Arcadia City Council
March 18, 2025

32 Orff, K., H. Brown, S. Caputo, E. J. McAdams, M. Fowle, G. Phillips, C. DeWitt, and Y.

Gelb. 2007. Bird-safe buildings guidelines. New York City Audubon, New York.

Parkins, K. L., S. B. Elbin, and E. Barnes. 2015. Light, glass, and bird–building collisions in an urban park. Northeastern Naturalist 22:84-94.

Porter, A., and A. Huang. 2015. Bird collisions with glass: UBC pilot project to assess bird collision rates in Western North America. UBC Social Ecological Economic Development Studies (SEEDS) Student Report. Report to Environment Canada, UBC SEEDS and UBC BRITE.

Riding, C. S., T. J. O’Connell, and S. R. Loss. 2020. Building façade-level correlates of bird–window collisions in a small urban area. The Condor: Ornithological Applications 122:1–14.

Rössler, M., E. Nemeth, and A. Bruckner. 2015. Glass pane markings to prevent bird- window collisions: less can be more. Biologia 70: 535—541. DOI: 10.1515/biolog- 2015-0057

Sabo, A. M., N. D. G. Hagemeyer, A. S. Lahey, and E. L. Walters. 2016. Local avian density inÀuences risk of mortality from window strikes. PeerJ 4:e2170; DOI

10.7717/peerj.2170

San Francisco Planning Department. 2011. Standards for bird-safe buildings. San Francisco Planning Department, City and County of San Francisco, California.

Santos, S. M., F. Carvalho, and A. Mira. 2011. How long do the dead survive on the road? Carcass persistence probability and implications for road-kill monitoring surveys.

PLoS ONE 6(9): e25383. doi:10.1371/journal.pone.0025383

Schneider, R. M., C. M. Barton, K. W. Zirkle, C. F. Greene, and K. B. Newman. 2018.

Year-round monitoring reveals prevalence of fatal bird-window collisions at the Virginia Tech Corporate Research Center. PeerJ 6:e4562 https://doi.org/10.7717/ peerj.4562

Sheppard, C., and G. Phillips. 2015. Bird-friendly building design, 2nd Ed., American Bird Conservancy, The Plains, Virginia.

Shuford, W. D., and T. Gardali, [eds.]. 2008. California bird species of special concern: a ranked assessment of species, subspecies, and distinct populations of birds of immediate conservation concern in California. Studies of Western Birds 1. Western Field Ornithologists, Camarillo, California.

Somerlot, K. E. 2003. Survey of songbird mortality due to window collisions on the Murray State University campus. Journal of Service Learning in Conservation Biology 1:1–19.

33 Smallwood, K.S. 2002. Habitat models based on numerical comparisons. Pages 83-95 in Predicting species occurrences: Issues of scale and accuracy, J. M. Scott, P. J.

Heglund, M. Morrison, M. Raphael, J. Haufler, and B. Wall, editors. Island Press, Covello, California.

Smallwood, K. S., and N. L. Smallwood. 2023. Measured effects of anthropogenic development on vertebrate wildlife diversity. Diversity 15, 1037. https://doi.org/10.3390/d15101037.

Smallwood, N.L. and E.M. Wood. 2022. The ecological role of native plant landscaping in residential yards to urban wildlife. Ecosphere 2022;e4360.

Terrill, R. S., C. A. Dean, J. Garrett, D. W. Maxwell, L. Hill, A. Farnsworth, A. M. Dokter, M. W. Tingley. 2021. A novel locality for the observation of thousands of passerine birds during spring migration in Los Angeles County, California. Western Birds 52:322̽339. doi 10.21199/WB52.4.4

Van Doren, B. M., D. E. Willardb, M. Hennenb, K. G. Hortonc, E. F. Stubera, D.

Sheldond, A. H. Sivakumare, J. Wanga, A. Farnswortha, and B. M. Winger. 2021.

Drivers of fatal bird collisions in an urban center. Proceedings of the National Academy of Sciences 118 (24). e2101666118








͓ʹͶǦͲͲʹǤšš
‡
‡„‡”ͳͺǡ ʹͲʹͶ

ƒ›Ž‡›‘
‘œ‡ƒ—”—”›
ͳͻ͵ͻ
ƒ””‹•‘–”‡‡–ǡ—‹–‡ͳͷͲ
ƒŽƒ†ǡͻͶ͸ͳʹ
SUBJECT: Arcadia Town Center Project
City of Arcadia, CA
Review and Comment on Noise Study
‡ƒ”•Ǥ‘ǡ
‡” ›‘—” ”‡“—‡•–ǡ ‹Ž•‘
Š”‹‰ Šƒ• ”‡˜‹‡™‡† –Š‡ ‹ˆ‘”ƒ–‹‘ ƒ† ‘‹•‡ ‹’ƒ
– ƒƒŽ›•‹• ‹ –Š‡
ˆ‘ŽŽ‘™‹‰†‘
—‡–•ǣ
Arcadia Town Center Project
Initial Study / Mitigated Negative Declaration, November 2024 (IS / MND) Appendix G Noise Calculations (Appendix G)
Š‡”‘’‘•‡†”
ƒ†‹ƒ‘™‡–‡””‘Œ‡
–ȋ”‘Œ‡
–Ȍ ™‘—Ž†”‡•—Ž–‹–Š‡
‘•–”—
–‹‘‘ˆƒ‹š‡†Ǧ—•‡
†‡˜‡Ž‘’‡–
‘•‹•–‹‰ ‘ˆ ƒ ˆ‹˜‡Ǧ•–‘”› „—‹Ž†‹‰ ™‹–Š •—„–‡””ƒ‡ƒ ƒ† ‰”‘—† Ž‡˜‡Ž ’ƒ”‹‰Ǥ Š‡ ’”‘Œ‡
–‹••—””‘—†‡†„› ”‡•‹†‡–‹ƒŽ—•‡•–‘–Š‡‘”–Š™‡•–ƒ†• ‘—–Š‡ƒ•–ǡƒ’ƒ”–‘–Š‡•‘—–Šǡƒ†

‘‡”
‹ƒŽ—•‡•Ǥ
Š‹•Ž‡––‡””‡’‘”–•‘—”
‘‡–•‘–Š‡‘‹•‡ƒŽ›•‹•‹‡
–‹‘͵Ǥͳ͵ ‘ˆ–Š‡
‹–‹ƒŽ–—†›Ȁ‹–‹‰ƒ–‡†
‡‰ƒ–‹˜‡ ‡
Žƒ”ƒ–‹‘ ƒ† –Š‡ ‘‹•‡ ƒŽ
—Žƒ–‹‘• ‹
Ž—†‡† ‹ ’’‡†‹š
Ǥ ‹Ž•‘
Š”‹‰ǡ 
‘—•–‹
ƒŽ
‘•—Ž–ƒ–•ǡ Šƒ• ’”ƒ
–‹
‡† ‡š
Ž—•‹˜‡Ž› ‹ –Š‡ ˆ‹‡Ž† ‘ˆ ƒ
‘—•–‹
• •‹
‡ͳͻ͸͸Ǥ—”‹‰ ‘—” ͷ͹ ›‡ƒ”•‘ˆ
‘’‡”ƒ–‹‘ǡ ™‡ Šƒ˜‡ ’”‡’ƒ”‡† Š—†”‡†• ‘ˆ ‘‹•‡ •–—†‹‡• ˆ‘” ˜‹”‘‡–ƒŽ ’ƒ
– ‡’‘”–• ƒ†
–ƒ–‡‡–•Ǥ‡Šƒ˜‡‘‡‘ˆ–Š‡Žƒ”‰‡•––‡
Š‹
ƒŽŽƒ„‘”ƒ–‘”‹‡• ‹–Š‡ƒ
‘—•–‹
ƒŽ
‘•—Ž–‹‰‹†—•–”›Ǥ
‡ƒŽ•‘—–‹Ž‹œ‡‹†—•–”›Ǧ•–ƒ†ƒ”†ƒ
‘—•–‹
ƒŽ’”‘‰”ƒ••—
Šƒ• ‘ƒ†™ƒ›‘•–”—
–‹‘‘‹•‡‘†‡Ž
ȋȌǡ ‘—†ǡ ƒ†Ǥ
•Š‘”–ǡ™‡ƒ”‡™‡ŽŽ“—ƒŽ‹ˆ‹‡†–‘ ’”‡’ ƒ ” ‡‡˜ ‹”‘ ‡– ƒ Ž  ‘‹•‡  •–—†‹‡•ƒ†”‡˜‹‡™•–—†‹‡•’”‡’ƒ”‡†„›‘–Š‡”•Ǥ
23

WILSON IHRIG
Arcadia Town Center Project
Review and Comment on Noise Report

Adverse Effects of Noise1
Ž–Š‘—‰Š–Š‡Š‡ƒŽ–Š‡ˆˆ‡
–•‘ˆ‘‹•‡ƒ”‡‘––ƒ‡ƒ••‡”‹‘—•Ž›‹–Š‡‹–‡†–ƒ–‡•ƒ•–Š‡›ƒ”‡‹‘–Š‡”

‘—–”‹‡•ǡ–Š‡›ƒ”‡”‡ƒŽƒ†ǡ‹ƒ›’ƒ”–•‘ˆ–Š‡
‘—–”›ǡ’‡”˜ƒ•‹˜‡Ǥ
Noise-Induced Hearing Loss.  
ˆ ƒ ’‡”•‘ ‹• ”‡’‡ƒ–‡†Ž› ‡š’‘•‡† –‘ Ž‘—† ‘‹•‡•ǡ Š‡ ‘” •Š‡ ƒ› ‡š’‡”‹‡
‡‘‹•‡Ǧ‹†—
‡†Š‡ƒ”‹‰‹’ƒ‹”‡–‘”Ž‘••Ǥ
–Š‡ ‹–‡†–ƒ–‡•ǡ„‘–Š–Š‡

—’ƒ–‹‘ƒŽ

‡ƒŽ–Š ƒ† ƒˆ‡–› †‹‹•–”ƒ–‹‘ ȋ
Ȍ ƒ† –Š‡ ƒ–‹‘ƒŽ
•–‹–—–‡ ˆ‘” 

—’ƒ–‹‘ƒŽ ƒˆ‡–› ƒ†

‡ƒŽ–Šȋ

Ȍ’”‘‘–‡•–ƒ†ƒ”†•ƒ†”‡‰—Žƒ–‹‘•–‘’”‘–‡
––Š‡Š‡ƒ”‹‰‘ˆ’‡‘’Ž‡‡š’‘•‡†–‘Š‹‰Š
Ž‡˜‡Ž•‘ˆ‹†—•–”‹ƒŽ‘‹•‡Ǥ
Speech Interference.‘–Š‡”
‘‘’”‘„Ž‡ƒ••‘
‹ƒ–‡†™‹–Š‘‹•‡‹••’‡‡
Š‹–‡”ˆ ‡”‡
‡Ǥ

ƒ††‹–‹‘–‘–Š‡‘„˜‹‘—•‹••—‡•–Šƒ–ƒ›ƒ”‹•‡ˆ”‘‹•—†‡”•–ƒ†‹‰•ǡ•’‡‡ Š‹–‡”ˆ‡”‡
‡ƒŽ•‘Ž‡ƒ†•
–‘’”‘„Ž‡•™‹–Š
‘
‡–”ƒ–‹‘ˆƒ–‹‰—‡ǡ‹””‹–ƒ–‹‘ǡ†‡
”‡ƒ•‡†™‘”‹‰
ƒ’ƒ
‹–›ǡƒ†ƒ—–‘ƒ–‹
•–”‡••
”‡ƒ
–‹‘•Ǥ ‘”
‘’Ž‡–‡•’‡‡
Š‹–‡ŽŽ‹‰‹„‹Ž‹–›ǡ–Š‡•‘—†Ž‡˜‡ Ž‘ˆ–Š‡•’‡‡
Š•Š‘—Ž†„‡ͳͷ–‘ͳͺ†
Š‹‰Š‡”–Šƒ–Š‡„ƒ
‰”‘—†‘‹•‡Ǥ›’‹
ƒŽ‹†‘‘”•’‡‡
ŠŽ‡˜‡Ž•ƒ”‡Ͷͷ–‘ͷͲ†ƒ–ͳ‡–‡”ǡ•‘ƒ›
‘‹•‡ƒ„‘˜‡͵Ͳ†„‡‰‹•–‘‹–‡”ˆ‡”‡™‹–Š•’‡‡
Š‹–‡ŽŽ‹‰‹„‹Ž ‹–›ǤŠ‡
‘‘”‡ƒ
–‹‘–‘Š‹‰Š‡”
„ƒ
‰”‘—†‘‹•‡Ž‡˜‡Ž•‹•–‘”ƒ‹•‡‘‡ǯ•˜‘‹
‡Ǥ
ˆ–Š‹•‹•”‡“—‹”‡†’‡”•‹•–‡–Ž›ˆ‘”Ž‘‰’‡”‹‘†•‘ˆ–‹‡ǡ •–”‡••”‡ƒ
–‹‘•ƒ†‹””‹–ƒ–‹‘™‹ŽŽŽ‹‡Ž›”‡•—Ž–Ǥ
Sleep Disturbance.  ‘‹•‡
ƒ †‹•–—”„•Ž‡‡’ „›ƒ‹‰ ‹–‘”‡ †‹ˆˆ‹
—Ž– –‘ ˆƒŽŽ ƒ•Ž‡‡’ǡ „› ™ƒ‹‰
•‘‡‘‡ƒˆ–‡”–Š‡›ƒ”‡ƒ•Ž‡‡’ǡ‘”„›ƒŽ–‡”‹‰–Š‡‹”•Ž‡‡’•–ƒ‰‡ǡ‡Ǥ‰Ǥǡ”‡†— ‹‰–Š‡ƒ‘—–‘ˆ”ƒ’‹†‡›‡
‘˜‡‡– ȋȌ •Ž‡‡’Ǥ  ‘‹•‡ ‡š’‘•—”‡ ˆ‘” ’‡‘’Ž‡ ™Š‘ ƒ”‡ •Ž‡‡’‹ ‰ Šƒ• ƒŽ•‘ „‡‡ Ž‹‡† –‘ ‹
”‡ƒ•‡†„Ž‘‘†’”‡••—”‡ǡ‹
”‡ƒ•‡†Š‡ƒ”–”ƒ–‡ǡ‹
”‡ƒ•‡‹„‘†›‘˜‡‡–•ǡƒ†‘–Š‡”’Š›•‹‘Ž‘‰‹
ƒŽ
‡ˆˆ‡
–•Ǥ‘–•—”’”‹•‹‰Ž›ǡ’‡‘’Ž‡™Š‘•‡•Ž‡‡’‹•†‹•–—”„‡†„›‘‹•‡‘ˆ–‡‡š’‡”‹‡ ‡•‡
‘†ƒ”›‡ˆˆ‡
–•
•—
Šƒ•‹
”‡ƒ•‡†ˆƒ–‹‰—‡ǡ†‡’”‡••‡†‘‘†ǡƒ††‡
”‡ƒ•‡†™‘”’‡”ˆ‘”ƒ
‡Ǥ
Cardiovascular and Physiological Effects.  
—ƒǯ• „‘†‹Ž› ”‡ƒ
–‹‘• –‘ ‘‹•‡ ƒ”‡ ”‘‘–‡† ‹ –Š‡
Dzˆ‹‰Š–‘”ˆŽ‹‰Š–dz”‡•’‘•‡–Šƒ–‡˜‘Ž˜‡†™Š‡ƒ›‘‹•‡••‹‰ƒŽ ‡†‹‹‡–†ƒ‰‡”ǤŠ‡•‡‹ Ž—†‡
‹
”‡ƒ•‡†„Ž‘‘†’”‡••—”‡ǡ‡Ž‡˜ƒ–‡†Š‡ƒ”–”ƒ–‡ǡƒ†˜ƒ•‘
‘•–”‹
–‹‘Ǥ”‘Ž‘‰‡†‡š’‘•—”‡–‘ƒ
—–‡
‘‹•‡•
ƒ”‡•—Ž–‹’‡”ƒ‡–‡ˆˆ‡
–••—
Šƒ•Š›’‡”–‡•‹‘ƒ†Š‡ƒ”–†‹•‡ƒ•‡Ǥ
Impaired Cognitive Performance.–—†‹‡•Šƒ˜‡‡•–ƒ„Ž‹•Š‡†–Šƒ–‘‹•‡‡š’‘•—”‡‹’ƒ‹”•’‡‘’Ž‡ǯ•  ƒ„‹Ž‹–‹‡•–‘’‡”ˆ‘”
‘’Ž‡š–ƒ••ȋ–ƒ••–Šƒ–”‡“—‹”‡ƒ––‡–‹‘–‘†‡–ƒ‹Ž‘”ƒƒŽ›–‹ ƒŽ’”‘
‡••‡•Ȍƒ†
‹–ƒ‡•”‡ƒ†‹‰ǡ ’ƒ›‹‰ƒ––‡–‹‘ǡ•‘Ž˜‹‰’”‘„Ž‡•ǡ ƒ†‡‘” ‹œ‹‰‘”‡†‹ˆˆ‹ —Ž–ǤŠ‹•‹•™Š›
–Š‡”‡ƒ”‡•–ƒ†ƒ”†•ˆ‘”
Žƒ••”‘‘„ƒ
‰”‘—†‘‹•‡Ž‡˜‡Ž•ƒ†™Š›‘ˆˆ‹
‡•ƒ†Ž‹„”ƒ”‹‡•ƒ”‡†‡•‹‰‡†
–‘’”‘˜‹†‡“—‹‡–™‘”‡˜‹”‘‡–•Ǥ





1 More information on these and other adverse effects of noise may be found in Guidelines for Community Noise, eds B Berglund, T Lindvall, and D Schwela, World Health Organization, Geneva, Switzerland, 1999. (https://www.who.int/docstore/peh/noise/Comnoise-1.pdf)

24

WILSON IHRIG
Arcadia Town Center Project
Review and Comment on Noise Report

Baseline Noise is Not Properly Established
Š‡ƒ‡”‹™Š‹
Š–Š‡
ȀŠƒ•†‡–‡”‹‡†–Š‡‡š‹•–‹‰‘‹• ‡‡˜‹”‘‡–‹•—•—’’‘”–‡†Ǥ Š‡
Ȁ †‘‡• ‘– •Š‘™ ƒ„‹‡– ‡ƒ•—”‡‡– Ž‘
ƒ–‹‘•Ǥ ƒ„Ž‡ ʹͲ ȏ’‰Ǥ ͵Ǧ͹ͳȐ ‹†‹
ƒ–‡• –Š‡
‡ƒ•—”‡‡–•™‡”‡–ƒ‡ƒ––Š‡’”‘Œ‡
–„‘—†ƒ”›ǡ”ƒ–Š‡”–Šƒƒ–•‡•‹–‹˜‡”‡
‡‹˜‡”•ǡ•—
Šƒ•‡ƒ”„›
”‡•‹†‡
‡•‘ƒ–ƒŽƒ”ƒȋͶͳͲˆ–ˆ”‘•‹–‡Ȍƒ†”‡•‹†‡
‡•‘ ƒ–ƒ‹–ƒǤȋʹͺͲˆ–ˆ”‘•‹–‡ȌǤŠ‡
ƒ„‹‡– Ž‡˜‡Ž• ’”‡•‡–‡† ‹ ƒ„Ž‡ ʹͲ ƒ”‡ „ƒ•‡† ‘ •Š‘”–Ǧ–‡” ʹͲ Ǧ‹—–‡ ‡ƒ•—”‡‡–•Ǥ • ƒ
‘™Ž‡†‰‡†‹–Š‡
ȀǡDz–Š‡ƒ„‹‡–™‘—Ž†ˆŽ—
–—ƒ–‡‘˜‡”–Š‡
‘—”•‡‘ˆ‡ƒ
Š™‘”†ƒ›ƒ•™‡ŽŽ
ƒ•„ƒ•‡†‘†‹•–ƒ
‡ƒ†”‡Žƒ–‹˜‡Ž‘
ƒ–‹‘ˆ”‘–Š‡•‹–‡dzȏ’‰Ǥ͵Ǧ͹ͻȐǤŠ‡‡ƒ•—”‡‡–•—•‡†ƒ

‘—–
ˆ‘” ‡‹–Š‡” ˆŽ—
–—ƒ–‹‘ ‘˜‡” –Š‡
‘—”•‡ ‘ˆ –Š‡ †ƒ›‘” ƒ†Œ—•–‡– ™‹–Š †‹•–ƒ
‡ ˆ”‘ –Š‡ •‘—”
‡•

ƒ’–—”‡†Ǥ —”–Š‡”ǡ ƒ• •–ƒ–‡† ‹ ƒ„Ž‡ ʹͲǡ –Š‡ ‡ƒ•—”‡‡– Ž‘•‡” –‘ ƒ–ƒ Žƒ”ƒ ”‡•‹†‡
‡• ™ƒ•
†‘‹ƒ–‡†„›
‘‹•‡†‹”‡
–Ž›ƒ†Œƒ
‡––‘–Š‡”‘Œ‡
–•‹–‡Ǥ
The Project must conduct properly documented ambient measurements near sensitive receptors that capture the current baseline conditions during quiet period of the day and night to determine the impact of construction and operational noise.

Figure 1 Project Site and Noise Sensitive Receivers
Potentially Significant Construction Noise Impacts
 Š ‡ 
 Ȁ    ˆ ƒ ‹ Ž • – ‘ † ‹ •
Ž ‘ • ‡ ƒ  †  ‹ – ‹ ‰ ƒ – ‡ – Š ‡  ” ‘ Œ ‡
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—” ‡ƒ”–Š‡’”‘Œ‡
–̶ȏ͵Ǧ͹ͺȐǡ‡˜‡–Š‘—‰Š
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‘•–”—
–‹‘ ‘‹•‡
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–‹‘• ƒ”‡ •Š‘™ ƒ– –Š‡•‡ ”‡•‹†‡
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–‹˜‹–› ”‡ˆ‡”‡
‡ Ž‡˜‡Ž• ’”‡•‡–‡† ‹ –Š‡

Ȁƒ„Ž‡ʹͷȏ’‰Ǥ͵Ǧ͹ͺȐƒ†’’‡†‹š
ǡ
‘•–”—
–‹‘‘‹•‡™‘—Ž†”ƒ‰‡ˆ”‘͸Ͳ†–‘͸ͻ†
ƒ––Š‡•‡ƒ–ƒ‹–ƒ”‡•‹†‡
‡•ƒ†ͷ͸†–‘͸ͷ†ƒ–ˆ—”–Š‡””‡•‹†‡
‡•‘ƒ–ƒŽƒ”ƒ–”‡‡–ǡƒ•
•Š‘™‹ƒ„Ž‡ͳ„‡Ž‘™Ǥ

Residences
Residences
Park /Memorial
25 26

WILSON IHRIG
Arcadia Town Center Project
Review and Comment on Noise Report

Table 1 Estimated Construction Noise Levels
Construction Phase
Noise Levels (Leq, dBA) 

95 feet –
Arcadia County
Park1
10 feet –
Elk Lodge1
280 feet –
Santa Anita
Residences 2
410 feet –
Santa Clara
Residences 2
Ground Cleaning /
Demolition ͹ͺ 98 69 65
Excavation ͹͵ 93 64 60
Foundation Construction ͹ʹ 92 63 59
Building Construction ͸ͻ 89 60 56
Paving and Site Cleanup ͸ͻ 89 60 56
ͳǤ ”‘ƒ„Ž‡ʹͷ‹
Ȁ
ʹǤƒŽ
—Žƒ–‡†„ƒ•‡†‘†‹•–ƒ
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Š‡
Ȁ†‘‡•‘–‡š’Ž‹
‹–Ž›‡•–ƒ„Ž‹•Š
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–‹‘‘‹•‡
”‹–‡”‹ƒǤ
–”‡ˆ‡”‡
‡•–Š‡‹–›‘ˆ”
ƒ†‹ƒ
‘‹•‡”†‹ƒ
‡Ž‹‹–•ȏ’‰Ǥ͵Ǧ͹ͷȐǡ„—–‘‹–•‡
–‹‘ͷ͸ͳͲǤ͵ȋ„Ȍ ǡ™Š‹
Š‹
Ž—†‡•
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2 https://library.municode.com/ca/arcadia/codes/code_of_ordinances?nodeId=ARTIVPUWEMOPO_CH6NORE_PT1G EPR_4610.3NOLI
26 cont
27 28

WILSON IHRIG
Arcadia Town Center Project
Review and Comment on Noise Report

”‡†—
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–‹‘.

The Project must properly evaluate construction noise impacts, including the noise increase over ambient levels at sensitive receptor locations. If the increase is significant the Project must properly evaluate mitigation measures to reduce the impacts to less than significant. Operational Analysis Incomplete
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Conclusion
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29 30
28 cont






2656 29th Street, Suite 201
Santa Monica, CA 90405
Matt Hagemann, P.G, C.Hg.
(949) 887-9013
[email protected]
Paul E. Rosenfeld, PhD
(310) 795-2335
[email protected]
December 18, 2024
Hayley Uno
Lozeau | Drury LLP
1939 Harrison Street, Suite 150
Oakland, CA 94618
Subject: Comments on the Arcadia Town Center Mixed Use Project (SCH No. 2024110749) Dear Ms. Uno,
We have reviewed the November 2024 Initial Study/Mitigation Negative Declaration (“IS/MND”) for the Arcadia Town Center Mixed Use Project (“Project”) located in the City of Arcadia (“City”). The Project proposes to construct 440,938-square-feet (“SF”) of residential space, including 181 dwelling units and 378 parking spaces on the 2.27-acre site.

Our review concludes that the IS/MND fails to adequately evaluate the Project’s air quality, health risk, and greenhouse gas (“GHG”) impacts. Emissions and health risk impacts associated with construction and operation of the proposed Project may be underestimated and inadequately addressed. An Environmental Impact Report (“EIR”) should be prepared to adequately assess and mitigate the potential air quality, health risk, and GHG impacts that the project may have on the environment.

Air Quality
Failure to Provide Complete CalEEMod Output Files
Land use development projects under the California Environmental Quality Act (“CEQA”) typically evaluate air quality impacts and calculate potential criteria air pollutant emissions using the California Emissions Estimator Model (“CalEEMod”).1 CalEEMod uses default values tailored to site-specific details such as land use type, meteorological data, lot size, project type, and typical equipment associated with that type. If project-specific details are available, users can modify these defaults, but CEQA requires substantial evidence to justify such changes. Once the inputs are finalized, the model calculates the

1 “CalEEMod User’s Guide.” California Air Pollution Control Officers Association (CAPCOA), May 2021, available at:
https://www.aqmd.gov/caleemod/user's-guide.
31 32

2 project's construction and operational emissions and generates "output files." These output files disclose to the reader what parameters are used in calculating the Project’s air pollutant emissions and demonstrate where default values are changed. Justifications are provided for the values selected.

Review of the Project’s CalEEMod output files in Appendix A of the IS/MND reveals that the “Arcadia Town Center v2” includes land use inputs but omits all other qualitative outputs regarding the Project’s construction-related and operational emission (pp. 38, 39).

Note: Only sections 1.2, 1.3, 2.1, and 2.2 are included for reader clarity.

Without access to specific emissions values, we are unable to verify the potential significance or accuracy of the Project’s model. Furthermore, the “Arcadia Town Center v2” model does not include the “User Changes to Default” table. (Appendix A, pp. 54)
Without access to the “User Changes to Default Data” table, we are unable to verify whether changes were made to the model’s default values. CEQA requires public disclosure of environmental impacts to 32 cont

3 ensure transparency with regards to potential environmental impacts of land use developments.2 An EIR should be prepared to disclose the Project’s complete CalEEMod output files and adhere to CEQA’s formal guidelines.

Diesel Particulate Matter Emissions Inadequately Evaluated The IS/MND determines that the Project would result in a negligible health risk impact without conducting a construction health risk analysis (“HRA”). CEQA requires all proposed projects to connect their emissions with potential adverse impacts on human health caused by those emissions. 3 As the
IS/MND does not establish a connection between the Project’s construction-related diesel particulate matter (“DPM”) emissions and potential health risks to nearby sensitive receptors, the Project violates CEQA’s requirement. Additionally, the IS/MND does not compare the Project's excess cancer risk to the South Coast Air Quality Management District’s (“SCAQMD”) threshold of 10 in one million. 4 An assessment of the health risk posed to nearby existing receptors due to Project construction should be conducted to comply with the most relevant guidance.

Screening-Level Analysis Demonstrates Potentially Significant Health Risk Impact We conducted an HRA using AERSCREEN, a screening-level air quality dispersion model that estimates maximum potential concentrations of air contaminants affecting nearby sensitive receptors.5 If AERSCREEN indicates a potential air quality hazard, a detailed modeling analysis is required before Project approval. 6
To conduct a preliminary, screening-level construction HRA, it is necessary to have an estimate of the Project's annual particulate matter 10 ("PM10") exhaust emissions.7 However, as detailed in the section of this letter titled Failure to Provide Complete CalEEMod Output Files, the Project's CalEEMod files exclude the projected values for construction-related emissions. In the absence of this requisite information, we created a model using the Project-specific details provided in the IS/MND and related documents to estimate PM
10 emissions.

2 “Environmental Review Guidelines.” San Diego County Air Pollution Control District, September 2024, available at: https://www.sdapcd.org/content/dam/sdapcd/documents/grants/planning/ceqa/DRAFT-SDAPCD-CEQA- Guidelines.pdf#:~:text=It%20is%20intended%20to%20require%20public%20disclosure,under%20what%20circumst ances%20to%20approve%20such%20projects.&text=In%20accordance%20with%20Section%2015063%20of%20th e,have%20a%20significant%20effect%20on%20the%20environment. 3 “Sierra Club v. County of Fresno.” Supreme Court of California, December 2018, available at:
https://ceqaportal.org/decisions/1907/Sierra%20Club%20v.%20County%20of%20Fresno.pdf . 4 “South Coast AQMD Air Quality Significance Thresholds.” SCAQMD, March 2023, available at:
https://www.aqmd.gov/docs/default-source/ceqa/handbook/south-coast-aqmd-air-quality-significance- thresholds.pdf?sfvrsn=25.
5 “Air Quality Dispersion Modeling - Screening Models,” U.S. EPA, available at: https://www.epa.gov/scram/air- quality-dispersion-modeling-screening-models.
6 “Guidelines for Exposure Assessment.” U.S. Environmental Protection Agency, 1992, available at:
https://cfpub.epa.gov/ncea/risk/recordisplay.cfm?deid=15263. 7 “Inhalable Particulate Matter and Health (PM2.5 and PM10).” CARB, available at:
https://ww2.arb.ca.gov/resources/inhalable-particulate-matter-and-health . 32 cont
33 34

4 Our analysis included 173,760-SF of “Apartments Mid Rise,” 151,200-SF of “Enclosed Parking with Elevator,” 4,000-SF of “Strip Mall,” 1-acre of “City Park,” 5,000-SF of “User Defined Commercial,” and 5,000-SF of “General Office Building,” consistent with the Project’s original model. Additionally, as the Project’s construction duration was not properly justified or disclosed, we developed a proportionately altered construction schedule to match the total construction duration of 29 months (IS/MND, p. 2-11).8 All other values were left as default.9
Following Office of Environmental Health Hazard Assessment’s (“OEHHA”) recommendations, we began residential exposure at the third trimester of life. Our CalEEMod emissions indicate that construction will produce approximately 380 pounds of diesel particulate matter (“DPM”) over the 730-day period. 10 The AERSCREEN model simulates maximum concentrations from emission sources using an average emission rate. We calculated this average DPM emission rate to account for variations in equipment usage and truck trips during construction using the following equation:

Emission Rate ቀ grams
secondቁ = 380 lbs
730 days × 453.6 grams
lbs × 1 day
24 hours × 1 hour
3,600 seconds = ૙. ૙૙૚૝૝ ܏/ܛ
We estimated a construction emission rate of 0.00144 grams per second (“g/s”). Construction was simulated as a 2.27-acre rectangular area source in AERSCREEN, with approximate dimensions of 136- by 68-meters. A release height of 3 meters was selected to represent the height of stacks of heavy-duty vehicles, and an initial vertical dimension of one and a half meters was used to simulate instantaneous plume dispersion upon release. An urban meteorological setting was selected with model-default inputs for wind speed and direction distribution. The population of the city of Arcadia was obtained from U.S. 2023 Census data.11
The AERSCREEN model generates maximum reasonable estimates of single-hour DPM concentrations from the Project Site. U.S. Environmental Protection Agency (“U.S. EPA”) guidance suggests that in screening procedures, the annualized average concentration of an air pollutant to be estimated by multiplying the single-hour concentration by 10%.12 According to the AERSCREEN output files the maximally exposed individual receptor would be located 75 meters from the Project site. However, the IS/MD states that the nearest sensitive receptors are residences located approximately 280 feet, or 85 meters, from the Project site (p. 3-10). The single-hour concentration estimated by AERSCREEN for Project construction is 2.670 ђg/m3 DPM at around 100 meters downwind.13 Multiplying this single-hour

8 See Attachment A for the proportionately altered construction phases’ calculations. 9 See Attachment B for SWAPE’s CalEEMod output files.
10 See Attachment C for health risk calculations.
11 “Arcadia” U.S. Census Bureau, 2023, available at: https://datacommons.org/place/geoId/0602462?q=arcadia. 12 “Screening Procedures for Estimating the Air Quality Impact of Stationary Sources Revised.” U.S. EPA, October 1992, available at: https://www.epa.gov/sites/default/files/2020-09/documents/epa-454r-92-019_ocr.pdf. 13 Note: AERSCREEN output files come in increments of 25 meters, so our emissions calculations are slightly underestimated.
34 cont

5 concentration by 10%, we get an annualized average concentration of 0.2670 ђg/m3 for Project construction at the nearest sensitive receptor.14
The excess cancer risk to the nearest sensitive receptor was calculated using applicable HRA methodologies as prescribed by OEHHA, in accordance with SCAQMD recommendation. 15 Guidance from OEHHA and California Air Resources Board (“CARB”) suggests utilizing a standard point estimate approach, with high-point estimate breathing rates and age sensitivity factors (“ASF”) to accurately assess risk, especially for susceptible populations like children. The residential exposure parameters considered in our screening-level HRA include daily breathing rates, exposure duration, ASFs, fraction of time at home, and exposure frequency for different age groups (see table below).

Exposure Assumptions for Residential Individual Cancer Risk Age Group
Breathing
Rate
(L/kg-day)16
Age
Sensitivity
Factor17
Exposure
Duration
(years)
Fraction of
Time at
Home18
Exposure
Frequency
(days/year)19
Exposure
Time
(hours/day)
3rd Trimester 361 10 0.25 1 350 24
Infant (0 – 2) 1090 10 2 1 350 24
Child (2 – 16) 572 3 14 1 350 24
Adult (16 –
30) 261 1 14 0.73 350 24
The procedure requires the incorporation of several discrete variates to effectively quantify dose per age group for the inhalation pathway. Contaminate dose is then multiplied by the cancer potency factor in units of inverse dose expressed in milligrams per kilogram per day (mg/kg/day-1) to derive the cancer risk estimate. The following dose algorithm was used to assess exposure assumptions:

14 See Attachment D for AERSCREEN output files.
15 “Supplemental Guidelines for Preparing Risk Assessments for the Air Toxics ‘Hot Spots’ Information and Assessment Act.” SCAQMD, October 2020, available at: http://www.aqmd.gov/docs/default-source/planning/risk- assessment/ab-2588-supplemental-guidelines.pdf?sfvrsn=19, p. 19; see also “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February 2015, available at:
https://oehha.ca.gov/media/downloads/crnr/2015guidancemanual.pdf . 16 “Supplemental Guidelines for Preparing Risk Assessments for the Air Toxics ‘Hot Spots’ Information and Assessment Act.” SCAQMD, October 2020, available at: http://www.aqmd.gov/docs/default-source/planning/risk- assessment/ab-2588-supplemental-guidelines.pdf?sfvrsn=19, p. 19; see also “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February 2015, available at:
https://oehha.ca.gov/media/downloads/crnr/2015guidancemanual.pdf . 17 “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February 2015, available at: https://oehha.ca.gov/media/downloads/crnr/2015guidancemanual.pdf , p. 8-5 Table 8.3. 18 “Risk Assessment Procedures.” SCAQMD, August 2017, available at: http://www.aqmd.gov/docs/default- source/rule-book/Proposed-Rules/1401/riskassessmentprocedures_2017_080717.pdf , p. 7. 19 “Risk Assessment Guidelines Guidance Manual for Preparation of Health Risk Assessments.” OEHHA, February 2015, available at: https://oehha.ca.gov/media/downloads/crnr/2015guidancemanual.pdf , p. 5-24. 34 cont

6 Dose୅୍ୖ,୮ୣ୰ ୟ୥ୣ ୥୰୭୳୮ = C ୟ୧୰ × E F × ൤ BR
BW൨ × A × C F
where:

DoseAIR = dose by inhalation (mg/kg/day), per age group Cair сĐŽŶĐĞŶƚƌĂƚŝŽŶŽĨĐŽŶƚĂŵŝŶĂŶƚŝŶĂŝƌ;ʅŐͬŵϯͿ
EF = exposure frequency (number of days/365 days)
BR/BW = daily breathing rate normalized to body weight (L/kg/day) A = inhalation absorption factor (default = 1)
CF = conversion factor (1x10-ϲ͕ʅŐƚŽŵŐ͕>ƚŽŵϯͿ
We used the following equation to calculate the overall cancer risk per appropriate age group:

Cancer Risk୅୍ୖ = Dose୅୍ୖ ×C P F ×A S F ×F A H ×ED
AT
where:

DoseAIR = dose by inhalation (mg/kg/day), per age group CPF = cancer potency factor, chemical-specific (mg/kg/day)-1 ASF = age sensitivity factor, per age group
FAH = fraction of time at home, per age group (for residential receptors only) ED = exposure duration (years)
AT = averaging time period over which exposure duration is averaged (always 70 years) Consistent with the 730-day construction schedule, the annualized average concentration for construction was used for the entire third trimester of pregnancy (0.25 years) and the first 1.75 years of the infantile stage of life (0 – 2 years). The results of our calculations are shown in the table below.

The Maximally Exposed Individual at an Existing Residential Receptor During Project Construction Age Group Duration (years) Concentration
(ug/m3) Cancer Risk
3rd Trimester 0.25 0.2670 3.63E-06
Infant (0 - 2) 1.75 0.2670 7.67E-05
Construction 2 8.04E-05
The excess cancer risks for the 3rd trimester of pregnancy and infant stage of life at the nearest sensitive receptor, over the course of Project construction are approximately 3.63 and 76.7 in one million, respectively. The excess cancer risk over just the course of the Project construction is approximately 34 cont
35

7 80.4 in one million, which exceeds the SCAQMD threshold of 10 in one million. This results in a potentially significant impact not previously addressed or identified in the IS/MND.

Our analysis represents a conservative screening-level HRA, which prioritizes public health. It is used to show the potential correlation between Project emissions and adverse health risks. The U.S. EPA recommends the use of a screening-level analysis as the first phase of a tiered approach to conducting exposure assumptions, as outlined in their Exposure Assessment Guidelines.20 Screening-level analyses require further evaluation with more developed modeling. Our initial HRA demonstrates that Project construction could lead to significant health risks. An EIR should be prepared to include a comprehensive HRA that properly evaluates impacts from construction.

Greenhouse Gas
Failure to Adequately Evaluate Greenhouse Gas Impacts
The IS/MND estimates that the Project will produce a net annual GHG emissions of 2,181-metric-tons of carbon dioxide equivalents per year (“MT CO2e/year”) (p. 3-50, Table 17).

The IS/MND indicates that the GHG emission values are included in Appendix A. However, as previously addressed, the IS/MND’s CalEEMod output files do not provide the emissions estimates or include any relevant inputs beyond the land uses. We are therefore unable to verify the legitimacy of the estimates presented in the table above and, as such, the Project’s GHG emissions could be underestimated. Until an EIR is prepared to include complete CalEEMod output files we cannot ensure the Project’s GHG emissions are accurately calculated and the IS/MND’s GHG analysis should not be relied upon for Project significance.

Mitigation
Feasible Mitigation Measures Available to Reduce Emissions As the Project would result in a potentially significant health risk impact to individuals in the community surrounding the Project site, the IS/MND must include all feasible mitigation to address the Project’s potential air quality and health risks. According to CEQA Guidelines § 15096(g)(2):
20 “Guidelines for Exposure Assessment.” U.S. Environmental Protection Agency, 1992, available at:
https://cfpub.epa.gov/ncea/risk/recordisplay.cfm?deid=15263. 35 cont
36 37

8 “When an updated EIR has been prepared for a project, the Responsible Agency shall not approve the project as proposed if the agency finds any feasible alternative or feasible mitigation measures within its powers that would substantially lessen or avoid any significant effect the project would have on the environment.”
The IS/MND should evaluate the following mitigation measures to reduce the DPM emissions associated with Project construction (see list below).

The Southern California Association of Governments’ 2020 Regional Transportation Plan/Sustainable Communities Strategy Program Environmental Impact Report provides the following mitigation measures:21
x Minimize unnecessary vehicular and machinery activities. x Require contractors to assemble a comprehensive inventory list (i.e., make, model, engine year, horsepower, emission rates) of all heavy-duty off-road (portable and mobile) equipment (50 horsepower and greater) that could be used an aggregate of 40 or more hours for the construction project.
x Ensure all construction equipment is properly tuned and maintained. x Minimizing idling time to 5 minutes or beyond regulatory requirements —saves fuel and reduces emissions.
x Utilize existing power sources (e.g., power poles) or clean fuel generators rather than temporary power generators.
x Develop a traffic plan to minimize community impacts due to traffic flow interference from construction activities. The plan may include advance public notice of routing, use of public transportation, and satellite parking areas with a shuttle service. Schedule operations affecting traffic for off-peak hours. Minimize obstruction of through-traffic lanes. Provide a flag person to guide traffic properly and ensure safety at construction sites. Project sponsors should consider developing a goal for the minimization of community impacts. x Require projects to use Tier 4 Final equipment or better for all engines above 50 horsepower (hp). If construction equipment cannot meet to Tier 4 Final engine certification, the Project representative or contractor must demonstrate through future study with written findings supported by substantial evidence that is approved by SCAG before using other technologies/strategies. Alternative applicable strategies may include, but would not be limited to, construction equipment with Tier 4 Interim or reduction in the number and/or horsepower rating of construction equipment and/or limiting the number of construction equipment operating at the same time. All equipment must be tuned and maintained in compliance with the manufacturer’s recommended maintenance schedule and specifications. All maintenance records for each equipment and their contractor(s) should make available for inspection and

21 “4.0 Mitigation Measures.” Connect SoCal Program Environmental Impact Report Addendum #1, September 2020, available at: https://scag.ca.gov/sites/main/files/file- attachments/fpeir_connectsocal_addendum_4_mitigationmeasures.pdf?1606004420 , p. 4.0-2 – 4.0-10; 4.0-19 –

4.0-23; See also: “Certified Final Connect SoCal Program Environmental Impact Report.” SCAG, May 2020, available at: https://scag.ca.gov/peir.
37 cont

9 remain on-site for a period of at least two years from completion of construction, unless the individual project can demonstrate that Tier 4 engines would not be required to mitigate emissions below significance thresholds. Project sponsors should also consider including ZE/ZNE technologies where appropriate and feasible.

The CalEEMod User’s Guide confirms that the methods for mitigating DPM emissions include the use of “alternative fuel, electric equipment, diesel particulate filters (DPF), oxidation catalysts, newer tier engines, and dust suppression.”
22 The proposed mitigation measures would effectively reduce Project-related DPM emissions by integrating lower-emitting design features into the Project, thereby minimizing emissions during construction. An EIR should be prepared to include all feasible mitigation measures and updated air quality, health risk, and GHG analyses. This will ensure that necessary mitigation measures are implemented to reduce emissions to the greatest extent possible.

Disclaimer
SWAPE has received limited documentation regarding this project. Additional information may become available in the future; thus, we retain the right to revise or amend this report when additional information becomes available. Our professional services have been performed using that degree of care and skill ordinarily exercised, under similar circumstances, by reputable environmental consultants practicing in this or similar localities at the time of service. No other warranty, expressed or implied, is made as to the scope of work, work methodologies and protocols, site conditions, analytical testing results, and findings presented. This report reflects efforts which were limited to information that was reasonably accessible at the time of the work, and may contain informational gaps, inconsistencies, or otherwise be incomplete due to the unavailability or uncertainty of information obtained or provided by third parties.

Sincerely,
Matt Hagemann, P.G., C.Hg.

Paul E. Rosenfeld, Ph.D.
22 “Calculation Details for CalEEMod.” CAPCOA, May 2021, available at: http://www.aqmd.gov/docs/default- source/caleemod/user-guide-2021/appendix-a2020-4-0.pdf?sfvrsn=6, Appendix A, p. 60. 37 cont
38

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DŽĚKƵƚƉƵƚ&ŝůĞƐ
ƚƚĂĐŚŵĞŶƚ͗,ĞĂůƚŚZŝƐŬĂůĐƵůĂƚŝŽŶƐ
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Z^Z

EKƵƚƉƵƚ&ŝůĞƐ
ƚƚĂĐŚŵĞŶƚ
͗DĂƚƚ,ĂŐĞŵĂŶŶs
ƚƚĂĐŚŵĞŶƚ&͗WĂƵůZŽƐĞŶĨĞůĚs

Phase
Default Phase
Length
Construction
Duration %
Construction
Duration
Revised Phase
Length
Demolition 20 381 0.0525 891 47
Site Preparation 3 381 0.0079 891 7
Grading 6 381 0.0157 891 14
Construction 220 381 0.5774 891 514
Paving 10 381 0.0262 891 23
Architectural Coating 10 381 0.0262 891 23
Total Default
Construction
Duration
Revised
Construction
Duration
Start Date 1/1/2026 1/1/2026
End Date 1/17/2027 6/10/2028
Total Days 381 891
Construction Schedule Calculations
ƚƚĂĐŚŵĞŶƚ

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Arcadia Town Center Detailed Report
Table of Contents

1. Basic Project Information

1.1. Basic Project Information

1.2. Land Use Types

1.3. User-Selected Emission Reduction Measures by Emissions Sector

2. Emissions Summary

2.1. Construction Emissions Compared Against Thresholds

2.2. Construction Emissions by Y ear, Unmitigated

2.4. Operations Emissions Compared Against Thresholds

2.5. Operations Emissions by Sector, Unmitigated

3. Construction Emissions Details

3.1. Demolition (2026) - Unmitigated

3.3. Site Preparation (2026) - Unmitigated

3.5. Grading (2026) - Unmitigated

3.7. Building Construction (2026) - Unmitigated

3.9. Building Construction (2027) - Unmitigated
ƚƚĂĐŚŵĞŶƚ

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3.11. Building Construction (2028) - Unmitigated

3.13. Paving (2028) - Unmitigated

3.15. Architectural Coating (2028) - Unmitigated

4. Operations Emissions Details

4.1. Mobile Emissions by Land Use

4.1.1. Unmitigated

4.2. Energy

4.2.1. Electricity Emissions By Land Use - Unmitigated

4.2.3. Natural Gas Emissions By Land Use - Unmitigated

4.3. Area Emissions by Source

4.3.1. Unmitigated

4.4. Water Emissions by Land Use

4.4.1. Unmitigated

4.5. Waste Emissions by Land Use

4.5.1. Unmitigated

4.6. Refrigerant Emissions by Land Use

4.6.1. Unmitigated

4.7. Offroad Emissions By Equipment Type

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4.7.1. Unmitigated

4.8. Stationary Emissions By Equipment Type

4.8.1. Unmitigated

4.9. User Defined Emissions By Equipment Type

4.9.1. Unmitigated

4.10. Soil Carbon Accumulation By Vegetation Type

4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated

4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated

4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated

5. Activity Data

5.1. Construction Schedule

5.2. Off-Road Equipment

5.2.1. Unmitigated

5.3. Construction Vehicles

5.3.1. Unmitigated

5.4. Vehicles

5.4.1. Construction Vehicle Control Strategies

5.5. Architectural Coatings

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5.6. Dust Mitigation

5.6.1. Construction Earthmoving Activities

5.6.2. Construction Earthmoving Control Strategies

5.7. Construction Paving

5.8. Construction Electricity Consumption and Emissions Factors

5.9. Operational Mobile Sources

5.9.1. Unmitigated

5.10. Operational Area Sources

5.10.1. Hearths

5.10.1.1. Unmitigated

5.10.2. Architectural Coatings

5.10.3. Landscape Equipment

5.11. Operational Energy Consumption

5.11.1. Unmitigated

5.12. Operational Water and Wastewater Consumption

5.12.1. Unmitigated

5.13. Operational Waste Generation

5.13.1. Unmitigated Page 76
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5.14. Operational Refrigeration and Air Conditioning Equipment

5.14.1. Unmitigated

5.15. Operational Off-Road Equipment

5.15.1. Unmitigated

5.16. Stationary Sources

5.16.1. Emergency Generators and Fire Pumps

5.16.2. Process Boilers

5.17. User Defined

5.18. Vegetation

5.18.1. Land Use Change

5.18.1.1. Unmitigated

5.18.1. Biomass Cover Type

5.18.1.1. Unmitigated

5.18.2. Sequestration

5.18.2.1. Unmitigated

6. Climate Risk Detailed Report

6.1. Climate Risk Summary

6.2. Initial Climate Risk Scores

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6.3. Adjusted Climate Risk Scores

6.4. Climate Risk Reduction Measures

7. Health and Equity Details

7.1. CalEnviroScreen 4.0 Scores

7.2. Healthy Places Index Scores

7.3. Overall Health & Equity Scores

7.4. Health & Equity Measures

7.5. Evaluation Scorecard

7.6. Health & Equity Custom Measures

8. User Changes to Default Data

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1. Basic Project Information

1.1. Basic Project Information
Data Field Value
Project Name Arcadia Town Center
Construction Start Date 1/1/2026
Operational Y ear 2028
Lead Agency —
Land Use Scale Project/site
Analysis Level for Defaults County
Windspeed (m/s) 0.50
Precipitation (days) 24.4
Location 34.140403578150526, -118.03194606892856
County Los Angeles-South Coast
City Arcadia
Air District South Coast AQMD
Air Basin South Coast
TAZ 4922
EDFZ 7
Electric Utility Southern California Edison
Gas Utility Southern California Gas
App Version 2022.1.1.29

1.2. Land Use Types
Land Use Subtype Size Unit Lot Acreage Building Area (sq ft) Landscape Area (sq ft)
Special Landscape
Area (sq ft)
Population Description
Apartments Mid
Rise
181 Dwelling Unit 2.27 173,760 2,000 — 536 —

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Enclosed Parking
with Elevator
378 Space 0.00 151,200 0.00 — — —
City Park 1.00 Acre 0.00 0.00 21,825 21,825 — —
User Defined
Recreational

5.00 User Defined Unit 0.00 5,000 1,000 1,000 — —
Strip Mall 4.00 1000sqft 0.09 4,000 800 — — —
General Office
Building

5.00 1000sqft 0.11 5,000 1,000 — — —

1.3. User-Selected Emission Reduction Measures by Emissions Sector No measures selected

2. Emissions Summary

2.1. Construction Emissions Compared Against Thresholds Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Unmit. 3.71 1.95 45.7 27.6 0.21 0.93 14.7 15.6 0.89 5.49 6.38 — 29,843 29,843 1.62 4.38 61.6 31,250 Daily,
Winter
(Max)
——————————————————
Unmit. 3.67 1.95 47.0 27.6 0.21 0.93 14.7 15.6 0.89 5.49 6.38 — 29,847 29,847 1.62 4.38 1.60 31,194 Average
Daily
(Max)
——————————————————
Unmit. 1.62 1.33 10.4 16.5 0.03 0.31 2.16 2.47 0.28 0.59 0.87 — 4,825 4,825 0.22 0.34 4.01 4,936 Annual
(Max)
——————————————————
Unmit. 0.30 0.24 1.89 3.01 0.01 0.06 0.40 0.45 0.05 0.11 0.16 — 799 799 0.04 0.06 0.66 817

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2.2. Construction Emissions by Y ear, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Y ear TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily -
Summer
(Max)
——————————————————
2026 3.71 1.95 45.7 27.6 0.21 0.93 14.7 15.6 0.89 5.49 6.38 — 29,843 29,843 1.62 4.38 61.6 31,250 2027 2.25 1.88 11.9 24.4 0.03 0.33 3.00 3.33 0.31 0.72 1.03 — 6,262 6,262 0.26 0.31 11.9 6,373 2028 0.79 0.66 5.58 9.02 0.01 0.20 0.52 0.54 0.19 0.12 0.23 — 1,440 1,440 0.05 0.02 1.48 1,447 Daily -
Winter
(Max)
——————————————————
2026 3.67 1.95 47.0 27.6 0.21 0.93 14.7 15.6 0.89 5.49 6.38 — 29,847 29,847 1.62 4.38 1.60 31,194 2027 2.24 1.86 12.1 22.6 0.03 0.33 3.00 3.33 0.31 0.72 1.03 — 6,126 6,126 0.18 0.31 0.31 6,223 2028 2.15 1.78 11.5 21.9 0.03 0.30 3.00 3.29 0.27 0.72 0.99 — 6,049 6,049 0.17 0.31 0.28 6,145 Average
Daily
——————————————————
2026 1.62 1.30 10.4 15.9 0.03 0.31 2.16 2.47 0.28 0.59 0.87 — 4,825 4,825 0.22 0.34 4.01 4,936 2027 1.60 1.33 8.68 16.5 0.02 0.24 2.11 2.34 0.22 0.51 0.72 — 4,402 4,402 0.13 0.22 3.68 4,474 2028 0.42 0.35 2.31 4.43 0.01 0.06 0.53 0.59 0.06 0.13 0.18 — 1,130 1,130 0.03 0.05 0.83 1,148 A n n u a l ——————————————————
2026 0.30 0.24 1.89 2.90 0.01 0.06 0.40 0.45 0.05 0.11 0.16 — 799 799 0.04 0.06 0.66 817 2027 0.29 0.24 1.58 3.01 < 0.005 0.04 0.38 0.43 0.04 0.09 0.13 — 729 729 0.02 0.04 0.61 741 2028 0.08 0.06 0.42 0.81 < 0.005 0.01 0.10 0.11 0.01 0.02 0.03 — 187 187 0.01 0.01 0.14 190

2.4. Operations Emissions Compared Against Thresholds
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Un/Mit. TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e

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——————————————————Daily,
Summer
(Max)
Unmit. 62.8 57.1 7.13 142 0.32 13.0 7.62 20.7 12.8 1.94 14.7 1,788 14,202 15,990 14.9 0.43 23.9 16,513 Daily,
Winter
(Max)
——————————————————
Unmit. 60.5 55.0 7.22 122 0.31 13.0 7.62 20.6 12.8 1.94 14.7 1,788 13,807 15,595 14.9 0.44 1.87 16,101 Average
Daily
(Max)
——————————————————
Unmit. 13.0 12.1 3.67 46.8 0.09 0.99 7.03 8.01 0.96 1.79 2.75 208 10,417 10,626 10.1 0.37 10.4 10,999 Annual
(Max)
——————————————————
Unmit. 2.36 2.21 0.67 8.54 0.02 0.18 1.28 1.46 0.18 0.33 0.50 34.5 1,725 1,759 1.68 0.06 1.73 1,821

2.5. Operations Emissions by Sector, Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Sector TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Mobile 4.07 3.69 2.66 31.9 0.08 0.05 7.62 7.67 0.04 1.94 1.98 — 8,161 8,161 0.37 0.31 22.6 8,286 Area 58.7 53.4 3.91 110 0.24 12.9 — 12.9 12.7 — 12.7 1,695 3,296 4,992 5.06 0.06 — 5,137 Energy 0.06 0.03 0.55 0.25 < 0.005 0.04 — 0.04 0.04 — 0.04 — 2,660 2,660 0.18 0.02 — 2,670 W a t e r ———————————1 5 . 2 8 4 . 7 9 9 . 9 1 . 5 6 0 . 0 4 —1 5 0 W a s t e ———————————7 7 . 0 0 . 0 0 7 7 . 0 7 . 6 9 0 . 0 0 —2 6 9 R e f r i g . ————————————————1 . 2 8 1 . 2 8
Total 62.8 57.1 7.13 142 0.32 13.0 7.62 20.7 12.8 1.94 14.7 1,788 14,202 15,990 14.9 0.43 23.9 16,513 Daily,
Winter
(Max)
——————————————————

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Mobile 4.03 3.65 2.91 29.4 0.08 0.05 7.62 7.67 0.04 1.94 1.98 — 7,823 7,823 0.39 0.33 0.59 7,931 Area 56.5 51.3 3.76 92.0 0.23 12.9 — 12.9 12.7 — 12.7 1,695 3,239 4,935 5.05 0.06 — 5,080 Energy 0.06 0.03 0.55 0.25 < 0.005 0.04 — 0.04 0.04 — 0.04 — 2,660 2,660 0.18 0.02 — 2,670 W a t e r ———————————1 5 . 2 8 4 . 7 9 9 . 9 1 . 5 6 0 . 0 4 —1 5 0 W a s t e ———————————7 7 . 0 0 . 0 0 7 7 . 0 7 . 6 9 0 . 0 0 —2 6 9 R e f r i g . ————————————————1 . 2 8 1 . 2 8
Total 60.5 55.0 7.22 122 0.31 13.0 7.62 20.6 12.8 1.94 14.7 1,788 13,807 15,595 14.9 0.44 1.87 16,101 Average
Daily
——————————————————
Mobile 3.75 3.39 2.75 28.2 0.07 0.04 7.03 7.07 0.04 1.79 1.83 — 7,411 7,411 0.36 0.31 9.14 7,522 Area 9.14 8.69 0.37 18.3 0.02 0.90 — 0.90 0.88 — 0.88 116 261 377 0.35 < 0.005 — 387 Energy 0.06 0.03 0.55 0.25 < 0.005 0.04 — 0.04 0.04 — 0.04 — 2,660 2,660 0.18 0.02 — 2,670 W a t e r ———————————1 5 . 2 8 4 . 7 9 9 . 9 1 . 5 6 0 . 0 4 —1 5 0 W a s t e ———————————7 7 . 0 0 . 0 0 7 7 . 0 7 . 6 9 0 . 0 0 —2 6 9 R e f r i g . ————————————————1 . 2 8 1 . 2 8
Total 13.0 12.1 3.67 46.8 0.09 0.99 7.03 8.01 0.96 1.79 2.75 208 10,417 10,626 10.1 0.37 10.4 10,999 A n n u a l ——————————————————
Mobile 0.68 0.62 0.50 5.16 0.01 0.01 1.28 1.29 0.01 0.33 0.33 — 1,227 1,227 0.06 0.05 1.51 1,245 Area 1.67 1.59 0.07 3.33 < 0.005 0.16 — 0.16 0.16 — 0.16 19.2 43.2 62.4 0.06 < 0.005 — 64.1 Energy 0.01 0.01 0.10 0.05 < 0.005 0.01 — 0.01 0.01 — 0.01 — 440 440 0.03 < 0.005 — 442 W a t e r ———————————2 . 5 2 1 4 . 0 1 6 . 5 0 . 2 6 0 . 0 1 —2 4 . 9 W a s t e ———————————1 2 . 7 0 . 0 0 1 2 . 7 1 . 2 7 0 . 0 0 —4 4 . 6 R e f r i g . ————————————————0 . 2 1 0 . 2 1
Total 2.36 2.21 0.67 8.54 0.02 0.18 1.28 1.46 0.18 0.33 0.50 34.5 1,725 1,759 1.68 0.06 1.73 1,821

3. Construction Emissions Details

3.1. Demolition (2026) - Unmitigated

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Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————
Daily,
Winter
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.66 1.39 12.9 14.6 0.02 0.51 — 0.51 0.47 — 0.47 — 2,494 2,494 0.10 0.02 — 2,503 Demoliti
on
——————0 . 0 0 0 . 0 0 —0 . 0 0 0 . 0 0 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.21 0.18 1.67 1.88 < 0.005 0.07 — 0.07 0.06 — 0.06 — 321 321 0.01 < 0.005 — 322 Demoliti
on
——————0 . 0 0 0 . 0 0 —0 . 0 0 0 . 0 0 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent

0.04 0.03 0.30 0.34 < 0.005 0.01 — 0.01 0.01 — 0.01 — 53.2 53.2 < 0.005 < 0.005 — 53.4 Demoliti
on
——————0 . 0 0 0 . 0 0 —0 . 0 0 0 . 0 0 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

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Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Daily,
Winter
(Max)
——————————————————
Worker 0.05 0.05 0.05 0.69 0.00 0.00 0.16 0.16 0.00 0.04 0.04 — 161 161 0.01 0.01 0.01 163 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Worker 0.01 0.01 0.01 0.09 0.00 0.00 0.02 0.02 0.00 < 0.005 < 0.005 — 21.0 21.0 < 0.005 < 0.005 0.03 21.3 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 3.47 3.47 < 0.005 < 0.005 0.01 3.52 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.3. Site Preparation (2026) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————
Daily,
Winter
(Max)
——————————————————

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2,725—0.020.112,7162,716—0.39—0.390.42—0.420.0310.89.841.131.34Off-Roa d
Equipm
Dust
From
Material
Movement
——————1 . 5 9 1 . 5 9 —0 . 1 7 0 . 1 7 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.03 0.02 0.19 0.21 < 0.005 0.01 — 0.01 0.01 — 0.01 — 52.1 52.1 < 0.005 < 0.005 — 52.3 Dust
From
Material
Movement
——————0 . 0 3 0 . 0 3 —< 0 . 0 0 5 < 0 . 0 0 5 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent
< 0.005 < 0.005 0.03 0.04 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 8.62 8.62 < 0.005 < 0.005 — 8.65 Dust
From
Material
Movement
——————0 . 0 1 0 . 0 1 —< 0 . 0 0 5 < 0 . 0 0 5 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————

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——————————————————Daily,
Winter
(Max)
Worker 0.03 0.03 0.03 0.41 0.00 0.00 0.10 0.10 0.00 0.02 0.02 — 96.3 96.3 < 0.005 < 0.005 0.01 97.5 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 1.87 1.87 < 0.005 < 0.005 < 0.005 1.90 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker < 0.005 < 0.005 < 0.005 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 0.31 0.31 < 0.005 < 0.005 < 0.005 0.31 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.5. Grading (2026) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.70 1.42 12.9 14.0 0.02 0.58 — 0.58 0.53 — 0.53 — 2,455 2,455 0.10 0.02 — 2,463 Dust
From
Material
Movement
——————7 . 1 0 7 . 1 0 —3 . 4 3 3 . 4 3 ———————

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0.000.000.000.000.000.00—0.000.000.000.000.000.000.000.000.000.000.00Onsite truck
Daily,
Winter
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.70 1.42 12.9 14.0 0.02 0.58 — 0.58 0.53 — 0.53 — 2,455 2,455 0.10 0.02 — 2,463 Dust
From
Material
Movement
——————7 . 1 0 7 . 1 0 —3 . 4 3 3 . 4 3 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.07 0.05 0.49 0.54 < 0.005 0.02 — 0.02 0.02 — 0.02 — 94.2 94.2 < 0.005 < 0.005 — 94.5 Dust
From
Material
Movement
——————0 . 2 7 0 . 2 7 —0 . 1 3 0 . 1 3 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent

0.01 0.01 0.09 0.10 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 15.6 15.6 < 0.005 < 0.005 — 15.6 Dust
From
Material
Movement
——————0 . 0 5 0 . 0 5 —0 . 0 2 0 . 0 2 ———————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

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Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Worker 0.04 0.04 0.04 0.65 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 135 135 0.01 < 0.005 0.46 137 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 1.97 0.43 32.8 12.9 0.19 0.35 7.43 7.78 0.35 2.03 2.39 — 27,252 27,252 1.51 4.35 61.1 28,649 Daily,
Winter
(Max)
——————————————————
Worker 0.04 0.04 0.04 0.55 0.00 0.00 0.13 0.13 0.00 0.03 0.03 — 128 128 0.01 < 0.005 0.01 130 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 1.93 0.41 34.1 13.0 0.19 0.35 7.43 7.78 0.35 2.03 2.39 — 27,264 27,264 1.51 4.35 1.59 28,601 Average
Daily
——————————————————
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 5.00 5.00 < 0.005 < 0.005 0.01 5.07 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.07 0.02 1.32 0.50 0.01 0.01 0.28 0.30 0.01 0.08 0.09 — 1,045 1,045 0.06 0.17 1.01 1,098 A n n u a l ——————————————————
Worker < 0.005 < 0.005 < 0.005 < 0.005 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 0.83 0.83 < 0.005 < 0.005 < 0.005 0.84 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.01 < 0.005 0.24 0.09 < 0.005 < 0.005 0.05 0.05 < 0.005 0.01 0.02 — 173 173 0.01 0.03 0.17 182

3.7. Building Construction (2026) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————

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2,208—0.020.092,2012,201—0.33—0.330.36—0.360.0211.810.11.181.41Off-Roa d
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.41 1.18 10.1 11.8 0.02 0.36 — 0.36 0.33 — 0.33 — 2,201 2,201 0.09 0.02 — 2,208 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.74 0.62 5.32 6.19 0.01 0.19 — 0.19 0.17 — 0.17 — 1,159 1,159 0.05 0.01 — 1,163 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent

0.14 0.11 0.97 1.13 < 0.005 0.03 — 0.03 0.03 — 0.03 — 192 192 0.01 < 0.005 — 192 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Worker 0.83 0.73 0.77 12.8 0.00 0.00 2.60 2.60 0.00 0.61 0.61 — 2,694 2,694 0.11 0.09 9.11 2,734 Vendor 0.10 0.04 1.60 0.77 0.01 0.02 0.40 0.42 0.01 0.11 0.12 — 1,447 1,447 0.06 0.21 3.91 1,514 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

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Daily,
Winter
(Max)
——————————————————
Worker 0.83 0.73 0.87 11.0 0.00 0.00 2.60 2.60 0.00 0.61 0.61 — 2,553 2,553 0.12 0.09 0.24 2,585 Vendor 0.10 0.04 1.67 0.79 0.01 0.02 0.40 0.42 0.01 0.11 0.12 — 1,448 1,448 0.06 0.21 0.10 1,511 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Worker 0.43 0.38 0.50 6.04 0.00 0.00 1.35 1.35 0.00 0.32 0.32 — 1,364 1,364 0.06 0.05 2.08 1,382 Vendor 0.05 0.02 0.88 0.41 0.01 0.01 0.21 0.22 0.01 0.06 0.06 — 762 762 0.03 0.11 0.89 796 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker 0.08 0.07 0.09 1.10 0.00 0.00 0.25 0.25 0.00 0.06 0.06 — 226 226 0.01 0.01 0.34 229 Vendor 0.01 < 0.005 0.16 0.08 < 0.005 < 0.005 0.04 0.04 < 0.005 0.01 0.01 — 126 126 0.01 0.02 0.15 132 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.9. Building Construction (2027) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.35 1.13 9.70 11.7 0.02 0.32 — 0.32 0.30 — 0.30 — 2,201 2,201 0.09 0.02 — 2,208 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————

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Off-Roa
Equipment

1.35 1.13 9.70 11.7 0.02 0.32 — 0.32 0.30 — 0.30 — 2,201 2,201 0.09 0.02 — 2,208 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.97 0.81 6.93 8.36 0.02 0.23 — 0.23 0.21 — 0.21 — 1,572 1,572 0.06 0.01 — 1,577 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent

0.18 0.15 1.26 1.53 < 0.005 0.04 — 0.04 0.04 — 0.04 — 260 260 0.01 < 0.005 — 261 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Worker 0.80 0.71 0.69 11.9 0.00 0.00 2.60 2.60 0.00 0.61 0.61 — 2,642 2,642 0.11 0.09 8.23 2,681 Vendor 0.09 0.04 1.53 0.73 0.01 0.01 0.40 0.41 0.01 0.11 0.12 — 1,419 1,419 0.06 0.20 3.70 1,483 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Worker 0.79 0.69 0.86 10.1 0.00 0.00 2.60 2.60 0.00 0.61 0.61 — 2,505 2,505 0.04 0.09 0.21 2,534 Vendor 0.09 0.04 1.59 0.74 0.01 0.01 0.40 0.41 0.01 0.11 0.12 — 1,420 1,420 0.06 0.20 0.10 1,480 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————

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Worker 0.57 0.49 0.61 7.59 0.00 0.00 1.83 1.83 0.00 0.43 0.43 — 1,815 1,815 0.03 0.07 2.53 1,839 Vendor 0.07 0.03 1.14 0.53 0.01 0.01 0.28 0.29 0.01 0.08 0.08 — 1,014 1,014 0.04 0.14 1.14 1,058 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker 0.10 0.09 0.11 1.39 0.00 0.00 0.33 0.33 0.00 0.08 0.08 — 301 301 < 0.005 0.01 0.42 304 Vendor 0.01 0.01 0.21 0.10 < 0.005 < 0.005 0.05 0.05 < 0.005 0.01 0.02 — 168 168 0.01 0.02 0.19 175 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.11. Building Construction (2028) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————
Daily,
Winter
(Max)
——————————————————
Off-Roa
d
Equipm
ent

1.29 1.08 9.23 11.7 0.02 0.28 — 0.28 0.26 — 0.26 — 2,201 2,201 0.09 0.02 — 2,209 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.21 0.18 1.52 1.92 < 0.005 0.05 — 0.05 0.04 — 0.04 — 362 362 0.01 < 0.005 — 363 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————

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Off-Roa
Equipment

0.04 0.03 0.28 0.35 < 0.005 0.01 — 0.01 0.01 — 0.01 — 59.9 59.9 < 0.005 < 0.005 — 60.1 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Daily,
Winter
(Max)
——————————————————
Worker 0.77 0.67 0.77 9.53 0.00 0.00 2.60 2.60 0.00 0.61 0.61 — 2,460 2,460 0.03 0.09 0.19 2,489 Vendor 0.09 0.03 1.52 0.71 0.01 0.01 0.40 0.41 0.01 0.11 0.12 — 1,387 1,387 0.05 0.20 0.09 1,447 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Worker 0.13 0.11 0.13 1.64 0.00 0.00 0.42 0.42 0.00 0.10 0.10 — 410 410 0.01 0.02 0.53 416 Vendor 0.02 0.01 0.25 0.12 < 0.005 < 0.005 0.06 0.07 < 0.005 0.02 0.02 — 228 228 0.01 0.03 0.25 238 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker 0.02 0.02 0.02 0.30 0.00 0.00 0.08 0.08 0.00 0.02 0.02 — 67.9 67.9 < 0.005 < 0.005 0.09 68.8 Vendor < 0.005 < 0.005 0.05 0.02 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 — 37.7 37.7 < 0.005 0.01 0.04 39.4 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.13. Paving (2028) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————

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Off-Roa
Equipment

0.73 0.61 5.53 8.18 0.01 0.20 — 0.20 0.19 — 0.19 — 1,244 1,244 0.05 0.01 — 1,248 P a v i n g 0 . 0 0 0 . 0 0 ————————————————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Off-Roa
d
Equipm
ent

0.73 0.61 5.53 8.18 0.01 0.20 — 0.20 0.19 — 0.19 — 1,244 1,244 0.05 0.01 — 1,248 P a v i n g 0 . 0 0 0 . 0 0 ————————————————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.05 0.04 0.35 0.52 < 0.005 0.01 — 0.01 0.01 — 0.01 — 78.4 78.4 < 0.005 < 0.005 — 78.6 P a v i n g 0 . 0 0 0 . 0 0 ————————————————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent

0.01 0.01 0.06 0.09 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 13.0 13.0 < 0.005 < 0.005 — 13.0 P a v i n g 0 . 0 0 0 . 0 0 ————————————————
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————

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——————————————————Daily,
Summer
(Max)
Worker 0.06 0.05 0.05 0.85 0.00 0.00 0.20 0.20 0.00 0.05 0.05 — 196 196 < 0.005 0.01 0.56 198 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Worker 0.06 0.05 0.06 0.72 0.00 0.00 0.20 0.20 0.00 0.05 0.05 — 186 186 < 0.005 0.01 0.01 188 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Average
Daily
——————————————————
Worker < 0.005 < 0.005 < 0.005 0.05 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 11.9 11.9 < 0.005 < 0.005 0.02 12.0 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker < 0.005 < 0.005 < 0.005 0.01 0.00 0.00 < 0.005 < 0.005 0.00 < 0.005 < 0.005 — 1.97 1.97 < 0.005 < 0.005 < 0.005 1.99 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

3.15. Architectural Coating (2028) - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Location TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e O n s i t e ——————————————————
Daily,
Summer
(Max)
——————————————————

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134—<0 . 0 0 50.01134134—0.01—0.010.02—0.02<0 . 0 0 51.120.810.110.13Off-Roa d
Equipm
Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Average
Daily
——————————————————
Off-Roa
d
Equipm
ent

0.01 0.01 0.05 0.07 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 8.41 8.41 < 0.005 < 0.005 — 8.44 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Off-Roa
d
Equipm
ent
< 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 1.39 1.39 < 0.005 < 0.005 — 1.40 Onsite
truck

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Offsite ——————————————————
Daily,
Summer
(Max)
——————————————————
Worker 0.15 0.14 0.14 2.24 0.00 0.00 0.52 0.52 0.00 0.12 0.12 — 519 519 0.01 0.02 1.48 526 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Daily,
Winter
(Max)
——————————————————
Average
Daily
——————————————————

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Worker 0.01 0.01 0.01 0.13 0.00 0.00 0.03 0.03 0.00 0.01 0.01 — 31.5 31.5 < 0.005 < 0.005 0.04 31.9 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 A n n u a l ——————————————————
Worker < 0.005 < 0.005 < 0.005 0.02 0.00 0.00 0.01 0.01 0.00 < 0.005 < 0.005 — 5.21 5.21 < 0.005 < 0.005 0.01 5.28 Vendor 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Hauling 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

4. Operations Emissions Details

4.1. Mobile Emissions by Land Use

4.1.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise

3.30 2.99 2.15 25.8 0.06 0.04 6.14 6.18 0.04 1.56 1.60 — 6,574 6,574 0.30 0.25 18.2 6,675 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 City
Park

0.01 0.01 < 0.005 0.06 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 — 15.2 15.2 < 0.005 < 0.005 0.04 15.5 User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

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1,2523.420.050.061,2331,233—0.300.290.011.161.150.010.014.800.400.540.60Strip Mall
General
Office
Building

0.16 0.15 0.11 1.32 < 0.005 < 0.005 0.32 0.32 < 0.005 0.08 0.08 — 339 339 0.02 0.01 0.94 344 Total 4.07 3.69 2.66 31.9 0.08 0.05 7.62 7.67 0.04 1.94 1.98 — 8,161 8,161 0.37 0.31 22.6 8,286 Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise

3.27 2.96 2.35 23.7 0.06 0.04 6.14 6.18 0.04 1.56 1.60 — 6,302 6,302 0.31 0.27 0.47 6,389 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00City Park

0.01 0.01 0.01 0.05 < 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 < 0.005 — 14.6 14.6 < 0.005 < 0.005 < 0.005 14.8 User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Strip
Mall

0.59 0.54 0.44 4.41 0.01 0.01 1.15 1.16 0.01 0.29 0.30 — 1,182 1,182 0.06 0.05 0.09 1,198 General
Office
Building

0.16 0.15 0.12 1.21 < 0.005 < 0.005 0.32 0.32 < 0.005 0.08 0.08 — 325 325 0.02 0.01 0.02 329 Total 4.03 3.65 2.91 29.4 0.08 0.05 7.62 7.67 0.04 1.94 1.98 — 7,823 7,823 0.39 0.33 0.59 7,931 A n n u a l ——————————————————
Apartme
nts
Mid Rise

0.56 0.51 0.41 4.22 0.01 0.01 1.05 1.06 0.01 0.27 0.27 — 1,003 1,003 0.05 0.04 1.24 1,018 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00

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City
Park
< 0.005 < 0.005 < 0.005 0.01 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — 1.28 1.28 < 0.005 < 0.005 < 0.005 1.30 User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 0.00 0.00 0.00 0.00 Strip
Mall

0.10 0.09 0.07 0.76 < 0.005 < 0.005 0.19 0.19 < 0.005 0.05 0.05 — 181 181 0.01 0.01 0.22 184 General
Office
Building

0.02 0.02 0.02 0.17 < 0.005 < 0.005 0.04 0.04 < 0.005 0.01 0.01 — 41.2 41.2 < 0.005 < 0.005 0.05 41.8 Total 0.68 0.62 0.50 5.16 0.01 0.01 1.28 1.29 0.01 0.33 0.33 — 1,227 1,227 0.06 0.05 1.51 1,245

4.2. Energy

4.2.1. Electricity Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise
————————————9 6 7 9 6 7 0 . 0 6 0 . 0 1 —9 7 1
Enclose
d
Parking
with
Elevator
————————————8 1 3 8 1 3 0 . 0 5 0 . 0 1 —8 1 7City
Park
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0
User
Defined
Recreational
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0

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57.5—<0 . 0 0 5< 0.00557.357.3————————————Strip
Mall
General
Office
Building
————————————1 3 0 1 3 0 0 . 0 1 < 0 . 0 0 5 —1 3 0
T o t a l ————————————1 , 9 6 8 1 , 9 6 8 0 . 1 2 0 . 0 1 —1 , 9 7 5 Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise
————————————9 6 7 9 6 7 0 . 0 6 0 . 0 1 —9 7 1
Enclose
d
Parking
with
Elevator
————————————8 1 3 8 1 3 0 . 0 5 0 . 0 1 —8 1 7City
Park
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0
User
Defined
Recreational
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0
Strip
Mall
————————————5 7 . 3 5 7 . 3 < 0 . 0 0 5 < 0 . 0 0 5 —5 7 . 5 General
Office
Building
————————————1 3 0 1 3 0 0 . 0 1 < 0 . 0 0 5 —1 3 0
T o t a l ————————————1 , 9 6 8 1 , 9 6 8 0 . 1 2 0 . 0 1 —1 , 9 7 5 A n n u a l ——————————————————
Apartme
nts
Mid Rise
————————————1 6 0 1 6 0 0 . 0 1 < 0 . 0 0 5 —1 6 1
Enclose
d
Parking
with
Elevator
————————————1 3 5 1 3 5 0 . 0 1 < 0 . 0 0 5 —1 3 5

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City
Park
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0
User
Defined
Recreational
————————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0
Strip
Mall
————————————9 . 4 8 9 . 4 8 < 0 . 0 0 5 < 0 . 0 0 5 —9 . 5 2 General
Office
Building
————————————2 1 . 5 2 1 . 5 < 0 . 0 0 5 < 0 . 0 0 5 —2 1 . 6 T o t a l ————————————3 2 6 3 2 6 0 . 0 2 < 0 . 0 0 5 —3 2 7

4.2.3. Natural Gas Emissions By Land Use - Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise

0.06 0.03 0.51 0.22 < 0.005 0.04 — 0.04 0.04 — 0.04 — 644 644 0.06 < 0.005 — 646 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 City
Park

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Strip
Mall
< 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 7.67 7.67 < 0.005 < 0.005 — 7.70

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40.7—<0 . 0 0 5< 0.00540.640.6—<0 . 0 0 5—< 0.005< 0.005—<0 . 0 0 5<0 . 0 0 50.030.03< 0.005<0 . 0 0 5General Office
Building
Total 0.06 0.03 0.55 0.25 < 0.005 0.04 — 0.04 0.04 — 0.04 — 693 693 0.06 < 0.005 — 694 Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise

0.06 0.03 0.51 0.22 < 0.005 0.04 — 0.04 0.04 — 0.04 — 644 644 0.06 < 0.005 — 646 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 City
Park

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Strip
Mall
< 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 7.67 7.67 < 0.005 < 0.005 — 7.70 General
Office
Building
< 0.005 < 0.005 0.03 0.03 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 40.6 40.6 < 0.005 < 0.005 — 40.7 Total 0.06 0.03 0.55 0.25 < 0.005 0.04 — 0.04 0.04 — 0.04 — 693 693 0.06 < 0.005 — 694 A n n u a l ——————————————————
Apartme
nts
Mid Rise

0.01 0.01 0.09 0.04 < 0.005 0.01 — 0.01 0.01 — 0.01 — 107 107 0.01 < 0.005 — 107 Enclose
d
Parking
with
Elevator

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 City
Park

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00

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User
Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 — 0.00 0.00 — 0.00 — 0.00 0.00 0.00 0.00 — 0.00 Strip
Mall
< 0.005 < 0.005 < 0.005 < 0.005 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 1.27 1.27 < 0.005 < 0.005 — 1.27 General
Office
Building
< 0.005 < 0.005 0.01 0.01 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 6.72 6.72 < 0.005 < 0.005 — 6.74 Total 0.01 0.01 0.10 0.05 < 0.005 0.01 — 0.01 0.01 — 0.01 — 115 115 0.01 < 0.005 — 115

4.3. Area Emissions by Source

4.3.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Source TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Hearths 52.4 47.3 3.76 92.0 0.23 12.9 — 12.9 12.7 — 12.7 1,695 3,239 4,935 5.05 0.06 — 5,080 Consum
er
Product
s
4 . 0 3 4 . 0 3 ————————————————
Landsca
pe
Equipm
ent

2.22 2.08 0.16 17.5 < 0.005 0.02 — 0.02 0.01 — 0.01 — 57.0 57.0 < 0.005 < 0.005 — 57.2 Total 58.7 53.4 3.91 110 0.24 12.9 — 12.9 12.7 — 12.7 1,695 3,296 4,992 5.06 0.06 — 5,137 Daily,
Winter
(Max)
——————————————————
Hearths 52.4 47.3 3.76 92.0 0.23 12.9 — 12.9 12.7 — 12.7 1,695 3,239 4,935 5.05 0.06 — 5,080

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————————————————4.034.03Consum
er
Product
s
Total 56.5 51.3 3.76 92.0 0.23 12.9 — 12.9 12.7 — 12.7 1,695 3,239 4,935 5.05 0.06 — 5,080 A n n u a l ——————————————————
Hearths 0.66 0.59 0.05 1.15 < 0.005 0.16 — 0.16 0.16 — 0.16 19.2 36.7 56.0 0.06 < 0.005 — 57.6 Consum
er
Product
s
0 . 7 4 0 . 7 4 ————————————————
Landsca
pe
Equipm
ent

0.28 0.26 0.02 2.18 < 0.005 < 0.005 — < 0.005 < 0.005 — < 0.005 — 6.46 6.46 < 0.005 < 0.005 — 6.49 Total 1.67 1.59 0.07 3.33 < 0.005 0.16 — 0.16 0.16 — 0.16 19.2 43.2 62.4 0.06 < 0.005 — 64.1

4.4. Water Emissions by Land Use

4.4.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise
———————————1 2 . 9 6 7 . 2 8 0 . 1 1 . 3 3 0 . 0 3 —1 2 3 Enclose
d
Parking
with
Elevator
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0

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5.28—<0 . 0 0 5< 0.0055.265.260.00———————————City
Park
User
Defined
Recreational
———————————0 . 0 0 0 . 2 4 0 . 2 4 < 0 . 0 0 5 < 0 . 0 0 5 —0 . 2 4 Strip
Mall
———————————0 . 5 7 3 . 0 3 3 . 5 9 0 . 0 6 < 0 . 0 0 5 —5 . 4 7 General
Office
Building
———————————1 . 7 0 8 . 9 3 1 0 . 6 0 . 1 8 < 0 . 0 0 5 —1 6 . 3 T o t a l ———————————1 5 . 2 8 4 . 7 9 9 . 9 1 . 5 6 0 . 0 4 —1 5 0 Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise
———————————1 2 . 9 6 7 . 2 8 0 . 1 1 . 3 3 0 . 0 3 —1 2 3 Enclose
d
Parking
with
Elevator
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0City Park
———————————0 . 0 0 5 . 2 6 5 . 2 6 < 0 . 0 0 5 < 0 . 0 0 5 —5 . 2 8 User
Defined
Recreational
———————————0 . 0 0 0 . 2 4 0 . 2 4 < 0 . 0 0 5 < 0 . 0 0 5 —0 . 2 4 Strip
Mall
———————————0 . 5 7 3 . 0 3 3 . 5 9 0 . 0 6 < 0 . 0 0 5 —5 . 4 7 General
Office
Building
———————————1 . 7 0 8 . 9 3 1 0 . 6 0 . 1 8 < 0 . 0 0 5 —1 6 . 3 T o t a l ———————————1 5 . 2 8 4 . 7 9 9 . 9 1 . 5 6 0 . 0 4 —1 5 0 A n n u a l ——————————————————
Apartme
nts
Mid Rise
———————————2 . 1 4 1 1 . 1 1 3 . 3 0 . 2 2 0 . 0 1 —2 0 . 3

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Enclose
Parking
with
Elevator
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 City
Park
———————————0 . 0 0 0 . 8 7 0 . 8 7 < 0 . 0 0 5 < 0 . 0 0 5 —0 . 8 7 User
Defined
Recreational
———————————0 . 0 0 0 . 0 4 0 . 0 4 < 0 . 0 0 5 < 0 . 0 0 5 —0 . 0 4 Strip
Mall
———————————0 . 0 9 0 . 5 0 0 . 6 0 0 . 0 1 < 0 . 0 0 5 —0 . 9 1 General
Office
Building
———————————0 . 2 8 1 . 4 8 1 . 7 6 0 . 0 3 < 0 . 0 0 5 —2 . 6 9 T o t a l ———————————2 . 5 2 1 4 . 0 1 6 . 5 0 . 2 6 0 . 0 1 —2 4 . 9

4.5. Waste Emissions by Land Use

4.5.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise
———————————7 2 . 2 0 . 0 0 7 2 . 2 7 . 2 1 0 . 0 0 —2 5 2 Enclose
d
Parking
with
Elevator
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 City
Park
———————————0 . 0 5 0 . 0 0 0 . 0 5 < 0 . 0 0 5 0 . 0 0 —0 . 1 6

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User
Defined
Recreational
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 Strip
Mall
———————————2 . 2 6 0 . 0 0 2 . 2 6 0 . 2 3 0 . 0 0 —7 . 9 2 General
Office
Building
———————————2 . 5 1 0 . 0 0 2 . 5 1 0 . 2 5 0 . 0 0 —8 . 7 7 T o t a l ———————————7 7 . 0 0 . 0 0 7 7 . 0 7 . 6 9 0 . 0 0 —2 6 9 Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise
———————————7 2 . 2 0 . 0 0 7 2 . 2 7 . 2 1 0 . 0 0 —2 5 2 Enclose
d
Parking
with
Elevator
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 City
Park
———————————0 . 0 5 0 . 0 0 0 . 0 5 < 0 . 0 0 5 0 . 0 0 —0 . 1 6 User
Defined
Recreational
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 Strip
Mall
———————————2 . 2 6 0 . 0 0 2 . 2 6 0 . 2 3 0 . 0 0 —7 . 9 2 General
Office
Building
———————————2 . 5 1 0 . 0 0 2 . 5 1 0 . 2 5 0 . 0 0 —8 . 7 7 T o t a l ———————————7 7 . 0 0 . 0 0 7 7 . 0 7 . 6 9 0 . 0 0 —2 6 9 A n n u a l ——————————————————
Apartme
nts
Mid Rise
———————————1 1 . 9 0 . 0 0 1 1 . 9 1 . 1 9 0 . 0 0 —4 1 . 8

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0.00—0.000.000.000.000.00———————————Enclose
d
Parking
with
Elevator
City
Park
———————————0 . 0 1 0 . 0 0 0 . 0 1 < 0 . 0 0 5 0 . 0 0 —0 . 0 3 User
Defined
Recreational
———————————0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 0 . 0 0 —0 . 0 0 Strip
Mall
———————————0 . 3 7 0 . 0 0 0 . 3 7 0 . 0 4 0 . 0 0 —1 . 3 1 General
Office
Building
———————————0 . 4 1 0 . 0 0 0 . 4 1 0 . 0 4 0 . 0 0 —1 . 4 5 T o t a l ———————————1 2 . 7 0 . 0 0 1 2 . 7 1 . 2 7 0 . 0 0 —4 4 . 6

4.6. Refrigerant Emissions by Land Use

4.6.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Apartme
nts
Mid Rise
————————————————1 . 2 4 1 . 2 4
City
Park
————————————————0 . 0 0 0 . 0 0
Strip
Mall
————————————————0 . 0 2 0 . 0 2

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0.010.01————————————————General
Office
Building
T o t a l ————————————————1 . 2 8 1 . 2 8
Daily,
Winter
(Max)
——————————————————
Apartme
nts
Mid Rise
————————————————1 . 2 4 1 . 2 4
City
Park
————————————————0 . 0 0 0 . 0 0
Strip
Mall
————————————————0 . 0 2 0 . 0 2
General
Office
Building
————————————————0 . 0 1 0 . 0 1
T o t a l ————————————————1 . 2 8 1 . 2 8
A n n u a l ——————————————————
Apartme
nts
Mid Rise
————————————————0 . 2 1 0 . 2 1
City
Park
————————————————0 . 0 0 0 . 0 0
Strip
Mall
————————————————< 0 . 0 0 5 < 0 . 0 0 5
General
Office
Building
————————————————< 0 . 0 0 5 < 0 . 0 0 5
T o t a l ————————————————0 . 2 1 0 . 2 1

4.7. Offroad Emissions By Equipment Type

4.7.1. Unmitigated

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Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipm
ent
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
T o t a l ——————————————————
Daily,
Winter
(Max)
——————————————————
T o t a l ——————————————————
A n n u a l ——————————————————
T o t a l ——————————————————

4.8. Stationary Emissions By Equipment Type

4.8.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipm
ent
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
T o t a l ——————————————————
Daily,
Winter
(Max)
——————————————————
T o t a l ——————————————————
A n n u a l ——————————————————
T o t a l ——————————————————

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4.9. User Defined Emissions By Equipment Type

4.9.1. Unmitigated
Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Equipm
ent
Type
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
T o t a l ——————————————————
Daily,
Winter
(Max)
——————————————————
T o t a l ——————————————————
A n n u a l ——————————————————
T o t a l ——————————————————

4.10. Soil Carbon Accumulation By Vegetation Type

4.10.1. Soil Carbon Accumulation By Vegetation Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Vegetati
on
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
T o t a l ——————————————————
Daily,
Winter
(Max)
——————————————————
T o t a l ——————————————————

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A n n u a l ——————————————————
T o t a l ——————————————————

4.10.2. Above and Belowground Carbon Accumulation by Land Use Type - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Land
Use
TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
T o t a l ——————————————————
Daily,
Winter
(Max)
——————————————————
T o t a l ——————————————————
A n n u a l ——————————————————
T o t a l ——————————————————

4.10.3. Avoided and Sequestered Emissions by Species - Unmitigated Criteria Pollutants (lb/day for daily, ton/yr for annual) and GHGs (lb/day for daily, MT/yr for annual) Species TOG ROG NOx CO SO2 PM10E PM10D PM10T PM2.5E PM2.5D PM2.5T BCO2 NBCO2 CO2T CH4 N2O R CO2e Daily,
Summer
(Max)
——————————————————
Avoided ——————————————————
S u b t o t a l ——————————————————
Sequest
ered
——————————————————
S u b t o t a l ——————————————————
Remove
d
——————————————————

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S u b t o t a l ——————————————————
———————————————————
Daily,
Winter
(Max)
——————————————————
Avoided ——————————————————
S u b t o t a l ——————————————————
Sequest
ered
——————————————————
S u b t o t a l ——————————————————
Remove
d
——————————————————
S u b t o t a l ——————————————————
———————————————————
A n n u a l ——————————————————
Avoided ——————————————————
S u b t o t a l ——————————————————
Sequest
ered
——————————————————
S u b t o t a l ——————————————————
Remove
d
——————————————————
S u b t o t a l ——————————————————
———————————————————

5. Activity Data

5.1. Construction Schedule
Phase Name Phase Type Start Date End Date Days Per Week Work Days per Phase Phase Description Demolition Demolition 1/1/2026 3/6/2026 5.00 47.0 —

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Site Preparation Site Preparation 3/7/2026 3/17/2026 5.00 7.00 — Grading Grading 3/18/2026 4/6/2026 5.00 14.0 —
Building Construction Building Construction 4/7/2026 3/24/2028 5.00 514 — Paving Paving 3/27/2028 4/26/2028 5.00 23.0 —
Architectural Coating Architectural Coating 4/27/2028 5/29/2028 5.00 23.0 —

5.2. Off-Road Equipment

5.2.1. Unmitigated
Phase Name Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor Demolition Concrete/Industrial
Saws
Diesel Average 1.00 8.00 33.0 0.73
Demolition Rubber Tired Dozers Diesel Average 1.00 8.00 367 0.40 Demolition Tractors/Loaders/Back
hoes
Diesel Average 3.00 8.00 84.0 0.37
Site Preparation Graders Diesel Average 1.00 8.00 148 0.41 Site Preparation Scrapers Diesel Average 1.00 8.00 423 0.48 Site Preparation Tractors/Loaders/Back
hoes
Diesel Average 1.00 7.00 84.0 0.37
Grading Graders Diesel Average 1.00 8.00 148 0.41
Grading Rubber Tired Dozers Diesel Average 1.00 8.00 367 0.40 Grading Tractors/Loaders/Back
hoes
Diesel Average 2.00 7.00 84.0 0.37
Building Construction Cranes Diesel Average 1.00 8.00 367 0.29 Building Construction Forklifts Diesel Average 2.00 7.00 82.0 0.20 Building Construction Generator Sets Diesel Average 1.00 8.00 14.0 0.74 Building Construction Tractors/Loaders/Back
hoes
Diesel Average 1.00 6.00 84.0 0.37
Building Construction Welders Diesel Average 3.00 8.00 46.0 0.45

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0.5610.08.001.00AverageDieselPaving Cement and Mortar
Mixers
Paving Pavers Diesel Average 1.00 8.00 81.0 0.42
Paving Paving Equipment Diesel Average 1.00 8.00 89.0 0.36 Paving Rollers Diesel Average 2.00 8.00 36.0 0.38
Paving Tractors/Loaders/Back
hoes
Diesel Average 1.00 8.00 84.0 0.37
Architectural Coating Air Compressors Diesel Average 1.00 6.00 37.0 0.48

5.3. Construction Vehicles

5.3.1. Unmitigated
Phase Name Tr ip Type One-Way Trips per Day Miles per Trip Vehicle Mix Demolition ————
Demolition Worker 12.5 18.5 LDA,LDT1,LDT2
Demolition Vendor — 10.2 HHDT,MHDT
Demolition Hauling 0.00 20.0 HHDT
Demolition Onsite truck — — HHDT
S i t e P r e p a r a t i o n ————
Site Preparation Worker 7.50 18.5 LDA,LDT1,LDT2
Site Preparation Vendor — 10.2 HHDT,MHDT
Site Preparation Hauling 0.00 20.0 HHDT
Site Preparation Onsite truck — — HHDT
Grading ————
Grading Worker 10.0 18.5 LDA,LDT1,LDT2
Grading Vendor — 10.2 HHDT,MHDT
Grading Hauling 401 20.0 HHDT
Grading Onsite truck — — HHDT
Building Construction ————

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Building Construction Worker 199 18.5 LDA,LDT1,LDT2
Building Construction Vendor 46.4 10.2 HHDT,MHDT
Building Construction Hauling 0.00 20.0 HHDT
Building Construction Onsite truck — — HHDT
P a v i n g ————
Paving Worker 15.0 18.5 LDA,LDT1,LDT2
Paving Vendor — 10.2 HHDT,MHDT
Paving Hauling 0.00 20.0 HHDT
Paving Onsite truck — — HHDT
A r c h i t e c t u r a l C o a t i n g ————
Architectural Coating Worker 39.8 18.5 LDA,LDT1,LDT2
Architectural Coating Vendor — 10.2 HHDT,MHDT
Architectural Coating Hauling 0.00 20.0 HHDT
Architectural Coating Onsite truck — — HHDT

5.4. Vehicles

5.4.1. Construction Vehicle Control Strategies
Non-applicable. No control strategies activated by user.

5.5. Architectural Coatings
Phase Name Residential Interior Area
Coated (sq ft)
Residential Exterior Area
Coated (sq ft)
Non-Residential Interior Area
Coated (sq ft)
Non-Residential Exterior Area
Coated (sq ft)
Parking Area Coated (sq ft)

5.6. Dust Mitigation

5.6.1. Construction Earthmoving Activities
Phase Name Material Imported (cy) Material Exported (cy) Acres Graded (acres) Material Demolished (Ton of Debris)
Acres Paved (acres)

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Demolition 0.00 0.00 0.00 0.00 —
Site Preparation — — 10.5 0.00 —
Grading — 44,870 6.00 0.00 —
Paving 0.00 0.00 0.00 0.00 0.00

5.6.2. Construction Earthmoving Control Strategies
Non-applicable. No control strategies activated by user.

5.7. Construction Paving
Land Use Area Paved (acres) % Asphalt
Apartments Mid Rise — 0%
Enclosed Parking with Elevator 0.00 100%
City Park 0.00 0%
User Defined Recreational 0.00 0%
Strip Mall 0.00 0%
General Office Building 0.00 0%

5.8. Construction Electricity Consumption and Emissions Factors kWh per Y ear and Emission Factor (lb/MWh)
Y ear kWh per Y ear CO2 CH4 N2O
2026 0.00 532 0.03 < 0.005
2027 0.00 532 0.03 < 0.005
2028 0.00 532 0.03 < 0.005

5.9. Operational Mobile Sources

5.9.1. Unmitigated
Land Use Type Trips/Weekday Trips/Saturday Trips/Sunday Trips/Y ear VMT/Weekday VMT/Saturday VMT/Sunday VMT/Y ear

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Apartments Mid
Rise
985 889 740 341,650 8,659 7,815 6,510 3,004,398
Enclosed Parking
with Elevator

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
City Park 0.78 1.96 2.19 420 7.15 18.0 20.1 3,848
User Defined
Recreational

0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00
Strip Mall 177 168 81.7 59,249 1,625 1,542 749 543,218
General Office
Building

48.7 11.1 3.50 13,455 447 101 32.1 123,365

5.10. Operational Area Sources

5.10.1. Hearths

5.10.1.1. Unmitigated
Hearth Type Unmitigated (number)
Apartments Mid Rise —
Wood Fireplaces 9
Gas Fireplaces 154
Propane Fireplaces 0
Electric Fireplaces 0
No Fireplaces 18
Conventional Wood Stoves 0
Catalytic Wood Stoves 9
Non-Catalytic Wood Stoves 9
Pellet Wood Stoves 0

5.10.2. Architectural Coatings

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Parking Area Coated (sq ft)Residential Interior Area Coated (sq ft)
Residential Exterior Area Coated (sq
ft)
Non-Residential Interior Area Coated
(sq ft)
Non-Residential Exterior Area
Coated (sq ft)
—————

5.10.3. Landscape Equipment
Season Unit Value
Snow Days day/yr 0.00
Summer Days day/yr 250

5.11. Operational Energy Consumption

5.11.1. Unmitigated
Electricity (kWh/yr) and CO2 and CH4 and N2O and Natural Gas (kBTU/yr) Land Use Electricity (kWh/yr) CO2 CH4 N2O Natural Gas (kBTU/yr) Apartments Mid Rise 663,516 532 0.0330 0.0040 2,010,339 Enclosed Parking with
Elevator
558,144 532 0.0330 0.0040 0.00
City Park 0.00 532 0.0330 0.0040 0.00
User Defined Recreational 0.00 532 0.0330 0.0040 0.00
Strip Mall 39,285 532 0.0330 0.0040 23,948
General Office Building 89,101 532 0.0330 0.0040 126,732

5.12. Operational Water and Wastewater Consumption

5.12.1. Unmitigated
Land Use Indoor Water (gal/year) Outdoor Water (gal/year) Apartments Mid Rise 6,746,558 34,282
Enclosed Parking with Elevator 0.00 0.00
City Park 0.00 680,192

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User Defined Recreational 0.00 31,166
Strip Mall 296,290 11,220
General Office Building 888,669 14,025

5.13. Operational Waste Generation

5.13.1. Unmitigated
Land Use Waste (ton/year) Cogeneration (kWh/year)
Apartments Mid Rise 134 —
Enclosed Parking with Elevator 0.00 —
City Park 0.09 —
User Defined Recreational 0.00 —
Strip Mall 4.20 —
General Office Building 4.65 —

5.14. Operational Refrigeration and Air Conditioning Equipment

5.14.1. Unmitigated
Land Use Type Equipment Type Refrigerant GWP Quantity (kg) Operations Leak Rate Service Leak Rate Times Serviced Apartments Mid Rise Average room A/C &
Other residential A/C
and heat pumps
R-410A 2,088 < 0.005 2.50 2.50 10.0
Apartments Mid Rise Household
refrigerators and/or
freezers
R-134a 1,430 0.12 0.60 0.00 1.00
City Park Other commercial A/C
and heat pumps
R-410A 2,088 < 0.005 4.00 4.00 18.0
City Park Stand-alone retail
refrigerators and
freezers
R-134a 1,430 0.04 1.00 0.00 1.00

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18.04.004.00<0 . 0 0 52,088R-410AStrip Mall Other commercial A/C and heat pumps
Strip Mall Stand-alone retail
refrigerators and
freezers
R-134a 1,430 0.04 1.00 0.00 1.00
Strip Mall Walk-in refrigerators
and freezers
R-404A 3,922 < 0.005 7.50 7.50 20.0
General Office
Building
Household
refrigerators and/or
freezers
R-134a 1,430 0.02 0.60 0.00 1.00
General Office
Building
Other commercial A/C
and heat pumps
R-410A 2,088 < 0.005 4.00 4.00 18.0

5.15. Operational Off-Road Equipment

5.15.1. Unmitigated
Equipment Type Fuel Type Engine Tier Number per Day Hours Per Day Horsepower Load Factor

5.16. Stationary Sources

5.16.1. Emergency Generators and Fire Pumps
Equipment Type Fuel Type Number per Day Hours per Day Hours per Y ear Horsepower Load Factor

5.16.2. Process Boilers
Equipment Type Fuel Type Number Boiler Rating (MMBtu/hr) Daily Heat Input (MMBtu/day) Annual Heat Input (MMBtu/yr)

5.17. User Defined
Equipment Type Fuel Type

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5.18. Vegetation

5.18.1. Land Use Change

5.18.1.1. Unmitigated
Vegetation Land Use Type Vegetation Soil Type Initial Acres Final Acres

5.18.1. Biomass Cover Type

5.18.1.1. Unmitigated
Biomass Cover Type Initial Acres Final Acres

5.18.2. Sequestration

5.18.2.1. Unmitigated
Tree Type Number Electricity Saved (kWh/year) Natural Gas Saved (btu/year)

6. Climate Risk Detailed Report

6.1. Climate Risk Summary
Cal-Adapt midcentury 2040–2059 average projections for four hazards are reported below for your project location. These are under Representation Concentration Pathway (RCP) 8.5 which assumes GHG emissions will continue to rise strongly through 2050 and then plateau around 2100.

Climate Hazard Result for Project Location Unit
Temperature and Extreme Heat 25.9 annual days of extreme heat Extreme Precipitation 9.15 annual days with precipitation above 20 mm Sea Level Rise — meters of inundation depth
Wildfire 16.9 annual hectares burned

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Temperature and Extreme Heat data are for grid cell in which your project are located. The projection is based on the 98th historical percentile of daily maximum/minimum temperatures from observed historical data (32 climate model ensemble from Cal-Adapt, 2040–2059 average under RCP 8.5). Each grid cell is 6 kilometers (km) by 6 km, or 3 .7 miles (mi) by 3.7 mi.

Extreme Precipitation data are for the grid cell in which your project are located. The threshold of 20 mm is equivalent to about ¾ an inch of rain, which would be light to moderate rainfall if received over a full day or heavy rain if received over a period of 2 to 4 hours. Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.

Sea Level Rise data are for the grid cell in which your project are located. The projections are from Radke et al. (2017), as reported in Cal-Adapt (Radke et al., 2017, CEC-500-2017-008), and consider inundation location and depth for the San Francisco Bay, the Sacramento-San Joaquin River Delta and California coast resulting different increments of sea level rise coupled with extreme storm events. Users may select from four scenarios to view the range in potential inundation depth for the grid cell. The four scenarios are: Norise, 0.5 meter, 1.0 meter, 1.41 meters Wildfire data are for the grid cell in which your project are located. The projections are from UC Davis, as reported in Cal-Adapt (2040–2059 average under RCP 8.5), and consider historical data of climate, vegetation, population density, and large (> 400 ha) fire history. Users may select from four model simulations to view the range in potential wildfire probabilities for the grid cell. The four simulations make different assumptions about expected rainfall and temperature are: Warmer/drier (HadGEM2-ES), Cooler/wetter (CNRM-CM5),Average conditions (CanESM2), Range of different rainfall and temperature possibilities (MIROC5). Each grid cell is 6 kilometers (km) by 6 km, or 3.7 miles (mi) by 3.7 mi.

6.2. Initial Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 3 0 0 N/A
Extreme Precipitation N/A N/A N/A N/A
S e a L e v e l R i s e 100N / A
Wildfire 1 0 0 N/A
Flooding N/A N/A N/A N/A
Drought N/A N/A N/A N/A
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 0 0 0 N/A
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of1 to 5, with a score of 5 representing the greatest exposure.

The adaptive capacity of a project refers to its ability to manage and reduce vulnerabilities from projected climate hazards. Adaptive capacity is rated on a scale of 1 to 5, with a score of 5 representing the greatest ability to adapt.

The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores do not include implementation of climate risk reduction measures.

6.3. Adjusted Climate Risk Scores
Climate Hazard Exposure Score Sensitivity Score Adaptive Capacity Score Vulnerability Score Temperature and Extreme Heat 3 1 1 3
Extreme Precipitation N/A N/A N/A N/A
S e a L e v e l R i s e 1112

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Wildfire 1112
Flooding N/A N/A N/A N/A
Drought N/A N/A N/A N/A
Snowpack Reduction N/A N/A N/A N/A
Air Quality Degradation 1 1 1 2
The sensitivity score reflects the extent to which a project would be adversely affected by exposure to a climate hazard. Exposure is rated on a scale of1 to 5, with a score of 5 representing the greatest exposure.

The adaptive capacity of a project refers to its ability to manage and reduce vulnerabilities from projected climate hazards. Adaptive capacity is rated on a scale of 1 to 5, with a score of 5 representing the greatest ability to adapt.

The overall vulnerability scores are calculated based on the potential impacts and adaptive capacity assessments for each hazard. Scores include implementation of climate risk reduction measures.

6.4. Climate Risk Reduction Measures

7. Health and Equity Details

7.1. CalEnviroScreen 4.0 Scores
The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state.

Indicator Result for Project Census Tract
Exposure Indicators —
AQ-Ozone 84.6
AQ-PM 70.7
AQ-DPM 57.7
Drinking Water 73.7
Lead Risk Housing 54.4
Pesticides 0.00
Toxic Releases 70.1
Traffic 80.3
Effect Indicators —
CleanUp Sites 74.9
Groundwater 0.00

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Haz Waste Facilities/Generators 59.8
Impaired Water Bodies 0.00
Solid Waste 70.4
Sensitive Population —
Asthma 6.04
Cardio-vascular 7.47
Low Birth Weights 7.29
Socioeconomic Factor Indicators —
Education 42.7
Housing 10.2
Linguistic 80.2
Poverty 27.9
Unemployment 45.8

7.2. Healthy Places Index Scores
The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.

Indicator Result for Project Census Tract
Economic —
Above Poverty 84.3320929
Employed 68.92082638
Median HI 57.88528166
Education —
Bachelor's or higher 80.67496471
High school enrollment 100
Preschool enrollment 84.88387014
Transportation —
Auto Access 70.20402926
Active commuting 5.915565251

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Social —
2-parent households 35.26241499
Voting 21.00603105
Neighborhood —
Alcohol availability 87.47593995
Park access 34.12036443
Retail density 39.49698447
Supermarket access 46.73424868
Tree canopy 66.75221352
Housing —
Homeownership 46.75991274
Housing habitability 43.07712049
Low-inc homeowner severe housing cost burden 33.1707943 Low-inc renter severe housing cost burden 70.48633389
Uncrowded housing 63.4800462
Health Outcomes —
Insured adults 52.11086873
Arthritis 0.0
Asthma ER Admissions 94.2
High Blood Pressure 0.0
Cancer (excluding skin) 0.0
Asthma 0.0
Coronary Heart Disease 0.0
Chronic Obstructive Pulmonary Disease 0.0
Diagnosed Diabetes 0.0
Life Expectancy at Birth 97.0
Cognitively Disabled 87.2
Physically Disabled 80.2

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Heart Attack ER Admissions 84.0
Mental Health Not Good 0.0
Chronic Kidney Disease 0.0
Obesity 0.0
Pedestrian Injuries 97.1
Physical Health Not Good 0.0
Stroke 0.0
Health Risk Behaviors —
Binge Drinking 0.0
Current Smoker 0.0
No Leisure Time for Physical Activity 0.0
Climate Change Exposures —
Wildfire Risk 0.0
SLR Inundation Area 0.0
Children 84.9
Elderly 16.5
English Speaking 18.2
Foreign-born 95.7
Outdoor Workers 60.7
Climate Change Adaptive Capacity —
Impervious Surface Cover 34.1
Traffic Density 80.4
Traffic Access 23.0
Other Indices —
Hardship 23.2
Other Decision Support —
2016 Voting 20.4

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7.3. Overall Health & Equity Scores
Metric Result for Project Census Tract
CalEnviroScreen 4.0 Score for Project Location (a) 30.0 Healthy Places Index Score for Project Location (b) 65.0 Project Located in a Designated Disadvantaged Community (Senate Bill 535) No Project Located in a Low-Income Community (Assembly Bill 1550) No Project Located in a Community Air Protection Program Community (Assembly Bill 617) No a: The maximum CalEnviroScreen score is 100. A high score (i.e., greater than 50) reflects a higher pollution burden compared to other census tracts in the state. b: The maximum Health Places Index score is 100. A high score (i.e., greater than 50) reflects healthier community conditions compared to other census tracts in the state.

7.4. Health & Equity Measures
No Health & Equity Measures selected.

7.5. Evaluation Scorecard
Health & Equity Evaluation Scorecard not completed.

7.6. Health & Equity Custom Measures
No Health & Equity Custom Measures created.

8. User Changes to Default Data
Screen Justification
Land Use Consistent with IS/MND's model.

Construction: Construction Phases Consistent with information provided by the IS/MND.

Annual Emissions (tons/year) 0.06 Total DPM (lbs) 380
Daily Emissions (lbs/day) 0.328767123 Total DPM (g) 90729.86301 Construction Duration (days) 365 Emission Rate (g/s) 0.001438513 Total DPM (lbs) 120 Release Height (meters) 3
Total DPM (g) 54432 Total Acreage 2.27
Start Date 1/1/2026 Max Horizontal (meters) 135.55
End Date 1/1/2027 Min Horizontal (meters) 67.77
Construction Days 365 Initial Vertical Dimension (meters) 1.5 Setting Arcadia
Annual Emissions (tons/year) 0.04 Population 54,157
Daily Emissions (lbs/day) 0.219178082 Start Date 1/1/2026 Construction Duration (days) 365 End Date 1/1/2028
Total DPM (lbs) 80 Total Construction Days 730
Total DPM (g) 36288 Total Years of Construction 2.00
Start Date 1/1/2027 Total Years of Operation 28.00
End Date 1/1/2028
Construction Days 365
Annual Emissions (tons/year) 0.01
Daily Emissions (lbs/day) 0.054794521
Construction Duration (days) 180
Total DPM (lbs) 9.863013699
Total DPM (g) 4473.863014
Start Date 1/1/2028
End Date 6/29/2028
Construction Days 180
2028
2027
Construction
2026 Total
ƚƚĂĐŚŵĞŶƚ

Age Group Duration (years) Concentration (ug/m3) Cancer Risk 3rd Trimester 0.25 0.2670 3.63E-06
Infant (0 - 2) 1.75 0.2670 7.67E-05
Construction 2 8.04E-05
The Maximally Exposed Individual at an Existing Residential Receptor During Project Construction

AERSCREEN21112/AERMOD21112 12/16/24
14:10:10
TITLE:ArcadiaTownCenter,Construction
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ******************************AREAPARAMETERS**************************** ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ SOURCEEMISSIONRATE: 0.144E Ş02g/s 0.114E Ş01lb/hr
AREAEMISSIONRATE: 0.157E Ş06g/(sŞm2) 0.124E Ş05lb/(hrŞm2) AREAHEIGHT: 3.00 meters 9.84 feet
AREASOURCELONGSIDE: 135.55 meters 444.72 feet
AREASOURCESHORTSIDE: 67.77 meters 222.34 feet
INITIALVERTICALDIMENSION: 1.50 meters 4.92 feet
RURALORURBAN: URBAN
POPULATION: 54157
INITIALPROBEDISTANCE= 5000. meters 16404. feet
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ***********************BUILDINGDOWNWASHPARAMETERS********************** ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ BUILDINGDOWNWASHNOTUSEDFORNONŞPOINTSOURCES
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ **************************FLOWSECTORANALYSIS*************************** 25meterreceptorspacing:1.metersŞ5000.meters
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ MAXIMUMIMPACTRECEPTOR
Zo SURFACE 1ŞHRCONCRADIALDISTTEMPORAL
SECTORROUGHNESS(ug/m3)(deg)(m)PERIOD ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ 1*1.0004.3412075.0WIN
*= worstcasediagonal
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ƚƚĂĐŚŵĞŶƚ

**********************MAKEMETMETEOROLOGYPARAMETERS********************* ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ MIN/MAXTEMPERATURE:250.0/310.0(K)
MINIMUMWINDSPEED: 0.5 m/s
ANEMOMETERHEIGHT:10.000meters
SURFACECHARACTERISTICSINPUT:AERMETSEASONALTABLES
DOMINANTSURFACEPROFILE:Urban
DOMINANTCLIMATETYPE:AverageMoisture
DOMINANTSEASON: Winter
ALBEDO: 0.35
BOWENRATIO: 1.50
ROUGHNESSLENGTH: 1.000 (meters)
SURFACEFRICTIONVELOCITY(U*)NOTADUSTED
METEOROLOGYCONDITIONSUSEDTOPREDICTOVERALLMAXIMUMIMPACT ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ YRMODYJDYHR
ŞŞŞŞŞŞŞŞŞŞŞ
1001101001
H0U*W*DT/DZZICNVZIMCHMŞOLENZ0BOWENALBEDOREFWS ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞ Ş1.300.043Ş9.0000.020Ş999.21.6.01.0001.500.350.50 HTREFTAHT
ŞŞŞŞŞŞŞŞŞŞŞ
10.0310.02.0
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
************************AERSCREENAUTOMATEDDISTANCES********************** OVERALLMAXIMUMCONCENTRATIONSBYDISTANCE
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ

MAXIMUM MAXIMUM
DIST1ŞHRCONC DIST 1ŞHRCONC
(m) (ug/m3) (m) (ug/m3)
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ

1.003.331 2525.00 0.3360EŞ01

25.003.828 2550.00 0.3315EŞ01

50.004.210 2575.00 0.3271EŞ01

75.004.341 2600.00 0.3228EŞ01
100.002.670 2625.00 0.3186EŞ01
125.001.980 2650.00 0.3145EŞ01
150.001.551 2675.00 0.3104EŞ01
175.001.260 2700.00 0.3065EŞ01
200.001.053 2725.00 0.3027EŞ01
225.000.8974 2750.00 0.2989EŞ01
250.000.7785 2775.00 0.2952EŞ01
275.000.6845 2800.00 0.2916EŞ01
300.000.6082 2825.00 0.2881EŞ01
325.000.5458 2850.00 0.2846EŞ01
350.000.4940 2875.00 0.2813EŞ01
375.000.4496 2900.00 0.2779EŞ01
400.000.4119 2925.000.2747EŞ01
425.000.3795 2950.00 0.2715EŞ01
450.000.3511 2975.00 0.2684EŞ01
475.000.3263 3000.00 0.2653EŞ01
500.000.3044 3025.00 0.2623EŞ01
525.000.2849 3050.00 0.2594EŞ01
550.000.2674 3075.00 0.2565EŞ01
575.000.2518 3100.00 0.2537EŞ01
600.000.2376 3125.00 0.2509EŞ01
625.000.2247 3150.00 0.2482EŞ01
650.000.2130 3175.00 0.2455EŞ01
675.000.2023 3200.00 0.2429EŞ01
700.000.1926 3225.00 0.2403EŞ01
725.000.1836 3250.00 0.2378EŞ01
750.000.1753 3275.000.2353EŞ01
775.000.1677 3300.00 0.2329EŞ01
800.000.1606 3325.00 0.2305EŞ01
825.000.1540 3350.00 0.2282EŞ01
850.000.1479 3375.00 0.2258EŞ01
875.000.1422 3400.00 0.2236EŞ01
900.000.1368 3425.00 0.2213EŞ01
925.000.1318 3450.00 0.2192EŞ01
950.000.1270 3475.00 0.2170EŞ01
975.000.1226 3500.00 0.2149EŞ01
1000.000.1185 3525.00 0.2128EŞ01
1025.000.1145 3550.00 0.2107EŞ01
1050.000.1108 3575.00 0.2087EŞ01
1075.000.1073 3600.00 0.2068EŞ01
1100.000.1040 3625.00 0.2048EŞ01
1125.000.1009 3650.000.2029EŞ01
1150.000.9792EŞ01 3675.00 0.2010EŞ01
1175.000.9510EŞ01 3700.00 0.1991EŞ01
1200.000.9242EŞ01 3725.00 0.1973EŞ01
1225.000.8986EŞ01 3750.00 0.1955EŞ01
1250.000.8742EŞ01 3775.00 0.1938EŞ01

1275.000.8570EŞ013800.000.1920EŞ01 1300.000.8344EŞ013825.000.1903EŞ01 1325.000.8129EŞ013850.000.1886EŞ01 1350.000.7923EŞ013875.000.1869EŞ01 1375.000.7726EŞ013900.000.1853EŞ01 1400.000.7538EŞ013925.000.1837EŞ01 1425.000.7357EŞ013950.000.1821EŞ01 1450.000.7184EŞ013975.000.1805EŞ01 1475.000.7017EŞ014000.000.1790EŞ01 1500.000.6857EŞ014025.000.1775EŞ01 1525.000.6704EŞ014050.000.1760EŞ01 1550.000.6556EŞ014075.000.1745EŞ01 1575.000.6414EŞ014100.000.1731EŞ01 1600.000.6277EŞ014125.000.1716EŞ01 1625.000.6145EŞ014150.000.1702EŞ01 1650.000.6017EŞ014175.000.1688EŞ01 1675.000.5895EŞ014200.000.1674EŞ01 1700.000.5776EŞ014225.000.1661EŞ01 1725.000.5662EŞ014250.000.1648EŞ01 1750.000.5551EŞ014275.000.1634EŞ01 1775.000.5444EŞ014300.000.1621EŞ01 1800.000.5341EŞ014325.000.1609EŞ01 1824.990.5241EŞ014350.000.1596EŞ01 1850.000.5144EŞ014375.000.1584EŞ01 1875.000.5050EŞ014400.000.1571EŞ01 1900.000.4960EŞ014425.000.1559EŞ01 1924.990.4871EŞ014450.000.1547EŞ01 1950.000.4786EŞ014475.000.1535EŞ01 1975.000.4703EŞ014500.000.1524EŞ01 2000.000.4623EŞ014525.000.1512EŞ01 2025.000.4545EŞ014550.000.1501EŞ01 2050.000.4469EŞ014575.000.1490EŞ01 2075.000.4396EŞ014600.000.1479EŞ01 2100.000.4324EŞ014625.000.1468EŞ01 2125.000.4255EŞ014650.000.1457EŞ01 2150.000.4187EŞ014675.000.1446EŞ01 2175.000.4121EŞ014700.000.1436EŞ01 2200.000.4057EŞ014725.000.1425EŞ01 2225.000.3995EŞ014750.000.1415EŞ01 2250.000.3934EŞ014775.000.1405EŞ01 2275.000.3875EŞ014800.000.1395EŞ01 2300.000.3818EŞ014825.000.1385EŞ01 2325.000.3761EŞ014850.000.1375EŞ01 2350.000.3707EŞ014875.000.1366EŞ01 2375.000.3653EŞ014900.000.1356EŞ01 2400.000.3601EŞ014925.000.1347EŞ01 2425.000.3551EŞ014950.000.1337EŞ01 2450.000.3501EŞ014975.000.1328EŞ01 2475.000.3453EŞ015000.000.1319EŞ01 2500.000.3406EŞ01

ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ **********************AERSCREENMAXIMUMIMPACTSUMMARY********************* ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ 3Şhour,8Şhour,and24Şhourscaled
concentrationsareequaltothe1Şhourconcentrationasreferencedin SCREENINGPROCEDURESFORESTIMATINGTHEAIRQUALITY
IMPACTOFSTATIONARYSOURCES,REVISED(Section4.5.4)
ReportnumberEPAŞ454/RŞ92Ş019
http://www.epa.gov/scram001/guidance_permit.htm
underScreeningGuidance
MAXIMUMSCALEDSCALEDSCALEDSCALED 1ŞHOUR3ŞHOUR8ŞHOUR24ŞHOURANNUAL
CALCULATION CONC CONC CONC CONC CONC
PROCEDURE (ug/m3) (ug/m3)(ug/m3)(ug/m3)(ug/m3) ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞ FLATTERRAIN 4.436 4.436 4.436 4.436 N/A
DISTANCEFROMSOURCE 72.00 meters
IMPACTATTHE
AMBIENTBOUNDARY3.331 3.331 3.331 3.331 N/A
DISTANCEFROMSOURCE 1.00 meters

2656 29th Street, Suite 201
Santa Monica, CA 90405
Matt Hagemann, P.G, C.Hg.
(949) 887-9013
[email protected]
Matthew F. Hagemann, P.G., C.Hg., QSD, QSP
Geologic and Hydrogeologic Characterization
Investigation and Remediation Strategies
Litigation Support and Testifying Expert
Industrial Stormwater Compliance
CEQA Review
Education:

M.S. Degree, Geology, California State University Los Angeles, Los Angeles, CA, 1984.

B.A. Degree, Geology, Humboldt State University, Arcata, CA, 1982.

Professional Certifications:

California Professional Geologist
California Certified Hydrogeologist
Qualified SWPPP Developer and Practitioner
Professional Experience:

Matt has 30 years of experience in environmental policy, contaminant assessment and remediation, stormwater compliance, and CEQA review. He spent nine years with the U.S. EPA in the RCRA and Superfund programs and served as EPA’s Senior Science Policy Advisor in the Western Regional Office where he identified emerging threats to groundwater from perchlorate and MTBE. While with EPA, Matt also served as a Senior Hydrogeologist in the oversight of the assessment of seven major military facilities undergoing base closure. He led numerous enforcement actions under provisions of the Resource Conservation and Recovery Act (RCRA) and directed efforts to improve hydrogeologic characterization and water quality monitoring. For the past 15 years, as a founding partner with SWAPE, Matt has developed extensive client relationships and has managed complex projects that include consultation as an expert witness and a regulatory specialist, and a manager of projects ranging from industrial stormwater compliance to CEQA review of impacts from hazardous waste, air quality and greenhouse gas emissions.

Positions Matt has held include:
x Founding Partner, Soil/Water/Air Protection Enterprise (SWAPE) (2003 – present); x Geology Instructor, Golden West College, 2010 – 2104, 2017; x Senior Environmental Analyst, Komex H2O Science, Inc. (2000 -- 2003); ƚƚĂĐŚŵĞŶƚ

2 x Executive Director, Orange Coast Watch (2001 – 2004); x Senior Science Policy Advisor and Hydrogeologist, U.S. Environmental Protection Agency (1989– 1998);
x Hydrogeologist, National Park Service, Water Resources Division (1998 – 2000); x Adjunct Faculty Member, San Francisco State University, Department of Geosciences (1993 – 1998);
x Instructor, College of Marin, Department of Science (1990 – 1995); x Geologist, U.S. Forest Service (1986 – 1998); and
x Geologist, Dames & Moore (1984 – 1986).

Senior Regulatory and Litigation Support Analyst:

With SWAPE, Matt’s responsibilities have included:
x Lead analyst and testifying expert in the review of over 300 environmental impact reports and negative declarations since 2003 under CEQA that identify significant issues with regard to hazardous waste, water resources, water quality, air quality, greenhouse gas emissions, and geologic hazards. Make recommendations for additional mitigation measures to lead agencies at the local and county level to include additional characterization of health risks and implementation of protective measures to reduce worker exposure to hazards from toxins and Valley Fever.
x Stormwater analysis, sampling and best management practice evaluation at more than 100 industrial facilities.
x Expert witness on numerous cases including, for example, perfluorooctanoic acid (PFOA) contamination of groundwater, MTBE litigation, air toxins at hazards at a school, CERCLA compliance in assessment and remediation, and industrial stormwater contamination. x Technical assistance and litigation support for vapor intrusion concerns. x Lead analyst and testifying expert in the review of environmental issues in license applications for large solar power plants before the California Energy Commission. x Manager of a project to evaluate numerous formerly used military sites in the western U.S. x Manager of a comprehensive evaluation of potential sources of perchlorate contamination in Southern California drinking water wells.
x Manager and designated expert for litigation support under provisions of Proposition 65 in the review of releases of gasoline to sources drinking water at major refineries and hundreds of gas stations throughout California.

With Komex H2O Science Inc., Matt’s duties included the following:
x Senior author of a report on the extent of perchlorate contamination that was used in testimony by the former U.S. EPA Administrator and General Counsel. x Senior researcher in the development of a comprehensive, electronically interactive chronology of MTBE use, research, and regulation.
x Senior researcher in the development of a comprehensive, electronically interactive chronology of perchlorate use, research, and regulation.
x Senior researcher in a study that estimates nationwide costs for MTBE remediation and drinking water treatment, results of which were published in newspapers nationwide and in testimony against provisions of an energy bill that would limit liability for oil companies. x Research to support litigation to restore drinking water supplies that have been contaminated by MTBE in California and New York.

3 x Expert witness testimony in a case of oil production-related contamination in Mississippi. x Lead author for a multi-volume remedial investigation report for an operating school in Los Angeles that met strict regulatory requirements and rigorous deadlines. x Development of strategic approaches for cleanup of contaminated sites in consultation with clients and regulators.

Executive Director:

As Executive Director with Orange Coast Watch, Matt led efforts to restore water quality at Orange County beaches from multiple sources of contamination including urban runoff and the discharge of wastewater. In reporting to a Board of Directors that included representatives from leading Orange County universities and businesses, Matt prepared issue papers in the areas of treatment and disinfection of wastewater and control of the discharge of grease to sewer systems. Matt actively participated in the development of countywide water quality permits for the control of urban runoff and permits for the discharge of wastewater. Matt worked with other nonprofits to protect and restore water quality, including Surfrider, Natural Resources Defense Council and Orange County CoastKeeper as well as with business institutions including the Orange County Business Council.

Hydrogeology:

As a Senior Hydrogeologist with the U.S. Environmental Protection Agency, Matt led investigations to characterize and cleanup closing military bases, including Mare Island Naval Shipyard, Hunters Point Naval Shipyard, Treasure Island Naval Station, Alameda Naval Station, Moffett Field, Mather Army Airfield, and Sacramento Army Depot. Specific activities were as follows:
x Led efforts to model groundwater flow and contaminant transport, ensured adequacy of monitoring networks, and assessed cleanup alternatives for contaminated sediment, soil, and groundwater.
x Initiated a regional program for evaluation of groundwater sampling practices and laboratory analysis at military bases.
x Identified emerging issues, wrote technical guidance, and assisted in policy and regulation development through work on four national U.S. EPA workgroups, including the Superfund Groundwater Technical Forum and the Federal Facilities Forum.

At the request of the State of Hawaii, Matt developed a methodology to determine the vulnerability of

groundwater to contamination on the islands of Maui and Oahu. He used analytical models and a GIS to show zones of vulnerability, and the results were adopted and published by the State of Hawaii and County of Maui.

As a hydrogeologist with the EPA Groundwater Protection Section, Matt worked with provisions of the Safe Drinking Water Act and NEPA to prevent drinking water contamination. Specific activities included the following:
x Received an EPA Bronze Medal for his contribution to the development of national guidance for the protection of drinking water.
x Managed the Sole Source Aquifer Program and protected the drinking water of two communities through designation under the Safe Drinking Water Act. He prepared geologic reports, conducted

4 public hearings, and responded to public comments from residents who were very concerned about the impact of designation.
x Reviewed a number of Environmental Impact Statements for planned major developments, including large hazardous and solid waste disposal facilities, mine reclamation, and water transfer.

Matt served as a hydrogeologist with the RCRA Hazardous Waste program. Duties were as follows:
x Supervised the hydrogeologic investigation of hazardous waste sites to determine compliance with Subtitle C requirements.
x Reviewed and wrote "part B" permits for the disposal of hazardous waste. x Conducted RCRA Corrective Action investigations of waste sites and led inspections that formed the basis for significant enforcement actions that were developed in close coordination with U.S.

EPA legal counsel.
x Wrote contract specifications and supervised contractor’s investigations of waste sites.

With the National Park Service, Matt directed service-wide investigations of contaminant sources to prevent degradation of water quality, including the following tasks:
x Applied pertinent laws and regulations including CERCLA, RCRA, NEPA, NRDA, and the Clean Water Act to control military, mining, and landfill contaminants. x Conducted watershed-scale investigations of contaminants at parks, including Yellowstone and Olympic National Park.
x Identified high-levels of perchlorate in soil adjacent to a national park in New Mexico and advised park superintendent on appropriate response actions under CERCLA. x Served as a Park Service representative on the Interagency Perchlorate Steering Committee, a national workgroup.
x Developed a program to conduct environmental compliance audits of all National Parks while serving on a national workgroup.
x Co-authored two papers on the potential for water contamination from the operation of personal watercraft and snowmobiles, these papers serving as the basis for the development of nation-

wide policy on the use of these vehicles in National Parks. x Contributed to the Federal Multi-Agency Source Water Agreement under the Clean Water Action Plan.

Policy:

Served senior management as the Senior Science Policy Advisor with the U.S. Environmental Protection Agency, Region 9.

Activities included the following:
x Advised the Regional Administrator and senior management on emerging issues such as the potential for the gasoline additive MTBE and ammonium perchlorate to contaminate drinking water supplies.
x Shaped EPA’s national response to these threats by serving on workgroups and by contributing to guidance, including the Office of Research and Development publication, Oxygenates in Water: Critical Information and Research Needs.
x Improved the technical training of EPA's scientific and engineering staff. x Earned an EPA Bronze Medal for representing the region’s 300 scientists and engineers in negotiations with the Administrator and senior management to better integrate scientific

5 principles into the policy-making process.
x Established national protocol for the peer review of scientific documents.

Geology:

With the U.S. Forest Service, Matt led investigations to determine hillslope stability of areas proposed for timber harvest in the central Oregon Coast Range. Specific activities were as follows:
x Mapped geology in the field, and used aerial photographic interpretation and mathematical models to determine slope stability.
x Coordinated his research with community members who were concerned with natural resource protection.
x Characterized the geology of an aquifer that serves as the sole source of drinking water for the city of Medford, Oregon.

As a consultant with Dames and Moore, Matt led geologic investigations of two contaminated sites (later

listed on the Superfund NPL) in the Portland, Oregon, area and a large hazardous waste site in eastern Oregon. Duties included the following:
x Supervised year-long effort for soil and groundwater sampling. x Conducted aquifer tests.
x Investigated active faults beneath sites proposed for hazardous waste disposal.

Teaching:

From 1990 to 1998, Matt taught at least one course per semester at the community college and university levels:
x At San Francisco State University, held an adjunct faculty position and taught courses in environmental geology, oceanography (lab and lecture), hydrogeology, and groundwater contamination.
x Served as a committee member for graduate and undergraduate students. x Taught courses in environmental geology and oceanography at the College of Marin.

Matt is currently a part time geology instructor at Golden West College in Huntington Beach, California where he taught from 2010 to 2014 and in 2017.

Invited Testimony, Reports, Papers and Presentations:

Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Presentation to the Public Environmental Law Conference, Eugene, Oregon.

Hagemann, M.F., 2008. Disclosure of Hazardous Waste Issues under CEQA. Invited presentation to U.S.

EPA Region 9, San Francisco, California.

Hagemann, M.F., 2005. Use of Electronic Databases in Environmental Regulation, Policy Making and Public Participation. Brownfields 2005, Denver, Coloradao.

Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Nevada and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Las Vegas, NV (served on conference organizing committee).

6 Hagemann, M.F., 2004. Invited testimony to a California Senate committee hearing on air toxins at schools in Southern California, Los Angeles.

Brown, A., Farrow, J., Gray, A. and Hagemann, M., 2004. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells.

Presentation to the Ground Water and Environmental Law Conference, National Groundwater Association.

Hagemann, M.F., 2004. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in Arizona and the Southwestern U.S. Presentation to a meeting of the American Groundwater Trust, Phoenix, AZ (served on conference organizing committee).

Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River and Impacts to Drinking Water in the Southwestern U.S. Invited presentation to a special committee meeting of the National Academy of Sciences, Irvine, CA.

Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a tribal EPA meeting, Pechanga, CA.

Hagemann, M.F., 2003. Perchlorate Contamination of the Colorado River. Invited presentation to a meeting of tribal repesentatives, Parker, AZ.

Hagemann, M.F., 2003. Impact of Perchlorate on the Colorado River and Associated Drinking Water Supplies. Invited presentation to the Inter-Tribal Meeting, Torres Martinez Tribe.

Hagemann, M.F., 2003. The Emergence of Perchlorate as a Widespread Drinking Water Contaminant.

Invited presentation to the U.S. EPA Region 9.

Hagemann, M.F., 2003. A Deductive Approach to the Assessment of Perchlorate Contamination. Invited presentation to the California Assembly Natural Resources Committee.

Hagemann, M.F., 2003. Perchlorate: A Cold War Legacy in Drinking Water. Presentation to a meeting of the National Groundwater Association.

Hagemann, M.F., 2002. From Tank to Tap: A Chronology of MTBE in Groundwater. Presentation to a meeting of the National Groundwater Association.

Hagemann, M.F., 2002. A Chronology of MTBE in Groundwater and an Estimate of Costs to Address Impacts to Groundwater. Presentation to the annual meeting of the Society of Environmental Journalists.

Hagemann, M.F., 2002. An Estimate of the Cost to Address MTBE Contamination in Groundwater (and Who Will Pay). Presentation to a meeting of the National Groundwater Association.

Hagemann, M.F., 2002. An Estimate of Costs to Address MTBE Releases from Underground Storage Tanks and the Resulting Impact to Drinking Water Wells. Presentation to a meeting of the U.S. EPA and State Underground Storage Tank Program managers.

7 Hagemann, M.F ., 2001. From Tank to Tap: A Chronology of MTBE in Groundwat er. Unpublished report.

Hagemann, M.F ., 2001. Estimated Cleanup Cost for MTBE in Groundwater Used as Drinking Water.

Unpublished report.

Hagemann, M.F., 2001. Estimated Costs to Address MTBE Releases from Leaking Underground Storage Tanks. Unpublished report.

Hagemann, M.F ., and VanMouwerik, M., 1999. Potential W a t e r Quality Concerns Related to Snowmobile Usage. Water Resources Division, National Park Service, Technical Report.

VanMouwerik, M. and Hagemann, M.F. 1999, Water Quality Concerns Related to Personal Watercraft Usage. Water Resources Division, National Park Service, Technical Report.

Hagemann, M.F ., 1999, Is Dilution the Solution to Pollution in National Parks? The George Wright Society Biannual Meeting, Asheville, North Carolina.

Hagemann, M.F ., 1997, The Potential for MTBE to Contaminate Groundwater. U.S. EPA Superfund Groundwater Technical Forum Annual Meeting, Las Vegas, Nevada.

Hagemann, M.F ., and Gill, M., 1996, Impediments to Intrinsic Remediation, Moffett Field Naval Air Station, Conference on Intrinsic Remediation of Chlorinated Hydrocarbons, Salt Lake City.

Hagemann, M.F., Fukunaga, G.L., 1996, The Vulnerability of Groundwater to Anthropogenic Contaminants on the Island of Maui, Hawaii. Hawaii Water Works Association Annual Meeting, Maui, October 1996.

Hagemann, M. F., Fukanaga, G. L., 1996, Ranking Groundwater Vulnerability in Central Oahu, Hawaii. Proceedings, Geographic Information Systems in Environmental Resources Management, Air and Waste Management Association Publication VIP-61.

Hagemann, M.F., 1994. Groundwater Ch ar ac te r i z a t i o n and Cl ean up a t Closing Military Bases in California. Proceedings, California Groundwater Resources Association Meeting.

Hagemann, M. F. and Sabol, M.A., 1993. Role of the U.S. EPA in the High Plains States Groundwater Recharge Demonstration Program. Proceedings, Sixth Biennial Symposium on the Artificial Recharge of Groundwater.

Hagemann, M.F ., 1993. U.S. EPA Policy on the Technical Impracticability of the Cleanup of DNAPL- contaminated Groundwater. California Groundwater Resources Association Meeting.

8 Hagemann, M.F., 1992. Dense Nonaqueous Phase Liquid Contamination of Groundwater: An Ounce of Prevention... Proceedings, Association of Engineering Geologists Annual Meeting, v. 35.

Other Experience:

Selected as subject matter expert for the California Professional Geologist licensing examinations, 2009-2011.

SOIL WATER AIR PROTECTION ENTERPRISE
2656 29th Street, Suite 201
Santa Monica, California 90405
Attn: Paul Rosenfeld, Ph.D.

Mobil: (310) 795-2335
Office: (310) 452-5555
Fax: (310) 452-5550
Email: [email protected]
Paul E. Rosenfeld, Ph.D. Page 1 of 12 October 2022
Paul Rosenfeld, Ph.D. Chemical Fate and Transport & Air Dispersion Modeling Principal Environmental Chemist Risk Assessment & Remediation Specialist Education
Ph.D. Soil Chemistry, University of Washington, 1999. Dissertation on volatile organic compound filtration.

M.S. Environmental Science, U.C. Berkeley, 1995. Thesis on organic waste economics.

B.A. Environmental Studies, U.C. Santa Barbara, 1991. Focus on wastewater treatment.

Professional Experience
Dr. Rosenfeld has over 25 years of experience conducting environmental investigations and risk assessments for evaluating impacts to human health, property, and ecological receptors. His expertise focuses on the fate and transport of environmental contaminants, human health risk, exposure assessment, and ecological restoration. Dr.

Rosenfeld has evaluated and modeled emissions from oil spills, landfills, boilers and incinerators, process stacks, storage tanks, confined animal feeding operations, industrial, military and agricultural sources, unconventional oil drilling operations, and locomotive and construction engines. His project experience ranges from monitoring and modeling of pollution sources to evaluating impacts of pollution on workers at industrial facilities and residents in surrounding communities. Dr. Rosenfeld has also successfully modeled exposure to contaminants distributed by water systems and via vapor intrusion.

Dr. Rosenfeld has investigated and designed remediation programs and risk assessments for contaminated sites containing lead, heavy metals, mold, bacteria, particulate matter, petroleum hydrocarbons, chlorinated solvents, pesticides, radioactive waste, dioxins and furans, semi- and volatile organic compounds, PCBs, PAHs, creosote, perchlorate, asbestos, per- and poly-fluoroalkyl substances (PFOA/PFOS), unusual polymers, fuel oxygenates (MTBE), among other pollutants. Dr. Rosenfeld also has experience evaluating greenhouse gas emissions from various projects and is an expert on the assessment of odors from industrial and agricultural sites, as well as the evaluation of odor nuisance impacts and technologies for abatement of odorous emissions. As a principal scientist at SWAPE, Dr. Rosenfeld directs air dispersion modeling and exposure assessments. He has served as an expert witness and testified about pollution sources causing nuisance and/or personal injury at sites and has testified as an expert witness on numerous cases involving exposure to soil, water and air contaminants from industrial, railroad, agricultural, and military sources.
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Paul E. Rosenfeld, Ph.D. Page 2 of 12 October 2022

Professional History:

Soil Water Air Protection Enterprise (SWAPE); 2003 to present; Principal and Founding Partner UCLA School of Public Health; 2007 to 2011; Lecturer (Assistant Researcher) UCLA School of Public Health; 2003 to 2006; Adjunct Professor UCLA Environmental Science and Engineering Program; 2002-2004; Doctoral Intern Coordinator UCLA Institute of the Environment, 2001-2002; Research Associate Komex H
2O Science, 2001 to 2003; Senior Remediation Scientist
National Groundwater Association, 2002-2004; Lecturer
San Diego State University, 1999-2001; Adjunct Professor Anteon Corp., San Diego, 2000-2001; Remediation Project Manager Ogden (now Amec), San Diego, 2000-2000; Remediation Project Manager Bechtel, San Diego, California, 1999 – 2000; Risk Assessor King County, Seattle, 1996 – 1999; Scientist
James River Corp., Washington, 1995-96; Scientist
Big Creek Lumber, Davenport, California, 1995; Scientist Plumas Corp., California and USFS, Tahoe 1993-1995; Scientist Peace Corps and World Wildlife Fund, St. Kitts, West Indies, 1991-1993; Scientist

Publications:

Rosenfeld P. E., Spaeth K., Hallman R., Bressler R., Smith, G., (2022) Cancer Risk and Diesel Exhaust Exposure Among Railroad Workers. Water Air Soil Pollution. 233, 171.

Remy, L.L., Clay T., Byers, V., Rosenfeld P. E. (2019) Hospital, Health, and Community Burden After Oil Refinery Fires, Richmond, California 2007 and 2012. Environmental Health. 18:48

Simons, R.A., Seo, Y. Rosenfeld, P., (2015) Modeling the Effect of Refinery Emission On Residential Property Value. Journal of Real Estate Research. 27(3):321-342

Chen, J. A, Zapata A. R., Sutherland A. J., Molmen, D.R., Chow, B. S., Wu, L. E., Rosenfeld, P. E., Hesse, R. C., (2012) Sulfur Dioxide and Volatile Organic Compound Exposure To A Community In Texas City Texas Evaluated Using Aermod and Empirical Data. American Journal of Environmental Science, 8(6), 622-632.

Rosenfeld, P.E. & Feng, L. (2011). The Risks of Hazardous Waste. Amsterdam: Elsevier Publishing.

Cheremisinoff, N.P., & Rosenfeld, P.E. (2011). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Agrochemical Industry, Amsterdam: Elsevier Publishing.

Gonzalez, J., Feng, L., Sutherland, A., Waller, C., Sok, H., Hesse, R., Rosenfeld, P. (2010). PCBs and Dioxins/Furans in Attic Dust Collected Near Former PCB Production and Secondary Copper Facilities in Sauget, IL.

Procedia Environmental Sciences. 113–125.

Feng, L., Wu, C., Tam, L., Sutherland, A.J., Clark, J.J., Rosenfeld, P.E. (2010). Dioxin and Furan Blood Lipid and Attic Dust Concentrations in Populations Living Near Four Wood Treatment Facilities in the United States. Journal of Environmental Health. 73(6), 34-46.

Cheremisinoff, N.P., & Rosenfeld, P.E. (2010). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Wood and Paper Industries. Amsterdam: Elsevier Publishing.

Cheremisinoff, N.P., & Rosenfeld, P.E. (2009). Handbook of Pollution Prevention and Cleaner Production: Best Practices in the Petroleum Industry. Amsterdam: Elsevier Publishing.

Paul E. Rosenfeld, Ph.D. Page 3 of 12 October 2022

Wu, C., Tam, L., Clark, J., Rosenfeld, P. (2009). Dioxin and furan blood lipid concentrations in populations living near four wood treatment facilities in the United States. WIT Transactions on Ecology and the Environment, Air Pollution, 123 (17), 319-327.

Tam L. K.., Wu C. D., Clark J. J. and Rosenfeld, P.E. (2008). A Statistical Analysis Of Attic Dust And Blood Lipid Concentrations Of Tetrachloro-p-Dibenzodioxin (TCDD) Toxicity Equivalency Quotients (TEQ) In Two Populations Near Wood Treatment Facilities. Organohalogen Compounds, 70, 002252-002255.

Tam L. K.., Wu C. D., Clark J. J. and Rosenfeld, P.E. (2008). Methods For Collect Samples For Assessing Dioxins And Other Environmental Contaminants In Attic Dust: A Review. Organohalogen Compounds , 70, 000527- 000530.

Hensley, A.R. A. Scott, J. J. J. Clark, Rosenfeld, P.E. (2007). Attic Dust and Human Blood Samples Collected near a Former Wood Treatment Facility. Environmental Research. 105, 194-197.

Rosenfeld, P.E., J. J. J. Clark, A. R. Hensley, M. Suffet. (2007). The Use of an Odor Wheel Classification for Evaluation of Human Health Risk Criteria for Compost Facilities. Water Science & Technology 55(5), 345-357.

Rosenfeld, P. E., M. Suffet. (2007). The Anatomy Of Odour Wheels For Odours Of Drinking Water, Wastewater, Compost And The Urban Environment. Water Science & Technology 55(5), 335-344.

Sullivan, P. J. Clark, J.J.J., Agardy, F. J., Rosenfeld, P.E. (2007). Toxic Legacy, Synthetic Toxins in the Food, Water, and Air in American Cities. Boston Massachusetts: Elsevier Publishing

Rosenfeld, P.E., and Suffet I.H. (2004). Control of Compost Odor Using High Carbon Wood Ash. Water Science and Technology. 49(9),171-178.

Rosenfeld P. E., J.J. Clark, I.H. (Mel) Suffet (2004). The Value of An Odor-Quality-Wheel Classification Scheme For The Urban Environment. Water Environment Federation’s Technical Exhibition and Conference (WEFTEC) 2004. New Orleans, October 2-6, 2004.

Rosenfeld, P.E., and Suffet, I.H. (2004). Understanding Odorants Associated With Compost, Biomass Facilities, and the Land Application of Biosolids. Water Science and Technology. 49(9), 193-199.

Rosenfeld, P.E., and Suffet I.H. (2004). Control of Compost Odor Using High Carbon Wood Ash, Water Science and Technology, 49( 9), 171-178.

Rosenfeld, P. E ., Grey, M. A., Sellew, P. (2004). Measurement of Biosolids Odor and Odorant Emissions from Windrows, Static Pile and Biofilter. Water Environment Research. 76(4), 310-315.

Rosenfeld, P.E., Grey, M and Suffet, M. (2002). Compost Demonstration Project, Sacramento California Using High-Carbon Wood Ash to Control Odor at a Green Materials Composting Facility. Integrated Waste Management Board Public Affairs Office, Publications Clearinghouse (MS–6), Sacramento, CA Publication #442-02-008.

Rosenfeld, P.E., and C.L. Henry. (2001). Characterization of odor emissions from three different biosolids. Water Soil and Air Pollution. 127(1-4), 173-191.

Rosenfeld, P.E., and Henry C. L., (2000). Wood ash control of odor emissions from biosolids application. Journal of Environmental Quality. 29, 1662-1668.

Rosenfeld, P.E., C.L. Henry and D. Bennett. (2001). Wastewater dewatering polymer affect on biosolids odor emissions and microbial activity. Water Environment Research. 73(4), 363-367.

Rosenfeld, P.E., and C.L. Henry. (2001). Activated Carbon and Wood Ash Sorption of Wastewater, Compost, and Biosolids Odorants. Water Environment Research, 73, 388-393.

Paul E. Rosenfeld, Ph.D. Page 4 of 12 October 2022

Rosenfeld, P.E., and Henry C. L., (2001). High carbon wood ash effect on biosolids microbial activity and odor.

Water Environment Research. 131(1-4), 247-262.

Chollack, T. and P. Rosenfeld. ( 1998). Compost Amendment Handbook For Landscaping. Prepared for and distributed by the City of Redmond, Washington State.

Rosenfeld, P. E. (1992). The Mount Liamuiga Crater Trail. Heritage Magazine of St. Kitts, 3(2).

Rosenfeld, P. E. (1993). High School Biogas Project to Prevent Deforestation On St. Kitts. Biomass Users Network, 7(1).

Rosenfeld, P. E. ( 1998). Characterization, Quantification, and Control of Odor Emissions From Biosolids Application To Forest Soil. Doctoral Thesis. University of Washington College of Forest Resources.

Rosenfeld, P. E. (1994). Potential Utilization of Small Diameter Trees on Sierra County Public Land. Masters thesis reprinted by the Sierra County Economic Council. Sierra County, California.

Rosenfeld, P. E. (1991). How to Build a Small Rural Anaerobic Digester & Uses Of Biogas In The First And Third World. Bachelors Thesis. University of California.

Presentations:

Rosenfeld, P.E ., "The science for Perfluorinated Chemicals (PFAS): What makes remediation so hard?" Law Seminars International, (May 9-10, 2018) 800 Fifth Avenue, Suite 101 Seattle, WA.

Rosenfeld, P.E., Sutherland, A; Hesse, R.; Zapata, A. (October 3-6, 2013). Air dispersion modeling of volatile organic emissions from multiple natural gas wells in Decatur, TX. 44th Western Regional Meeting, American Chemical Society. Lecture conducted from Santa Clara, CA.

Sok, H.L.; Waller, C.C.; Feng, L.; Gonzalez, J.; Sutherland, A.J.; Wisdom-Stack, T.; Sahai, R.K.; Hesse, R.C.; Rosenfeld, P.E. (June 20-23, 2010). Atrazine: A Persistent Pesticide in Urban Drinking Water .

Urban Environmental Pollution. Lecture conducted from Boston, MA.

Feng, L.; Gonzalez, J.; Sok, H.L.; Sutherland, A.J.; Waller, C.C.; Wisdom-Stack, T.; Sahai, R.K.; La, M.; Hesse, R.C.; Rosenfeld, P.E. (June 20-23, 2010). Bringing Environmental Justice to East St. Louis, Illinois. Urban Environmental Pollution. Lecture conducted from Boston, MA.

Rosenfeld, P.E . (April 19-23, 2009). Perfluoroctanoic Acid (PFOA) and Perfluoroactane Sulfonate (PFOS) Contamination in Drinking Water From the Use of Aqueous Film Forming Foams (AFFF) at Airports in the United States. 2009 Ground Water Summit and 2009 Ground Water Protection Council Spring Meeting , Lecture conducted from Tuscon, AZ.

Rosenfeld, P.E. (April 19-23, 2009). Cost to Filter Atrazine Contamination from Drinking Water in the United States” Contamination in Drinking Water From the Use of Aqueous Film Forming Foams (AFFF) at Airports in the United States. 2009 Ground Water Summit and 2009 Ground Water Protection Council Spring Meeting . Lecture conducted from Tuscon, AZ.

Wu, C., Tam, L., Clark, J., Rosenfeld, P . (20-22 July, 2009). Dioxin and furan blood lipid concentrations in populations living near four wood treatment facilities in the United States. Brebbia, C.A. and Popov, V., eds., Air Pollution XVII: Proceedings of the Seventeenth International Conference on Modeling, Monitoring and Management of Air Pollution. Lecture conducted from Tallinn, Estonia.

Rosenfeld, P. E. (October 15-18, 2007). Moss Point Community Exposure To Contaminants From A Releasing Facility. The 23
rd Annual International Conferences on Soils Sediment and Water. Platform lecture conducted from University of Massachusetts, Amherst MA.

Paul E. Rosenfeld, Ph.D. Page 5 of 12 October 2022

Rosenfeld, P. E. (October 15-18, 2007). The Repeated Trespass of Tritium-Contaminated Water Into A Surrounding Community Form Repeated Waste Spills From A Nuclear Power Plant . The 23 rd Annual International
Conferences on Soils Sediment and Water . Platform lecture conducted from University of Massachusetts, Amherst MA.

Rosenfeld, P. E. (October 15-18, 2007). Somerville Community Exposure To Contaminants From Wood Treatment Facility Emissions. The 23
rd Annual International Conferences on Soils Sediment and Water . Lecture conducted from University of Massachusetts, Amherst MA.

Rosenfeld P. E. (March 2007). Production, Chemical Properties, Toxicology, & Treatment Case Studies of 1,2,3- Trichloropropane (TCP). The Association for Environmental Health and Sciences (AEHS) Annual Meeting . Lecture conducted from San Diego, CA.

Rosenfeld P. E. (March 2007). Blood and Attic Sampling for Dioxin/Furan, PAH, and Metal Exposure in Florala, Alabama. The AEHS Annual Meeting. Lecture conducted from San Diego, CA.

Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. (August 21 – 25, 2006). Dioxin Containing Attic Dust And Human Blood Samples Collected Near A Former Wood Treatment Facility. The 26th International Symposium on Halogenated Persistent Organic Pollutants – DIOXIN2006 . Lecture conducted from Radisson SAS Scandinavia Hotel in Oslo Norway.

Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. (November 4-8, 2006). Dioxin Containing Attic Dust And Human Blood Samples Collected Near A Former Wood Treatment Facility . APHA 134 Annual Meeting & Exposition. Lecture conducted from Boston Massachusetts.

Paul Rosenfeld Ph.D . (October 24-25, 2005). Fate, Transport and Persistence of PFOA and Related Chemicals.

Mealey’s C8/PFOA. Science, Risk & Litigation Conference. Lecture conducted from The Rittenhouse Hotel, Philadelphia, PA.

Paul Rosenfeld Ph.D . (September 19, 2005). Brominated Flame Retardants in Groundwater: Pathways to Human Ingestion, Toxicology and Remediation PEMA Emerging Contaminant Conference . Lecture conducted from Hilton Hotel, Irvine California.

Paul Rosenfeld Ph.D . (September 19, 2005). Fate, Transport, Toxicity, And Persistence of 1,2,3-TCP. PEMA Emerging Contaminant Conference. Lecture conducted from Hilton Hotel in Irvine, California.

Paul Rosenfeld Ph.D. (September 26-27, 2005). Fate, Transport and Persistence of PDBEs. Mealey’s Groundwater Conference. Lecture conducted from Ritz Carlton Hotel, Marina Del Ray, California.

Paul Rosenfeld Ph.D . (June 7-8, 2005). Fate, Transport and Persistence of PFOA and Related Chemicals.

International Society of Environmental Forensics: Focus On Emerging Contaminants . Lecture conducted from Sheraton Oceanfront Hotel, Virginia Beach, Virginia.

Paul Rosenfeld Ph.D . (July 21-22, 2005). Fate Transport, Persistence and Toxicology of PFOA and Related Perfluorochemicals. 2005 National Groundwater Association Ground Water And Environmental Law Conference .

Lecture conducted from Wyndham Baltimore Inner Harbor, Baltimore Maryland.

Paul Rosenfeld Ph.D . (July 21-22, 2005). Brominated Flame Retardants in Groundwater: Pathways to Human Ingestion, Toxicology and Remediation. 2005 National Groundwater Association Ground Water and Environmental Law Conference. Lecture conducted from Wyndham Baltimore Inner Harbor, Baltimore Maryland.

Paul Rosenfeld, Ph.D. and James Clark Ph.D. and Rob Hesse R.G. (May 5-6, 2004). Tert-butyl Alcohol Liability and Toxicology, A National Problem and Unquantified Liability. National Groundwater Association. Environmental Law Conference. Lecture conducted from Congress Plaza Hotel, Chicago Illinois.

Paul E. Rosenfeld, Ph.D. Page 6 of 12 October 2022

Paul Rosenfeld, Ph.D. (March 2004). Perchlorate Toxicology. Meeting of the American Groundwater Trust .

Lecture conducted from Phoenix Arizona.

Hagemann, M.F., Paul Rosenfeld, Ph.D. and Rob Hesse (2004). Perchlorate Contamination of the Colorado River.

Meeting of tribal representatives. Lecture conducted from Parker, AZ.

Paul Rosenfeld, Ph.D. (April 7, 2004). A National Damage Assessment Model For PCE and Dry Cleaners.

Drycleaner Symposium. California Ground Water Association . Lecture conducted from Radison Hotel, Sacramento, California.

Rosenfeld, P. E ., Grey, M., (June 2003) Two stage biofilter for biosolids composting odor control. Seventh International In Situ And On Site Bioremediation Symposium Battelle Conference Orlando, FL.

Paul Rosenfeld, Ph.D. and James Clark Ph.D. (February 20-21, 2003) Understanding Historical Use, Chemical Properties, Toxicity and Regulatory Guidance of 1,4 Dioxane. National Groundwater Association. Southwest Focus Conference. Water Supply and Emerging Contaminants .. Lecture conducted from Hyatt Regency Phoenix Arizona.

Paul Rosenfeld, Ph.D. (February 6-7, 2003). Underground Storage Tank Litigation and Remediation. California CUPA Forum. Lecture conducted from Marriott Hotel, Anaheim California.

Paul Rosenfeld, Ph.D . (October 23, 2002) Underground Storage Tank Litigation and Remediation. EPA Underground Storage Tank Roundtable. Lecture conducted from Sacramento California.

Rosenfeld, P.E . and Suffet, M. (October 7- 10, 2002). Understanding Odor from Compost, Wastewater and Industrial Processes. Sixth Annual Symposium On Off Flavors in the Aquatic Environment. International Water Association. Lecture conducted from Barcelona Spain.

Rosenfeld, P.E. and Suffet, M. (October 7- 10, 2002). Using High Carbon Wood Ash to Control Compost Odor.

Sixth Annual Symposium On Off Flavors in the Aquatic Environment. International Water Association . Lecture conducted from Barcelona Spain.

Rosenfeld, P.E. and Grey, M. A. (September 22-24, 2002). Biocycle Composting For Coastal Sage Restoration.

Northwest Biosolids Management Association. Lecture conducted from Vancouver Washington..

Rosenfeld, P.E. and Grey, M. A. (November 11-14, 2002). Using High-Carbon Wood Ash to Control Odor at a Green Materials Composting Facility. Soil Science Society Annual Conference. Lecture conducted from Indianapolis, Maryland.

Rosenfeld. P.E. (September 16, 2000). Two stage biofilter for biosolids composting odor control. Water Environment Federation. Lecture conducted from Anaheim California.

Rosenfeld. P.E. ( October 16, 2000). Wood ash and biofilter control of compost odor. Biofest. Lecture conducted from Ocean Shores, California.

Rosenfeld, P.E. ( 2000). Bioremediation Using Organic Soil Amendments. California Resource Recovery Association. Lecture conducted from Sacramento California.

Rosenfeld, P.E ., C.L. Henry, R. Harrison. (1998). Oat and Grass Seed Germination and Nitrogen and Sulfur Emissions Following Biosolids Incorporation With High-Carbon Wood-Ash. Water Environment Federation 12th Annual Residuals and Biosolids Management Conference Proceedings . Lecture conducted from Bellevue Washington.

Rosenfeld, P.E., and C.L. Henry. (1999). An evaluation of ash incorporation with biosolids for odor reduction. Soil Science Society of America. Lecture conducted from Salt Lake City Utah.

Paul E. Rosenfeld, Ph.D. Page 7 of 12 October 2022

Rosenfeld, P.E. , C.L. Henry, R. Harrison. (1998). Comparison of Microbial Activity and Odor Emissions from Three Different Biosolids Applied to Forest Soil. Brown and Caldwell. Lecture conducted from Seattle Washington.

Rosenfeld, P.E. , C.L. Henry. (1998). Characterization, Quantification, and Control of Odor Emissions from Biosolids Application To Forest Soil. Biofest. Lecture conducted from Lake Chelan, Washington.

Rosenfeld, P.E, C.L. Henry, R. Harrison. (1998). Oat and Grass Seed Germination and Nitrogen and Sulfur Emissions Following Biosolids Incorporation With High-Carbon Wood-Ash. Water Environment Federation 12th Annual Residuals and Biosolids Management Conference Proceedings. Lecture conducted from Bellevue Washington.

Rosenfeld, P.E. , C.L. Henry, R. B. Harrison, and R. Dills. (1997). Comparison of Odor Emissions From Three Different Biosolids Applied to Forest Soil. Soil Science Society of America . Lecture conducted from Anaheim California.

Teaching Experience:

UCLA Department of Environmental Health (Summer 2003 through 20010) Taught Environmental Health Science 100 to students, including undergrad, medical doctors, public health professionals and nurses. Course focused on the health effects of environmental contaminants.

National Ground Water Association, Successful Remediation Technologies. Custom Course in Sante Fe, New Mexico. May 21, 2002. Focused on fate and transport of fuel contaminants associated with underground storage tanks.

National Ground Water Association; Successful Remediation Technologies Course in Chicago Illinois. April 1, 2002. Focused on fate and transport of contaminants associated with Superfund and RCRA sites.

California Integrated Waste Management Board, April and May, 2001. Alternative Landfill Caps Seminar in San Diego, Ventura, and San Francisco. Focused on both prescriptive and innovative landfill cover design.

UCLA Department of Environmental Engineering, February 5, 2002. Seminar on Successful Remediation Technologies focusing on Groundwater Remediation.

University Of Washington, Soil Science Program, Teaching Assistant for several courses including: Soil Chemistry, Organic Soil Amendments, and Soil Stability.

U.C. Berkeley, Environmental Science Program Teaching Assistant for Environmental Science 10.

Academic Grants Awarded:

California Integrated Waste Management Board. $41,000 grant awarded to UCLA Institute of the Environment.

Goal: To investigate effect of high carbon wood ash on volatile organic emissions from compost. 2001.

Synagro Technologies, Corona California: $10,000 grant awarded to San Diego State University.

Goal: investigate effect of biosolids for restoration and remediation of degraded coastal sage soils. 2000.

King County, Department of Research and Technology, Washington State. $100,000 grant awarded to University of Washington: Goal: To investigate odor emissions from biosolids application and the effect of polymers and ash on VOC emissions. 1998.

Northwest Biosolids Management Association, Washington State. $20,000 grant awarded to investigate effect of polymers and ash on VOC emissions from biosolids. 1997.

Paul E. Rosenfeld, Ph.D. Page 8 of 12 October 2022

James River Corporation, Oregon: $10,000 grant was awarded to investigate the success of genetically engineered Poplar trees with resistance to round-up. 1996.

United State Forest Service, Tahoe National Forest: $15,000 grant was awarded to investigating fire ecology of the Tahoe National Forest. 1995.

Kellogg Foundation, Washington D.C. $500 grant was awarded to construct a large anaerobic digester on St. Kitts in West Indies. 1993

Deposition and/or Trial Testimony:

In the Superior Court of the State of California, County of San Bernardino Billy Wildrick, Plaintiff vs. BNSF Railway Company
Case No. CIVDS1711810
Rosenfeld Deposition 10-17-2022

In the State Court of Bibb County, State of Georgia
Richard Hutcherson, Plaintiff vs Norfolk Southern Railway Company Case No. 10-SCCV-092007
Rosenfeld Deposition 10-6-2022

In the Civil District Court of the Parish of Orleans, State of Louisiana Millard Clark, Plaintiff vs. Dixie Carriers, Inc. et al.

Case No. 2020-03891
Rosenfeld Deposition 9-15-2022

In The Circuit Court of Livingston County, State of Missouri, Circuit Civil Division Shirley Ralls, Plaintiff vs. Canadian Pacific Railway and Soo Line Railroad Case No. 18-LV-CC0020
Rosenfeld Deposition 9-7-2022

In The Circuit Court of the 13th Judicial Circuit Court, Hillsborough County, Florida Civil Division Jonny C. Daniels, Plaintiff vs. CSX Transportation Inc.

Case No. 20-CA-5502
Rosenfeld Deposition 9-1-2022

In The Circuit Court of St. Louis County, State of Missouri Kieth Luke et. al. Plaintiff vs. Monsanto Company et. al.

Case No. 19SL-CC03191
Rosenfeld Deposition 8-25-2022

In The Circuit Court of the 13th Judicial Circuit Court, Hillsborough County, Florida Civil Division Jeffery S. Lamotte, Plaintiff vs. CSX Transportation Inc.

Case No. NO. 20-CA-0049
Rosenfeld Deposition 8-22-2022

In State of Minnesota District Court, County of St. Louis Sixth Judicial District Greg Bean, Plaintiff vs. Soo Line Railroad Company
Case No. 69-DU-CV-21-760
Rosenfeld Deposition 8-17-2022

In United States District Court Western District of Washington at Tacoma, Washington John D. Fitzgerald Plaintiff vs. BNSF
Case No. 3:21-cv-05288-RJB
Rosenfeld Deposition 8-11-2022

Paul E. Rosenfeld, Ph.D. Page 9 of 12 October 2022

In Circuit Court of the Sixth Judicial Circuit, Macon Illinois Rocky Bennyhoff Plaintiff vs. Norfolk Southern
Case No. 20-L-56
Rosenfeld Deposition 8-3-2022

In Court of Common Pleas, Hamilton County Ohio
Joe Briggins Plaintiff vs. CSX
Case No. A2004464
Rosenfeld Deposition 6-17-2022

In the Superior Court of the State of California, County of Kern George LaFazia vs. BNSF Railway Company.

Case No. BCV-19-103087
Rosenfeld Deposition 5-17-2022

In the Circuit Court of Cook County Illinois
Bobby Earles vs. Penn Central et. al.

Case No. 2020-L-000550
Rosenfeld Deposition 4-16-2022

In United States District Court Easter District of Florida Albert Hartman Plaintiff vs. Illinois Central
Case No. 2:20-cv-1633
Rosenfeld Deposition 4-4-2022

In the Circuit Court of the 4
th Judicial Circuit, in and For Duval County, Florida
Barbara Steele vs. CSX Transportation
Case No.16-219-Ca-008796
Rosenfeld Deposition 3-15-2022

In United States District Court Easter District of New York Romano et al. vs. Northrup Grumman Corporation
Case No. 16-cv-5760
Rosenfeld Deposition 3-10-2022

In the Circuit Court of Cook County Illinois
Linda Benjamin vs. Illinois Central
Case No. No. 2019 L 007599
Rosenfeld Deposition 1-26-2022

In the Circuit Court of Cook County Illinois
Donald Smith vs. Illinois Central
Case No. No. 2019 L 003426
Rosenfeld Deposition 1-24-2022

In the Circuit Court of Cook County Illinois
Jan Holeman vs. BNSF
Case No. 2019 L 000675
Rosenfeld Deposition 1-18-2022

In the State Court of Bibb County State of Georgia
Dwayne B. Garrett vs. Norfolk Southern
Case No. 20-SCCV-091232
Rosenfeld Deposition 11-10-2021

Paul E. Rosenfeld, Ph.D. Page 10 of 12 October 2022

In the Circuit Court of Cook County Illinois
Joseph Ruepke vs. BNSF
Case No. 2019 L 007730
Rosenfeld Deposition 11-5-2021

In the United States District Court For the District of Nebraska Steven Gillett vs. BNSF
Case No. 4:20-cv-03120
Rosenfeld Deposition 10-28-2021

In the Montana Thirteenth District Court of Yellowstone County James Eadus vs. Soo Line Railroad and BNSF
Case No. DV 19-1056
Rosenfeld Deposition 10-21-2021

In the Circuit Court Of The Twentieth Judicial Circuit, St Clair County, Illinois Martha Custer et al.cvs. Cerro Flow Products, Inc.

Case No. 0i9-L-2295
Rosenfeld Deposition 5-14-2021
Trial October 8-4-2021

In the Circuit Court of Cook County Illinois
Joseph Rafferty vs. Consolidated Rail Corporation and National Railroad Passenger Corporation d/b/a

AMTRAK,
Case No. 18-L-6845
Rosenfeld Deposition 6-28-2021

In the United States District Court For the Northern District of Illinois Theresa Romcoe vs. Northeast Illinois Regional Commuter Railroad Corporation d/b/a METRA Rail Case No. 17-cv-8517
Rosenfeld Deposition 5-25-2021

In the Superior Court of the State of Arizona In and For the Cunty of Maricopa Mary Tryon et al. vs. The City of Pheonix v. Cox Cactus Farm, L.L.C., Utah Shelter Systems, Inc.

Case No. CV20127-094749
Rosenfeld Deposition 5-7-2021

In the United States District Court for the Eastern District of Texas Beaumont Division Robinson, Jeremy et al vs. CNA Insurance Company et al.

Case No. 1:17-cv-000508
Rosenfeld Deposition 3-25-2021

In the Superior Court of the State of California, County of San Bernardino Gary Garner, Personal Representative for the Estate of Melvin Garner vs. BNSF Railway Company.

Case No. 1720288
Rosenfeld Deposition 2-23-2021

In the Superior Court of the State of California, County of Los Angeles, Spring Street Courthouse Benny M Rodriguez vs. Union Pacific Railroad, A Corporation, et al.

Case No. 18STCV01162
Rosenfeld Deposition 12-23-2020

In the Circuit Court of Jackson County, Missouri
Karen Cornwell, Plaintiff, vs. Marathon Petroleum, LP, Defendant.

Case No. 1716-CV10006
Rosenfeld Deposition 8-30-2019

Paul E. Rosenfeld, Ph.D. Page 11 of 12 October 2022

In the United States District Court For The District of New Jersey Duarte et al, Plaintiffs, vs. United States Metals Refining Company et. al. Defendant.

Case No. 2:17-cv-01624-ES-SCM
Rosenfeld Deposition 6-7-2019

In the United States District Court of Southern District of Texas Galveston Division M/T Carla Maersk vs. Conti 168., Schiffahrts-GMBH & Co. Bulker KG MS “Conti Perdido” Defendant.

Case No. 3:15-CV-00106 consolidated with 3:15-CV-00237
Rosenfeld Deposition 5-9-2019

In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica Carole-Taddeo-Bates et al., vs. Ifran Khan et al., Defendants Case No. BC615636
Rosenfeld Deposition 1-26-2019

In The Superior Court of the State of California In And For The County Of Los Angeles – Santa Monica The San Gabriel Valley Council of Governments et al. vs El Adobe Apts. Inc. et al., Defendants Case No. BC646857
Rosenfeld Deposition 10-6-2018; Trial 3-7-19

In United States District Court For The District of Colorado Bells et al. Plaintiffs vs. The 3M Company et al., Defendants Case No. 1:16-cv-02531-RBJ
Rosenfeld Deposition 3-15-2018 and 4-3-2018

In The District Court Of Regan County, Texas, 112
th Judicial District
Phillip Bales et al., Plaintiff vs. Dow Agrosciences, LLC, et al., Defendants Cause No. 1923
Rosenfeld Deposition 11-17-2017

In The Superior Court of the State of California In And For The County Of Contra Costa Simons et al., Plaintifs vs. Chevron Corporation, et al., Defendants Cause No. C12-01481
Rosenfeld Deposition 11-20-2017

In The Circuit Court Of The Twentieth Judicial Circuit, St Clair County, Illinois Martha Custer et al., Plaintiff vs. Cerro Flow Products, Inc., Defendants Case No.: No. 0i9-L-2295
Rosenfeld Deposition 8-23-2017

In United States District Court For The Southern District of Mississippi Guy Manuel vs. The BP Exploration et al., Defendants
Case No. 1:19-cv-00315-RHW
Rosenfeld Deposition 4-22-2020

In The Superior Court of the State of California, For The County of Los Angeles Warrn Gilbert and Penny Gilber, Plaintiff vs. BMW of North America LLC Case No. LC102019 (c/w BC582154)
Rosenfeld Deposition 8-16-2017, Trail 8-28-2018

In the Northern District Court of Mississippi, Greenville Division Brenda J. Cooper, et al., Plaintiffs, vs. Meritor Inc., et al., Defendants Case No. 4:16-cv-52-DMB-JVM
Rosenfeld Deposition July 2017

Paul E. Rosenfeld, Ph.D. Page 12 of 12 October 2022

In The Superior Court of the State of Washington, County of Snohomish Michael Davis and Julie Davis et al., Plaintiff vs. Cedar Grove Composting Inc., Defendants Case No. 13-2-03987-5
Rosenfeld Deposition, February 2017
Trial March 2017

In The Superior Court of the State of California, County of Alameda Charles Spain., Plaintiff vs. Thermo Fisher Scientific, et al., Defendants Case No. RG14711115
Rosenfeld Deposition September 2015

In The Iowa District Court In And For Poweshiek County
Russell D. Winburn, et al., Plaintiffs vs. Doug Hoksbergen, et al., Defendants Case No. LALA002187
Rosenfeld Deposition August 2015

In The Circuit Court of Ohio County, West Virginia
Robert Andrews, et al. v. Antero, et al.

Civil Action No. 14-C-30000
Rosenfeld Deposition June 2015

In The Iowa District Court for Muscatine County
Laurie Freeman et. al. Plaintiffs vs. Grain Processing Corporation, Defendant Case No. 4980
Rosenfeld Deposition May 2015

In the Circuit Court of the 17
th Judicial Circuit, in and For Broward County, Florida Walter Hinton, et. al. Plaintiff, vs. City of Fort Lauderdale, Florida, a Municipality, Defendant.

Case No. CACE07030358 (26)
Rosenfeld Deposition December 2014

In the County Court of Dallas County Texas
Lisa Parr et al, Plaintiff, vs. Aruba et al, Defendant.

Case No. cc-11-01650-E
Rosenfeld Deposition: March and September 2013
Rosenfeld Trial April 2014

In the Court of Common Pleas of Tuscarawas County Ohio
John Michael Abicht, et al., Plaintiffs, vs. Republic Services, Inc., et al., Defendants Case No. 2008 CT 10 0741 (Cons. w/ 2009 CV 10 0987)
Rosenfeld Deposition October 2012

In the United States District Court for the Middle District of Alabama, Northern Division James K. Benefield, et al., Plaintiffs, vs. International Paper Company, Defendant.

Civil Action No. 2:09-cv-232-WHA-TFM
Rosenfeld Deposition July 2010, June 2011

In the Circuit Court of Jefferson County Alabama
Jaeanette Moss Anthony, et al., Plaintiffs, vs. Drummond Company Inc., et al., Defendants Civil Action No. CV 2008-2076
Rosenfeld Deposition September 2010

In the United States District Court, Western District Lafayette Division Ackle et al., Plaintiffs, vs. Citgo Petroleum Corporation, et al., Defendants.

Case No. 2:07CV1052
Rosenfeld Deposition July 2009




 






  
 


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APPENDIX B

CALEEMOD DETAILED REPORT

APPENDIX C

HEALTH RISK ASSESSMENT

Arcadia Town Center

CONSTRUCTION HEALTH RISK ASSESSMENT

CITY OF ARCADIA
PREPARED BY:

Haseeb Qureshi
[email protected]
Michael Tirohn
[email protected]
FEBRUARY 17, 2025
16493-03 HRA Report

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
i

TABLE OF CONTENTS
TABLE OF CONTENTS ............................................................................................................................. I APPENDICES .......................................................................................................................................... I LIST OF EXHIBITS .................................................................................................................................. II LIST OF TABLES ................................................................................................................ .................... II LIST OF ABBREVIATED TERMS ............................................................................................................. III EXECUTIVE SUMMARY ......................................................................................................................... 1 1 INTRODUCTION ........................................................................................................................... 2

1.1 Site Location .................................................................................................................................. 2

1.2 Project Description ........................................................................................................................ 3 2 BACKGROUND............................................................................................................................. 6

2.1 Background on Recommended Methodology .............................................................................. 6

2.2 Construction Health Risk Assessment ........................................................................................... 6

2.3 Exposure Quantification................................................................................................................ 9

2.4 Carcinogenic Chemical Risk ......................................................................................................... 10

2.5 Non-carcinogenic Exposures ....................................................................................................... 11

2.6 Potential Project DPM-Source Cancer and Non-Cancer Risks .................................................... 12 3 REFERENCES .............................................................................................................................. 15 4 CERTIFICATIONS ........................................................................................................................ 17

APPENDICES
APPENDIX 2.1: CALEEMOD OUTPUTS AND EMISSION CALCULATIONS APPENDIX 2.2: AERMOD MODEL INPUT/OUTPUT
APPENDIX 2.3: RISK CALCULATIONS
APPENDIX 2.4: MODELED RECEPTORS

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
ii

LIST OF EXHIBITS
EXHIBIT 1-A: LOCATION MAP .............................................................................................................. 4 EXHIBIT 2-A: MODELED CONSTRUCTION EMISSION SOURCES .............................................................. 8 EXHIBIT 2-B: RECEPTOR LOCATIONS .................................................................................................. 13

LIST OF TABLES
TABLE ES-1: SUMMARY OF CONSTRUCTION CANCER AND NON-CANCER RISKS ................................... 1 TABLE 2-1: CONSTRUCTION DURATION ................................................................................................ 6 TABLE 2-2: CONSTRUCTION EQUIPMENT ASSUMPTIONS ...................................................................... 7 TABLE 2-5: AERMOD MODEL PARAMETERS .......................................................................................... 9 TABLE 2-3: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK ................................................ 10

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
iii

LIST OF ABBREVIATED TERMS
(1) Reference
μg Microgram
AERMOD American Meteorological Society/Environmental
Protection Agency Regulatory Model
ASF Age Sensitivity Factor
AQMD Air Quality Management District
ARB Air Resources Board
CEQA California Environmental Quality Act
CPF Cancer Potency Factor
DPM Diesel Particulate Matter
EMFAC Emission Factor Model
EPA Environmental Protection Agency
FAH Fraction of Time at Home
HHD Heavy Heavy-Duty
HI Hazard Index
HRA Health Risk Assessment
IS/MND Initial Study/Mitigated Negative Declaration
LHD Light Heavy-Duty
MEIR Maximally Exposed Individual Receptor
MHD Medium Heavy-Duty
NAD North American Datum
NED National Elevation Dataset
OEHHA Office of Environmental Health Hazard Assessment
PM
10 Particulate Matter 10 microns in diameter or less
Project Arcadia Town Center
REL Reference Exposure Level
RM Recommended Measures
SCAQMD South Coast Air Quality Management District
SRA Source Receptor Area
TAC Toxic Air Contaminant
URF Unit Risk Factor
UTM Universal Transverse Mercator
VMT Vehicle Miles Traveled
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report

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Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
1 EXECUTIVE SUMMARY
This report evaluates the potential health risk im pacts to sensitive receptors (which are residents) associated with the development of the Project, more specifically, health risk impacts as a result of exposure to Toxic Air Contaminants (TACs) including diesel particulate matter (DPM) as a result of heavy-duty diesel trucks and construction equi pment used during construction of the proposed Project. This section summarizes the significance criteria and Project health risks.

The results of the health risk assessment fr om Project construction-generated DPM emissions are provided in Table ES-1 below for the Project. Because the proposed Project would not generate TAC emissions during long-term operation, an operational HRA is not required.

C

ONSTRUCTION IMPACTS
The land use with the greatest potential exposure to Project construction-source DPM emissions is Location R1 which is located approximately 406 feet northwest of the Project site at an existing residence located at 200 San Miguel Drive. R1 is placed in the private outdoor living areas (backyard) facing the Project site. At the maxi mally exposed individual receptor (MEIR), the maximum incremental cancer risk attributable to Project construction-source DPM emissions is estimated at 3.57 in one million, which is less than the SCAQMD’s significance threshold of 10 in one million. At this same location, non-cancer ri sks were estimated to be less than 0.01, which would not exceed the applicable threshold of 1. 0. Although Location R1 is not the nearest receptor to the Project site, it would experi ence the highest concentrations of DPM during Project construction due to meteorological conditions in the vicinity of the Project site. Because all other modeled receptors would experience lower concentrations of DPM during Project construction, all other receptors in the vicinity of the Project would be exposed to less emissions and therefore less risk than the MEIR identified herein. As such, the Project will not cause a significant human health or cancer risk to adjacent land uses as a result of Project construction activity. All other receptors during construction ac tivity would experience less risk than what is identified for this location. The modeled receptors are illustrated on Exhibit 2-B.

TABLE ES-1: SUMMARY OF CONSTRUCTION CANCER AND NON-CANCER RISKS Time Period Location
Maximum
Lifetime
Cancer Risk
(Risk per
Million)
Significance
Threshold
(Risk per
Million)
Exceeds
Significance
Threshold

2.40 Year
Exposure1
Maximum Exposed Sensitive Receptor
(Location R1) 3.57 10 NO
Time Period Location
Maximum
Hazard
Index
Significance
Threshold
Exceeds
Significance
Threshold
Annual
Average
Maximum Exposed Sensitive Receptor
(Location R1) <0.01 1.0 NO
1 2.40 years Is the expected duration of construction activities.

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
2 1 INTRODUCTION
This HRA has been prepared in accordance with the document Health Risk Assessment Guidance for Analyzing Cancer Risk from Mobile Source Diesel Idling Emissions for CEQA Air Quality Analysis (1) and is comprised of all relevant and appropriate procedures presented by the United States Environmental Protection Agency (U.S. EPA), Ca lifornia EPA and SCAQMD. Cancer risk is expressed in terms of expected incremental in cidence per million population. The SCAQMD has established an incidence rate of ten (10) p ersons per million as the maximum acceptable incremental cancer risk due to TAC exposure from a project such as the proposed Project. This threshold serves to determine whether or not a given project has a potentially significant development-specific and cumulatively considerable impact.

The AQMD has published a report on how to address cumulative impacts from air pollution: White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution (2). In this report the AQMD states (Page D-3):
“…the AQMD uses the same significance thresholds for project specific and cumulative impacts for all environmental topics analyzed in an Environm ental Assessment or EIR. The only case where the significance thresholds for project specific and cumulative impacts differ is the Hazard Index (HI) significance threshold for toxic air contaminant (TAC) emissions. The project specific (project increment) significance threshold is HI > 1.0 while the cumulative (facility-wide) is HI > 3.0. It should be noted that the HI is only one of three TAC emission significance thresholds considered (when applicable) in a CEQA analysis. The other two are the maximum individual cancer risk (MICR) and the cancer burden, both of which use the same significance thresholds (MICR of 10 in 1 million and cancer burden of 0.5) for project specific and cumulative impacts.

Projects that exceed the project-specific significance thresholds are considered by the SCAQMD to be cumulatively considerable. This is the reason project-specific and cumulative significance thresholds are the same. Conversely, projects that do no t exceed the project-specific thresholds are generally not considered to be cumulatively significant.” The SCAQMD has also established non-carcinogenic risk parameters for use in HRAs. Non- carcinogenic risks are quantified by calculating a "hazard index," expressed as the ratio between the ambient pollutant concentration and its toxicity or Reference Exposure Level (REL). A REL is a concentration at or below which health effects are not likely to occur. A hazard index less than one (1.0) means that adverse health effects are not expected. In this HRA, non-carcinogenic exposures of less than 1.0 are considered less-t han-significant. Both the cancer risk and non- carcinogenic risk thresholds are applied to the nearest sensitive receptors below.

1.1 S ITE LOCATION
The proposed Project is located at the northwes t corner of Santa Anita Avenue and Huntington Drive in the City of Arcadia. The Project’s location in relation to the surrounding area is shown on Exhibit 1-A.

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
3 1.2 P ROJECT DESCRIPTION
The Project consists of the development of a mixed-use development on the approximately 2.27- acre site consisting of 181 residential dwelling units, 3,890 square feet (sf) of residential amenities, 38,713 sf of public and private open space, and 13,130 sf of ground-floor commercial uses.

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
4 EXHIBIT 1-A: LOCATION MAP

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
5 This page intentionally left blank

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
6 2 BACKGROUND

2.1 B ACKGROUND ON RECOMMENDED METHODOLOGY
This HRA is based on applicable guidelines to produce conservative estimates of human health risk posed by exposure to DPM. The conservative n ature of this analysis is due primarily to the following factors:
x The ARB-adopted diesel exhaust Unit Risk Factor (URF) of 300 in one million per μg/m3 is based upon the upper 95 percentile of estimated risk for each of the epidemiological studies utilized to develop the URF. Using the 95th percentile URF represents a very conservative (health-protective) risk posed by DPM because it represents breathing rates that are high for the human body.

2.2 C ONSTRUCTION HEALTH RISK ASSESSMENT

2.2.1 E MISSIONS CALCULATIONS
The emissions calculations for the construction HRA component are based on an assumed mix of construction equipment and hauling activity as presented in the Arcadia Town Center Initial Study/Mitigated Negative Declaration (“IS/MND”) prepared by Psomas (3).

Construction related DPM emissions are expected to occur primarily as a function of the operation of heavy-duty construction equipment.

As discussed in the IS/MND, the Project would result in approximately 627 total working days of construction activity. The construction duration by phase is shown on Table 2-1. It should be noted that the dates modeled in the IS/MND are conservative in nature and overstate potential impacts should construction occur anytime after the dates identified in Table 2-1 since emissions decrease due to the turnover of an older flee t of construction equipment being replaced by newer less polluting equipment as the analys is year increases. A detailed summary of construction equipment assumptions by phase is provided at Table 2-2. The CalEEMod emissions outputs are presented in Appendix 2.1. The mode led emission sources for construction activity are illustrated on Exhibit 2-A. It should be note d that emissions from overlapping construction activities is accounted for in the analysis.

TABLE 2-1: CONSTRUCTION DURATION
Construction Activity Start Date End Date Days
Demolition 1/1/2024 1/19/2024 15
Site Preparation 1/20/2024 1/26/2024 5
Grading 1/27/2024 5/26/2024 85
Building Construction 5/27/2024 5/26/2026 522
Paving 3/27/2026 5/26/2026 43
Architectural Coating 2/25/2026 5/25/2026 64
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
7 TABLE 2-2: CONSTRUCTION EQUIPMENT ASSUMPTIONS
Construction Activity Equipment Amount Hours Per Day
Demolition
Concrete/Industrial Saws 1 8
Tractors/Loaders/Backhoes 3 8
Rubber Tired Dozers 1 8
Site Preparation
Tractors/Loaders/Backhoes 1 7
Graders 1 8
Scrapers 1 8
Grading
Graders 1 8
Rubber Tired Dozers 1 8
Tractors/Loaders/Backhoes 2 7
Building Construction
Cranes 1 8
Forklifts 2 7
Generator Sets 1 8
Tractors/Loaders/Backhoes 1 6
Welders 3 8
Pavers 1 8
Paving Equipment 1 8
Rollers 2 8
Cement and Mortar Mixers 1 8
Tractors/Loaders/Backhoes 1 8
Architectural Coating Air Compressors 1 6

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
8 EXHIBIT 2-A: MODELED CONSTRUCTION EMISSION SOURCES

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
9 2.3 E XPOSURE QUANTIFICATION
The analysis herein has been conducted in accord ance with the guidelines in the Health Risk Assessment Guidance for Analyzing Cancer Risks fr om Mobile Source Diesel Idling Emissions for CEQA Air Quality Analysis (1). The Environm ental Protection Agency’s (U.S. EPA’s) AERMOD model has been utilized. For purposes of this analysis, the Lakes AERMOD View (Version 13.0.0) was used to calculate annual average particulate concentrations associated with site operations.

Lakes AERMOD View was utilized to incorporate the U.S. EPA’s latest AERMOD Version 24142 (4).

The model offers additional flexibility by allowing the user to assign an initial release height and vertical dispersion parameters for mobile sources representative of a roadway. For this HRA, the roadways were modeled as adjacent volume so urces. Roadways were modeled using the U.S.

EPA’s haul route methodology for modeling construction haul truck and vendor truck movement.

More specifically, the Haul Road Volume Source Calculator in Lakes AERMOD View has been utilized to determine the release height para meters. Based on the US EPA methodology, the Project’s modeled sources would result in a release height of 3.49 meters and an initial lateral dimension of 4.0 meters, and an initial vertical dimension of 3.25 meters.

Model parameters are presented in Table 2-5 (5). The model requires additional input parameters including emission data and local meteorology. Meteorological data from the SCAQMD’s Azusa monitoring station was used to represent local weather conditions and prevailing winds (6).

TABLE 2-5: AERMOD MODEL PARAMETERS
Dispersion Coefficient (Urban/Rural) Urban (population 9,663,345) Terrain (Flat/Elevated) Elevated (Regulatory Default)
Averaging Time 1 year (5-year Meteorological Data Set)
Receptor Height 0 meters (Regulatory Default)
Universal Transverse Mercator (UTM) coordinates for World Geodetic System (WGS) 84 were used to locate the Project site boundaries, each volume source location, and receptor locations in the Project vicinity. The AERMOD dispersion model summary output files for the Project are presented in Appendix 2.2. Modeled sensitive receptors were placed at residential and non- residential locations.

Receptors may be placed at applicable struct ure locations for residential property and not necessarily the boundaries of the properties containing these uses because the human receptors spend a majority of their time at the residence’s building, and not on the property line. It should be noted that the primary purpose of receptor placement is focused on long-term exposure.

Notwithstanding, as a conservative measure, receptors were placed at either the outdoor living area or the building façade, whichever is closer to the Project site.

For purposes of this HRA, receptor s include residential land uses in the vicinity of the Project.

These receptors are included in the HRA since residents may be exposed at these locations over the course of Project construction. This met hodology is consistent with SCAQMD and OEHHA recommended guidance.

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
10 Any impacts to residents located further away from the Project site than the modeled receptors would have a lesser impact than what has already been disclosed in the HRA at the MEIR because concentrations dissipate with distance.

All receptors were set to existing elevation he ight so that only ground-level concentrations are analyzed. United States Geological Survey (USG S) National Elevation Data (NED) terrain data using AERMAP was utilized in the HRA modeling to set elevations (7).

Discrete variants for daily breathing rates, exposure frequency, and exposure duration were obtained from relevant distribution profiles presented in the 2015 OEHHA Guidelines. Table 2-3 summarizes the exposure parameters for Residents based on 2015 OEHHA Guidelines. Appendix

2.3 includes the detailed risk calculation.

TABLE 2-3: EXPOSURE ASSUMPTIONS FOR INDIVIDUAL CANCER RISK Age Daily
Breathing
Rate (L/kg-
day)
Age
Specific
Factor
Exposure
Duration
(years)
Fraction
of Time
at Home
Exposure
Frequency
(days/year)
Exposure
Time
(hours/day)
-0.25 to 0 361 10 0.25 1.00 250 8
0 to 2 1,090 10 2.00 1.00 250 8
2 to 16 572 3 0.15 1.00 250 8

2.4 C ARCINOGENIC CHEMICAL RISK
Excess cancer risks are estimated as the upper-boun d incremental probability that an individual will develop cancer over a lifetime as a direct res ult of exposure to potential carcinogens over a specified exposure duration. The estimated risk is expressed as a unitless probability. The cancer risk attributed to a chemical is calculated by multiplying the chemical intake or dose at the human exchange boundaries (e.g., lungs) by the chemical-specific cancer potency factor (CPF). A risk level of 10 in one million implies a likelihood that up to 10 people, out of one million equally exposed people would contract cancer if exposed continuously (24 hours per day) to the levels of toxic air contaminants over a specified duration of time.

Guidance from CARB and the California En vironmental Protection Agency, Office of Environmental Health Hazard Assessment (OEHHA) recommends a refinement to the standard point estimate approach when alternate human body weights and breathing rates are utilized to assess risk for susceptible subpopulations such as children. For the inhalation pathway, the procedure requires the incorporation of several discrete variates to effectively quantify dose.

Once determined, contaminant dose is multiplied by the cancer potency factor (CPF) in units of inverse dose expressed in milligrams per kilogram per day (mg/kg/day) -1 to derive the cancer risk
estimate. Therefore, to assess exposures, the following dose algorithm was utilized. ஺ூோ =஺ூோ ×ܴܤ
ܹܤ×ܣ×൰ × (1×1 0 ି଺)
Where:

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
11 ஺ூோ = chronic daily intake (mg/kg/day)
஺ூோ = concentration of contaminant in air ( μg/m3)
஻ோ
஻ௐ = daily breathing rate normalized to body weight
(L/kg BW-day)
ܣinhalation absorption factor
ܨܧexposure frequency (days/365 days)
ܹܤbody weight (kg)
1×1 0 ି଺ = conversion factors ( μg to mg, L to m3)

஺ூோ =஺ூோ ×ܨܲܥ×ܨܵܣ×ܪܣܨ×ܦܧ
ܶܣ
Where:
஺ூோ = chronic daily intake (mg/kg/day)
ܨܲܥcancer potency factor
ܨܵܣage sensitivity factor
ܨܵܣfraction of time at home
ܦܧnumber of years within particular age group
ܶܣaveraging time

2.5 N ON-CARCINOGENIC EXPOSURES
An evaluation of the potential noncarcinogenic effects of chronic exposures was also conducted.

Adverse health effects are evaluated by compar ing a compound’s annual concentration with its toxicity factor or Reference Exposure Level (REL ). The REL for diesel particulates was obtained from OEHHA for this analysis. The chronic reference exposure level (REL) for DPM was established by OEHHA as 5 μg/m3 (8).

Non-cancer health effects are expressed as a hazard index (HI), which is calculated using the following equation:
஽௉ெ =஽௉ெ
஽௉ெ

Where:
஽௉ெ = Hazard index (unitless)
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
12 ஽௉ெ = Annual average DPM concentration ( μg/m3)
஽௉ெ = REL for DPM (the DPM concentration at which no adverse health effects are anticipated).

2.6 P OTENTIAL PROJECT DPM-SOURCE CANCER AND NON-CANCER RISKS

CONSTRUCTION IMPACTS
The land use with the greatest potential exposure to Project construction-source DPM emissions is Location R1 which is located approximately 406 feet northwest of the Project site at an existing residence located at 200 San Miguel Drive. R1 is placed in the private outdoor living areas (backyard) facing the Project site. At the MEIR, the maximum incremental cancer risk attributable to Project construction-source DPM emissions is estimated at 3.57 in one million, which is less than the SCAQMD’s significance threshold of 10 in one million. At this same location, non-cancer risks were estimated to be less than 0.01, whic h would not exceed the applicable threshold of

1.0. Although Location R1 is not the nearest receptor to the Project site, it would experience the highest concentrations of DPM during Project cons truction due to meteorological conditions in the vicinity of the Project site. Because all other modeled receptors would experience lower concentrations of DPM during Project construction , all other receptors in the vicinity of the Project would be exposed to less emissions and therefore less risk than the MEIR identified herein. As such, the Project will not cause a signif icant human health or cancer risk to adjacent land uses as a result of Project construction activity. All other receptors during construction activity would experience less risk than what is identified for this location. The modeled receptors are illustrated on Exhibit 2-B.

It should be noted that the receptors presente d in Exhibit 2-B do not represent all modeled receptors, rather it is intended to represent the nearest and/or most impacted receptors. A total of 54 receptors were modeled in the vicinity of the Project site. Appendix 2.4 graphically presents all modeled receptors.

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
13 EXHIBIT 2-B: RECEPTOR LOCATIONS

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Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
15 3 REFERENCES

1. South Coast Air Quality Managment District. Mobile Source Toxics Analysis. [Online] 2003. http://www.aqmd.gov/ceqa/handbook/mobile_toxic/mobile_toxic.html.

2. Goss, Tracy A and Kroeger, Amy. White Paper on Potential Control Strategies to Address Cumulative Impacts from Air Pollution. [Online] South Coast Air Quality Management District, 2003. [Cited: June 6, 2019.] http://www.aqmd.gov/docs/default-sour ce/Agendas/Environmental-Justice/cumulative- impacts-working-group/cumulative-impacts-white-paper.pdf?sfvrsn=2.

3. Psomas. Arcadia Town Center Project Initial Study/Mitigated Negative Declaration. 2024.

4. Environmental Protection Agency. User's Guide for the AMS/E PA Regulatory Model (AERMOD). [Online] June 2022.
https://gaftp.epa.gov/Air/aqmg/SCRAM/models/preferred/aermod/aermod_userguide.pdf.

5. —. User's Guide for the AMS/EPA Regu latory Model (AERMOD). [Online] April 2018. https://www3.epa.gov/ttn/scram/models/aermod/aermod_userguide.pdf.

6. South Coast Air Quality Management District. Data for AERMOD. [Online] [Cited: May 9, 2022.] https://www.aqmd.gov/home/air-quality/air-quality-data-studies/meteorological-data/data-for- aermod.

7. Environmental Protection Agency. User's Guide for the AERMOD Terrain Preprocessor (AERMAP). [Online] 2018.
https://gaftp.epa.gov/Air/aqmg/SCRAM/models/related/aermap/aermap_userguide_v18081.pdf.

8. Office of Environmental Health Hazard Assessment. Chemical Toxicity Database. [Online] https://oehha.ca.gov/chemicals.

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Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
17 4 CERTIFICATIONS
The contents of this health risk assessment rep resent an accurate depiction of the impacts to sensitive receptors associated with the proposed Arcadia Town Center Project. The information contained in this health risk assessment report is based on the best available data at the time of preparation. If you have any questions, please contact me at (949) 660-1994.

Haseeb Qureshi
Principal
URBAN CROSSROADS, INC.
(949) 660-1994
[email protected]

EDUCATION
Master of Science in Environmental Studies
California State University, Fullerton • May 2010
Bachelor of Arts in Environmental Analysis and Design
University of California, Irvine • June 2006

PROFESSIONAL AFFILIATIONS
AEP – Association of Environmental Professionals
AWMA – Air and Waste Management Association
ASTM – American Society for Testing and Materials

PROFESSIONAL CERTIFICATIONS
Environmental Site Assessment – American Society for Testing and Materials • June 2013 Planned Communities and Urban Infill – Urban Land Institute • June 2011 Indoor Air Quality and Industrial Hygiene – EMSL Analytical • April 2008 Principles of Ambient Air Monitoring – California Air Resources Board • August 2007 AB2588 Regulatory Standards – Trinity Consultants • November 2006 Air Dispersion Modeling – Lakes Environmental • June 2006

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Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
APPENDIX 2.1:

EMISSION CALCULATIONS

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
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Emissions Phase Lb/Day # Days Emissions Avg/Lb Day Avg/Hourly On-Site Demolition 0.67 15 10.05 0.67 0.08375
Exhaust PM-10 Site Preparation 0.55 5 2.75 0.55 0.06875 Grading 0.74 85 62.9 0.74 0.0925
Building Construction 0.41 522 212.28 0.406666667 0.050833333 Paving 0.25 43 10.75 0.25 0.03125
Architectural Coating 0.02 64 1.28 0.02 0.0025
lb/hour/source

2.64 627 300.01 0.478484848 0.059810606 3.52E-03
Off-Site Demolition 3.00E-02 15 0.45 0.03 0.00375
Exhaust PM-10 Site Preparation 5.00E-03 5 0.025 0.005 0.000625 Grading 6.00E-02 85 5.1 0.06 0.0075
Building Construction 2.00E-02 522 10.44 0.02 0.0025
Paving 0.00E+00 43 0 0 0
Architectural Coating 0.00E+00 64 0 0 0
lb/hour/source

1.15E-01 627 16.015 0.025542265 0.003192783 3.19E-03
Start Date End Date No. Days
1/1/2024 1/19/2024 15
1/20/2024 1/26/2024 5
1/27/2024 5/26/2024 85
5/27/2024 5/26/2026 522
3/27/2026 5/26/2026 43
2/25/2026 5/25/2026 64
627
Phase
Total Days of Construction
Demolition
Site Preparation
Grading
Building Construction
Paving
Architectural Coating
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
APPENDIX 2.2:

AERMOD MODEL INPUT/OUTPUT

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
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EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.01.01.01.01.0
EMISFACTVOL3HRDOW1.01.01.01.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
EMISFACTVOL3HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.01.01.01.01.0
EMISFACTVOL4HRDOW1.01.01.01.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
EMISFACTVOL4HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.01.01.01.01.0
EMISFACTVOL5HRDOW1.01.01.01.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
EMISFACTVOL5HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.01.01.01.01.0
EMISFACTVOL6HRDOW1.01.01.01.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
EMISFACTVOL6HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.01.01.01.01.0
EMISFACTVOL7HRDOW1.01.01.01.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
EMISFACTVOL7HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.01.01.01.01.0
EMISFACTVOL8HRDOW1.01.01.01.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
EMISFACTVOL8HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.01.01.01.01.0
EMISFACTVOL9HRDOW1.01.01.01.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
EMISFACTVOL9HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.01.01.01.01.0
EMISFACTVOL10HRDOW1.01.01.01.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
EMISFACTVOL10HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.01.01.01.01.0
EMISFACTVOL11HRDOW1.01.01.01.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
EMISFACTVOL11HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.01.01.01.01.0
EMISFACTVOL12HRDOW1.01.01.01.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
EMISFACTVOL12HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.01.01.01.01.0
EMISFACTVOL13HRDOW1.01.01.01.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
EMISFACTVOL13HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.01.01.01.01.0
EMISFACTVOL14HRDOW1.01.01.01.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
EMISFACTVOL14HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.01.01.01.01.0
EMISFACTVOL15HRDOW1.01.01.01.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
EMISFACTVOL15HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.01.01.01.01.0
EMISFACTVOL16HRDOW1.01.01.01.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
EMISFACTVOL16HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.01.01.01.01.0
EMISFACTVOL17HRDOW1.01.01.01.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
EMISFACTVOL17HRDOW0.00.00.00.00.00.0
**WeekDays:
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.01.01.01.01.0
EMISFACTL0000001HRDOW1.01.01.01.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.01.01.01.01.0
EMISFACTL0000002HRDOW1.01.01.01.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.01.01.01.01.0
EMISFACTL0000003HRDOW1.01.01.01.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.01.01.01.01.0
EMISFACTL0000004HRDOW1.01.01.01.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.01.01.01.01.0
EMISFACTL0000005HRDOW1.01.01.01.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.01.01.01.01.0
EMISFACTL0000006HRDOW1.01.01.01.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.01.01.01.01.0
EMISFACTL0000007HRDOW1.01.01.01.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.01.01.01.01.0
EMISFACTL0000008HRDOW1.01.01.01.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.01.01.01.01.0
EMISFACTL0000009HRDOW1.01.01.01.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.01.01.01.01.0
EMISFACTL0000010HRDOW1.01.01.01.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.01.01.01.01.0
EMISFACTL0000011HRDOW1.01.01.01.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.01.01.01.01.0
EMISFACTL0000012HRDOW1.01.01.01.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.01.01.01.01.0
EMISFACTL0000013HRDOW1.01.01.01.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.01.01.01.01.0
EMISFACTL0000014HRDOW1.01.01.01.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.01.01.01.01.0
EMISFACTL0000015HRDOW1.01.01.01.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.01.01.01.01.0
EMISFACTL0000016HRDOW1.01.01.01.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.01.01.01.01.0
EMISFACTL0000017HRDOW1.01.01.01.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.01.01.01.01.0
EMISFACTL0000018HRDOW1.01.01.01.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.01.01.01.01.0
EMISFACTL0000019HRDOW1.01.01.01.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.01.01.01.01.0
EMISFACTL0000020HRDOW1.01.01.01.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.01.01.01.01.0
EMISFACTL0000021HRDOW1.01.01.01.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.01.01.01.01.0
EMISFACTL0000022HRDOW1.01.01.01.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.01.01.01.01.0
EMISFACTL0000023HRDOW1.01.01.01.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.01.01.01.01.0
EMISFACTL0000024HRDOW1.01.01.01.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.01.01.01.01.0
EMISFACTL0000025HRDOW1.01.01.01.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.01.01.01.01.0
EMISFACTL0000026HRDOW1.01.01.01.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.01.01.01.01.0
EMISFACTL0000027HRDOW1.01.01.01.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.01.01.01.01.0
EMISFACTL0000028HRDOW1.01.01.01.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.01.01.01.01.0
EMISFACTL0000029HRDOW1.01.01.01.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.01.01.01.01.0
EMISFACTL0000030HRDOW1.01.01.01.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.01.01.01.01.0
EMISFACTL0000031HRDOW1.01.01.01.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.01.01.01.01.0
EMISFACTL0000032HRDOW1.01.01.01.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.01.01.01.01.0
EMISFACTL0000033HRDOW1.01.01.01.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.01.01.01.01.0
EMISFACTL0000034HRDOW1.01.01.01.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.01.01.01.01.0
EMISFACTL0000035HRDOW1.01.01.01.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.01.01.01.01.0
EMISFACTL0000036HRDOW1.01.01.01.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.01.01.01.01.0
EMISFACTL0000037HRDOW1.01.01.01.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.01.01.01.01.0
EMISFACTL0000038HRDOW1.01.01.01.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.01.01.01.01.0
EMISFACTL0000039HRDOW1.01.01.01.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.01.01.01.01.0
EMISFACTL0000040HRDOW1.01.01.01.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.01.01.01.01.0
EMISFACTL0000041HRDOW1.01.01.01.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.01.01.01.01.0
EMISFACTL0000042HRDOW1.01.01.01.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.01.01.01.01.0
EMISFACTL0000043HRDOW1.01.01.01.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.01.01.01.01.0
EMISFACTL0000044HRDOW1.01.01.01.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.01.01.01.01.0
EMISFACTL0000045HRDOW1.01.01.01.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.01.01.01.01.0
EMISFACTL0000046HRDOW1.01.01.01.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.01.01.01.01.0
EMISFACTL0000047HRDOW1.01.01.01.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.01.01.01.01.0
EMISFACTL0000048HRDOW1.01.01.01.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.01.01.01.01.0
EMISFACTL0000049HRDOW1.01.01.01.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.01.01.01.01.0
EMISFACTL0000050HRDOW1.01.01.01.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.01.01.01.01.0
EMISFACTL0000051HRDOW1.01.01.01.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.01.01.01.01.0
EMISFACTL0000052HRDOW1.01.01.01.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.01.01.01.01.0
EMISFACTL0000053HRDOW1.01.01.01.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.01.01.01.01.0
EMISFACTL0000054HRDOW1.01.01.01.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.01.01.01.01.0
EMISFACTL0000055HRDOW1.01.01.01.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.01.01.01.01.0
EMISFACTL0000056HRDOW1.01.01.01.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.01.01.01.01.0
EMISFACTL0000057HRDOW1.01.01.01.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.01.01.01.01.0
EMISFACTL0000058HRDOW1.01.01.01.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.01.01.01.01.0
EMISFACTL0000059HRDOW1.01.01.01.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.01.01.01.01.0
EMISFACTL0000060HRDOW1.01.01.01.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.01.01.01.01.0
EMISFACTL0000061HRDOW1.01.01.01.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.01.01.01.01.0
EMISFACTL0000062HRDOW1.01.01.01.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.01.01.01.01.0
EMISFACTL0000063HRDOW1.01.01.01.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.01.01.01.01.0
EMISFACTL0000064HRDOW1.01.01.01.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.01.01.01.01.0
EMISFACTL0000065HRDOW1.01.01.01.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
**Saturday:
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
**Sunday:
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000001HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000002HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000003HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000004HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000005HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000006HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000007HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000008HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000009HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000010HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000011HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000012HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000013HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000014HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000015HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000016HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000017HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000018HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000019HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000020HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000021HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000022HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000023HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000024HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000025HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000026HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000027HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000028HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000029HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000030HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000031HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000032HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000033HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000034HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000035HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000036HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000037HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000038HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000039HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000040HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000041HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000042HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000043HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000044HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000045HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000046HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000047HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000048HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000049HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000050HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000051HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000052HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000053HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000054HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000055HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000056HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000057HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000058HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000059HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000060HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000061HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000062HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000063HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000064HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
EMISFACTL0000065HRDOW0.00.00.00.00.00.0
SRCGROUPALL
SOFINISHED
**
****************************************
**AERMODReceptorPathway
****************************************
**
**
RESTARTING
INCLUDED"16493Cons.rou"
REFINISHED
**
****************************************
**AERMODMeteorologyPathway
****************************************
**
**
MESTARTING
SURFFILEazus_sfc_pfl\AZUS_V11_trimmed.sfc
PROFFILEazus_sfc_pfl\AZUS_V11_trimmed.PFL
SURFDATA31792017

UAIRDATA31902017
SITEDATA603700022017
PROFBASE187.0METERS
MEFINISHED
**
****************************************
**AERMODOutputPathway
****************************************
**
**
OUSTARTING
**AutoŞGeneratedPlotfiles
PLOTFILEPERIODALL"16493Cons.AD\PE00GALL.PLT"31
SUMMFILE"16493Cons.sum"
OUFINISHED
***MessageSummaryForAERMODModelSetup***
ŞŞŞŞŞŞŞŞŞSummaryofTotalMessagesŞŞŞŞŞŞŞŞ

ATotalof0FatalErrorMessage(s)
ATotalof2WarningMessage(s)
ATotalof0InformationalMessage(s)


********FATALERRORMESSAGES********
***NONE***


********WARNINGMESSAGES********
MEW1861287MEOPEN:THRESH_1MIN
1ŞminASOSwindspeedthresholdused
0.50
MEW1871287MEOPEN:ADJ_U*OptionforStableLowWindsusedinAERMET 
***********************************
***SETUPFinishesSuccessfully***
***********************************
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE1
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***MODELSETUPOPTIONSSUMMARY ***
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
**ModelOptionsSelected:
*ModelUsesRegulatoryDEFAULTOptions
*ModelIsSetupForCalculationofAverageCONCentrationValues. *NOGASDEPOSITIONDataProvided.
*NOPARTICLEDEPOSITIONDataProvided.
*ModelUsesNODRYDEPLETION.DDPLETE=F
*ModelUsesNOWETDEPLETION.WETDPLT=F
*StackŞtipDownwash.
*ModelAccountsforELEVatedTerrainEffects.
*UseCalmsProcessingRoutine.
*UseMissingDataProcessingRoutine.
*NoExponentialDecay.
*ModelUsesURBANDispersionAlgorithmfortheSBLfor82Source(s), forTotalof1UrbanArea(s):
UrbanPopulation=9663345.0;UrbanRoughnessLength=1.000m *UrbanRoughnessLengthof1.0MeterUsed.
*ADJ_U*ŞUseADJ_U*optionforSBLinAERMET
*CCVR_SubŞMeteorologicaldataincludesCCVRsubstitutions *TEMP_SubŞMeteorologicaldataincludesTEMPsubstitutions *ModelAssumesNoFLAGPOLEReceptorHeights.
*TheUserSpecifiedaPollutantTypeof:DPM 
**ModelCalculatesPERIODAveragesOnly

**ThisRunIncludes:82Source(s);1SourceGroup(s);and54 Receptor(s)
with:0POINT(s),including
0POINTCAP(s)and0
POINTHOR(s)
and:82VOLUMEsource(s)
and:0AREAtypesource(s)
and:0LINEsource(s)
and:0RLINE/RLINEXTsource(s)
and:0OPENPITsource(s)
and:0BUOYANTLINEsource(s)withatotalof0line(s) and:0SWPOINTsource(s)

**ModelSetToContinueRUNningAftertheSetupTesting. **TheAERMETInputMeteorologicalDataVersionDate:22112 
**OutputOptionsSelected:
ModelOutputsTablesofPERIODAveragesbyReceptor ModelOutputsExternalFile(s)ofHighValuesforPlotting(PLOTFILE Keyword)
ModelOutputsSeparateSummaryFileofHighRankedValues(SUMMFILE Keyword)

**NOTE:TheFollowingFlagsMayAppearFollowingCONCValues:cforCalmHours  m forMissing
Hours
 bforBothCalm andMissingHours

**Misc.Inputs:BaseElev.forPot.Temp.Profile(mMSL)=187.00;Decay Coef.=0.000;Rot.Angle=0.0
EmissionUnits=GRAMS/SEC; EmissionRateUnitFactor=0.10000E+07
OutputUnits=MICROGRAMS/M**3 
**ApproximateStorageRequirements
ofModel=3.6MBofRAM.

**InputRunstreamFile:aermod.inp 
**OutputPrintFile:aermod.out 
**DetailedError/MessageFile:16493Cons.err 
**FileforSummaryofResults:16493Cons.sum 
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE2
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***VOLUMESOURCEDATA*** NUMBEREMISSIONRATEBASERELEASEINIT. INIT.URBANEMISSIONRATEAIRCRAFT
SOURCEPART.(GRAMS/SEC)XYELEV.HEIGHTSY SZSOURCESCALARVARY
IDCATS.(METERS)(METERS)(METERS)(METERS)(METERS) (METERS)BY
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
VOL100.44351EŞ03404806.23778282.5148.71.525.88

1.40YESHRDOWNO
VOL200.44351EŞ03404810.13778192.7146.91.525.88

1.40YESHRDOWNO
VOL300.44351EŞ03404828.63778284.2148.71.525.88

1.40YESHRDOWNO
VOL400.44351EŞ03404848.23778284.2148.71.525.88

1.40YESHRDOWNO
VOL500.44351EŞ03404868.83778285.0148.81.525.88

1.40YESHRDOWNO
VOL600.44351EŞ03404827.83778260.1148.61.525.88

1.40YESHRDOWNO
VOL700.44351EŞ03404849.23778259.9148.51.525.88

1.40YESHRDOWNO
VOL800.44351EŞ03404869.63778260.7148.61.525.88

1.40YESHRDOWNO
VOL900.44351EŞ03404826.23778237.5148.51.525.88

1.40YESHRDOWNO
VOL1000.44351EŞ03404869.43778237.5148.41.525.88

1.40YESHRDOWNO
VOL1100.44351EŞ03404847.43778237.9148.51.525.88

1.40YESHRDOWNO
VOL1200.44351EŞ03404870.43778192.4147.21.525.88

1.40YESHRDOWNO
VOL1300.44351EŞ03404826.43778192.0146.91.525.88

1.40YESHRDOWNO
VOL1400.44351EŞ03404848.63778192.2147.21.525.88

1.40YESHRDOWNO
VOL1500.44351EŞ03404869.83778215.9148.01.525.88

1.40YESHRDOWNO
VOL1600.44351EŞ03404826.63778214.5148.11.525.88

1.40YESHRDOWNO
VOL1700.44351EŞ03404848.23778214.5148.01.525.88

1.40YESHRDOWNO
L000000100.61840EŞ05404899.63778189.7147.43.496.51

3.25YESHRDOWNO
L000000200.61840EŞ05404899.63778203.7147.63.496.51

3.25YESHRDOWNO
L000000300.61840EŞ05404899.63778217.7147.83.496.51

3.25YESHRDOWNO
L000000400.61840EŞ05404899.63778231.7148.03.496.51

3.25YESHRDOWNO
L000000500.61840EŞ05404899.63778245.7148.23.496.51

3.25YESHRDOWNO
L000000600.61840EŞ05404899.63778259.7148.33.496.51

3.25YESHRDOWNO
L000000700.61840EŞ05404899.63778273.7148.53.496.51

3.25YESHRDOWNO
L000000800.61840EŞ05404899.63778287.7148.73.496.51

3.25YESHRDOWNO
L000000900.61840EŞ05404899.63778301.7148.83.496.51

3.25YESHRDOWNO
L000001000.61840EŞ05404899.63778315.7149.03.496.51

3.25YESHRDOWNO
L000001100.61840EŞ05404899.63778329.7149.23.496.51

3.25YESHRDOWNO
L000001200.61840EŞ05404899.63778343.7149.43.496.51

3.25YESHRDOWNO
L000001300.61840EŞ05404899.63778357.7149.63.496.51

3.25YESHRDOWNO
L000001400.61840EŞ05404899.63778371.7150.03.496.51

3.25YESHRDOWNO
L000001500.61840EŞ05404899.63778385.7150.33.496.51

3.25YESHRDOWNO
L000001600.61840EŞ05404899.63778399.7150.63.496.51

3.25YESHRDOWNO
L000001700.61840EŞ05404899.63778413.7150.73.496.51

3.25YESHRDOWNO
L000001800.61840EŞ05404899.63778427.7150.83.496.51

3.25YESHRDOWNO
L000001900.61840EŞ05404899.63778441.7151.03.496.51

3.25YESHRDOWNO
L000002000.61840EŞ05404899.63778455.7151.23.496.51

3.25YESHRDOWNO
L000002100.61840EŞ05404899.63778469.7151.33.496.51

3.25YESHRDOWNO
L000002200.61840EŞ05404899.63778483.7151.53.496.51

3.25YESHRDOWNO
L000002300.61840EŞ05404899.43778497.7151.73.496.51

3.25YESHRDOWNO
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE3
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***VOLUMESOURCEDATA*** NUMBEREMISSIONRATEBASERELEASEINIT. INIT.URBANEMISSIONRATEAIRCRAFT
SOURCEPART.(GRAMS/SEC)XYELEV.HEIGHTSY SZSOURCESCALARVARY
IDCATS.(METERS)(METERS)(METERS)(METERS)(METERS) (METERS)BY
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
L000002400.61840EŞ05404899.33778511.7151.93.496.51

3.25YESHRDOWNO
L000002500.61840EŞ05404899.23778525.7152.23.496.51

3.25YESHRDOWNO
L000002600.61840EŞ05404899.13778539.7152.43.496.51

3.25YESHRDOWNO
L000002700.61840EŞ05404898.93778553.7152.63.496.51

3.25YESHRDOWNO
L000002800.61840EŞ05404898.83778567.7152.83.496.51

3.25YESHRDOWNO
L000002900.61840EŞ05404898.73778581.7153.03.496.51

3.25YESHRDOWNO
L000003000.61840EŞ05404898.63778595.7153.23.496.51

3.25YESHRDOWNO
L000003100.61840EŞ05404898.43778609.7153.73.496.51

3.25YESHRDOWNO
L000003200.61840EŞ05404898.33778623.7154.13.496.51

3.25YESHRDOWNO
L000003300.61840EŞ05404898.23778637.7154.13.496.51

3.25YESHRDOWNO
L000003400.61840EŞ05404898.13778651.7154.23.496.51

3.25YESHRDOWNO
L000003500.61840EŞ05404897.93778665.7154.43.496.51

3.25YESHRDOWNO
L000003600.61840EŞ05404897.83778679.7154.73.496.51

3.25YESHRDOWNO
L000003700.61840EŞ05404897.73778693.7154.63.496.51

3.25YESHRDOWNO
L000003800.61840EŞ05404897.63778707.7154.73.496.51

3.25YESHRDOWNO
L000003900.61840EŞ05404897.43778721.7154.93.496.51

3.25YESHRDOWNO
L000004000.61840EŞ05404897.33778735.7155.13.496.51

3.25YESHRDOWNO
L000004100.61840EŞ05404897.23778749.7155.33.496.51

3.25YESHRDOWNO
L000004200.61840EŞ05404897.13778763.7155.53.496.51

3.25YESHRDOWNO
L000004300.61840EŞ05404896.93778777.7155.73.496.51

3.25YESHRDOWNO
L000004400.61840EŞ05404896.83778791.7155.93.496.51

3.25YESHRDOWNO
L000004500.61840EŞ05404896.73778805.7156.13.496.51

3.25YESHRDOWNO
L000004600.61840EŞ05404896.63778819.7156.33.496.51

3.25YESHRDOWNO
L000004700.61840EŞ05404896.43778833.7156.63.496.51

3.25YESHRDOWNO
L000004800.61840EŞ05404896.43778847.7156.83.496.51

3.25YESHRDOWNO
L000004900.61840EŞ05404896.53778861.7157.13.496.51

3.25YESHRDOWNO
L000005000.61840EŞ05404896.63778875.7157.33.496.51

3.25YESHRDOWNO
L000005100.61840EŞ05404896.83778889.7157.53.496.51

3.25YESHRDOWNO
L000005200.61840EŞ05404896.93778903.7157.83.496.51

3.25YESHRDOWNO
L000005300.61840EŞ05404897.03778917.7158.03.496.51

3.25YESHRDOWNO
L000005400.61840EŞ05404897.23778931.7158.33.496.51

3.25YESHRDOWNO
L000005500.61840EŞ05404897.33778945.7158.53.496.51

3.25YESHRDOWNO
L000005600.61840EŞ05404897.43778959.7158.73.496.51

3.25YESHRDOWNO
L000005700.61840EŞ05404897.63778973.7159.03.496.51

3.25YESHRDOWNO
L000005800.61840EŞ05404897.73778987.7159.23.496.51

3.25YESHRDOWNO
L000005900.61840EŞ05404897.83779001.7159.43.496.51

3.25YESHRDOWNO
L000006000.61840EŞ05404898.03779015.7159.63.496.51

3.25YESHRDOWNO
L000006100.61840EŞ05404898.13779029.7159.83.496.51

3.25YESHRDOWNO
L000006200.61840EŞ05404898.23779043.7160.13.496.51

3.25YESHRDOWNO
L000006300.61840EŞ05404898.33779057.7160.33.496.51

3.25YESHRDOWNO
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE4
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***VOLUMESOURCEDATA*** NUMBEREMISSIONRATEBASERELEASEINIT. INIT.URBANEMISSIONRATEAIRCRAFT
SOURCEPART.(GRAMS/SEC)XYELEV.HEIGHTSY SZSOURCESCALARVARY
IDCATS.(METERS)(METERS)(METERS)(METERS)(METERS) (METERS)BY
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
L000006400.61840EŞ05404898.33779071.7160.63.496.51

3.25YESHRDOWNO
L000006500.61840EŞ05404898.33779085.7160.93.496.51

3.25YESHRDOWNO
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE5
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***SOURCEIDsDEFININGSOURCEGROUPS ***
SRCGROUPIDSOURCEIDs ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞ ALLVOL1,VOL2,VOL3,VOL4,VOL5, VOL6,VOL7,VOL8,
VOL9,VOL10,VOL11,VOL12,VOL13, VOL14,VOL15,VOL16,
VOL17,L0000001,L0000002,L0000003,L0000004, L0000005,L0000006,L0000007,
L0000008,L0000009,L0000010,L0000011,L0000012, L0000013,L0000014,L0000015,
L0000016,L0000017,L0000018,L0000019,L0000020, L0000021,L0000022,L0000023,
L0000024,L0000025,L0000026,L0000027,L0000028, L0000029,L0000030,L0000031,
L0000032,L0000033,L0000034,L0000035,L0000036, L0000037,L0000038,L0000039,
L0000040,L0000041,L0000042,L0000043,L0000044, L0000045,L0000046,L0000047,
L0000048,L0000049,L0000050,L0000051,L0000052, L0000053,L0000054,L0000055,
L0000056,L0000057,L0000058,L0000059,L0000060, L0000061,L0000062,L0000063,
L0000064,L0000065,
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE6
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***SOURCEIDsDEFINEDASURBANSOURCES ***
URBANIDURBANPOPSOURCEIDs ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞ 9663345.VOL1,VOL2,VOL3,VOL4, VOL5,VOL6,VOL7,
VOL8,
VOL9,VOL10,VOL11,VOL12,VOL13, VOL14,VOL15,VOL16,
VOL17,L0000001,L0000002,L0000003,L0000004, L0000005,L0000006,L0000007,
L0000008,L0000009,L0000010,L0000011,L0000012, L0000013,L0000014,L0000015,
L0000016,L0000017,L0000018,L0000019,L0000020, L0000021,L0000022,L0000023,
L0000024,L0000025,L0000026,L0000027,L0000028, L0000029,L0000030,L0000031,
L0000032,L0000033,L0000034,L0000035,L0000036, L0000037,L0000038,L0000039,
L0000040,L0000041,L0000042,L0000043,L0000044, L0000045,L0000046,L0000047,
L0000048,L0000049,L0000050,L0000051,L0000052, L0000053,L0000054,L0000055,
L0000056,L0000057,L0000058,L0000059,L0000060, L0000061,L0000062,L0000063,
L0000064,L0000065,
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE7
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
SOURCEID=VOL1;SOURCETYPE=VOLUME:
HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+0110.1000E+0111
.1000E+0112.1000E+0113.1000E+01
14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SUNDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE8
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
SOURCEID=VOL2;SOURCETYPE=VOLUME:
HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+0110.1000E+0111
.1000E+0112.1000E+0113.1000E+01
14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SUNDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE9
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
SOURCEID=VOL3;SOURCETYPE=VOLUME:
HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+0110.1000E+0111
.1000E+0112.1000E+0113.1000E+01
14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SUNDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE10
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
SOURCEID=VOL4;SOURCETYPE=VOLUME:
HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+01
10.1000E+0111.1000E+0112.1000E+0113.1000E+01 14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
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***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
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DAY
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***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
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***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
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***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
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HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+01
10.1000E+0111.1000E+0112.1000E+0113.1000E+01 14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SUNDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE88
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* *SOURCEEMISSIONRATESCALARSWHICHVARYDIURNALLYANDBYDAY OFWEEK(HRDOW)*
SOURCEID=L0000065;SOURCETYPE=VOLUME:
HOURSCALARHOURSCALARHOURSCALARHOURSCALARHOURSCALAR HOURSCALARHOURSCALARHOURSCALAR
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
DAYOFWEEK=WEEKDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.1000E+0110.1000E+0111
.1000E+0112.1000E+0113.1000E+01
14.1000E+0115.1000E+0116.1000E+01
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SATURDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
DAYOFWEEK=SUNDAY 1.0000E+002.0000E+003.0000E+004.0000E+005.0000E+00 6.0000E+007.0000E+008.0000E+00
9.0000E+0010.0000E+0011.0000E+0012.0000E+0013.0000E+00 14.0000E+0015.0000E+0016.0000E+00
17.0000E+0018.0000E+0019.0000E+0020.0000E+0021.0000E+00 22.0000E+0023.0000E+0024.0000E+00
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE89
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***DISCRETECARTESIANRECEPTORS*** (XŞCOORD,YŞCOORD,ZELEV,ZHILL,ZFLAG)  (METERS) (404922.8,3778297.2,149.0,1878.7,0.0);(404857.5, 3778322.5,149.4,1878.7,0.0);
(404835.5,3778319.9,148.7,1878.7,0.0);(404795.1, 3778312.1,148.6,1878.7,0.0);
(404814.2,3778315.2,148.7,1878.7,0.0);(404775.0, 3778302.9,148.4,1878.7,0.0);
(404747.2,3778286.5,147.9,1878.7,0.0);(404721.9, 3778271.1,147.6,1878.7,0.0);
(404694.5,3778255.1,147.5,1878.7,0.0);(404793.2, 3778266.6,149.2,1878.7,0.0);
(404790.3,3778195.6,148.4,1878.7,0.0);(404791.5, 3778228.6,149.0,1878.7,0.0);
(404921.9,3778319.5,149.4,1878.7,0.0);(404916.5, 3778193.8,147.4,1878.7,0.0);
(404925.2,3778205.9,147.5,1878.7,0.0);(404947.2, 3778203.2,147.4,1878.7,0.0);
(404920.2,3778337.4,149.5,1878.7,0.0);(404938.8, 3778130.1,146.8,1878.7,0.0);
(404961.3,3778150.1,146.9,1878.7,0.0);(404919.5, 3778098.6,146.3,1878.7,0.0);
(404879.7,3778150.4,146.8,1878.7,0.0);(404823.4, 3778150.2,146.5,1878.7,0.0);
(404749.6,3778149.9,146.1,1878.7,0.0);(404933.1, 3778100.2,146.2,1878.7,0.0);
(404965.8,3778098.2,146.3,1878.7,0.0);(404714.9, 3778442.7,150.8,1878.7,0.0);
(404713.7,3778419.0,150.1,1878.7,0.0);(404716.4, 3778392.2,149.7,1878.7,0.0);
(404701.9,3778375.4,149.5,1878.7,0.0);(404684.0, 3778354.7,148.9,1878.7,0.0);
(404671.3,3778337.1,148.6,1878.7,0.0);(404656.7, 3778318.3,148.4,1878.7,0.0);
(404642.3,3778298.7,148.0,1878.7,0.0);(404621.0, 3778277.4,147.8,1878.7,0.0);
(404606.8,3778257.1,147.4,1878.7,0.0);(404574.9, 3778257.9,147.1,1878.7,0.0);
(404484.8,3778210.0,146.0,1878.7,0.0);(404483.2, 3778255.3,146.6,1878.7,0.0);
(404693.0,3778151.1,145.8,1878.7,0.0);(404917.8, 3777789.3,142.3,1878.7,0.0);
(404768.3,3778394.5,149.8,1878.7,0.0);(404839.4, 3778411.9,150.6,1878.7,0.0);
(404765.1,3778179.5,146.3,1878.7,0.0);(404705.7, 3778203.3,146.6,1878.7,0.0);
(404959.3,3778715.3,155.3,1878.7,0.0);(404879.2, 3778787.7,156.0,1878.7,0.0);
(404874.5,3778890.9,157.9,1878.7,0.0);(404916.3, 3778882.5,157.7,1878.7,0.0);
(404917.5,3778818.1,156.6,1878.7,0.0);(404916.5, 3778835.7,156.8,1878.7,0.0);
(404919.0,3778848.9,157.1,1878.7,0.0);(404872.9, 3779103.2,161.4,1878.7,0.0);
(404918.4,3779136.5,162.1,1878.7,0.0);(404475.2, 3778114.7,144.6,1878.7,0.0);
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE90
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***METEOROLOGICALDAYSSELECTEDFOR PROCESSING***
 (1=YES;0=NO) 111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111111111111111111111 11111111111111111
111111111111111
NOTE:METEOROLOGICALDATAACTUALLYPROCESSEDWILLALSODEPENDON WHATISINCLUDEDINTHEDATAFILE.
***UPPERBOUNDOFFIRSTTHROUGHFIFTHWINDSPEED CATEGORIES***
 (METERS/SEC) 1.54,3.09,5.14,8.23,

10.80,
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE91
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***UPTOTHEFIRST24HOURSOFMETEOROLOGICAL DATA***
Surfacefile:azus_sfc_pfl\AZUS_V11_trimmed.sfc MetVersion:22112
Profilefile:azus_sfc_pfl\AZUS_V11_trimmed.PFL 
Surfaceformat:FREE 
Profileformat:FREE 
Surfacestationno.:3179Upperairstationno.:3190 Name:UNKNOWNName:UNKNOWN 
Year:2017Year:2017 First24hoursofscalardata
YRMODYJDYHRH0U*W*DT/DZZICNVZIMCHMŞOLENZ0BOWEN ALBEDO
REFWSWDHTREFTAHT
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
170101101Ş11.30.154Ş9.000Ş9.000Ş999.145.28.60.340.75

1.001.3697.10.0281.49.5
170101102Ş5.90.110Ş9.000Ş9.000Ş999.88.20.00.290.75

1.001.0588.10.0281.09.5
170101103Ş6.60.117Ş9.000Ş9.000Ş999.95.21.10.290.75

1.001.1169.10.0280.59.5
170101104Ş6.90.119Ş9.000Ş9.000Ş999.99.21.70.330.75

1.001.08132.10.0279.89.5
170101105Ş4.10.091Ş9.000Ş9.000Ş999.66.16.10.170.75

1.001.00314.10.0279.59.5
170101106Ş18.00.193Ş9.000Ş9.000Ş999.204.41.00.210.75

1.001.9635.10.0279.89.5
170101107Ş10.50.147Ş9.000Ş9.000Ş999.136.27.00.290.75

1.001.3880.10.0279.69.5
170101108Ş6.30.118Ş9.000Ş9.000Ş999.97.22.90.290.75

0.551.1274.10.0279.49.5
17010110925.40.2090.4200.005103.230.Ş31.80.290.75

0.321.5570.10.0282.29.5
17010111064.60.2961.0200.005581.386.Ş35.40.330.75

0.252.13126.10.0283.69.5
17010111191.00.3251.3500.005956.444.Ş33.20.330.75

0.222.32130.10.0284.19.5
17010111287.80.2481.3930.0051087.299.Ş15.30.320.75

0.211.62152.10.0285.19.5
170101113103.20.1821.5140.0051188.187.Ş5.10.330.75

0.210.97144.10.0286.19.5
17010111474.80.2251.3850.0051256.255.Ş13.40.230.75

0.221.61214.10.0286.99.5
17010111550.90.1501.2330.0051300.142.Ş5.90.070.75

0.261.37273.10.0286.79.5
1701011161.20.1220.3560.0051300.102.Ş130.20.230.75

0.351.08210.10.0286.69.5
170101117Ş13.10.175Ş9.000Ş9.000Ş999.176.36.00.320.75

0.621.55172.10.0286.39.5
170101118Ş13.70.171Ş9.000Ş9.000Ş999.169.32.20.320.75

1.001.53179.10.0285.89.5
170101119Ş9.00.136Ş9.000Ş9.000Ş999.121.24.70.230.75

1.001.38215.10.0285.49.5
170101120Ş3.70.086Ş9.000Ş9.000Ş999.61.14.90.120.75

1.001.03259.10.0285.09.5
170101121Ş1.80.070Ş9.000Ş9.000Ş999.44.16.40.160.75

1.000.58349.10.0284.99.5
170101122Ş3.40.086Ş9.000Ş9.000Ş999.61.16.60.290.75

1.000.7861.10.0284.89.5
170101123Ş14.00.170Ş9.000Ş9.000Ş999.168.31.80.210.75

1.001.7443.10.0284.29.5
170101124Ş21.50.220Ş9.000Ş9.000Ş999.248.53.30.210.75

1.002.2243.10.0283.99.5
Firsthourofprofiledata
YRMODYHRHEIGHTFWDIRWSPDAMB_TMPsigmaAsigmaWsigmaV 170101019.50Ş999.Ş99.00281.499.0Ş99.00Ş99.00 1701010110.0197.1.36Ş999.099.0Ş99.00Ş99.00 Findicatestopofprofile(=1)orbelow(=0)
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE92
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***THEPERIOD(43824HRS)AVERAGECONCENTRATION VALUESFORSOURCEGROUP:ALL***
INCLUDINGSOURCE(S):VOL1,VOL2 ,VOL3,VOL4,VOL5,
VOL6,VOL7,VOL8,VOL9,VOL10 ,VOL11,VOL12,VOL13,
VOL14,VOL15,VOL16,VOL17,L0000001 ,L0000002,L0000003,L0000004,
L0000005,L0000006,L0000007,L0000008,L0000009 ,L0000010,L0000011,...,
***DISCRETECARTESIANRECEPTORPOINTS ***
**CONCOFDPMINMICROGRAMS/M**3 **
XŞCOORD(M)YŞCOORD(M)CONCXŞCOORD(M) YŞCOORD(M)CONC
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
404922.773778297.210.10727404857.48 3778322.490.11796
404835.493778319.900.12460404795.14 3778312.10
0.09675
404814.193778315.220.12280404775.05 3778302.930.06907
404747.173778286.470.03794404721.88 3778271.060.02396
404694.523778255.130.01560404793.23 3778266.560.21337
404790.293778195.560.19015404791.50 3778228.630.15539
404921.903778319.550.07805404916.53 3778193.820.11034
404925.193778205.950.10456404947.18 3778203.180.06338
404920.173778337.390.05707404938.75 3778130.140.02092
404961.273778150.060.02251404919.53 3778098.620.01513
404879.703778150.400.07249404823.42 3778150.230.08973
404749.643778149.880.02686404933.13 3778100.240.01391
404965.813778098.170.01043404714.88 3778442.700.00548
404713.713778419.000.00669404716.36 3778392.200.00866
404701.933778375.420.00885404683.97 3778354.670.00874
404671.313778337.150.00852404656.74 3778318.300.00796
404642.313778298.720.00729404620.96 3778277.380.00611
404606.833778257.060.00543404574.89 3778257.950.00405
404484.793778209.960.00205404483.17 3778255.300.00206
404693.043778151.080.01173404917.76 3777789.260.00107
404768.323778394.460.01249404839.39 3778411.950.01343
404765.153778179.550.05559404705.73 3778203.290.01794
404959.303778715.280.00278404879.18 3778787.700.00542
404874.493778890.900.00420404916.34 3778882.460.00556
404917.463778818.100.00549404916.52 3778835.740.00559
404918.963778848.870.00512404872.86 3779103.210.00144
404918.383779136.510.00078404475.19 3778114.680.00170
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE93
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***THESUMMARYOFMAXIMUMPERIOD(43824 HRS)RESULTS***
**CONCOFDPMINMICROGRAMS/M**3 **
  NETWORK
GROUPIDAVERAGECONCRECEPTOR(XR,YR, ZELEV,ZHILL,ZFLAG)OFTYPEGRIDŞID
ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞ ŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞŞ
ALL1STHIGHESTVALUEIS0.21337AT(404793.23,3778266.56, 149.16,1878.68,0.00)DC
2NDHIGHESTVALUEIS0.19015AT(404790.29,3778195.56, 148.38,1878.68,0.00)DC
3RDHIGHESTVALUEIS0.15539AT(404791.50,3778228.63, 149.01,1878.68,0.00)DC
4THHIGHESTVALUEIS0.12460AT(404835.49,3778319.90, 148.68,1878.68,0.00)DC
5THHIGHESTVALUEIS0.12280AT(404814.19,3778315.22, 148.65,1878.68,0.00)DC
6THHIGHESTVALUEIS0.11796AT(404857.48,3778322.49, 149.40,1878.68,0.00)DC
7THHIGHESTVALUEIS0.11034AT(404916.53,3778193.82, 147.39,1878.68,0.00)DC
8THHIGHESTVALUEIS0.10727AT(404922.77,3778297.21, 148.98,1878.68,0.00)DC
9THHIGHESTVALUEIS0.10456AT(404925.19,3778205.95, 147.54,1878.68,0.00)DC
10THHIGHESTVALUEIS0.09675AT(404795.14,3778312.10, 148.60,1878.68,0.00)DC
***RECEPTORTYPES:GC=GRIDCART
GP=GRIDPOLR
DC=DISCCART
DP=DISCPOLR
ཪ***AERMODŞVERSION24142******C:\Users\MichaelTirohn\Desktop\HRAs\16493 ArcadiaTownCtr\16493Co***02/11/25
***AERMETŞVERSION22112****** ***14:36:37
  PAGE94
***MODELOPTs:RegDFAULTCONCELEVURBANADJ_U* ***MessageSummary:AERMODModelExecution***
ŞŞŞŞŞŞŞŞŞSummaryofTotalMessagesŞŞŞŞŞŞŞŞ

ATotalof0FatalError
Message(s)
ATotalof2WarningMessage(s)
ATotalof474InformationalMessage(s)
ATotalof43824HoursWereProcessed
ATotalof41CalmHoursIdentified
ATotalof433MissingHoursIdentified(0.99Percent) 

********FATALERRORMESSAGES********
***NONE***


********WARNINGMESSAGES********
MEW1861287MEOPEN:THRESH_1MIN1ŞminASOSwindspeedthresholdused 

0.50 MEW1871287MEOPEN:ADJ_U*OptionforStableLowWindsusedinAERMET 
************************************
***AERMODFinishesSuccessfully***
************************************
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
APPENDIX 2.3:

RISK CALCULATIONS

Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
This page intentionally left blank
URF CPF Dose Risk (per
million) REL RfD RESP CNS/PNS CV/BL IMMUN KIDN REPRO EYES -0.25 to 0 0.01513 250 0.25 361 1 70 1.00 10 3.0E-04 1.1E+00 3.7E-06 0.14 5.0E+00 1.4E-03 3.0E-03 0 to 2 0.01513 250 2.00 1090 1 70 1.00 10 3.0E-04 1.1E+00 1.1E-05 3.39 5.0E+00 1.4E-03 3.0E-03 2 to 16 0.01513 250 0.15 572 1 70 1.00 3 3.0E-04 1.1E+00 5.9E-06 0.04 5.0E+00 1.4E-03 3.0E-03

3.57 9.1E-03 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 -0.25 to 0 0.00885 250 0.25 361 1 70 1.00 10 3.0E-04 1.1E+00 2.2E-06 0.08 5.0E+00 1.4E-03 1.8E-03 0 to 2 0.00885 250 2.00 1090 1 70 1.00 10 3.0E-04 1.1E+00 6.6E-06 1.98 5.0E+00 1.4E-03 1.8E-03 2 to 16 0.00885 250 0.15 572 1 70 1.00 3 3.0E-04 1.1E+00 3.5E-06 0.02 5.0E+00 1.4E-03 1.8E-03

2.09 5.3E-03 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 16 to 41 0.21337 250 2.40 230 1 70 1.00 1 3.0E-04 1.1E+00 3.4E-05 1.21 5.0E+00 1.4E-03 4.3E-02

1.21 4.3E-02 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 4 to 13 0.08973 180 2.40 572 1 70 1.00 3 3.0E-04 1.1E+00 2.5E-05 2.73 5.0E+00 1.4E-03 1.8E-02

2.73 1.8E-02 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 4 to 13 0.00107 180 2.40 572 1 70 1.00 3 3.0E-04 1.1E+00 3.0E-07 0.03 5.0E+00 1.4E-03 2.1E-04

0.03 2.1E-04 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 0.0E+00 5 (MEISC) Total
3 (MEIW) Total
Total
1 (MEIR)
2 Total
Total4
Construction Risk
Non-Cancer Risk
Receptor No. Age Bin DPM Conc.
(μg/m3)
Exposure
Frequency
(days)
Exposure
Duration (years)
Inhalation Rate
(L/kg-day)
Inhalation
Absorption
Factor
Averaging
Time (years) FAH ASF
Cancer Risk
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
APPENDIX 2.4:

MODELED RECEPTORS
Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report
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Arcadia Town Center Construction Health Risk Assessment 16493-03 HRA Report

Mitigation Monitoring and Reporting
Program

Arcadia Town Center Project
SCH No. 2024110749

Prepared for City of Arcadia
Development Services Department
240 West Huntington Drive
Arcadia, California 91066
Contact: Edwin Arreola
T: (626) 821-4334

Prepared by Psomas
150 South Arroyo Parkway, Suite 102
Pasadena, California 91105
T: (626) 351-2000
January 2025

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

i Table of Contents

TABLE OF CONTENTS

Section Page
Section 1.0 Mitigation Monitoring and Reporting Program ............................................ 1-1

1.1 Introduction .......................................................................................... 1-1

1.2 Mitigation Monitoring and Reporting Program ....................................... 1-1

TABLES

Table Page

1 Mitigation Monitoring and Reporting Program .............................................................. 1-2

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-1 Mitigation Monitoring and Reporting Program
SECTION 1.0 MITIGATION MONITORING AND REPORTING PROGRAM

1.1 INTRODUCTION
In accordance with the requirements of Section 21081.6 of the California Public Resources Code, and as part of its adoption of Initial Study and Mitigated Negative Declaration (IS/MND) for the Arcadia Town Center Project, the City of Arcadia (City) adopts this Mitigation Monitoring and Reporting Program (MMRP). The City adopts this MMRP in its capacity as the lead agency for the IS/MND in accordance with the provisions of the California Environmental Quality Act (CEQA) (California Public Resources Code Section 21000 et seq.) and the State CEQA Guidelines (California Code of Regulations, Title 14, Section 15000 et seq.).

The principal purpose of this MMRP is to ensure that the mitigation measures and regulatory requirements for the approved Project are reported and monitored to ensure compliance with their requirements. In general, the City of Arcadia Development Services Department is responsible for overseeing implementation and completion of the adopted measures. This includes the review of all monitoring reports, enforcement actions, and document disposition, unless otherwise noted in the attached MMRP table.

1.2 MITIGATION MONITORING AND REPORTING PROGRAM
The MMRP is provided in tabular format to facilitate effective tracking and documentation of the status of mitigation measures. The attached MMRP table provides the following monitoring information:
y
y Regulatory Requirements and Mitigation Measures. The text of all adopted mitigation measures (MMs) from the IS/MND has been provided in this MMRP. Regulatory requirements (RRs) that are applicable to the Project are also included in the MMRP, which include laws, rules, regulations, and ordinances that would avoid and/or minimize environmental impacts of the Project.
y Responsible for Implementation. This MMRP identifies the party that is responsible for implementing each of the RRs and MMs that is specified in the IS/MND. y Timing. This MMRP includes information related to when each RR and MM in the IS/MND will be implemented.
y Responsibility for Monitoring. This MMRP identifies the City Department(s) or other public agency(ies) that are responsible for overseeing the implementation and completion of each mitigation measure.
y Completion Date. The completion date column of this MMRP is used to record the date that each mitigation measure is completed. This column of the MMRP table will be filled in by the City in the future as the Project is implemented and the RRs and MMs are completed. Upon completion, the MMRP and associated documentation will be kept on file at the City of Arcadia Development Services Department.

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-2 Mitigation Monitoring and Reporting Program
TABLE 1

MITIGATION MONITORING AND REPORTING PROGRAM

Regulatory Requirements and Mitigation Measures Responsible for Implementation Timing Responsibility for Monitoring Completion Date
(Signature Required)
Aesthetics
RR AES-1 The Project Applicant/Property Owner shall prepare a Lighting Plan that provides the type and location of proposed exterior lighting and signage, subject to the review and approval of the City’s Development Services Department. All new lighting will be shielded and down-cast, such that the light is not cast onto adjacent properties or visible from above, and all new lighting would be reviewed to ensure compliance with the standards codified in Section 9103.01 of the City of Arcadia Development Code.

Applicant/Property Owner Prior to issuance of a building permit City of Arcadia Development Services Department, Planning
Division

Air Quality
RR AQ-1 The Project shall be conducted in compliance with all applicable South Coast Air Quality Management District (SCAQMD) rules and permitting requirements, including but not limited to:
x SCAQMD Rule 403, Fugitive Dust, for controlling fugitive dust and avoiding nuisance. Compliance with this rule will reduce short term particulate pollutant emissions. x SCAQMD Rule 402, Nuisance, which states that a Project will not “discharge from any source whatsoever such quantities of air contaminants or other material which cause injury, detriment, nuisance, or annoyance to any considerable number of persons or to the public, or which endanger the comfort, repose, health or safety of any such persons or the public, or which cause, or have a natural tendency to cause, injury or damage to business or property”.
x SCAQMD Rule 1113, Architectural Coatings, which limits the volatile organic content (VOC) of architectural coatings used for the Project.

Applicant/Property Owner

Construction Contractor
Throughout construction City of Arcadia Development
Services Department, Building
Division

Biological Resources
RR BIO-1 Prior to approval of grading plans, the Development Services Department shall verify that the following note is included on the contractor specifications to ensure compliance with the Migratory Bird Treaty Act (MBTA):

To avoid impacts on nesting birds, vegetation on the Project site should be cleared between September 1 and January

31. If vegetation clearing occurs during the peak nesting season (between February 1 and August 31), a pre-construction survey shall be conducted by a qualified biologist to identify if there are any active nesting locations. If the biologist does not find any active nests within the impact area, the vegetation clearing/construction work will be allowed. If the biologist finds an active nest within the construction area and determines that the nest may be impacted by construction activities, the biologist will delineate an appropriate buffer zone around the nest depending on the species and the type of construction activity. Construction activities shall be prohibited in the buffer zone until a qualified biologist determines the nest is abandoned.

Applicant/Property Owner

Construction Contractor

Qualified Biologist
Prior to approval of grading plans

Within 5 days of vegetation clearing
if between February 1 and August 31

City of Arcadia Development
Services Department Planning
Division

RR BIO-2 As required by the City’s Comprehensive Tree Management Program, the Project Applicant/Property Owner shall obtain a permit from the Arcadia Public Works Services Department for the removal and planting of street trees associated with the Project. The Project Applicant/Property Owner will abide by the standards set forth in the permit, as well as standards contained in the Comprehensive Tree Management Program and other applicable sections of the Arcadia Development and Municipal Codes.

Applicant/Property Owner

Prior to issuance of a building permit. City of Arcadia Public Works Services Department

RR BIO-3 The Project Applicant/Property Owner shall submit the Project’s landscape plans, which will include the proposed locations and species of replacement street trees, to the Arcadia Public Works Services Department for review. Street tree species will consist of those set forth in the City’s Street Tree Master Plan.

Applicant/Property Owner

During plan-check for approval and
the trees must be planted prior to
issuance of a Certificate of
Occupancy

City of Arcadia Public Works
Services Department

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-3 Mitigation Monitoring and Reporting Program
TABLE 1

MITIGATION MONITORING AND REPORTING PROGRAM

Regulatory Requirements and Mitigation Measures Responsible for Implementation Timing Responsibility for Monitoring Completion Date
(Signature Required)
Cultural Resources
RR CUL-1 If human remains are encountered during excavation activities, all work shall halt in the immediate vicinity of the discovery and the Los Angeles County Coroner shall be notified (California Public Resources Code §5097.98). The Coroner shall determine whether the remains are of forensic interest. If the Coroner determines that the remains are prehistoric, s/he will contact the Native American Heritage Commission (NAHC). The NAHC shall be responsible for designating the most likely descendant (MLD), who will be responsible for the ultimate disposition of the remains, as required by Section 7050.5 of the California Health and Safety Code. The MLD shall make his/her recommendation within 48 hours of being granted access to the site. The MLD’s recommendation shall be followed if feasible and may include scientific removal and non destructive analysis of the human remains and any items associated with Native American burials (California Health and Safety Code §7050.5). If the landowner rejects the MLD’s recommendations, the landowner shall rebury the remains with appropriate dignity on the property in a location that will not be subject to further subsurface disturbance (California Public Resources Code §5097.98).

Applicant/Property Owner

Construction Contractor

Los Angeles County Coroner

Native American Heritage Commission
and MLD
During excavation activities City of Arcadia Development Services Department, Planning
and Building Divisions

MM CUL-1 Prior to the issuance of a demolition permit, the Project Applicant/Property Owner shall submit the name and qualifications of a qualified archaeologist to the City of Arcadia Development Services Department for review and approval. Once approved, the qualified archaeologist shall be retained by the Project Applicant/Property Owner. If suspected cultural (archaeological) resources or tribal cultural resources are inadvertently unearthed during excavation activities, the contractor shall immediately cease all earth-disturbing activities within a 100-foot radius of the area of discovery. The Project contractor or Project Applicant/Property Owner shall contact the qualified archaeologist to request an evaluation of the significance of the find and determine an appropriate course of action. If avoidance of the resource(s) is not feasible, salvage operation requirements pursuant to Section 15064.5 of the State California Environmental Quality Act Guidelines shall be followed. After the find has been appropriately avoided or mitigated, work in the area may resume.

Applicant/Property Owner

Construction Contractor

Qualified Archaeologist
Prior to issuance of a demolition
permit
City of Arcadia Development
Services Department, Planning
Division

Energy
RR ENR-1 The Project shall be consistent with the Title 24 energy efficiency standards and the mandatory requirements of the CALGreen code. Construction activities shall comply with idling requirements and maintenance requirements for on- and off-road vehicles.

Applicant/Property Owner
Construction Contractor
Prior to issuance of a building permit
and during construction activities
City of Arcadia Development
Services Department, Building
Division

Geology and Soils
RR GEO-1 Geotechnical design considerations for Project implementation are governed by the Arcadia Building Code, as set forth in Article VIII of the Arcadia Municipal Code, which incorporates by reference the California Building Code (CBC), including the California Building, Plumbing, Mechanical, Electrical and Existing Building Codes (CBSC 2022).

Future buildings and structures shall be designed in accordance with applicable requirements of the CBC, the Arcadia Municipal Code, and any applicable building and seismic codes in effect at the time the grading plans are approved.

Applicant/Property Owner Prior to approval of grading plans City of Arcadia Development Services Department, Building
Division

RR GEO-2 The Project building design specifications shall include recommendations from the Geotechnical Investigation, Proposed Huntington Park View Mixed-Use Development, 25 North Santa Anita, Arcadia, California (Geocon West, Inc. 2021, Appendix D). These recommendations include, but are not limited to, specifications for the following:
x Demolition and site preparation
x Fill placement
x Remedial grading and over excavation
x Foundation recommendations
x Building Floor Slabs and reinforcement
The Project building design specifications shall be verified by the City of Arcadia Building Official prior to issuance of a demolition permit.

Applicant/Property Owner

City of Arcadia Building Official
Prior to issuance of a demolition
permit
City of Arcadia Development
Services Department, Building
Division

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-4 Mitigation Monitoring and Reporting Program
TABLE 1

MITIGATION MONITORING AND REPORTING PROGRAM

Regulatory Requirements and Mitigation Measures Responsible for Implementation Timing Responsibility for Monitoring Completion Date
(Signature Required)
Hazards and Hazardous Materials
RR HAZ-1 Activities at the Project site shall comply with existing federal, State, and local regulations regarding hazardous material use, storage, disposal, and transport to prevent Project-related risks to public health and safety. All on-site generated waste that meets hazardous waste criteria shall be stored, manifested, transported, and disposed of in accordance with the California Code of Regulations (Title 22) and in a manner to the satisfaction of the local Certified Unified Program Agency (CUPA), as applicable. Any hazardous materials removed from the Project site shall be transported only by a Licensed Hazardous Waste Hauler, who shall be in compliance with all applicable State and federal requirements, including U.S. Department of Transportation regulations under Title 49 (Hazardous Materials Transportation Act) and Title 40, Section 263 (Subtitle C of the Resource Conservation and Recovery Act) of the Code of Federal Regulations; California Department of Transportation (Caltrans) standards; and Division of Occupational Safety and Health (Cal/OSHA) standards.

Applicant/Property Owner

Construction Contractor

During construction City of Arcadia Development
Services Department, Building
Division

Hydrology and Water Quality
RR HWQ-1 Prior to the City’s issuance of a demolition permit, the Project Applicant/Property Owner shall obtain coverage under the General Permit for Storm Water Discharges Associated with the Construction and Land Disturbance Activities (Order No 2022-0057-DWQ, NPDES No. CAS000002), which will require the development and implementation of a project-specific Storm Water Pollution Prevention Plan (SWPPP).

Applicant/Property Owner

Construction Contractor
Prior to issuance of a demolition
permit
City of Arcadia Development
Services Department –
Engineering and Building
Divisions

Noise
MM NOI-1 The Project Applicant/Property Owner shall require that all construction contractors restrict the operation of the following construction equipment to beyond the following distances from off-site buildings: (1) vibratory rollers – 25 feet, and (2) Caisson drilling, large bulldozers, loaded trucks, and other large equipment (vehicle weight greater than 25,000 lbs.) – 15 feet. Any activities occurring within 5 feet of existing property line shall use non-vibration intensive methods such as use of concrete saws, universal processors, and/or expansive agents for demolition.

Applicant/Property Owner

Construction Contractor
During any demolition, grading, and
construction
City of Arcadia Development
Services Department, Building
Division

Public Services
RR PUB-1 The Project Applicant/Property Owner shall comply with all applicable codes, ordinances, and regulations, including the most current edition of the California Fire Code and the Arcadia Municipal and Development Codes, regarding fire prevention and suppression measures; fire hydrants; fire access; water availability; and other, similar requirements. Prior to issuance of building permits, the City of Arcadia Development Services Department and the Arcadia Fire Department shall verify compliance with applicable codes and that appropriate fire safety measures are included in the Project design. All such codes and measures shall be implemented prior to occupancy.

Applicant/Property Owner Prior to issuance of a building permit

Implementation prior to issuance of a
Certificate of Occupancy permit
City of Arcadia Development
Services Department, Planning
and Building Divisions

City of Arcadia Fire Department

RR PUB-2 In accordance with the City’s Ordinance 7492, prior to the issuance of the building permit, the Project Applicant/Property Owner shall remit the most current fire protection facilities impact fee to the City. All money collected as fees imposed shall be used against the capital and infrastructure costs required to maintain acceptable life safety and fire protection in the City. The Development Services Department shall confirm compliance with this requirement prior to issuance of a building permit.

Applicant/Property Owner Prior to issuance of a building permit City of Arcadia Development Services Department, Building
Division and Arcadia’s Fire
Department

RR PUB-3 Prior to issuance of the building permit, the Project Applicant/Property Owner shall pay new development fees to the AUSD pursuant to Section 65995 of the California Government Code. As an option to the payment of developer fees, the AUSD and the Property Owner can enter into a facility and funding agreement, if approved by both parties. Evidence that agreements have been executed shall be submitted to the Development Services Department, or fees shall be paid with each building permit.

Applicant/Property Owner

Arcadia Unified School District
Prior to issuance of a building permit City of Arcadia Development Services Department, Building
Division

RR PUB-4 In accordance with the City’s Ordinance 2237 and Section 9105.15 of the City’s Development Code, prior to the issuance of the building permit, the Project Applicant/Property Owner shall remit the most current park facilities impact fee and/or other negotiated park fees to the City. All money collected as fees imposed shall be deposited in the Park Facilities Impact Fee Program and shall be used for the acquisition, development, and improvement of public parks and recreational facilities in the City, as proposed by the City’s Parks and Recreation Master Plan. The Development Services Department shall confirm compliance with this requirement prior to issuance of a building permit.

Applicant/Property Owner

Prior to issuance of a building permit City of Arcadia Development Services Department, Building
Division

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-5 Mitigation Monitoring and Reporting Program
TABLE 1

MITIGATION MONITORING AND REPORTING PROGRAM

Regulatory Requirements and Mitigation Measures Responsible for Implementation Timing Responsibility for Monitoring Completion Date
(Signature Required)
Transportation/Traffic
RR TRANS-1 Require the Applicant/Property Owner to contribute, on a cost-share basis, to the City’s Transportation Impact Fee program, for any intersections affected by the Project, based on the net new PM Peak House vehicle trips generated, per the City’s Transportation Impact Fee Program Update adopted on October 18, 2016.

Applicant/Property Owner Prior to issuance of a building permit City of Arcadia Development Services Department, Building
and Engineering Divisions

MM TRANS-1 Prior to the issuance of a grading permit, a Construction Management Plan shall be prepared by the Project Applicant/Property Owner for the review and approval of the City of Arcadia and any other affected jurisdictions in accordance with the Manual on Uniform Traffic Control Devices (MUTCD). Construction activities shall comply with the approved plan to the satisfaction of the City of Arcadia. The Applicant/Property Owner will coordinate begin coordination with the City on the Construction Management Plan as soon as practicable during the final design process and in advance of construction so that effective measures can be developed to avoid, minimize, and mitigate construction impacts to parking and circulation within the City of Arcadia downtown.

At a minimum, the Construction Management Plan shall:
x Describe the duration and location of lane closures (if any). x Address traffic control for any partial street closures, detours, or other disruption to traffic circulation during project construction, including as-needed use of flagpersons and signage. x Identify the routes that construction vehicles would utilize for the delivery of construction materials to access the project site. Haul routes would follow the City’s approved truck routes and avoid residential streets. x Identify the location of parking and materials storage for construction workers during all phases of construction.

Parking for construction workers would be provided on-site or at additional off-site locations that are not on public streets.
x Identify of emergency access points/routes.
x Specify the hours during which transport activities can occur and methods to mitigate construction-related impacts to adjacent streets.
x Require the contractor to keep all haul routes clean and free of debris including but not limited to gravel and dirt as a result of its operations. The contractor shall clean adjacent streets, as directed by the City Engineer (or representative of the City Engineer), of any material, which may have been spilled, tracked, or blown onto adjacent streets or areas.
x All hauling or transport of oversize loads would occur between the hours of 7:00 AM and 5:00 PM only, Monday through Friday, unless approved otherwise by the City Engineer. No hauling or transport shall be allowed during nighttime hours, weekends or Federal holidays.
x Include details on the maintenance of bicycle and pedestrian facilities and connectivity through the Project to the satisfaction of the City Engineer.
x Require that haul trucks entering or exiting public streets shall at all times yield to public traffic, pedestrians, bicyclists, and other users.
x Provisions for the contractor to repair existing pavement, streets, curbs, sidewalks, and/or gutters that may be altered during project construction. The repairs shall be completed in consultation with and to the satisfaction of the City Engineer.
x Require that all construction-related parking and staging of vehicles will be kept out of the adjacent public roadways and will occur either on-site or on designated off-site parcels that would not adversely affect access to or parking within the downtown.

Applicant/Property Owner

Construction Contractor
Prior to issuance of a grading permit City of Arcadia Development Services Department, Planning
and Engineering Divisions

Arcadia Town Center Project
Mitigation Monitoring and Reporting Program

1-6 Mitigation Monitoring and Reporting Program
TABLE 1

MITIGATION MONITORING AND REPORTING PROGRAM

Regulatory Requirements and Mitigation Measures Responsible for Implementation Timing Responsibility for Monitoring Completion Date
(Signature Required)
Tribal Cultural Resources
MM TCR-1 Retain a Native American Monitor Prior to Commencement of Ground-Disturbing Activities A. The Project Applicant/Property Owner shall retain a Native American Monitor from or approved by the Gabrieleño Band of Mission Indians – Kizh Nation. The monitor shall be retained prior to the commencement of any “ground- disturbing activity” for the subject project at all project locations (i.e., both on-site and any off-site locations that are included in the project description/definition and/or required in connection with the project, such as public improvement work). “Ground-disturbing activity” shall include, but is not limited to, demolition, pavement removal, potholing, auguring, grubbing, tree removal, boring, grading, excavation, drilling, and trenching.

B. A copy of the executed monitoring agreement shall be submitted to the lead agency prior to the earlier of the commencement of any ground-disturbing activity, or the issuance of any permit necessary to commence a ground- disturbing activity.

C. The monitor will complete daily monitoring logs that will provide descriptions of the relevant ground-disturbing activities, the type of construction activities performed, locations of ground-disturbing activities, soil types, cultural- related materials, and any other facts, conditions, materials, or discoveries of significance to the Tribe. Monitor logs will identify and describe any discovered tribal cultural resources, including but not limited to, Native American cultural and historical artifacts, remains, places of significance, etc., (collectively, tribal cultural resources, or “TCR”), as well as any discovered Native American (ancestral) human remains and burial goods. Copies of monitor logs will be provided to the Project Applicant/City upon written request to the Tribe.

D. On-site tribal monitoring shall conclude upon the latter of the following (1) written confirmation to the Kizh from a designated point of contact for the project applicant/lead agency that all ground-disturbing activities and phases that may involve ground-disturbing activities on the project site or in connection with the project are complete; or (2) a determination and written notification by the Kizh to the project applicant/lead agency that no future, planned construction activity and/or development/construction phase at the project site possesses the potential to impact Kizh TCRs.

Applicant/Property Owner

Construction Contractor

Native American Monitor – Kizh Nation
Prior to commencement a grading
permit or any ground disturbing
activities

During construction
City of Arcadia Development
Services Department, Planning
and Building Divisions

MM TCR-2 Unanticipated Discovery of Tribal Cultural Resource Objects (Non-Funerary/Non-Ceremonial) Upon discovery of any TCRs, all construction activities in the immediate vicinity of the discovery shall cease (i.e., not less than the surrounding 50 feet) and shall not resume until the discovered TCR has been fully assessed by the Kizh monitor and/or Kizh archaeologist. The Kizh will recover and retain all discovered TCRs in the form and/or manner the Tribe deems appropriate, in the Tribe’s sole discretion, and for any purpose the Tribe deems appropriate, including for educational, cultural and/or historic purposes.

Applicant/Property Owner

Construction Contractor

Native American Monitor – Kizh Nation
During any grading or ground-
disturbing activities
City of Arcadia Development
Services Department, Planning
and Building Divisions

MM TCR-3 Unanticipated Discovery of Human Remains and Associated Funerary or Ceremonial Objects A. Native American human remains are defined in Public Resources Code section 5097.98 (d)(1) as an inhumation or cremation, and in any state of decomposition or skeletal completeness. Funerary objects, called associated grave goods in Public Resources Code Section 5097.98, are also to be treated according to this statute.

B. If Native American human remains and/or grave goods are discovered or recognized on the project site, then Public Resource Code 5097.9 as well as Health and Safety Code Section 7050.5 shall be followed.

C. Human remains and grave/burial goods shall be treated alike per California Public Resources Code section 5097.98(d)(1) and (2).

D. Preservation in place (i.e., avoidance) is the preferred manner of treatment for discovered human remains and/or burial goods.