5.0
8.0 9.5
10.0 12.0
0.5 5.0
SM
CL
6-in. CONCRETE
Medium dense reddish-brown silty fine SAND, no odor, moist, with trace angular fine gravel 3- in. dark brown silty medium SAND with trace angular fine gravel and slight petroleum hydro-carbon odor at
1.5 ft bgs
Becomes moderate olive-brown at 3.5 ft
-FILLVery stiff reddish-brown fine sandy CLAY, no odor, moist B29-35C-010
48/48
B29-35C-050
48/48
48/48
B29-35C-100
48/48
ND
0.5 ND
-
Depth (ft) to:
Drilling Equipment and Procedures
Summary
Field Tests:
2 Drill Mud:
Hammer Weight (lb) ---
Boring No.
Casing
Casing:
PID Make & Model:
Hoist/Hammer:
Elapsed Riser Pipe
Start
Bit Type:
G H&A Rep.
Plasticity: N - Nonplastic L - Low M - Medium H - High
Dry Strength: N - None L - Low M - Medium H - High V - Very High 1 127827-007
See Plan
Type
Location
B29-35C
Time (hr.)
-
of Casing
Bottom
Automatic Hammer
Time
Water Level Data
Boring No.
Note: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Sample ID
Geoprobe shoe 21.0
O - Open End Rod
T - Thin Wall Tube
Barrel
Water
NAVD88
File No.
Concrete
Hammer Fall (in.)
Bentonite Seal
Finish
U - Undisturbed Sample
S - Split Spoon Sample
Sampler
Overburden (ft)
Rock Cored (ft)
of
Rig Make & Model:
Grout
Screen
Well Diagram
Geoprobe 6620 DT
Sheet No.
January 8, 2020
of Hole
-
1.75 -
Inside Diameter (in.)
Driller
-
-
Date Bottom
Filter Sand
Dilatancy: R - Rapid S - Slow N - None
Toughness: L - Low M - Medium H - High
*Note: Maximum particle size is determined by direct observation within the limitations of sampler size.
Cuttings
MiniRAE 3000 10.6 eV bulb
B29-35C
Samples
Datum
Elevation
M. Juarez
H. Heffeness
January 8, 2020
S - Split Spoon Sample
G - Geoprobe
Client
Project
Contractor
Rohr, Inc. a Collins Aerospace Company
Interphase Environmental, Inc.
Parcel A Data Gap Assessment-Building 29
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)Depth (ft)
0 5
10 15
Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
16.0 20.0
25.0 18.0
24.0 25.0
ML
SM
Very stiff yellowish-brown clayey SILT, no odor, moist
Becomes yellowish-gray, micaceous at 21.0 ft
Becomes yellowish-brown with mottled light yellowish-gray at 22.0 ft Becomes wet at 23.0 ft
Loose yellowish-brown silty fine SAND, no odor, saturated, micaceous BOTTOM OF EXPLORATION 25.0 FT
Notes:
-Groundwater encountered at 24.0 ft bgs during drilling -Groundwater sample collected between 20.0 and 25.0 ft bgs. 48/48
48/48
24/24
NOTE: Soil identification based on visual-manual methods of the USCS as practiced by Haley & Aldrich, Inc.
Boring No.
File No.
Sheet No. 2 of 2
Boring No. B29-35C
B29-35C
127827-007
H&A WNC TEST BORING LOG R4 127827-007_HA-LIB09.GLB HA-TB+CORE+WELL-07-1.GDT \\HALEYALDRICH.COM\SHARE\SDG_COMMON\127827_NORTH CAMPUS\007_PROJECT SPRINGSTEEN PARCEL A, BLDGS 29 99 100\PARCEL A DATA GAP ASSESSMENT\GINT\127827-007TB_DATABASE.GPJ Feb 18, 20
TEST BORING REPORT
Sample
Depth (ft)
Depth (ft)
15 20
25 Stratum
Change
Elev/Depth (ft)
USCS Symbol
VISUAL-MANUAL IDENTIFICATION AND DESCRIPTION
(Density/consistency, color, GROUP NAME, max. particle size*, structure, odor, moisture, optional descriptions
GEOLOGIC INTERPRETATION)
Sample No.
& Rec. (in.)
PID
Readings
APPENDIX B
Groundwater Protection Levels
TABLE 10
GROUNDWATER PROTECTION LEVELS
FORMER SOUTH CAMPUS, NORTH OF EXCHANGE PARCEL
CHULA VISTA, CA