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KEVIN T. CARMICHAEL
CHRISTINA M. CARO
THOMAS A. ENSLOW
KELILAH D. FEDERMAN
RICHARD M. FRANCO
ANDREW J. GRAF
TANYA A. GULESSERIAN
RACHAEL E. KOSS
AIDAN P. MARSHALL
TARA C. RENGIFO
Of Counsel
MARC D. JOSEPH
DANIEL L. CARDOZO
SACRAMENTO OFFICE
520 CAPITOL MALL, SUITE 350
SACRAMENTO, CA 95814 -4721
TEL: (916) 444- 6201
FAX: (916) 444 - 6209
ADAMS BROADWELL JOSEPH & CARDOZO
A PROFESSIONAL CORPORATION
ATTORNEYS AT LAW
601 GATEWAY BOULEVARD, SUITE 1000
SOUTH SAN FRANCISCO, CA 94080 - 7037
___________
TEL: (650) 589- 1660
FAX: (650) 589 - 5062
[email protected]
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July 18, 2023
Via Email and Hand Delivery
Renee Berlin, Chair
Tim Burkhart, Vice Chair
Patsy Ayala, Commissioner
Lisa Eichman, Commissioner
Dennis Ostrom, Commissioner
City of Santa Clarita Planning
Commission
23920 Valencia Blvd., Suite 140
Santa Clarita, CA 91355
Jason Crawford, Director of Community
Development
Erika Iverson, Associate Planner
City of Santa Clarita Planning Division
23920 Valencia Blvd., Suite 302
Santa Clarita, CA 91355
Email: [email protected];
[email protected]
Re: Agenda Item #1 - July 18, 2023 Planning Commission Meeting Shadowbox Studios Project (Master Case 21-109)
Dear Chair Berlin, Honorable Planning Commission members, Mr. Crawford and Ms. Iverson:
We are writing on behalf of the Coalition for Responsible Equitable Economic Development Los Angeles (“CREED LA”) with respect to the July 18, 2023 Planning Commission Meeting Agenda Item #1, the Shadowbox Studios Project (Master Case 21-109) (“Project”) proposed by L.A. Railroad 93, LLC (“Applicant”).
The Project proposes to develop a full-service film and television studio campus that would consist of approximately 476,000-square feet of sound stages; approximately 571,000-square feet of workshops, warehouses, and support uses; approximately 210,000-square feet of production and administrative offices, and approximately 37,500-square feet of catering and specialty service areas. The approximately 93-acre Project site is generally located at the northeast corner of Railroad Avenue and 13th Street and bounded by 12th Street, Arch Street, and 13th Street on the south; Railroad Avenue on the west; Metropolitan Water District (MWD) right-of-way (ROW) on the east; and HOA maintained slopes associated with adjacent residential uses to the north.
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The staff report for the July 18 meeting recommends that the Planning Commission take the following actions:
1. Receive the staff presentation and continue the public hearing;
2. Close the public hearing;
3. Adopt a resolution recommending that the City Council certify the Draft Final Environmental Impact Report prepared for the Project;
4. Adopt a resolution recommending that the City Council approve the Project’s entitlements, including Architectural Design Review, Conditional Use Permit, General Plan Amendment, Hillside Development Review, Minor Use Permit, Oak Tree Permit (Class 4), Ridgeline Alteration Permit, Zone Change, and Tentative Tract Map; and
5. Take other action as determined by the Planning Commission. 1 The Planning Commission cannot recommend approval at this time because the City has not complied with the California Environmental Quality Act (“CEQA”).2 Rather than recommending that the City Council (“Council”) certify the Draft Final EIR (“FEIR”), the Commission should instead direct staff to revise and recirculate the DEIR to address the numerous deficiencies described herein and in CREED LA’s previous comments. In our May 22, 20233 and June 20, 2023 comment letters, we detailed several ways in which the DEIR fails to comply with CEQA. The FEIR fails to respond to or resolve many of these deficiencies.
We reviewed the FEIR with the assistance of air quality expert James Clark, noise expert Ani Toncheva, biological resources expert Shawn Smallwood, and transportation expert Norman Marshall. The further comments and qualifications of these experts are attached hereto
4 and are incorporated by reference as if set
1 City of Santa Clarita Planning Commission Agenda Report (July 18, 2023) (“Staff Report”), pg. 1. 2 Pub. Resources Code §§ 21000 et seq.; 14 Cal. Code Regs (“CEQA Guidelines”) §§ 15000 et seq. (“CEQA Guidelines”).
3 May 22, 2023 letter from Richard M. Franco, Adams Broadwell Joseph & Cardozo to Jason Crawford and Erika Iverson, City of Santa Clarita re Comments on Draft Environmental Impact Report for Shadowbox Studios Project (Master Case 21-109; SCH Number 2022030762) (“DEIR Comments”).
4 Exhibit A , July 17, 2023 Letter from James J.J. Clark to Richard M. Franco, Adams Broadwell Joseph & Cardozo re: Comment Letter on Final Environmental Impact Report ( FEIR) Shadowbox Studios Project, SCH NO. 2022030762 (hereinafter “Clark FEIR Comments”); Exhibit B , July 17, 2023 Letter from Ani Toncheva, Wilson Ihrig to Richard M. Franco, Adams Broadwell Joseph & July 18, 2023
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forth herein. As explained below, the FEIR fails to address or resolve many of the issues raised in our DEIR Comments, and fails to mitigate potentially significant impacts to the greatest extent feasible. Moreover, the FEIR includes significant new information which requires that the DEIR be recirculated for further public review and comment. Accordingly, we respectfully request that the Planning Commission direct staff to prepare and circulate a revised DEIR that fully complies with CEQA.
I. STATEMENT OF INTEREST
CREED LA is an unincorporated association of individuals and labor organizations that may be adversely affected by the potential public and worker health and safety hazards, and the environmental and public service impacts of the Project. The coalition includes Santa Clarita residents Corey Wood, Greg Lewis and Michael de Francis, the Sheet Metal Workers Local 105, International Brotherhood of Electrical Workers Local 11, Southern California Pipe Trades District Council 16, and District Council of Iron Workers of the State of California, along with their members, their families, and other individuals who live and work in the City of Santa Clarita and surrounding areas.
Individual members of CREED LA and its member organizations live, work, recreate, and raise their families in the City of Santa Clarita and surrounding communities. Accordingly, they would be directly affected by the Project’s environmental and health and safety impacts. Individual members may also work on the Project itself. They will be first in line to be exposed to any health and safety hazards that exist onsite.
In addition, CREED LA has an interest in enforcing environmental laws that encourage sustainable development and ensure a safe working environment for its members. Environmentally detrimental projects can jeopardize future jobs by making it more difficult and more expensive for business and industry to expand in the region, and by making the area less desirable for new businesses and new residents. Continued environmental degradation can, and has, caused construction moratoriums and other restrictions on growth that, in turn, reduce future employment opportunities.
Cardozo re: City of Santa Clarita Shadowbox Studio Project FEIR Comments on the Draft EIR and Responses (hereinafter “Toncheva FEIR Comments”); Exhibit C, July 15, 2023 Letter from Shawn Smallwood to Erika Iverson, City of Santa Clarita re: Shadowbox Studios Project (hereinafter “Smallwood FEIR Comments”); Exhibit D , July 17, 2023 Letter from Norman Marshall, Smart Mobility to Richard M. Franco re: Responses to the Shadowbox Studios Project Draft Final EIR (hereinafter “Marshall FEIR Comments”).
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II. THE CITY MUST PREPARE AND CIRCULATE A REVISED DEIR
Lead agencies are required to recirculate an EIR for further public review and comment if significant new information is added to the EIR after notice of public review but before certification.5 Recirculation is required when the addition of new information deprives the public of a meaningful opportunity to comment on a substantial adverse environmental effect of the project or a feasible way to mitigate or avoid such an effect.6 New information can include “changes in the project or environmental setting as well as additional data or other information.”7 The purpose of recirculation is to give the public and other agencies an opportunity to evaluate the new data and the validity of conclusions drawn from it. 8 Recirculation is also required where significant new information surfaces prior to certification of an EIR but the lead agency failed to add that information to the EIR.9 Such information must be added to the EIR—and the EIR must be recirculated—if the information would trigger the recirculation requirement under CEQA Guidelines section 15088.5. Failure to include such information thwarts the goals of the EIR process by not disclosing to the public and government agencies critical information necessary to evaluate the significance of the Project’s impacts. 10 CREED LA’s DEIR Comments described a number of ways in which the DEIR failed to comply with CEQA, requiring that the City revise and recirculate the DEIR for further public review and comment. In addition, in response to DEIR comments from the California Department of Fish and Wildlife (“CDFW”), the FEIR includes new information regarding the Project’s potentially significant impacts to biological resources and proposes several new mitigation measures purportedly designed to mitigate such impacts.11 However, the FEIR lacks the facts or analysis necessary to provide decision makers or the public with the information needed assess these impacts, in violation of CEQA. Moreover, without a proper analysis of the Project’s impacts to biological resources, the City is unable to evaluate whether the newly proposed mitigation measures will be effective.
In its DEIR comments, CDFW notes that the Project may result in loss of suitable nesting and foraging habitat for Crotch’s bumblebee, a species that is a
5 Pub. Resources Code § 21092.1; 14 CCR § 15088.5.
6 14 CCR § 15088.5(a).
7 Id.
8 Spring Valley Lake Ass’n v. City of Victorville (2016) 248 Cal.App.4th 91, 108. 9 Cadiz Land Co. v. Rail Cycle (2000) 83 Cal.App.4th 74, 95. 10 Id.
11 FEIR, pgs. 2-50—2-60.
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candidate for California Endangered Species Act (“CESA”) listing.12 The CDFW letter explains why impacts would occur and provides evidence that such impacts would be significant, and points out that the DEIR fails to discuss the species or the Project’s impacts on it.13 CDFW also provides a number of recommendations, including that prior to finalizing the CEQA document, “the DEIR should provide full disclosure of the presence of Crotch’s bumble bee within the Project site” and “should analyze the Project’s impacts on floral resources, nesting habitat and overwintering habitat.”
14 CDFW further recommends that conclusions regarding
habitat quality and suitability be substantiated by scientific and factual date, and that potential direct and indirect impacts on the species be discussed in the DEIR.15
In response to CDFW’s comments, the City acknowledges that the Project site may provide suitable nesting and foraging habitat for Crotch’s bumblebee, and purports to revise the DEIR to “discuss the potential for the species to occur, evaluate potential project impacts, and provide species-specific avoidance and mitigation measures” in accordance with CDFW’s recommendations. 16 The DEIR
was revised to include proposed mitigation measure MM-BIO-6, requiring a qualified biologist to conduct surveys to determine the species’ presence or absence.17 If the surveys detect Crotch’s bumblebee on the Project site, then proposed new mitigation measures MM-BIO-7, MM-BIO-8 and MM-BIO-9 would require buffer zones around any active nests and replacement of floral resources.
None of this information was included in the DEIR and has not been provided to the public for review and comment, as required by CEQA.
Additionally, while these revisions include some of the recommendations from CDFW, the City ignores the most important ones: to “provide full disclosure” of the species’ presence on the Project site, to analyze the Project’s direct and indirect impacts on the species, and to support its conclusions with scientific and factual data prior to finalizing the CEQA document.
18 Without such disclosure, analysis
and supporting data, the Project’s impacts are unknown and the efficacy of the newly proposed mitigation measures in the FEIR cannot be evaluated.
The City admits that none of these steps have been completed: “[f]ocused site surveys are currently underway to confirm that the absence of Crotch’s bumble bee
12 May 22, 2023 letter from CDFW to Erika Iverson, City of Santa Clarita, re Shadowbox Studios Project Draft Environmental Impact Report (“CDFW Letter”). 13 Id., pgs. 4-5.
14 Id., Attachment A: Draft Mitigation and Monitoring Reporting Plan. 15 Id.
16 FEIR, pg. 2-51.
17 Id., pg. 2-52.
18 CDFW Letter, Attachment A, pg. 1.
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on the Project Site [sic].”19 Without disclosure of the results of completed surveys and analysis of potential Project impacts and mitigation, responsible agencies, the public and the City’s decision makers are deprived of any meaningful opportunity to comment on a substantial adverse environmental effect of the project or a feasible way to mitigate or avoid such an effect.20 This violates CEQA. The City must revise and recirculate the DEIR after completion of surveys for Crotch’s bumblebee.
III. THE FEIR FAILS TO ADEQUATELY DISCLOSE, ANALYZE OR
MITIGATE THE PROJECT’S POTENTIALLY SIGNIFICANT NOISE
IMPACTS
A. The Noise Impact Analysis Violates CEQA Because it Fails to Consider Increases Over Ambient Noise Levels
CREED LA’s DEIR Comments explained in detail how the DEIR’s failure to evaluate the Project’s construction and operational noise impacts using an ambient- based significance threshold violated CEQA. These comments were based on the settled legal principle that lead agencies “do not have discretion…to consider only maximum noise levels and ignore increases in noise relative to existing conditions.
In applying significance thresholds, the lead agency must consider both the ‘absolute noise level’ associated with a project as well as the increase in the level of noise that will result from a project [emphasis added].” 21 The DEIR
failed to include this analysis and the FEIR fails to correct this omission.
In King & Gardiner Farms, the Court of Appeal held that the lead agency violated CEQA by “using a single standard relating to the absolute noise level as a threshold of significance for evaluating all ambient noise impacts.” 22 The approach
used by the City “does not provide a complete picture of the noise impacts that may result from the project.”23 Similarly, in Keep our Mountains Quiet, the Court of Appeals held the “the lead agency should consider both the increase in noise level and the absolute noise level associated with a project.” 24 Despite the clear holdings
19 Staff Report, pg. 5.
20 14 CCR § 15088.5(a).
21 Kostka & Zischke, Practice Under the California Environmental Quality Act (2d ed Cal CEB), §13.63A, citing King & Gardiner Farms, LLC v. County of Kern (2020) 45 Cal. App. 5th 814, 887 and 893 and Keep Our Mountains Quiet v. County of Santa Clara (2015) 236 Cal. App. 4 th 714, 733. 22 King & Gardiner Farms, supra, 45 Cal. App. 5th at 893. 23 Id. at 894.
24 Keep Our Mountains Quiet, supra, 236 Cal. App. 4th at 733. See also, Berkeley Keep Jets Over the Bay Comm. v. Board of Port Cmrs. (2001) 91 Cal. App. 1344, 1382 (potential noise impact of nighttime flights required further study where there had been no meaningful analysis of existing ambient noise levels.)
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by California courts regarding the need to evaluate noise impacts using both an absolute threshold and an ambient threshold, the FEIR fails to evaluate the Project’s impacts using an increase over ambient threshold. Instead, the FEIR attempts to justify this failure by misstating the law: “King & Gardiner Farms…does not explicitly require an analysis of an increase over ambient noise.”25 Rather, the FEIR suggests, the City may rely solely on an absolute noise threshold and dispense with use of an ambient noise increase threshold if that approach “is properly supported,” and claims that there is substantial evidence to support the exclusive use of an absolute threshold as the basis of its noise analysis. 26 As an initial matter, the City’s statement of the law is flatly contradicted by the decisions quoted above. At best, King & Gardiner Farms suggests that, while the lead agency should consider both the increase in noise level and the absolute noise level associated with a project, it may be able to show substantial evidence that the magnitude of a noise increase may not be relevant in determining the significance of a change in noise.27 This does not support the City’s position that it need not analyze the Project’s increase over ambient noise levels at all.
In addition, the FEIR falsely claims that there is substantial evidence supporting its sole use of an absolute noise threshold.
First, the FEIR asserts that the single, absolute threshold approach is “consistent with many jurisdictions within the State…which do not have a threshold for numeric increase in ambient noise levels.” 28 The fact that other cities’
noise ordinances lack a numerical threshold for evaluating the significance of a project’s increase over ambient noise levels is neither surprising, nor is it relevant.
Whether or not the municipal codes of Beverly Hills, Fresno and Pasadena contain such thresholds does not affect the City’s duty to comply with CEQA’s disclosure requirements with regard to the Project’s noise impact. CEQA would require those other cities to evaluate their projects’ noise increases over ambient levels, just as CEQA requires the City to perform such an analysis with respect to this Project.
The FEIR also cites Caltrans as an example of an agency that does not have a threshold for a numeric increase in ambient noise levels. 29 Even if true, that does
not change CEQA’s requirement to evaluate the Project’s increase in noise over ambient levels. In fact, as Ms. Toncheva points out, Caltrans’ Traffic Noise
25 FEIR, pg. 2-1005.
26 Id.
27 King & Gardiner Farms, supra, 45 Cal. App. 5th at 894. 28 FEIR, pg. 2-1005.
29 Id.
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Analysis Protocol (“Caltrans Noise Protocol”) that the significance of noise impacts is determined based on the project-related increase in noise and, while no single numerical threshold is used on all projects, what is considered a substantial increase can vary depending on current environment.
30 The City’s citation to the
Caltrans Noise Protocol directly contradicts the City’s position that it may rely solely on an absolute noise threshold and ignore ambient noise increases.
Next, the FEIR contends that, because construction would be limited to daytime hours, its absolute 80 dBA threshold for construction noise would avoid sleep disruption.
31 It also claims that, since daytime construction noise will be limited to 80 dBA, the Project would not cause hearing loss which according to OSHA can begin to occur at 90 dBA.32 The FEIR is logically flawed, essentially arguing that if the Project complies with the absolute 80 dBA significance threshold, the City need not analyze the Project’s noise increase over ambient. This is a non sequitur that is directly at odds with the CEQA jurisprudence cited above. Nor is there support for the FEIR’s false implication that sleep disturbance and hearing loss are the only relevant noise impacts that the City must consider. As pointed out in her DEIR comments, CREED LA’s noise expert identified speech interference, cardiovascular and other physiological effects, and impaired cognitive performance as other adverse effects of noise on humans.
In addition, relying solely on an 80 dB absolute limit for construction noise would allow a 31 dB increase at receptor NM4 and a 33 dB increase at NM6. 33 The
DEIR’s noise analysis actually predicts construction noise increases of 20 dB over ambient levels.34 The City does not, and cannot, provide any rational explanation for why an increase of 20-30 dB over ambient is insignificant. Ultimately, the City has no support for its failure to evaluate the Project’s noise increase over ambient levels.
With regard to operational noise, the FEIR makes similar specious arguments. It claims, without support or explanation, that “the significance of the magnitude of an ambient noise level increase is inherently accounted for by the City’s fixed noise limits utilized for the noise analysis in the Draft EIR.” 35 Again,
the City’s approach violates CEQA because it relies on “a single standard relating to the absolute noise level as a threshold of significance for evaluating all ambient
30 Toncheva FEIR Comments, pg. 1.
31 Id.
32 Id.
33 Toncheva FEIR Comments, pg. 2.
34 Toncheva DEIR Comments, pg. 3.
35 Id., pg. 2-1006.
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noise impacts.”36 The FEIR admits that operational noise will exceed ambient levels at some receptor locations, but suggests there will be no significant impact because the increase does not exceed 5 dBA over ambient levels.37 If the City intends to adopt “5 dBA over ambient” as a significance threshold to evaluate the Project’s noise impacts, it must do so in a revised DEIR and support its chosen threshold with substantial evidence.
Ultimately, the City’s position that it is not required to “evaluate increased ambient noise levels attributable to Project construction and operation”38 violates CEQA, and the FEIR fails to remedy this violation. The DEIR must be revised and recirculated for further public review and comment.
IV. THE FEIR FAILS TO ADEQUATELY DISCLOSE, ANALYZE OR
MITIGATE THE PROJECT’S SIGNIFICANT TRANSPORTATION
IMPACTS
In CREED LA’s DEIR Comments (including expert comments by Mr.
Marshall), we explained the ways in which the DEIR’s analysis with respect to the Project’s vehicle miles traveled (“VMT”) was unsupported by substantial evidence.
The FEIR fails to correct those issues. Moreover, the FEIR directly contradicts the DEIR with respect to the significance threshold used to evaluate VMT impacts. As discussed below, the VMT analysis is so unclear as to be indecipherable. The City must revise and recirculate the DEIR to address these issues.
A. The FEIR Lacks a Clear VMT Significance Threshold
Supported by Substantial Evidence
In its VMT analysis, the DEIR stated “[t]he City’s threshold of significance is
15.7 VMT per employee based on the 2012 Citywide home-based work VMT per employee of 21.0.”
39 It further stated that “only the 2012 base year with project scenario was executed in the model.”40 In direct contrast, the FEIR now states that the “14.0 work VMT per employee calculated for the Project was compared to the calculated 2028 threshold of 14.0 work VMT per employee.”41 The purported significance threshold of “14.0 work VMT per employee is an interpolation between the citywide threshold of 15.7 for Year 2020 conditions and the projected 11.5
36 King & Gardiner Farms, supra, 45 Cal. App. 5th at 893. 37 FEIR, pg. 2-1007.
38 Id., pg. 2-1006.
39 DEIR, pg. 4.14-18.
40 Id., pg. 4.14-10.
41 FEIR, pg. 2-1011.
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threshold for 2040 conditions. The 14.0 represents the threshold for year 2028 conditions, which is the Opening Year of the Project.”42
In short, the DEIR claimed to use a VMT significance threshold of 15.7 based on a Citywide 2012 VMT of 21.0 (though it doesn’t explain how 15.7 was derived from 21.0). The FEIR now asserts a VMT significance threshold of 14.0, which is a 2028 estimate based on an “interpolation” between Year 2020 and Year 2040 conditions. Beyond the obvious discrepancy between the 15.7 and 14.0 significance thresholds set forth in the DEIR and FEIR, respectively, it appears that the FEIR is comparing Project VMT estimates calculated on 2012 base year conditions with a significance threshold calculated on 2028 conditions. Adding to the confusion are the following additional inconsistencies:
• DEIR Appendix L
43 states “[a]s shown in Table 10 and the VMT Memo44 the Project is estimated to generate an average home-based work VMT per employee of 14.0, which is less than the Citywide impact threshold of 15.7 and, therefore, would not result in a significant VMT impact.” 45 • Appendix L’s Table 10, however, sets forth an “Impact Threshold (2028 Estimate)” of 14.0.46 Additionally, Table 10 notes that the 2028 threshold is extrapolated based on the 2020 regional (not citywide) VMT estimate of 15.7 and 2040 regional estimate of 11.5.47
• The VMT Memo sets forth the City’s VMT significance threshold as 17.9, which is “15% below” the “2012 Citywide Home-Based Work VMT per Employee.”
48 “Table 4 [in the VMT Memo] indicates that project Home-Based Work VMT per employee is forecast to be below the City’s threshold of significance of 17.9 Home-Based Work VMT per employee.”49
Based on the foregoing, it is impossible to know what VMT significance threshold the City is actually relying on, how it was derived, or whether it is valid.
The threshold is variously set forth as 14.0, 15.7 and 17.9 home-based work VMT
42 Id.
43 DEIR Appendix L, January 2023 Transportation Assessment for Shadowbox Studios Project (“Transportation Assessment”).
44 “VMT Memo” refers to the technical memorandum Blackhall Studios-City of Santa Clarita VMT Modeling Summary (Iteris, August 24, 2021).
45 DEIR, Appendix L, pg. 48.
46 DEIR, Appendix L, Table 10 at pg. 50.
47 Id.
48 DEIR, Appendix L VMT Memo, pgs. 3-4.
49 Id., pg. 4.
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per employee. The DEIR stated that the threshold was “based on the 2012 Citywide home-based work VMT per employee of 21.0,”50 while the FEIR states that the threshold “represents the threshold for Year 2028 conditions,” interpolated between “the citywide thresholds for Year 2020 and Year 2040 conditions.”51 The DEIR’s technical transportation analysis stated that the 2028 threshold was extrapolated based on 2020 and 2028 regional, not citywide, estimates,52 which is inconsistent with the discussion in the FEIR. Given that the DEIR and FEIR reach the same conclusions regarding the severity of the Project’s transportation impacts, it is critical that the public (and City decision makers) understand the threshold used to derive the conclusions in the FEIR’s transportation analysis in order to evaluate the accuracy of the FEIR. Given these many discrepancies, the FEIR violates the basic CEQA requirement that it include “an identifiable, quantitative, qualitative or performance level” for VMT that is supported by substantial evidence.53 These discrepancies can only be resolved in a revised and recirculated DEIR, so that the public and City decision makers can evaluate the validity of the City’s VMT analysis.
B. The FEIR’s Use of the 2016 SCAG Travel Demand Model to Estimate VMT is Not Supported by Substantial Evidence
As Mr. Marshall explained in his DEIR comments, the DEIR’s significance threshold and Project VMT estimates were derived using an outdated model known to underestimate VMT.
54 The DEIR used the 2016 Southern California Association of Governments (“SCAG”) 2016 travel demand model, rather than the updated 2020 model. A crucial difference between the two models is that the 2020 version incorporates census data (which was not used in the 2016 version) to calibrate the tail of the trip length distribution, because there were few observations of these long commute patterns captured in the California Household Travel Survey (“CHTS”) data used to calibrate the 2016 model.
55 Importantly, the census data showed
average commute lengths 65% higher than the average in the CHTS data used to calibrate the outdated model.56
The FEIR does not address or refute Mr. Marshall’s criticisms of the 2016 model. Rather, the FEIR attempts to justify the use of the outdated model by asserting that because the 2016 SCAG model was used to establish the VMT
50 DEIR, pg. 4.14-18.
51 FEIR, pg. 2-1011.
52 DEIR, Appendix L, Table 10, note c.
53 CEQA Guidelines §15064.7.
54 DEIR Comments, Exhibit D.
55 Marshall FEIR Comments, pg. 1.
56 Id., pgs. 1-2.
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thresholds in the Santa Clarita area, it is “the most logical model to use in the analysis of the Project.”57 The City’s response ignores the underlying issue of whether it was valid to use the 2016 model in the first place, and provides no evidence refuting Mr. Marshall’s criticisms. Instead, the FEIR simply asserts that is making an “apples-to-apples” comparison between Project-generated VMT and the thresholds of significance.58 As Mr. Marshall points out, though, such comparisons are of little value when both “apples” are rotten.59 In other words, if the model used to generate significance thresholds and Project VMT is suspect, the resulting analysis is similarly suspect. Moreover, given the many discrepancies in the description of the City’s VMT significance threshold described above, it is far from clear that the DEIR’s analysis even used an “apples-to-apples” approach.
The City’s VMT analysis lacks substantial evidence supporting the methodology used to evaluate the Project’s transportation impacts or the threshold of significance used in the analysis. The DEIR must be revised to include a proper VMT analysis supported by substantial evidence.
V. THE FEIR FAILS TO ADEQUATELY DISCLOSE, ANALYZE OR
MITIGATE THE PROJECT’S POTENTIALLY SIGNIFICANT AIR
QUALITY IMPACTS
CREED LA’s DEIR Comments identified a number of significant defects in the DEIR’s analysis of the Project’s air quality and related health impacts. The FEIR still fails to justify the use of optional and unenforceable Project Design Features (“PDFs”) with respect to construction equipment. The FEIR also still fails to adequately address health risks from diesel emissions from generators that will be used during Project operations, and completely ignores expert evidence of a significant health risk to nearby residents from such operations.
A. The FEIR Continues to Rely on Unenforceable Project Design Features in Analyzing Construction Emissions
As discussed in detail in CREED LA’s DEIR Comments, the DEIR underestimates the significance of Project construction emissions by relying on optional and unenforceable emissions controls to support the conclusion that such emissions will be less than significant. PDF AQ-1 and PDF-AQ-2 “propose” that the Project use off-road diesel-powered construction equipment that meets or exceeds the CARB and USEPA Tier 3 off-road emissions standards with Level 3 diesel
57 FEIR, pg. 2-1011.
58 Id.
59 Marshall FEIR Comments, pg. 1.
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particulate filters or be alternatively (non-diesel) fueled to reduce diesel exhaust emissions during Project construction.60 The DEIR Comments explained why this violates CEQA, as these PDFs are in fact unenforceable mitigation of the Project’s construction emissions.
In response to another commenters’ comment on the same issue, the FEIR admits that “PDFs typically provide a benefit or a reduction to impacts [emphasis added].”
61 Under CEQA, this is a mitigation measure. CEQA defines mitigation as including any measures designed to avoid, minimize, rectify, reduce, eliminate, or compensate for a significant impact.62 Still, the FEIR claims that these measures, admittedly designed to reduce impacts, “are not considered mitigation because [they] are part of the construction design of the Project, and there are no current regulations requiring specific construction equipment to be used.”
63 This statement has nothing to do with the definition of “mitigation” under CEQA, and does not remedy the City’s failure to make its construction emissions mitigation binding.
CEQA requires that mitigation measures be fully enforceable through permit conditions, agreements or other legally binding instruments. 64 Because the City
has not characterized PDF AQ-1 or PDF AQ-2 as mitigation measures, they are not binding on the Applicant, and will not be included in the Project’s Mitigation Monitoring and Reporting Program (“MMRP”).65 Reliance on “proposed” nonmandatory and unenforceable PDFs to reduce impacts therefore provides no assurance that the Applicant would later comply with the “design features.” The PDFs therefore fail to provide the binding mechanism required by CEQA to compel the Applicant’s compliance with mitigation following Project approval. Indeed, after we commented on the lack of enforceability of the PDFs at the June 20, 2023 Planning Commission meeting, Chair Berlin requested that the PDFs be included in the Conditions of Approval.
66 However, they have not been included in the draft
Conditions of Approval attached to Resolution P23-12 that will be considered by the Commission at its July 18 meeting. Staff therefore failed to follow the Commission’s direction.
The DEIR further violates CEQA by failing to first disclose the Project’s unmitigated construction emissions (i.e., construction emissions before applying the
60 DEIR, p. 4.2-18.
61 FEIR, pg. 2-739.
62 14 CCR § 15370.
63 FEIR, pgs. 2-739—2-740.
64 14 CCR §15126.4(a)(2).
65 DEIR, Table ES-1 at pgs. ES-6—ES-26.
66 July 18, 2023 Planning Commission Meeting Agenda Packet, pg. 5.
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PDFs). Without disclosing the Project’s unmitigated construction emissions, the DEIR only discloses estimated emissions with the application of PDF-AQ-1 and PDF-AQ-2. This “downward adjustment” of the Project’s construction emissions artificially reduces their significance. The DEIR concludes that the Project’s construction emissions (mitigated by PDF-AQ-1 and PDF-AQ-2) are less than significant, without application of any binding mitigation measures.67
This approach violates CEQA’s requirement that an EIR disclose the significance of an impact prior to mitigation.
68 The purpose of this analysis is both
to require public disclosure of a project’s impacts, and to require the lead agency to “identify and focus on the significant environmental effects of the proposed project.”69 In evaluating the significance of an impact, an EIR must discuss the physical changes in the environment that the project will cause, including:
relevant specifics of the area, the resources involved, physical changes, alterations to ecological systems, and changes induced in population distribution, population concentration, the human use of the land (including commercial and residential development), health and safety problems caused by the physical changes, and other aspects of the resource base such as water, historical resources, scenic quality, and public services. 70 Only after this discussion occurs may the agency identify and apply mitigation measures to reduce potentially significant impacts to less than significant levels.
71 The discussion is rendered meaningless (or, as here, omitted entirely) if the EIR falsely concludes that a project’s impact is less than significant based on premature application of mitigation measures. In this case, the DEIR failed to undertake the requisite analysis required by CEQA Guidelines Section 15126.2 for the Project’s construction emissions because the DEIR did not disclose the Project’s air quality impacts prior to incorporating PDF AQ-1 and PDF-AQ-2.
The FEIR responds to this argument by claiming that “application of all Tier 3 equipment in the CalEEMod emissions analysis does not result in meaningfully different emissions than the default construction equipment fleet in the model.” 72 But this raises additional unanswered questions. Is the City suggesting that the “default construction equipment fleet” represents the Project’s unmitigated
67 DEIR, 4.2-19—21.
68 14 CCR § 15126.2.
69 14 CCR § 15126.2(a).
70 14 CCR § 15126.2(a).
71 14 CCR § 15126.4.
72 FEIR, pg. 2-740.
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emissions? What is the composition of the default construction fleet? The FEIR states that the default fleet includes “some Tier 4 equipment,” but does not otherwise define the default fleet.
73 Why were the “default fleet” emissions not
reported in the DEIR? Indeed, the FEIR includes Table O5-1, purporting to report CalEEMod Default Fleet Emissions; the table, however, indicates that the source of information set forth is “Rincon Consultants, Inc., June 2023.” 74 This suggests it
was prepared after the close of the public review and comment period for the DEIR.
The FEIR claims that “without or with the PDFs that require a minimum of Tier 3 equipment, Project emissions would be below the South Coast AQMD thresholds of significance and, therefore, less than significance.”75 This statement is not supported by substantial evidence and therefore does not comply with CEQA.
The City must revise and recirculate the DEIR to address the many defects discussed above.
B. The FEIR Does Not Resolve the Failure to Analyze the Potential Health Risks to Nearby Residents from Project Emissions
CREED LA’s DEIR comments set forth the legal requirements under CEQA for agencies to analyze public health impacts of the Project. 76 The comments also
explained that the DEIR’s justification for not performing a health risk analysis is unfounded, as it is based on a misapplication of SCAQMD’s localized significance thresholds (“LSTs”). LSTs are not intended to provide health risk significance thresholds for toxic air contaminants (“TACs”) such as diesel particulate matter (“DPM”). Finally, we provided substantial evidence of the Project’s significant health impacts to neighboring residents from exposure to DPM from diesel generators used during Project operations. Dr. James Clark used the DEIR’s CalEEMod analysis of the Project’s emissions from diesel generators to assess cancer risk to nearby sensitive receptors, and found a risk at one of several nearby residents to be approximately 20 in one million, exceeding the 10 in one million significance threshold set by SCAQMD and representing a significant impact under CEQA.
77 73 Id.
74 Id.
75 FEIR, 2-740.
76 See e.g., Sierra Club v. County of Fresno (2018) 6 Cal.5th 502, 518–522; see also, Cleveland National Forest Foundation v. San Diego Assn. of Governments (2017) 3 Cal.5th 497, 514–515. 77 DEIR Comments, pg. 17 and Exhibit A.
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In the FEIR, the City continues to incorrectly maintain that a health risk analysis for the Project’s operational DPM emissions is not required, and completely ignores the substantial evidence of a significant health impact provided by Dr.
Clark.78 CEQA requires a good faith, reasoned analysis in response to comments on a DEIR, particularly in response to comments made by experts or other agencies.79 Indeed, another agency has echoed Dr. Clark’s comments that a health risk analysis for the Project’s operation DPM emissions should be performed. In its May 19, 2023 comment letter on the Project, the SCAQMD recommends that the City “conduct an operational phase HRA [Health Risk Assessment]…which is essential for determining the potential cancer risk impacts associated with the operation of the Proposed Project to the offsite sensitive receptors and workers so that they can be compared to the South Coast AQMD Air Quality Significance Thresholds for TACs [footnote omitted] to determine whether there will be a potentially significant air quality impact.”
80 In response to the SCAQMD’s recommendation, the City suggests that it need not evaluate the health risk from diesel generators that would be used during Project operations, stating that “generators would not be part of the Project and, as needed, would only be implemented by production that was leasing space from the studio. These generators would need to be permitted through the South Coast AQMD and the risk associated with the generators would be required to be below regulatory thresholds as part of the permitting process.” 81 However, the DEIR
assumed that the Project would utilize six diesel generators, and analyzed DPM emissions from those generators though, as noted, did not assess health risks from their operation. Regardless of who will use the generators on the Project site, the City is aware that such generators will be used and will emit DPM, and the EIR must therefore disclose and analyze the associated emissions and health risks.
Finally, the DEIR’s CalEEMod analysis of the six generators expected to be used on the Project site assumed that the generators would be equipped with Tier 3 emissions controls.
82 This assumption, like the PDFs relating to the Project construction fleet, is an unenforceable mitigation measure. Because there is nothing requiring the Project utilize only Tier 3 diesel generators, the emissions reported are unreliable and likely underestimated.
78 FEIR, pgs. 2-1003—2-1004.
79 CEQA Guidelines §15088(c); Berkeley Keep Jets Over the Bay, supra, 91 Cal. App. 4 th at 1367, 1371.
80 May 19, 2023 letter from Sam Wang, South Coast Air Quality Management District to Erika Iverson, City of Santa Clarita re Draft Environmental Impact Report for the Proposed Shadowbox Studios Project, pgs. 3-4.
81 FEIR, pg. 2-73.
82 Id., pg. 2-71.
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The City must revise and recirculate the DEIR with accurate estimates of the Project’s DPM emissions supported by substantial evidence, and must perform a health risk analysis that discloses the health risks to the Project’s neighbors.
VI. THE FEIR FAILS TO ADEQUATELY DISCLOSE, ANALYZE OR MITIGATE THE PROJECT’S POTENTIALLY SIGNIFICANT
IMPACTS TO BIOLOGICAL RESOURCES
CREED LA’s DEIR comments include a lengthy letter from wildlife biologist Shawn Smallwood in which he details numerous deficiencies in the DEIR’s analysis of the Project’s impacts to biological resources.
83 The FEIR fails to adequately
address or resolve many of these issues, as explained in Dr. Smallwood’s reply to the FEIR.84 Chief among these issues is the FEIR’s failure to correct the DEIR’s errors with respect to evaluating and reporting the environmental baseline on the Project site.
Dr. Smallwood commented at length regarding the DEIR’s serious flaws in its disclosure of the baseline environmental conditions related to the presence of wildlife, including special status species, on the Project site. Describing the environmental setting accurately and completely for each environmental condition in the vicinity of the Project is critical to an accurate, meaningful evaluation of environmental impacts. The courts have clearly stated that “[b]efore the impacts of a project can be assessed and mitigation measures considered, an [environmental review document] must describe the existing environment. It is only against this baseline that any significant environmental effects can be determined.” 85 Dr. Smallwood’s DEIR comments also explained that the DEIR failed to adequately assess the Project site’s background setting with respect to wildlife species. In particular, he noted that the DEIR’s surveys of the Project site for biological resources and review of literature, databases and local experts for documented occurrences of special-status species were incomplete and misleading, and that none of those limitations were disclosed.
86 Among other things, the DEIR
relied on an “unrealistically short list of potentially occurring species as a starting point for the analysis.”87 Indeed, Dr. Smallwood’s associate surveyed the Project site from the perimeter with binoculars and detected multiple wildlife species on
83 See DEIR Comments, Exhibit C.
84 See Smallwood FEIR Comments.
85 County of Amador v. El Dorado County Water Agency (1999) 76 Cal.App.4th 931, 952. 86 See generally, Smallwood DEIR Comments, pgs. 13-29.
87 Smallwood FEIR Comments, pg. 3.
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and near the Project site that the City’s consultants failed to detect or report, including 4 special-status species.88
The FEIR’s response to Dr. Smallwood’s evidence is that the reconnaissance survey performed by its consultants was not intended to be a comprehensive inventory of all species that inhabit the Project site, and that such a comprehensive inventory is unnecessary to support a sound impacts analysis. 89 Dr. Smallwood did
not assert, however, that a “comprehensive inventory” of all species on the Project site is necessary. Rather, he noted that the survey that was performed in support of the DEIR’s analysis did not accurately characterize the existing environmental setting, and therefore could not support inferences made by the City’s consultants regarding the likelihood of various species being present or absent from the Project site.
90 Dr. Smallwood also analyzed and commented on the shortcomings in the DEIR’s focused burrowing owl survey. His discussion was based on City’s consultants’ failure to comply with CDFW standards for performing and reporting such surveys. Dr. Smallwood noted that the consultant’s report met none of the CDFW standards on reporting qualifications of survey personnel, and fewer than half of the standards for habitat assessment.91 He specifically identified more than 30 specific CDFW standards for burrowing owl surveys, and indicates that the survey done for the DEIR met about half of the standards. 92 In response, the FEIR describes what the City’s consultant did (which was previously reported in the DEIR), but does not correct their errors or omissions.
Rather than address Dr. Smallwood’s specific listing of standards not followed, the FEIR simply reiterates the standards that were followed.93 The FEIR claims, therefore, that the burrowing owl survey “complied with established protocol” and CEQA. However, Dr. Smallwood’s specific comments regarding the DEIR’s failure to meet 16 of the 34 applicable minimum burrowing owl protocol survey standards remain unresolved and uncontested. The FEIR’s conclusions regarding the burrowing owl therefore remain unsupported by substantial evidence.
88 Id., pg. 4.
89 FEIR, pg. 2-1023.
90 Smallwood FEIR comments, pg. 3.
91 Smallwood DEIR Comments, Table 3; Smallwood FEIR comments, pg. 13. 92 Id.
93 FEIR, pg. 2-1000.
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VII. THE FEIR CONTINUES TO IMPROPERLY RELY ON
UNENFORCEABLE PROJECT DESIGN FEATURES IN ITS IMPACT
ANALYSES
CREED LA’s DEIR Comments explained how the DEIR violated CEQA by improperly relying on proposed and unenforceable project design features (“PDFs”) to mitigate Project impacts with respect to air quality (discussed above), geology, energy, public services and wildfire. While none of these PDFs are mandatory nor enforceable, the DEIR assumed that the PDFs would be implemented and would reduce the Project’s impacts, and were used as supported for the DEIR’s conclusions that impacts will be less than significant. As discussed in the DEIR Comments and below, this approach violates CEQA.
CREED LA’s DEIR Comments explained why, under CEQA, the PDFs are actually mitigation measures. CEQA defines mitigation as including any measures designed to avoid, minimize, rectify, reduce, or compensate for a significant impact.
94 The PDFs described in the DEIR are actually mitigation measures because they perform these functions. Indeed, the FEIR admits that this is the purpose of the PDFs: “PDFs typically provide a benefit or a reduction to impacts [emphasis added].”95
As detailed in our DEIR Comments, CEQA requires that mitigation measures be fully enforceable through permit conditions, agreements or other legally binding instruments.96 Because the City has not characterized any of the PDFs as mitigation measures, they are not binding on the Applicant, and will not be included in the Project’s MMRP. Reliance on “proposed” nonmandatory and unenforceable PDFs to reduce impacts therefore provides no assurance that the Applicant will later comply with the “design features.” The PDFs therefore fail to provide the binding mechanism required by CEQA to compel the Applicant’s compliance with mitigation following Project approval.
The Courts have made clear that mitigation must be incorporated directly into a project’s MMRP to be considered enforceable. In Lotus v. Department of Transportation,
97 an EIR approved by Caltrans contained several measures “[t]o help minimize potential stress on the redwood trees” during construction of a highway. Although those measures were clearly separate mitigation, the project proponents considered them “part of the project.” The EIR concluded that due to
94 14 CCR § 15370.
95 FEIR, pg. 2-739.
96 14 CCR §15126.4(a)(2).
97 Lotus v. Dep't of Transp. (2014) 223 Cal. App. 4th 645, 651-52.
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the planned implementation of those measures, the project would not result in significant impacts. The Court disagreed, finding that the EIR had “disregard[ed] the requirements of CEQA” by “compressing the analysis of impacts and mitigation measures into a single issue.” The Court continued, stating “[a]bsent a determination regarding the significance of the impacts … it is impossible to determine whether mitigation measures are required or to evaluate whether other more effective measures than those proposed should be considered.” 98 The FEIR fails to address any of the legal standards and case law set forth above and in CREED LA’s DEIR Comments. Instead, it simply offers the conclusory statement that “PDFs are features of the Project that would be included in the construction and operation of the Project that would be implemented above and beyond compliance with specific regulations and requirements.” 99 As in the Lotus
case, the City h as compressed the analysis of impacts and mitigation into a single issue by insisting that the PDFs are part of the Project , and assuming the implementation of the PDFs in performing its impact analysis with respect to geology, energy, public service and wildfire impacts.
100 By failing to first analyze and disclose
the Project’s impacts without consideration of the PDFs, the F EIR does not comply with CEQA.
VIII. CONCLUSION
For the reasons discussed above, the FEIR for the Project is wholly inadequate under CEQA. It must be revised to provide legally adequate analysis of, and mitigation for, all of the Project’s potentially significant impacts. These revisions will necessarily require that the DEIR be recirculated for additional public review. Until the DEIR has been revised and recirculated, as described herein, the City may not lawfully approve the Project.
Thank you for your consideration of these comments. Please include them in the record of proceedings for the Project.
Sincerely,
Richard M. Franco
Attachments
RMF:acp
98 Id.
99 FEIR, pg. 2-1015.
100 See DEIR Comments, pgs. 35-39.
EXHIBIT A
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July 17, 2023
Adams Broadwell Joseph & Cardozo
601 Gateway Boulevard, Suite 1000
South San Francisco, CA 94080
Attn: Mr. Richard Franco
Subject: Comment Letter on Final Environmental Impact Report (FEIR) Shadowbox Studios Project, SCH NO.
2022030762.
Dear Mr. Franco:
At the request of Adams Broadwell Joseph & Cardozo
(ABJC), Clark and Associates (Clark) has reviewed materials related to the above referenced project.
The FEIR concludes that only minor changes to the text of the Draft EIR occurred since public circulation, and none of the chan ges constitute “significant new information,” which would require its recirculation. This conclusion is in conflict with the facts provided within the DEIR and FEIR.
Specific Comments:
1. The City’s Response That Generators Should Not Be
Included In The FEIR Analysis Is Illogical.
The City’s response to comments about the emissions from generators on site is illogical. In my analysis of the D EIR, I demonstrated that the emissions from the generators would be result in a cancer risk in excess of the S outh Coast Air Quality Management District (SCAQMD) threshold levels (10 in 1,000,000) using the Tier 3 EPA certified generators. Whether the Proponent is responsible for permitting the generators or 3rd parties are responsible is immaterial to Clark & Associates
Environmental Consulting, Inc.
OFFICE
12405 Venice Blvd
Suite 331
Los Angeles, CA 90066
PHONE
310-907-6165
FAX
310-398-7626
EMAIL
[email protected]
2 | P a g e
the air quality analysis. The generators will produce the same amount of air toxins independent of the responsible party . The City’s response that “Generators, as needed, would be brought on -site by individual production entities, which would need to permit the generator use independent of the Project development.”1 Since the City cannot predict the actual usage of the BUG onsite it is clear that t hey must use a predictive method to ensure that they do not underestimate their impacts on the community.
The City’s logic is in conflict with the need to accurately assess emissions from the Project in the CEQA process.
The City did not address the concerns over power outages and need for BUGs noted in the Air Quality Analysis of the DEIR. According to Note 2 of the Blackhall Studios – Santa Clarita Project Generator Assumptions (page 66 of Appendix C to DEIR) the analysis clearly demonstrates the need for BUGs. The note states “ In 2021 the entire Santa Clarita area (54 circuits) had an average of 1.1 disruptions for an average of 180 minutes for the entire year of 2021…. In statistical terms it appears that the Shadowbox Studio project circuit would actually have a 1 in 54 chance of a sustained outage one time per year. For purposes of this analysis we utilized the most extreme potential of one city - wide power outage per year.”
Among the commenting agencies, SCAQMD, which woul d permit any generator for the Project, provided comments in line with my own regarding the emissions from diesel back -up generators (BUGs) onsite and the need for a comprehensive dispersion model of emissions and a health risk assessment. Whether the BUGs are brought on by the individual production entities or are brought on by the Shadowbox facility, they will be present and emitting onsite. The City must revise the FEIR to include all sources of pollutants from the Project in a supplemental FEIR.
2. The City’s Response To Questions Regarding Flaws In The Air Quality Analysis And The Need To Perform A Quantitative Health Risk Assessment Of The Impacts Of Toxic Air Contaminants (including Diesel Particulate Matter (DPM) and Other Air Toxins) Emissions From The Construction & Operational Phase Of The Project For The Nearest Sensitive Receptor(s) Is Not In Line With The Comments From The Air Permitting Agency (SCAQMD) & The Generally Accepted Practice Among Environmental Professionals.
1 FEIR. 2023. Pg. 2-71 and page 2-1000
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In response to comm ents from myself and the SCAQMD regarding the health impacts from diesel generators onsite, the City has chosen to respond by saying that as “part of the permitting process, the risk associated with the generators would be required to be below regulatory t hresholds. See Response to Comment Nos. A3-3, A3-4, and A3-6 for additional information. As demonstrated therein, the Draft EIR adequately disclosed the health risks from exposure to DPM ”2 The responses to A3-3, A3-4, and A3-6 do not address the concerns, rather they place the burden for determining which BUGs will be used on unknown production entities, ignores the clearly defined health risk from exposure to diesel particulate matter, and fails to assess the long-term impacts for residents located immediately adjacent to the Project site from the emissions produced onsite.
By relying on the Air Quality Management Plan (AQMPs) control strategies for construction equipment and other activities to mitigate DPM emissions, and lo calized significance thresholds (LSTs) which analyze criteria pollutants but do not specifically evaluate TACs, the City cannot attest as to whether there is a cancer risk presented to the community by the Project. The City must address this concern by performing an air dispersion model of the sources on site and off site, quantifying the annual concentrations of DPM for each of the receptors, and performing a health risk assessment of the DPM concentrations. Using a risk assessment process in which the age adjustment factors (ADAF) for various age groups would the California Air Resources Board Toxic Hot Spot Guidance, and present the results in a supplement FEIR.
Under CEQA the City is required to provide a detailed health risk analysis for all projects that emit TACs with potential human exposure. TACs, including diesel particulate matter (DPM) 3, contribute to a host of respiratory impacts and may lead to the development of various cancers. Failing to quantify those impacts places the community at risk for unwanted adverse health impacts. Even brief exposures to the TACs could lead to the development of adverse health impacts over the life of an individual.
2 FEIR. 2023. Pg 2-1004
3 Because DPM is a TAC, it is a different air pollutant than criteria particulate matter (PM) emissions such as PM10, PM2.5, and fugitive dust. DPM exposure causes acute health effects that are different from the effects of exposure to PM alone.
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3. The City’s Response To Comment O6-13 Ignores The Substantial Evidence That The Project Site Will Emit Significant Quantities Of TACs.
The City’s response in Comment O6-13 ignores the evidence provide in my previous comment letter and the SCAQMD’s comment letter that the Project Site wi ll have toxic air contaminants that will be released from the construction and operational phases of the Project. The method for assessing the risk from exposure to these known human carcinogens is clearly outlined in guidance from OEHHA, DTSC, and SCAQMD. Failing to assess the health risks to nearby residents and sensitive receptors in the area is a significant flaw in the DEIR and FEIR.
Given the volume of TACs previously identified that will be emitted during the construction and operational phases of the Project and the proximity of the Project to the receptors, the failure to assess the risk a priori is a critical flaw in the City’s analysis.
Conclusion
The facts identified and referenced in this comment letter lead me to reasonably conclude that the Project could result in significant impacts (including an increase in the potential for residents along Alderbrook Avenue to be exposed to DPM, resulting in an increased health risk) if allowed to proceed.
A supplemental FEIR should be prepared to address these substantial concerns.
Sincerely,
Exhibit A:
Curriculum Vitae
James J. J. Clark, Ph.D.
Principal Toxicologist
Toxicology/Exposure Assessment Modeling
Risk Assessment/Analysis/Dispersion Modeling
Education:
Ph.D., Environmental Health Science, University of California, 1995 M.S., Environmental Health Science, University of California, 1993 B.S., Biophysical and Biochemical Sciences, University of Houston, 1987
Professional Experience:
Dr. Clark is a well recognized to xicologist, air modeler, and health scientist. He has 20 years of experience in researching the eff ects of environmental contaminants on human health including environmental fate and transport modeling (SCREEN3, AEROMOD, ISCST3, Johnson-Ettinger Vapor Intrusion Modeling); exposure assessment modeling (partitioning of contaminants in the environment as well as PBPK modeling); conducting and managing human health risk assessments for regulatory compliance and risk-based clean-up levels; and toxicological and medical literature research.
Significant projects performed by Dr. Clark include the following:
LITIGATION SUPPORT
Case: James Harold Caygle, et al, v. Drummond Company, Inc. Circuit Court for the Tenth Judicial Circuit, Jefferson County, Alabama. Civil Action. CV-2009 Client: Environmental Litgation Group, Birmingham, Alabama
Dr. Clark performed an air quality assessment of emissions from a coke factory located in Tarrant, Alabama. The assessment reviewed include a comprehensive review of air quality standards, measured concentrations of pollutants from factory, an inspection of the facility and detailed assessment of the impacts on the community. The results of the assessment and literature have been provided in a declaration to the court.
Clark & Associates
Environmental Consulting, Inc
OFFICE
12405 Venice Blvd.
Suite 331
Los Angeles, CA 90066
PHONE
310-907-6165
FAX
310-398-7626
EMAIL
[email protected]
Case Result: Settlement in favor of plaintiff.
Case: Rose Roper V. Nissan North America, et al. Superior Court of the State Of California for the County Of Los Angeles – Central Civil West. Civil Action.
NC041739
Client: Rose, Klein, Marias, LLP, Long Beach, California
Dr. Clark performed a toxicological assessment of an individual occupationally exposed to multiple chemicals, including benzene, who later developed a respiratory distress. A review of the individual’s medical and occupational history was performed to prepare an exposure assessment. The exposure asse ssment was evaluated against the known outcomes in published literature to exposure to respiratory irritants. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: O’Neil V. Sherwin Williams, et al. United States District Court Central District of California
Client: Rose, Klein, Marias, LLP, Long Beach, California Dr. Clark performed a toxicological assessment of an individual occupationally exposed to petroleum distillates who later developed a bladder cancer. A review of the individual’s medical and occupational history was performed to prepare a quantitative exposure assessment. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Summary judgment for defendants.
Case: Moore V., Shell Oil Company, et al. Superior Court of the State Of California for the County Of Los Angeles
Client: Rose, Klein, Marias, LLP, Long Beach, California Dr. Clark performed a toxicological assessment of an individual occupationally exposed to chemicals while benzene who later develope d a leukogenic disease. A review of the individual’s medical and occupational history was performed to prepare a quantitative exposure assessment. The exposure asse ssment was evaluated against the known outcomes in published literature to exposure to refined petroleum hydrocarbons. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: Raymond Saltonstall V. Fuller O’Brie n, KILZ, and Zinsser, et al. United States District Court Central District of California
Client: Rose, Klein, Marias, LLP, Long Beach, California
Dr. Clark performed a toxicological assessment of an individual occupationally exposed to benzene who later developed a leukogenic disease. A review of the individual’s medical and occupational history was performed to prepare a quantitative exposure assessment. The exposure assessment was ev aluated against the known outcomes in published literature to exposure to refined petroleum hydrocarbons. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: Richard Boyer and Elizabeth Boyer, husband and wife, V. DESCO Corporation, et al. Circuit Court of Brooke County, West Virginia. Civil Action Number 04-C-7G.
Client: Frankovitch, Anetakis, Colantonio & Simon, Morgantown, West Virginia.
Dr. Clark performed a toxicological assessment of a family exposed to chlorinated solvents released from the defendant’s facility into local drinking water supplies. A review of the individual’s medical and occupational history was performed to prepare a qualitative exposure assessment. The exposu re assessment was evaluated against the known outcomes in published literature to expo sure to chlorinated solvents. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: JoAnne R. Cook, V. DESCO Corporation, et al. Circuit Court of Brooke County, West Virginia. Civil Action Number 04-C-9R
Client: Frankovitch, Anetakis, Colantonio & Simon, Morgantown, West Virginia.
Dr. Clark performed a toxicological assessment of an individual exposed to chlorinated solvents released from the defendant’s facility into local drinking water supplies. A review of the individual’s medical and occupational history was performed to prepare a qualitative exposure assessment. The exposu re assessment was evaluated against the known outcomes in published literature to expo sure to chlorinated solvents. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: Patrick Allen And Susan Allen, husband and wife, and Andrew Allen, a minor, V. DESCO Corporation, et al. Circuit Court of Brooke County, West Virginia. Civil Action Number 04-C-W
Client: Frankovitch, Anetakis, Colantonio & Simon, Morgantown, West Virginia.
Dr. Clark performed a toxicological assessment of a family exposed to chlorinated solvents released from the defendant’s facility into local drinking water supplies. A review of the individual’s medical and occupational history was performed to prepare a qualitative exposure assessment. The exposu re assessment was evaluated against the known outcomes in published literature to expo sure to chlorinated solvents. The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: Michael Fahey, Susan Fahey V. Atla ntic Richfield Compan y, et al. United States District Court Central District of California Civil Action Number CV-06 7109 JCL.
Client: Rose, Klein, Marias, LLP, Long Beach, California
Dr. Clark performed a toxicological assessment of an individual occupationally exposed to refined petroleum hydrocarbons who later developed a leukogenic disease. A review of the individual’s medical and occupational history was performed to prepare a qualitative exposure assessment. The exposu re assessment was evaluated against the known outcomes in published literature to exposure to refined petroleum hydrocarbons.
The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Settlement in favor of plaintiff.
Case: Constance Acevedo, et al., V. California Spray-Chemical Company, et al., Superior Court of the State Of California, County Of Santa Cruz. Case No. CV 146344
Dr. Clark performed a comprehensive exposure assessment of community members exposed to toxic metals from a former lead arsenate manufacturing facility. The former manufacturing site had undergone a DTSC mandated removal action/remediation for the presence of the toxic metals at the site. Op inions were presented regarding the elevated levels of arsenic and lead (in attic dust and soils) found throughout the community and the potential for harm to the plaintiffs in question.
Case Result: Settlement in favor of defendant.
Case: Michael Nawrocki V. The Coastal Corporation, Kurk Fuel Company, Pautler Oil Service, State of New York Supreme Court, County of Erie, Index Number I2001-11247
Client: Richard G. Berger Attorney At Law, Buffalo, New York
Dr. Clark performed a toxicological assessment of an individual occupationally exposed to refined petroleum hydrocarbons who later developed a leukogenic disease. A review of the individual’s medical and occupational history was performed to prepare a qualitative exposure assessment. The exposu re assessment was evaluated against the known outcomes in published literature to exposure to refined petroleum hydrocarbons.
The results of the assessment and literature have been provided in a declaration to the court.
Case Result: Judgement in favor of defendant.
SELECTED AIR MODELING RESEARCH/PROJECTS
Client – Confidential
Dr. Clark performed a comprehensive evaluation of criteria pollutants, air toxins, and particulate matter emissions from a carbon black production facility to determine the impacts on the surrounding communities. The results of the dispersion model will be used to estimate acute and chronic exposure concentrations to multiple contaminants and will be incorporated into a comprehensive risk evaluation.
Client – Confidential
Dr. Clark performed a comprehensive evaluation of air toxins and particulate matter emissions from a railroad tie manufacturing facility to determine the impacts on the surrounding communities. The results of the dispersion model have been used to estimate acute and chronic exposure concentrations to multiple contaminants and have been incorporated into a comprehensive risk evaluation.
Client – Los Angeles Alliance for a New Economy (LAANE), Los Angeles, California
Dr. Clark is advising the LAANE on air quality issues related to current flight operations at the Los Angeles International Airport (LAX) operated by the Los Angeles World Airport (LAWA) Authority. He is working with the LAANE and LAX staff to develop a comprehensive strategy for meeting local community concerns over emissions from flight operations and to engage federal agencies on the issue of local impacts of community airports.
Client – City of Santa Monica, Santa Monica, California Dr. Clark is advising the City of Santa Monica on air quality issues related to current flight operations at the facility. He is working with the City staff to develop a comprehensive strategy for meeting local community concerns over emissions from flight operations and to engage federal agencies on the issue of local impacts of community airports.
Client: Omnitrans, San Bernardino, California
Dr. Clark managed a public health survey of three communities near transit fueling facilities in San Bernardino and Montclair California in compliance with California Senate Bill 1927. The survey included an epidemiological survey of the effected communities, emission surveys of local businesses, dispersion modeling to determine potential emission concentrations within the communities, and a comprehensive risk assessment of each community. The results of the study were presented to the Governor as mandated by Senate Bill 1927.
Client: Confidential, San Francisco, California
Summarized cancer types associ ated with exposure to meta ls and smoking. Researched the specific types of cancers a ssociated with exposure to me tals and smoking. Provided causation analysis of the association betw een cancer types and exposure for use by non-public health professionals.
Client: Confidential, Minneapolis, Minnesota
Prepared human health risk assessment of workers exposed to VOCs from neighboring petroleum storage/transport facility. Reviewed the systems in place for distribution of petroleum hydrocarbons to identify ch emicals of concern (COCs), prepared comprehensive toxicological summaries of COCs, and quantified potential risks from carcinogens and non-carcinogens to receptors at or adjacent to site. This evaluation was used in the support of litigation.
Client – United Kingdom Environmental Agency
Dr. Clark is part of team that performed comprehensive evaluation of soil vapor intrusion of VOCs from former landfill adjacent residences for the United Kingdom’s Environment Agency. The evaluation included collection of liquid and soil vapor samples at site, modeling of vapor migration using the Johnson Ettinger Vapor Intrusion model, and calculation of site-specific health based vapor thresholds for chlorinated solvents, aromatic hydrocarbons, and semi-volatile organic compounds. The evaluation also included a detailed evaluation of the use, chemi cal characteristics, fate and transport, and toxicology of chemicals of concern (COC). The results of the evaluation have been used as a briefing tool for public health professionals.
EMERGING/PERSISTENT CONTAMINANT RESEARCH/PROJECTS
Client: Ameren Services, St. Louis, Missouri
Managed the preparation of a comprehensive human health risk assessment of workers and residents at or near an NPL site in Missouri. The former operations at the Property included the servicing and repair of electrical transformers, which resulted in soils and groundwater beneath the Property and adja cent land becoming impacted with PCB and chlorinated solvent compounds. The results were submitted to U.S. EPA for evaluation and will be used in the final ROD.
Client: City of Santa Clarita, Santa Clarita, California Dr. Clark is managing the oversight of the characterization, remediation and development activities of a former 1,000 acre munitions manufacturing facility for the City of Santa Clarita. The site is impacted with a number of contaminants including perchlorate, unexploded ordinance, and vola tile organic compounds (VOCs). The site is currently under a number of regulatory consent orders, including an Immanent and Substantial Endangerment Order. Dr. Clark is assisting the impacted municipality with the development of remediation strategies, interaction with the responsible parties and stakeholders, as well as interfacing with the regulatory agency responsible for oversight of the site cleanup.
Client: Confidential, Los Angeles, California
Prepared comprehensive evaluation of perchlorate in environment. Dr. Clark evaluated the production, use, chemical characteristics, fate and transport, toxicology, and remediation of perchlorate. Perchlorates form the basis of solid rocket fuels and have recently been detected in water supplies in the United States. The results of this research were presented to the USEPA, National GroundWater, and ultimately published in a recent book entitled Perchlorate in the Environment.
Client – Confidential, Los Angeles, California
Dr. Clark is performing a comprehensive revi ew of the potential for pharmaceuticals and their by-products to impact groundwater and surface water supplies. This evaluation will include a review if available data on the history of pharmaceutical production in the United States; the chemical characteristics of various ph armaceuticals; environmental fate and transport; uptake by xenobiotics; the potential effects of pharmaceuticals on water treatment systems; and the potential threat to public health. The results of the evaluation may be used as a briefing tool for non-public health professionals.
PUBLIC HEALTH/TOXICOLOGY
Client: Brayton Purcell, Novato, California
Dr. Clark performed a toxicological assessment of residents exposed to methyl-tertiary butyl ether (MTBE) from leaking underground storage tanks (LUSTs) adjacent to the subject property. The symptomology of residents and guests of the subject property were evaluated against the known outcomes in published literature to exposure to MTBE. The study found that residents had been exposed to MTBE in their drinking water; that concentrations of MTBE detected at the site were above regulatory guidelines; and, that the symptoms and outcomes expressed by residents and guests were consistent with symptoms and outcomes documented in published literature.
Client: Confidential, San Francisco, California
Identified and analyzed fifty years of epid emiological literature on workplace exposures to heavy metals. This research resulted in a summary of the types of cancer and non-cancer diseases associated with occupa tional exposure to chromium as well as the mortality and morbidity rates.
Client: Confidential, San Francisco, California
Summarized major public health research in United States. Identified major public health research efforts within United States over last twenty year s. Results were used as a briefing tool for non-public health professionals.
Client: Confidential, San Francisco, California
Quantified the potential multi-pathway dose received by humans from a pesticide applied indoors. Part of team that developed exposure model and evaluated exposure concentrations in a comprehensive report on the plausible range of doses received by a specific person. This evaluation was used in the support of litigation.
Client: Covanta Energy, Westwood, California
Evaluated health risk from metals in biosolids applied as soil amendment on agricultural lands. The biosolids were created at a forest waste cogeneration facility using 96% whole tree wood chips and 4 percent green waste. Mass loading calculations were used to estimate Cr(VI) concentrations in agricultura l soils based on a maximum loading rate of 40 tons of biomass per acre of agricultural soil. The results of the study were used by the Regulatory agency to determine that the application of biosolids did not constitute a health risk to workers applying the biosolids or to residences near the agricultural lands.
Client – United Kingdom Environmental Agency
Oversaw a comprehensive toxicological evaluation of methyl-tertiary butyl ether (MtBE) for the United Kingdom’s Environment Agency. The evaluation included available data on the production, use, chemical characteris tics, fate and trans port, toxicology, and remediation of MtBE. The results of the evaluation have been used as a briefing tool for public health professionals.
Client – Confidential, Los Angeles, California
Prepared comprehensive evaluation of tertiary butyl alcohol (TBA) in municipal drinking water system. TBA is the primary breakdown product of M tBE, and is suspected to be the primary cause of M tBE toxicity. This evaluation will include available information on the production, use, chemical characteristic s, fate and transport in the environment, absorption, distribution, routes of detoxificat ion, metabolites, carcinogenic potential, and remediation of TBA. The results of the evaluation were used as a briefing tool for non- public health professionals.
Client – Confidential, Los Angeles, California
Prepared comprehensive evaluation of methyl tertiary butyl ether (MTBE) in municipal drinking water system. MTBE is a chemical added to gasoline to increase the octane rating and to meet Federally mandated emission criteria. The evaluation included available data on the production, use, chemi cal characteristics, fate and transport, toxicology, and remediation of MTBE. The results of the evaluation have been were used as a briefing tool for non-public health professionals.
Client – Ministry of Environment, Lands & Parks, British Columbia Dr. Clark assisted in the development of water quality guidelines for methyl tertiary-butyl ether (MTBE) to protect water uses in British Columbia (BC). The water uses to be considered includes freshwater and marine life, wildlife, industrial, and agricultural (e.g., irrigation and livestock watering) water uses. Guidelines from other jurisdictions for the protection of drinking water, recreation and aesthetics were to be identified.
Client: Confidential, Los Angeles, California
Prepared physiologically based pharmacokinetic (PBPK) assessment of lead risk of receptors at middle school built over former in dustrial facility. This evaluation is being used to determine cleanup goals and will be basis for regulatory closure of site.
Client: Kaiser Venture Incorporated, Fontana, California Prepared PBPK assessment of lead risk of r eceptors at a 1,100-acre former steel mill.
This evaluation was used as the basis for gran ting closure of the site by lead regulatory agency.
RISK ASSESSMENTS/REMEDIAL INVESTIGATIONS
Client: Confidential, Atlanta, Georgia
Researched potential exposure and health risks to community members potentially exposed to creosote, polycyclic aromatic hydrocarbons, pentachlorophenol, and dioxin compounds used at a former wood treatm ent facility. Prepar ed a comprehensive toxicological summary of the chemicals of concern, including the chemical characteristics, absorption, distribution, a nd carcinogenic potential. Prepared risk characterization of the carcinogenic and non-carcinogenic chemicals based on the exposure assessment to quantify the potential risk to members of the surrounding community. This evaluation was used to help settle class-action tort.
Client: Confidential, Escondido, California
Prepared comprehensive Preliminary Endangerment Assessment (PEA) of dense non- aqueous liquid phase hydrocarbon (chlorinated solvents) contamination at a former printed circuit board manufacturing facility. This evaluation was used for litigation support and may be used as the basis for r eaching closure of the site with the lead regulatory agency.
Client: Confidential, San Francisco, California
Summarized epidemiological evidence for connective tissue and autoimmune diseases for product liability litigation. Identified epidemiological research efforts on the health effects of medical prostheses. This research was used in a meta-analysis of the health effects and as a briefing tool for non-public health professionals.
Client: Confidential, Bogotá, Columbia
Prepared comprehensive evaluation of the pot ential health risks as sociated with the redevelopment of a 13.7 hectares plastic manufacturing facility in Bogotá, Colombia The risk assessment was used as the basis for the remedial goals and closure of the site.
Client: Confidential, Los Angeles, California
Prepared comprehensive human health risk assessment of students, staff, and residents potentially exposed to heavy metals (principally cadmium) and VOCs from soil and soil vapor at 12-acre former crude oilfield and muni cipal landfill. The site is currently used as a middle school housing approximately 3,000 children. The evaluation determined that the site was safe for the current and future uses and was used as the basis for regulatory closure of site.
Client: Confidential, Los Angeles, California
Managed remedial investigation (RI) of heavy metals and volatile organic chemicals (VOCs) for a 15-acre former manufacturing f acility. The RI investigation of the site included over 800 different sampling locations and the collection of soil, soil gas, and groundwater samples. The s ite is currently used as a year round school housing approximately 3,000 children. The Remedial Investigation was performed in a manner that did not interrupt school activities and met the time restrictions placed on the project by the overseeing regulatory agency. The RI Report identified the off-site source of metals that impacted groundwater beneath the site and the sources of VOCs in soil gas and groundwater. The RI included a numerical model of vapor intrusion into the buildings at the site from the vadose zone to determine exposure concentrations and an air dispersion model of VOCs from the proposed soil vapor treatment system. The Feasibility Study for the Site is currently bei ng drafted and may be used as the basis for granting closure of the site by DTSC.
Client: Confidential, Los Angeles, California
Prepared comprehensive human health risk assessment of students, staff, and residents potentially exposed to heavy metals (principally lead), VOCs, SVOCs, and PCBs from soil, soil vapor, and groundwater at 15-acre fo rmer manufacturing facility. The site is currently used as a year round school housing approximately 3,000 children. The evaluation determined that the site was safe for the current and future uses and will be basis for regulatory closure of site.
Client: Confidential, Los Angeles, California
Prepared comprehensive evaluation of VOC vapor intrusion into classrooms of middle school that was former 15-acre industrial facility. Using the Johnson-Ettinger Vapor Intrusion model, the evaluation determined accep table soil gas concentrations at the site that did not pose health threat to students, staff, and residents. This evaluation is being used to determine cleanup goals and will be basis for regulatory closure of site.
Client –Dominguez Energy, Carson, California
Prepared comprehensive evaluation of the pot ential health risks as sociated with the redevelopment of 6-acre portion of a 500-acre oil and natural gas production facility in Carson, California. The risk assessment was used as the basis for closure of the site.
Kaiser Ventures Incorporated, Fontana, California
Prepared health risk assessment of semi-volatile organic chemicals and metals for a fifty- year old wastewater treatment facility used at a 1,100-acre former steel mill. This evaluation was used as the basis for granting closure of the site by lead regulatory agency.
ANR Freight - Los Angeles, California
Prepared a comprehensive Preliminary Enda ngerment Assessment (PEA) of petroleum hydrocarbon and metal contamination of a former freight depot. This evaluation was as the basis for reaching closure of the site with lead regulatory agency.
Kaiser Ventures Incorporated, Fontana, California
Prepared comprehensive health risk assessment of semi-volatile organic chemicals and metals for 23-acre parcel of a 1,100-acre form er steel mill. The h ealth risk assessment was used to determine clean up goals and as the basis for granting closure of the site by lead regulatory agency. Air dispersion modeling using ISCST3 was performed to determine downwind exposure point concentr ations at sensitive receptors within a 1 kilometer radius of the site. The results of the health risk assessment were presented at a public meeting sponsored by the Department of Toxic Substances Control (DTSC) in the community potentially affected by the site.
Unocal Corporation - Los Angeles, California
Prepared comprehensive assessment of petroleum hydrocarbons and metals for a former petroleum service station located next to sens itive population center (elementary school).
The assessment used a probabilistic approach to estimate risks to the community and was used as the basis for granting closure of the site by lead regulatory agency.
Client: Confidential, Los Angeles, California
Managed oversight of remedial investigation most contaminated heavy metal site in California. Lead concentrations in soil exce ss of 68,000,000 parts per billion (ppb) have been measured at the site. This State Supe rfund Site was a former hard chrome plating operation that operated for approximately 40-years.
Client: Confidential, San Francisco, California
Coordinator of regional monitoring program to determine background concentrations of metals in air. Acted as liaison with SCAQMD and CARB to perform co-location sampling and comparison of accepted regulatory method with ASTM methodology.
Client: Confidential, San Francisco, California
Analyzed historical air monitoring data for South Coast Air Basin in Southern California and potential health risks related to ambient concentrations of carcinogenic metals and volatile organic compounds. Identified and reviewed the available literature and calculated risks from toxins in South Coast Air Basin.
IT Corporation, North Carolina
Prepared comprehensive evaluation of potential exposure of workers to air-borne VOCs at hazardous waste storage facility unde r SUPERFUND cleanup decree. Assessment used in developing health based clean-up levels.
Professional Associations
American Public Health Association (APHA)
Association for Environmental Health and Sciences (AEHS) American Chemical Society (ACS)
California Redevelopment Association (CRA)
International Society of Environmental Forensics (ISEF) Society of Environmental Toxicology and Chemistry (SETAC)
Publications and Presentations:
Books and Book Chapters
Sullivan, P., J.J. J. Clark, F.J. Agardy, and P.E. Rosenfeld. (2007). Synthetic Toxins In The Food, Water and Air of American Cities. Elsevier, Inc. Burlington, MA.
Sullivan, P. and J.J. J. Clark . 2006. Choosing Safer Foods, A Guide To Minimizing Synthetic Chemicals In Your Diet. Elsevier, Inc. Burlington, MA.
Sullivan, P., Agardy, F.J., and J.J.J. Clark . 2005. The Environmental Science of Drinking Water. Elsevier, Inc. Burlington, MA.
Sullivan, P.J., Agardy, F.J., Clark, J.J.J. 2002. America’s Threatened Drinking Water:
Hazards and Solutions. Trafford Publishing, Victoria B.C.
Clark, J.J.J. 2001. “TBA: Chemical Properties, Production & Use, Fate and Transport, Toxicology, Detection in Groundwater, and Regulatory Standards” in Oxygenates in the Environment. Art Diaz, Ed.. Oxford University Press: New York.
Clark, J.J.J. 2000. “Toxicology of Perchlorate” in Perchlorate in the Environment.
Edward Urbansky, Ed. Kluwer/Plenum: New York.
Clark, J.J.J. 1995. Probabilistic Forecastin g of Volatile Organic Compound Concentrations At The Soil Surface From Contaminated Groundwater. UMI.
Baker, J.; Clark, J.J.J. ; Stanford, J.T. 1994. Ex Situ Remediation of Diesel Contaminated Railroad Sand by Soil Washing. Principles and Practices for Diesel Contaminated Soils, Volume III. P.T. Kost ecki, E.J. Calabrese, and C.P.L. Barkan, eds. Amherst Scientific Publishers, Amherst, MA. pp 89-96.
Journal and Proceeding Articles
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 Equialency Quotients (TEQ) In Two Populations Near Wood Treatment Facilities. Organohalogen Compounds, Volume 70 (2008) page 002254.
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, Volume 70 (2008) page 000527 Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. (2007). “Attic Dust And Human Blood Samples Collected Near A Former Wood Treatment Facility.” Environmental Research. 105:194-199.
Rosenfeld, P.E., Clark, J. J., Hensley, A.R., and Suffet, I.H. 2007. “The Use Of An Odor Wheel Classification Fo r The Evaluation of Human Health Risk Criteria For Compost Facilities” Water Science & Technology. 55(5): 345-357.
Hensley A.R., Scott, A., Rosenfeld P.E., Clark, J.J.J. 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, August 21 – 25, 2006. Radisson SAS Scandinavia Hotel in Oslo Norway.
Rosenfeld, P.E., Clark, J. J. and Suffet, I.H. 2005. “The Value Of An Odor Quality Classification Scheme For Compost Facility Evaluations” The U.S. Composting Council’s 13
th Annual Conference January 23 - 26, 2005, Crowne Plaza Riverwalk, San Antonio, TX.
Rosenfeld, P.E., Clark, J. J. and Suffet, I.H. 2004. “The Value Of An Odor Quality Classification Scheme For Urban Odor” WEFTEC 2004. 77th Annual Technical Exhibition & Conference October 2 - 6, 2004, Ernest N. Morial Convention Center, New Orleans, Louisiana.
Clark, J.J.J . 2003. “Manufacturing, Use, Regulation, and Occurrence of a Known Endocrine Disrupting Chemical (EDC), 2,4-Dichlorophnoxyacetic Acid (2,4-D) in California Drinking Water Supplies.” National Groundwater Association Southwest Focus Conference: Water Supply and Em erging Contaminants. Minneapolis, MN.
March 20, 2003.
Rosenfeld, P. and J.J.J. Clark . 2003. “Understanding Historical Use, Chemical Properties, Toxicity, and Regulatory Guid ance” National Groundwater Association Southwest Focus Conference: Water Supply and Emerging Contaminants. Phoenix, AZ. February 21, 2003.
Clark, J.J.J., Brown A. 1999. Perchlorate Contamination: Fate in the Environment and Treatment Options. In Situ and On-Site Bioremediation, Fifth International Symposium. San Diego, CA, April, 1999.
Clark, J.J.J. 1998. Health Effects of Perchlorat e and the New Reference Dose (RfD).
Proceedings From the Groundwater Resour ce Association Seventh Annual Meeting, Walnut Creek, CA, October 23, 1998.
Browne, T., Clark, J.J.J. 1998. Treatment Options For Perchlorate In Drinking Water.
Proceedings From the Groundwater Resour ce Association Seventh Annual Meeting, Walnut Creek, CA, October 23, 1998.
Clark, J.J.J., Brown, A., Rodriguez, R. 1998. The Public Health Implications of MtBE and Perchlorate in Water: Risk Manage ment Decisions for Water Purveyors.
Proceedings of the National Ground Water Association, Anahei m, CA, June 3-4, 1998.
Clark J.J.J., Brown, A., Ulrey, A. 1997. Impacts of Perchlorate On Drinking Water In The Western United States. U.S. EPA Symposium on Biological and Chemical Reduction of Chlorate and Perchlorate, Cincinnati, OH, December 5, 1997.
Clark, J.J.J. ; Corbett, G.E.; Kerger, B.D.; Finley , B.L.; Paustenbach, D.J. 1996.
Dermal Uptake of Hexavalent Chromium In Human Volunteers: Measures of Systemic Uptake From Immersion in Water At 22 PPM. Toxicologist. 30(1):14.
Dodge, D.G.; Clark, J.J.J.; Kerger, B.D.; Richter, R.O.; Fi nley, B.L.; Paustenbach, D.J. 1996. Assessment of Airborne Hexavalent Chromium In The Home Following Use of Contaminated Tapwater. Toxicologist. 30(1):117-118.
Paulo, M.T.; Gong, H., Jr.; Clark, J.J.J. (1992). Effects of Pretreatment with Ipratroprium Bromide in COPD Patients Exposed to Ozone. American Review of Respiratory Disease. 145(4):A96.
Harber, P.H.; Gong, H., Jr.; Lachenbruch, A.; Clark, J.; Hsu, P. (1992). Respiratory Pattern Effect of Acute Sulfur Dioxide Exposure in Asthmatics. American Review of Respiratory Disease. 145(4):A88.
McManus, M.S.; Gong, H., Jr.; Clements, P.; Clark, J.J.J. (1991). Respiratory Response of Patients With Interstitial Lung Disease To Inhaled Ozone. American Review of Respiratory Disease. 143(4):A91.
Gong, H., Jr.; Simmons, M.S.; McManus, M.S.; Tashkin, D.P.; Clark, V.A.; Detels, R.; Clark, J.J. (1990). Relationship Between Responses to Chronic Oxidant and Acute Ozone Exposures in Residents of Los Angeles County. American Review of Respiratory Disease. 141(4):A70.
Tierney, D.F. and J.J.J. Clark. (1990). Lung Polyamine Content Can Be Increased By Spermidine Infusions Into Hyperoxic Rats. American Review of Respiratory Disease. 139(4):A41.
EXHIBIT B
Letter EMY WI 23-002.15
July 17, 2023
Richard M. Franco
Adams Broadwell Joseph & Cardozo
601 Gateway Boulevard, Suite 1000
South San Francisco, CA 94080
SUBJECT: City of Santa Clarita Shadowbox Studio Project FEIR Comments on the Draft EIR and Responses
Shadowbox Studio Project
Dear Mr. Franco
Wilson Ihrig previously provided comments to you on May 19 , 2023 regarding the City of Santa Clarita Shadowbox Studio Project Draft Environmental Impact Report (DEIR). The Noise and Vibration Impact Analysis is contained in Section 4.11 of the DEIR, with supplemental calculations in Appendix J Noise Study (Noise Study).
The Final Environmental Impact Report (FEIR) was recently provided on July 6 th in advance of the next Planning Commission hearing (on July 18th). In that FEIR, responses to comments (RTC) on the Noise and Vibration Impact Analysis were provided starting on page 2-1004. In addition, Wilson Ihrig has reviewed the Staff Report prepared for the June 20 th hearing, including a memorandum titled “Shadowbox Studios Operations FAQ’s.” This letter focuses on the RTC and the new operational information provided in the Staff Report.
1. The RTC states that there is substantial evidence to support the use of an absolute threshold only as the basis of analysis [FEIR 2-1005].
• The RTC is unresponsive to our comment regarding the CEQA threshold. The CEQA Guidelines clearly state that a project would normally have a significant effect on the environment if the project would result in “generation of a substantial temporary or permanent increase in ambient noise levels” [DEIR page 4.11-11]. • The RTC states that an absolute thre shold approach is consistent with other jurisdictions within the state and that Caltrans does not have a threshold for a numeric increase in ambient noise levels [FEIR 2 -1005]. Caltrans has used 12 dB in the past, consistent with FHWA guidance of using 5 t o 15 dB. In its current discussion of CEQA , the Caltrans Traffic Noise Analysis Protocol (Protocol)1 states that the significance of noise impacts is determined based on the project-related increase in noise and, while no single numerical threshold is use d on all projects, what is considered a substantial increase can vary depending on current environment [Protocol page 7-1]. Caltrans allows for project -specific ambient thresholds to account for difference in sensitivity to noise increase in quiet rural an d noisy urban environments.
1 https://dot.ca.gov/-/media/dot-media/programs/environmental-analysis/documents/env/traffic-noise-protocol- april-2020-a11y.pdf
WILSON IHRIG
FOUND Residences
Discussion of RTC on the Noise Analysis
• The RTC posits that “ the significance of the magnitude of an ambient noise level increase is inherently accounted for by the City’s fixed noise limits utilized for the [operational] noise analysis in the Draft EIR ” [FEIR 2 -1006]. This is unsubstantiated, since the ambient environment varies greatly within the City , as shown by the Project measurements on the north and south side of the site.
• The RTC states that compliance with the FTA is sufficient to protect human health [FEIR 2- 10006]. The cited FTA Transit Noise and Vibration Impact Assessment Manual is a guidance document, and it discourages projects against using its absolute criteria values without consideration of local conditions (FTA page 179, see Figure 1 below); the FTA threshold could be too high and the RTC provides no discussion why 80 dBA should be deemed acceptable.
Therefore, it is not accurate to characterize that the DEIR analysis has completely addressed and protected human health.
Figure 1 FTA Manual, Section on Construction Noise and Vibration (page 179)
• Relying solely on an 80 dB absolute limit, would allow for a 31 dB increase at NM4 and a 33 dB increase at NM6. As stated in the DEIR, “a 5 dB change is generally recognized as a clearly discernible difference” [DEIR page 4.11-14] and as stated by Caltrans, “a 10 dB increase [is] generally perceived as a doubling of loudness” [Caltrans page 3-2]. As shown in Table 1 of our original letter, predicted construction noise levels range from 64 to 83 dBA at 200 feet. The RTC does not provide a rational explanation for why an increase of more than 30 dB during grading and 15-27 dB during other phases is an insignificant increase.
2. The RTC states that “permanent noise level increases associated with continuous operational noise sources typically result in adverse community reaction at lower magnitudes of increase than temporary noise level increases associated with construction activities” [FEIR 2-1006]. • The RTC is unresponsive to our comment regarding the CEQA threshold. The CEQA Guidelines clearly state that a project would normally have a significant effect on the environment if the project would result in “generation of a substan tial temporary or permanent increase in ambient noise levels” [DEIR page 4.11-11]. • The RTC cites Caltrans regarding “temporary” activities [FEIR 2-1021]. The text quoted from the Caltrans Technical Noise Supplement to the Traffic Noise Analysis Protocol (TeNS)2 refers to vibration damage not community annoyance . Caltrans discusses variation in residents’ tolerance toward construction noise depending on duration, but in the context of stressing the importance of a good community communication plan [TeNS 7-27].
2 https://dot.ca.gov/-/media/dot-media/programs/environmental-analysis/documents/env/tens-sep2013- a11y.pdf
WILSON IHRIG
FOUND Residences
Discussion of RTC on the Noise Analysis
• Citing one agency, Caltrans, is not equivalent to “expert state agencies agree that construction noise levels are more tolerable because construction activities are temporary” as asserted in the RTC [FEIR 2-1021].
3. The RTC states that the construction noise predictions in our original letter are overestimated. • The RTC states that “equipment is typically operated in groups of two or three on different parts of the site” [FEIR 2 -1022]. The FTA Manual has two options of thresholds and assessment procedures for construction noise: general and detailed assessment. A detailed assessment requires information on the equipment to be used and site layout, which the DEIR document provides and the Project used the detailed assessment FTA threshold of 80 dBA in the DEIR construction noise analysis. Per Chapter 12 of the FTA Manual , the det ailed construction assessment uses ALL equipment for each phase, not 2 -3 pieces [FTA 179] and accounts for the percent of time each piece is used by applying a usage factor [FTA 178]. The predictions included in Table 1 of our original letter used usage fa ctors provided by FHWA RCNM, which is standard practice.
• The RTC posits that FTA guidance recommends the use of a distance to the center of the site for predictions and that 500 feet should have been used for calculations [FEIR 2-1022]. The detailed assessment procedure in the FTA Manual uses distances to each piece of equipment, not the center of the site. And, as stated in the DEIR [DEIR 4.11-15], the average distance used in the original noise analysis was 200 feet and the closest distance was 105 feet (used specifically for grading activities in Table 1, per site plan of the closest lot). The construction noise predictions in our letter use those same distances (there is a missing footnote for the grading calculation).
• Finally, the RTC claims that the predictions in our original letter overestimate noise based on a misinterpretation of the equipment tables provided in the DEIR Air Quality Report [FEIR 2- 1022]. This is incorrect. As stated in the RTC, “tractors/loaders/backhoe” amount two was assumed to mean two pieces of equipment, not two each. Per Eq. 7-1 in the FTA Manual:
Using an 80 dB reference level and 40 % usage factor, the Leq for one tractor, loader, or backhoe at 105 feet is 70 dBA and two pieces are 73 dBA. For building construction, three pieces at 200 feet are 69 dBA.
Please feel free to contact me with any questions on this information.
Very truly yours,
WILSON IHRIG
Ani Toncheva
Senior Consultant
ANI TONCHEVA
Senior Consultant
Since joining the firm in 2011, Ani has
con
ducted analyses for
transit
systems, vibration sensitive research facilities, public infrastructure, construction,
and other environmental noise. She has contributed to
literature reviews, including research on current practices of historical preservation.
She has extensive
e
xperience working on construction
projects in New York City
and is
well versed in local noise codes.
Education
B.A.
,
Physics
;
Bard College, New York
Professional Associations
Member
, National Council of Acoustical Consultants (NCAC)
Member
,
Acoustical Society of America (ASA)
Board Member,
Transportation Research Forum (TRF), NY Chapter and
I
nternational board
Research Paper
NCHRP 25
-
25,
Current Practices to Address Construction Vibration and Potential Effects to Historic Buildings
Adjacent to Transportation Projects
Relevant
Experience
BART Berryessa Station Transit Noise Impact and Mitigation, San Jose, CA
Assisted with noise
predictions and barrier design recommendations.
Massachusetts Bay Transportation Authority (MBTA) Green Line Extension (GLX), Boston , MA
Lead analyst on noise predictions and barrier design.
RTD Eagle P3 Northwest Corridor Noise
and Impacts, Denver, CO
Assisted with data analysis and
helped prepare final technical report.
Alameda CTC, I
-
880 Interchange Improvements Project (Whipple
Road
-
Industrial Southwest
and Industrial Parkway West), Hayward, CA
Project Manager for traffic noise study.
Alameda CTC, I
-
80/Ashby Avenue Interchange Improvements, Berkeley, CA
Project Manager for
traffic noise study.
Millennium Bulk Terminal, Longview, WA
Prepared noise analysis for the project’s NEPA and SEPA environmental impact statements.
Peninsula Humane Society & SPCA Haskin Hill Sanctuary, Loma Mar, CA
Prepared an
environmental study for a planned animal sanctuary in Loma Mar.
Analog (ArtX) Hotel, Palo Alto, CA
Prepared preliminary basis of design guidelines for a new five -
story boutique hotel in a residential area.
Sunnydale Block 3A & 3B Mixed
-
Use
Residential Development, San Francisco, CA
Prepared
a CCR
Title 24 Noise Study Report for two
,
mixed
-
use
,
5 -
story buildings
.
WILSON IHRIG
Ani Toncheva
–
Page
2 Columbia University Medical Center Medical and Graduate Education Building, New York, NY
Conducted baseline noise
survey and performed attended noise measurements during preliminary construction work.
Hudson Yards Tower C Foundations and Utilities, New York, NY
Conducted a baseline noise
survey prior to construction work including a combination of long -
term u
nattended and short
-
term
attended noise measurements.
PANYNJ
Lincoln Tunnel Helix Rehabilitation,
NJ
Assisted in developing construction noise control
and mitigation plan and implementing a remote long
-
term noise monitoring program at three
locations.
M
SK 74th Street,
New York, NY
Conducted baseline noise survey, assisted in developing construction noise control and mitigation plan, and implemented a long -
term noise monitoring
program at two locations.
NY
MTA No. 7 Line Subway Extension
Ventilation Facility Construction
, New York, NY
The
project involved mining and lining of two shafts and construction of a 2 -
story ventilation building
.
NY
MTA ESA/LIRR Grand Central Terminal Fit
-
Out,
New York, NY
Prepared the Contractor’s noise
and vibration control plan
updates for fit
-
out work conducted underground at the Grand Central
Terminal Suburban Level.
San Francisco Planning Department,
Alameda Street Wet Weather Tunnel and Folsom Area
Sewer
Improvement
, San Francisco, CA
N
oise and vibration analysis for Folsom Area stormwater
infrastructure improvements
.
World T
rade Center Vehicle Security Center
, New York, NY
Conducted baseline noise surveys,
assisted in developing construction noise control plans, and implementing a remote long -
term
noise monitoring program
.
50 Pine Street Condominiums, New York, NY
Project involved evaluating
m
echanic
al
noise at residential
dwelling units for NYC noise code
Uptown Newport, Newport Beach, CA
Evaluation of noise levels due to mechanical equipment at adjacent property.
EXHIBIT C
1 Shawn Smallwood, PhD
3108 Finch Street
Davis, CA 95616
Erika Iverson, Senior Planner
City Of Santa Clarita
Community Development Department
23920 Valencia Boulevard, Suite 302
Santa Clarita, CA 91355 15 July 2023
RE: Shadowbox Studios Project
Dear Ms. Iverson,
I write to reply to the City’s responses to my comments on potential impacts to wildlife that were analyzed in the Draft Environmental Impact Report (“DEIR”) that was prepared for the Shadowbox Studios Project. I also reply to some of the responses to 22 May 2023 comments from the California Department of Fish and Wildlife. My qualifications as an expert on wildlife ecology were summarized in my comment letter of 19 May 2023.
Please note that some of the responses address multiple comments or issues. In these cases, I split out my replies to responses, and where I did this, I repeat the numbered response but I add a sequential alphabetical letter to each.
Response to Comment No. O6-40
The comment states their qualifications as a biologist for providing comments on the Draft EIR and biological resources report. The comment also introduces and states the qualifications for wildlife biologist Noriko Smallwood, describes the weather and vegetation observed by Ms. Smallwood during the site visit conducted on May 14, 2023, and provides photographs and a table listing the wildlife observed during the site visit.
According to Ms. Smallwood, 40 species of vertebrate wildlife were observed on the Project Site during a 3.52-hour survey. Ms. Smallwood’s survey results are noted for the administrative record and will be forwarded to the decision-makers for review and consideration.
Reply: The response is essentially a “comment noted” response. It ignores significant environmental issues that are raised by my comments, but which the City lumps into one numbered comment. According to the City’s response, my comment is simply that Noriko Smallwood detected 40 species of wildlife during her 3.52-hour survey. In truth, my comments also identified the 6 special-status species she detected at the project site, as well as her detections of ecological keystone species whose presence raise the likelihoods that special-status species occur on the site but which had not yet been detected by her or by Rincon. My comments also raise the issue of evidence of breeding observed by Noriko, and that the site is important to wildlife productivity in the region.
In fact, most of my comments lumped into Comment No. 06-40 are ignored by the City.
2 Response to Comment No. O6-41a
The comment states that a reconnaissance-level survey should serve only as a starting point toward characterization of a site’s wildlife community, but it cannot alone provide an inventory of species that use the site and asserts that a much greater survey effort is needed at the site in order to characterize the existing environmental setting with sufficient accuracy to support a sound impacts analysis. To support this assertion, the comment cites data from past surveys to demonstrate that more time spent on or repeat surveys result in more species detected. The presented data are noted for the record and will be forwarded to the decision-makers for review and consideration.
Reply: The response is another “comment noted” response that does not seriously consider my comments. The lead agency needs to address my comment “in detail giving reasons why” the comment is “not accepted. There must be good faith, reasoned analysis in response,”1 particularly in response to comments that are made by agencies or experts.2 I note, however, that the response does not attempt to refute the relationship I summarize between the number of species detected in a survey and the survey’s founding level of effort. I assume the City agrees with my comment that the effort put into a survey largely determines the number of species detected at the project site.
Response to Comment No. O6-41b
The reconnaissance survey conducted by Rincon was not intended to be a comprehensive inventory of all species that inhabit the Project Site, and it is not represented as such in the Rincon Biological Resources Assessment (BRA).
Reply: According to Rincon (2023), “All biological resources encountered on-site were recorded.” This statement falsely implies that Rincon recorded all biological resources that were on the project site. Adding to this impression that Rincon’s survey should be regarded as an inventory is Rincon’s (2023) interpretation of whichever biological resources had not been detected during the Rincon’s survey as evidence of absence. For example, breeding Cooper’s hawks on site is regarded as unlikely because Rincon (2023) failed to see a Cooper’s hawk nest during its surveys on one day in January. In another example, Rincon (2023) uses its survey outcome as evidence of low occurrence likelihood of American badger. The impression given by Rincon (2023) is that if its biologists failed to detect a Cooper’s hawk nest or sign of American badger at burrows, then the site does not support breeding by Cooper’s hawks or use by badgers. Species that Rincon detected are characterized as “present,” whereas those that Rincon did not detect are treated as unlikely, consistent with the outcome of an inventory.
Except for Rincon’s (2023) caveat that the biological reconnaissance survey was limited by the environmental conditions present at the time of the survey, nowhere does Rincon (2023) or the DEIR characterize either the list of plant or wildlife species observed on
1 14 CCR § 15088(c); see Laurel Heights Improvement Assn. v. Regents of University of California (1993) 6 Cal.4th 1112, 1124 (“Laurel II”); The Flanders Foundation v. City of Carmel-by-the-Sea (2012) 202 Cal.
App. 4th 603, 615.
2 Berkeley Keep Jets Over the Bay Comm. v. Board of Port Commissioners (2001) 91 Cal.App.4th 1344, 1367, 1371; People v. County of Kern (1976) 62 Cal.App.3d 761, 772).
3 site as something other than an inventory. If the lists of species detected were viewed as samples of the plant and wildlife community, then nowhere does Rincon (2023) or the DEIR describe them as samples. Nor are the samples given any sort of context, such as about what percentages of the project site’s plant and wildlife species are represented by the samples.
I agree that the Rincon survey was not a comprehensive inventory of all species that inhabit the Project Site. What it was remains unclear, other than it was an undefined sampling of plants and animals that occur on the project site. No attempt is made by Rincon (2023) or the DEIR to estimate the number of species that were not detected due to insufficient survey effort. This is a poor basis from which to analyze potential project impacts to biological resources.
Response to Comment No. O6-41c
A comprehensive biological inventory of the Project Site is not necessary to support a sound impacts analysis because professional biologists are able to make inferences about the potential for special-status wildlife to occur based upon known ranges, habitat preferences for the species, species occurrence records from scientific database queries, previous reports for the Project Site, and the results of surveys of the Project Site. Based on the results of the initial habitat assessment, focused surveys were performed for specific special-status species determined to have the potential to occur based on the distribution and quality of the vegetation and associated habitats on the Project Site, such as for western burrowing owl and coastal California gnatcatcher. As such, additional repeat or focused surveys are not necessary.
Reply: I agree that a comprehensive biological inventory of the project site is not necessary to support a sound impacts analysis, but not for the reasons cited in the response. An important first step to a sound impacts analysis is an accurate characterization of the existing environmental setting, including the species that compose the site’s plant and animal communities. A single survey in January is not going to support an accurate characterization of the existing environmental setting unless the limitations of the survey are well understood and factored into the characterization of the environmental setting.
Short of an accurate species inventory stemming from field surveys, the analyst should err on the side of caution when determining whether each species whose range overlaps the project site potentially occurs on the project site. Rincon (2023) and the DEIR fail to do this, and in fact misapply CNDDB to establish an unrealistically short list of potentially-occurring species as the starting point of the analysis. And once this unrealistically short list of species is established, the response claims that Rincon’s biologists are able to infer occurrence likelihoods of species based on the very survey completed at the site, but which was not designed nor at all suitable for this purpose; that Rincon’s biologists are able to infer occurrence likelihoods of species based on the very species occurrence databases they queried, none of which are designed or at all suitable for this purpose; Rincon’s biologists are able to infer occurrence likelihoods of species based on known habitat preferences for the species, which are in fact often
4 poorly understood and vulnerable to abuses noted in my comment letter, such as the pigeon-holing of species into unrealistically narrow portions of the environment.
The response further defends the DEIR’s approach to founding its impacts analysis by pointing out that focused surveys were also completed for the two special-status species determined to have some potential to occur. This is true to a degree. The focused surveys were of course focused on particular species, so they were not necessarily the most productive surveys for other species of wildlife that were not the focus of the surveys. Additional species were detected during the focused surveys, but nothing is said in the DEIR about the detection probabilities of these species or of the species that were not detected.
The response fails to address my comment, based on ample data, that the project site hosts a richer wildlife community than the vast majority of the nearly 300 other project sites Noriko Smallwood and I have surveyed in California over the last several years. The response is silent on my use of an analytical bridge between what Noriko found at the project site and what I found at a much more extensively sampled research site, leading to my prediction that the project site hosts at least 163 species of vertebrate wildlife, including 24 special-status species of wildlife.
Response to Comment No. O6-42a
The comment states that the Draft EIR’s surveys of the Project Site for biological resources and reviews of literature, databases, and local experts for documented occurrences of special-status species are incomplete and misleading and that survey limitations should be disclosed. The comment does not specify why the information provided in the Draft EIR is incomplete or misleading, and the comment’s claim is not supported by substantial evidence.
Reply: I commented that “it helps for the analysis to be informed of which biological species are known to occur at the proposed project site, which special-status species are likely to occur, as well as the limitations of the survey effort directed to the site.” Other than Rincon’s (2023) caveat that the biological reconnaissance survey was limited by the environmental conditions present at the time of the survey, there is no discussion of the limitations of the survey effort in the DEIR, not even in the City’s responses to my comments. And in my comments, I also noted that Noriko Smallwood detected multiple species of wildlife at and near the project site that Rincon failed to detect, including 4 special-status species of wildlife. Failing to detect species of wildlife does not necessarily lead to an incomplete and misleading characterization of the existing environmental setting, but it does so if the species that were detected are implied to have been the only species available to be detected. And it does so if the desktop review results in determinations that are refuted by the outside expert’s (Noriko’s) survey finding. In the case of this project, the analysis is incomplete and misleading for the above-stated reasons and for the reasons that followed in my comment letter. Indeed, my comments that were addressed in Response 06-42 were introductory comments to the section of commenting that followed.
5 Response to Comment No. O6-42b
As stated in the BRA prepared for the Project, surveys were conducted in accordance with applicable USFWS and CDFW guidelines and requirements. Literature review consisted of queries of the USFWS Information, Planning and Conservation System, CDFW California Natural Diversity Database (CNDDB), and the California Native Plant Society Online Inventory of Rare, Threatened and Endangered Plants of California.
Furthermore, the BRA stated that the biological reconnaissance survey was limited by the environmental conditions present at the time of the survey.
Reply: Wildlife surveys were not conducted in accordance with applicable USFWS and CDFW guidelines and requirements, which the response fails to identify. I assume the response is referring the guidelines on California gnatcatcher and burrowing owl. If my assumption is accurate, then I disagree that the standards of the recommended guidelines were achieved (see my comment letter). As for the January reconnaissance survey, there were no guidelines to follow in the case of wildlife.
To the rest of the response, it is not enough to go through the motions of querying species occurrence databases; the analysis needs to make use of these data bases as they were intended, and it needs to avoid drawing conclusions that the databases cannot support.
Response to Comment No. O6-42c
As noted in Response to Comment Nos. A1-9 and O6-41, additional focused surveys for SSC species are not necessary to reduce Project impacts to a less-than-significant level.
Reply: The response is incorrect. The surveys completed to date cannot support absence determinations for California gnatcatcher and burrowing owl, because the failed to meet the standards of the available survey guidelines. The protocol-level survey guidelines for these species need to be implemented full as intended to determine whether California gnatcatcher and burrowing owl are present or absent from the project site.
Response to Comment No. O6-43
The comment states that the Rincon’s statement in the BRA that “all biological resources encountered on-site were recorded” is false and misleading because no biologist is capable of recognizing all evidence of wildlife. The comment recommends that the Draft EIR be revised to more carefully report what was seen and understood by the biologists. In addition, the Draft EIR should describe the limitations of the surveys and the reporting of survey outcomes. As discussed above in Response to Comment No.
O6-42, the BRA disclosed the limitations of the biological reconnaissance survey. The last sentence under “FIELD RECONNAISSANCE SURVEY” on page 4.3-16 in Section 4.3, Biological Resources, of the Draft EIR was revised to state that all vertebrate wildlife species observed were documented, as follows (see Section 3.0, Errata and Clarifications to the Draft EIR, of this Final EIR, for this revision):
Representative photographs of the Project Site were taken and an inventory of all plant and vertebrate wildlife species observed was compiled (provided in Appendix D).
6 Reply: The change to the DEIR in the Errata is an improvement by specifying that the species recorded were those that were observed by Rincon’s biologists. However, the change in wording does not go far enough. As I commented, the species that were recorded by Rincon’s biologists were not just the species they observed, but the species they recognized. Again, Rincon’s biologists failed to report harvester ants on the project site, not because harvester ants were absent, but presumably because Rincon’s biologists either know nothing about harvester ants or regarded harvester ants as unimportant.
The change in wording also fails to resolve the false impression that Rincon’s survey was for the purpose of inventory of wildlife species that use the project site. Response to Comment No. O6-41b insisted that Rincon’s (2023) reconnaissance survey was not intended as an inventory of wildlife species, but the last sentence of the language change in the Errata employs the word, inventory. It would be less confusing to write, “Representative photographs of the Project Site were taken and a list of all plant and vertebrate wildlife species observed was compiled. This list represents an unquantified portion of the number of species of plant and vertebrate wildlife species that use the site.”
On the whole, I do not believe the DEIR, as revised, sufficiently characterizes what the species detected by Rincon’s (2023) survey actually represent. The species detected by Rincon do not represent an inventory of the wildlife community, nor do they represent a defined sampling of the wildlife community. Nor does the DEIR accurately characterize what the species represent that occur on the site but were not detected by Rincon’s (2023) survey on one day in January. In fact, these undetected species represent the majority of the species that occur on the project site, including special-status species, many of which have not been analyzed in the DEIR for occurrence likelihood and potential project impacts (see my comment letter).
Response to Comment No. O6-44
The comment states that the duration of the reconnaissance survey is unreported and that Rincon’s biologists should have seen more species of wildlife. This comment is similar to Comment No. O6-7. Please refer to Response to Comment No. O6-7 above.
Reply: I referred to response to comment No. 06-7, which appears below.
Response to Comment No. O6-7a
The biological surveys performed by Rincon were intended to assess current conditions of the Project Site for potentially supporting sensitive biological resources (e.g., special- status species, aquatic resources, sensitive habitats and vegetation, and wildlife movement). Based on the results of the initial habitat assessment, focused surveys were performed for specific special-status species determined to have the potential to occur based on the distribution and quality of the vegetation and associated habitats on-site, such as for western burrowing owl and coastal California gnatcatcher.
Reply: If the survey was merely about assessing current conditions of the site, then what was the point of recording the species detected during the survey? The recording of species detected during a survey, as is typically done in support of CEQA review, is the
7 most effective method for assessing whether a site provides habitat for species of wildlife. The site supports habitat for each and every species that is detected, because by definition, a species’ habitat is that part of the environment that is used by members of a species. For this reason, it is most efficient, and most accurate, to complete a more rigorous survey of a proposed project site, thereby leaving uncertainty around determinations of occurrence to a smaller suite of potentially-occurring species. In other words, a more rigorous survey effort minimizes the workload and the potential errors of a desktop analysis.
As for the role of the reconnaissance survey in determining whether focused surveys should be implemented, I concede that this is one of the roles of reconnaissance surveys, but again there is a problem with it that the DEIR fails to address. The problem is that a cursory reconnaissance survey is less likely to lead to sound determinations over whether focused surveys should be implemented.
Response to Comment No. O6-7b
The species referenced in this comment are common and are not “special status” in accordance with CEQA.
Reply: The response is unclear about which species are being referenced in comment no. 06-7. In fact, some of the species found by Noriko were special-status species, and some were not. But even of those that were not, they were the same types of species that Rincon (2023) opted to report. Biologists report these so-called “common species” (many are not, in fact, common) that are detected because they compose part of the wildlife community, which is part of the existing environmental setting, and because biologists are well aware that the presence of special-status species often depends on the presence of these “common species.”
Response to Comment No. O6-7c
Additionally, the discrepancy between the number of species observed by Rincon during the reconnaissance survey on January 20, 2022, and the number observed by Dr.
Smallwood’s associate on May 14, 2023, can be attributed to seasonal variability.
Reply: The response merely speculates that seasonal variability would explain the discrepancy between the numbers of species detected by Rincon and Noriko Smallwood.
The response, however, offers no evidence in support of this explanation.
I examined my own data from a Rancho Cordova project site I have surveyed 36 times since December 2020. I found no seasonality of the numbers of species I detected over the same survey durations. In fact, the average number of species detected among surveys in winter were nearly exactly the same as the average among surveys in May, the same seasons surveyed by Rincon and Noriko Smallwood at the project site.
I also compared my counts of species per survey at other project sites that had also been surveyed by Rincon. At one of these sites (Diamond Street Industrial Project in San Marcos), both Rincon and I surveyed during the same season -- in June. Rincon detected 16 species of wildlife after 20 person-hours, whereas I detected 27 species after
8 my first survey of 1.5 person-hours, and eventually 63 species after two more surveys and a total 8.4 person hours. Even in the same season and at the same site, I am finding >9 times the number of species per hour as is Rincon’s biologists. These discrepancies cannot be attributed to seasonality.
At another project site, Rincon reported 7 species of wildlife, whereas I detected 47. At a desert site, Rincon detected 15 species of wildlife, whereas Noriko detected 19 species from only the site’s southeast edge. In most comparisons, Noriko or I detected more species of wildlife than did Rincon even though we regard our survey efforts at these project sites a very minimal.
Response to Comment No. O6-7d
Furthermore, information on the additional species observed by Rincon is provided in the Appendix D of the Draft EIR (see Table 2 of the Burrowing Owl Habitat Assessment and Focused Survey Results for the Blackhall Studios Project [Burrowing Owl Report] and Appendix A of the Blackhall Property Project Coastal California Gnatcatcher Focused Survey Report [Coastal California Gnatcatcher Report], both of which were included in Appendix D of the Draft EIR).
Reply: The response fails to address my comment that despite these other species having been detected, the DEIR reports that 23 species of wildlife have been detected on the project site. This reporting is obviously inaccurate and misleading.
Back to Response to Comment No. O6-44
Which referred me to Response to Comment No. O6-7.
Reply: The response ultimately fails to address my comment about the DEIR’s insufficiency in failing to report the start time and duration of Rincon’s (2023) reconnaissance survey. These two attributes are of critical importance to sound interpretation of the survey findings, but they continue to go unreported.
Response to Comment No. O6-45a
The comment states that the number of species detected on-site is greater than the number of species Rincon reported. The comment also claims that Rincon’s survey effort was deficient and states that the Draft EIR needs to be revised with the outcomes of more surveys and more complete reporting to include the total number of species detected and not just the species detected during the reconnaissance survey. Please see Response to Comment No. O6-41 regarding the sufficiency of the reconnaissance survey effort to evaluate existing conditions and potential Project impacts to sensitive biological resources.
Reply: The response again fails to mention that 60 species of wildlife have been detected by Rincon and Noriko Smallwood, whereas the DEIR reports that 23 species were detected. Please see my reply to response 06-41. Rincon (2023) knew well enough to report the species of wildlife they detected during the reconnaissance survey, but the City is now arguing that representation of the species richness of the project site is
9 irrelevant to the impacts analysis. In reality, the richness of the wildlife community at the project site is highly relevant, and it is so far grossly under-represented by the EIR.
Response to Comment No. O6-45b
The comment also states that USFWS Birds of Conservation Concern (BCC) are special status and should be reported as such. Birds of Conservation Concern are a USFWS effort to identify non-listed birds that might become candidates for listing in the future.
The Draft EIR evaluated USFWS-listed or candidate species but did not consider species that might become candidates for listing in the future. This is a reasonable approach.
The City understands that there is a long list of plants and animals – not just birds – that might experience increased pressure in the future and that might become candidates for listing or, subsequently, become listed species. The Draft EIR presented an appropriately broad reach to include candidate species, as well as listed species and is not required to include potential candidates. However, birds not specifically identified as listed or candidate species were not excluded from consideration in the Draft EIR, which recognized the importance of the federal Migratory Bird Treaty Act as an applicable law and prescribes Mitigation Measure MM-BIO-3 that requires specific actions to protect nesting birds from construction impacts.
Reply: The Response is inaccurate and misleading in its portrayal of the meaning of the US Fish and Wildlife Service’s list of Birds of Conservation Concern. The response begins accurately, as the US Fish and Wildlife Service describes its list as “all migratory nongame birds that without additional conservation action are likely to become candidates for listing under the Endangered Species Act (ESA) of 1973.” However, missing from the response are the factors that contribute to this list, which are “population abundance and trends, threats on breeding and nonbreeding grounds, and size of breeding and nonbreeding ranges.” The first factor goes directly to the meaning of the term special-status species per §15380 of the CEQA Guidelines, which defines special-status species as Endangered, Rare, or Threatened, and further defines each of these terms. Rare is defined as “(A) Although not presently threatened with extinction, the species is existing in such small numbers throughout all or a significant portion of its range that it may become endangered if its environment worsens; or (B) The species is likely to become endangered within the foreseeable future throughout all or a significant portion of its range and may be considered “threatened” as that term is used in the Federal Endangered Species Act.” Thus, the CEQA Guidelines’ definition of Rare relies on the same factors that are relied upon by the US Fish and Wildlife Service for assigning birds as Birds of Conservation Concern. Birds of Conservation Concern are special-status species.
Response to Comment No. O6-46 The comment asserts that Rincon’s statement that an individual Cooper’s hawk was observed during the January 2022 reconnaissance survey, but a nest was not observed is misleading because it gives the false impression that the failure to observe a nest in January would indicate the species is not nesting on the Project Site. The comment also states that the same false impression was conveyed by the observation of a single, inactive passerine nest during the reconnaissance survey, implying that nesting is not taking place. The comment’s assertion that the Draft EIR is misleading regarding Cooper’s hawk and nesting birds is inaccurate. The Draft EIR
10 acknowledged that the potential for Cooper’s hawk and nesting birds to be present within the Project Site is high and stated the following on page 4.3-18 in Section 4.3, Biological Resources, of the Draft EIR: As potentially suitable habitat for these special- status wildlife species exists on the Project Site, implementation of the Project would potentially impact existing habitat. Construction of the Project would potentially result in direct impacts during initial ground-disturbing activities or indirect adverse impacts to special-status wildlife species if present. Construction activities have the potential to directly impact nesting birds through the destruction of nests or disturbances leading to nest failure. As such, impacts to special-status wildlife species (i.e., nesting birds) that exist on the Project Site or the areas immediately surrounding the Project Site would be potentially significant. The Draft EIR included Mitigation Measures MM-BIO-1 through MM-BIO-3 to reduce impacts to special-status wildlife species and nesting birds to a less-than-significant level.
Reply: If the response is accurate, then it is hard to understand why the DEIR (p. 4.3-5) reported, “An individual Cooper’s hawk was observed perched on top of a coast live oak tree within the project site during the January 2022 reconnaissance survey...; however, a nest was not observed.” That last phrase – “a nest was not observed” -- is not one that would appear unless the desired implication was that Cooper’s hawk does not nest on the site. Otherwise, what was the significance of the observation? The DEIR could have just as readily reported, “however, a prey item was not in the hawk’s clutches, or” however, a second hawk was not observed.” As for the above-quoted text that appears on DEIR page 4.3-18, it does not specifically acknowledge that Cooper’s hawks likely nest on the project site. The statement refers to bird nesting in general, which can include nesting by Cooper’s hawk. However, the impression had already been delivered in the DEIR that no Cooper’s hawk nests had been seen....in January.
Response to Comment No. O6-47 The comment states that the yellow warbler observed on-site in April 2022 relied on the Project Site for its migration to breeding habitat or may have been nesting on-site and that, contrary to Rincon’s assessment, the Project Site provides important habitat value to yellow warbler. Required habitat elements for yellow warbler nesting, such as riparian thickets of willow, cottonwoods, sycamores, ash, and alders, are not present within the Project Site. Not only does most of the Project Site consist of non-native grassland, but it is isolated and already fragmented from intact native habitats in the region and is surrounded by development that limits opportunities for wildlife movement, both locally and regionally. The large tracts of open space to the north and east of the Project Site, including the Quigley Canyon Open Space located approximately one mile to the east and the Angeles National Forest just east of the SR-14, contain suitable riparian habitat for yellow warbler and are far more likely to provide important nesting and migratory habitat value to the species.
Reply: In my experience, species of wildlife often defy the neat boxes that consulting biologists attempt to put them into. Yes, yellow warblers nest within vegetation communities composed of the plant species listed in the response, but like other species, they can nest elsewhere. Yellow warblers sometimes nest in shrubland, farmland, forest edges, urban parks and urban areas. All this said, alternative nest substrates are not
11 necessary to determine that yellow warblers might nest on the project site. Habitat exists on site.
Yellow warblers most often nest in willows, and sometimes within willows that occur as isolated individuals or in small clusters (Strusis-Timmer 2009). In fact, Rincon (2023) reports three species of willow on the project site. In one California study, 85% of the yellow warbler nests were in arroyo willows (Timmer et al. 2011), which is one of the species of willow found on the project site. With the presence of willows on the project site, it is mysterious why the City so adamantly insists that nesting opportunities are not to be found on the project site.
eBird records provide additional evidence that yellow warblers might breed on the site. eBird includes many records of yellow warblers in the project area during the breeding season. Jonathan Feenstra reported 8 yellow warblers, including recently fledged young, on the Iron Horse Trailhead on 20 June 2023, i.e., three weeks prior to the time of my replies. These nesting yellow warblers were located only 3.25 miles from the project site.
Considering this observation so close to the project site, I must upgrade my assessment of the likelihood of breeding on site from maybe to very likely.
The one yellow warbler that was seen on the project site was seen incidental to another consultant visit right at the beginning of the breeding season. Rather than continuing to speculate the reasons why the City wants to believe that yellow warblers do not nest on the project site, the City would do well to survey the site for yellow warblers. No surveys that were appropriate to yellow warbler were completed in the breeding season.
Considering the presence of willows on the project site, at least one yellow warbler on the site at the beginning of the breeding season, and the recent observation of fledgling yellow warblers barely farther than 3 miles away, the available evidence leaves the City’s argument weak; yellow warblers very likely breed on the project site.
The response fails to address my comment that even if the site does not support breeding by yellow warblers, and if the City’s speculated purpose of the incidentally detected yellow warbler was to use the site as part of its travel route to a breeding site elsewhere, then the site nevertheless provides important habitat value to yellow warblers. The yellow warbler observed on site was not a wayward warbler that was present on site by mistake. It was there either to breed or on route to a breeding location. Rincon (2023) concludes the site is unimportant to wildlife movement in the region, while at the same time arguing that the site provided this yellow warbler with stopover opportunity on its way to breed elsewhere. As I commented, the City cannot have it both ways.
Response to Comment No. O6-48 The comment states that non-breeding surveys for coastal California gnatcatcher were not completed for the Project Site. The comment also states that the burrowing owl surveys were not compliant with the available survey protocol by failing to meet 16 of the 34 applicable minimum standards and only partly complying with another four of the standards. The comment recommends that the burrowing owl surveys be repeated in accordance with the survey and reporting
12 standards and that they should be completed by qualified biologists. This comment is similar to Comment No. O6-8. Please refer to Response to Comment No. O6-8 above.
Reply: The response refers me to Response to Comment No. O6-8, so I reviewed the referenced response and reply to it below.
Response to Comment No. O6-8a
The comment states that the focused detection surveys for burrowing owl and California gnatcatcher performed by Rincon failed to comply with minimum standards of the available survey protocols for these species. Focused surveys were completed by a qualified biologist with over 20 years of experience and an active U.S. Fish and Wildlife Service (USFWS) permit in compliance with USFWS Section 10(a) of the Federal Endangered Species Act (FESA), Special Terms and Conditions for Endangered and Threatened Wildlife Species Permit. The survey included six breeding season surveys in accordance with the USFWS current Coastal California Gnatcatcher Presence/Absence Survey Protocol. According to the USFWS, the protocol for the breeding season was designed to provide a 95-percent confidence level of detecting coastal California gnatcatchers at a site when they are present. The accepted standard for protocol presence/absence surveys for coastal California gnatcatcher is either six breeding season surveys or nine non-breeding season surveys; USFWS does not require completion of both breeding and non-breeding season surveys for the results to be considered valid.
Furthermore, the potential habitat on the Project Site for supporting coastal California gnatcatcher is of marginal quality, in addition to the site being generally surrounding by existing development and urban sprawl and relatively fragmented from suitable habitat for coastal California gnatcatcher. Accordingly, conducting additional surveys during the non-breeding season (July 1 through March 14) is not necessary.
Reply: The USFWS survey protocol states, “If the surveys fall outside such process [NCCP interim section 4(d) process], then 6 surveys separated by ≥7 days shall be performed between 15 March and 30 June, and 9 surveys separated by ≥14 days shall be performed between 1 July and 14 March.” The guidelines do not specify that either one survey period or the other can be implemented. I concede the possibility that the USFWS clarified the survey requirement to be either one period or the other, but if so, then I have seen no documentation of it. If the USFWS permits surveys be completed during either one season or the other, then I would agree that Rincon’s California gnatcatcher surveys were consistent with the USFWS’s guidelines. However, in its comments of 22 May 2023, CDFW shares my understanding of the USFWS (1997) survey guidelines that both breeding season and non-breeding season surveys are expected.
As for the City’s characterization of the habitat as marginal, I have found California gnatcatchers in fragments of scrub vegetation located immediately adjacent to hotel parking lots. At another location I found them in highly disturbed scrub vegetation next to a housing development and an apartment complex – at the same site in San Marcos where Rincon had not detected the species during its reconnaissance surveys but later detected it during the protocol-level detection surveys that were requested by CDFW.
The City’s argument that the habitat is marginal is not compelling.
13 Response to Comment No. O6-8b
With regards to burrowing owl, the comment states that the burrowing owl surveys failed to meet nearly half of the applicable California Department of Fish and Wildlife (CDFW) survey and reporting protocols. Rincon performed four breeding season surveys in accordance with the requirements specified in CDFW’s Staff Report on Burrowing Owl Mitigation.17 This included a habitat assessment, focused burrow survey, and focused breeding season owl surveys by systematically searching for potential foraging and nesting habitat within the study area, which included the Project Site plus a 150-meter buffer (where access was available). The surveys were conducted by a qualified biologist with experience and knowledge of burrowing owl life history and sign walking transects spaced approximately 10 meters apart in suitable habitat and were appropriately adjusted to allow for 100-percent visual coverage of the ground surface. Suitable habitat was identified by the presence of low vegetation cover, presence of potentially suitable small mammal burrows, and perch sites. As indicated in the Draft EIR and the Burrowing Owl Report (included in Appendix D of the Draft EIR), no evidence of burrowing owl presence (e.g., direct observations or sign of presence, such as feathers, pellets, tracks, or potentially occupied burrows) was observed during the breeding season surveys.
Reply: As I commented (see Table 3 of my comment letter), Rincon’s (2023) report met none of the CDFW (2012) guideline standards on reporting the qualifications of survey personnel, and only 3 of the reporting standards. Rincon (2023) failed to meet 5 of the standards on habitat assessment, and only partially achieved another 2 of the standards.
Regarding the surveys themselves, Rincon (2023) completed no survey after June 15, made no mention of the use of binoculars at the start of each pedestrian transect, surveyed on one day when it was too cool, and made no mention of any adverse conditions such as disease, predation, drought, high rainfall or site disturbance. To support a determination of absence of burrowing owls, the City needs to follow the CDFW (2012) survey guidelines, not partially or selectively, but entirely.
Response to Comment No. O6-8c
Based on the above, the surveys for the coastal California gnatcatchers and burrowing owls comply with established protocols for each species and, thus, with the requirements of CEQA as well. As such, the comment’s claim that the Draft EIR did not provide substantial evidence to support the findings related to the coastal California gnatcatchers and burrowing owls is incorrect.
Reply: The City is incorrect that it followed the available guidelines, most certainly so in the case of burrowing owls.
I also noticed in the response that the burrowing owl survey personnel surveyed what they regarded as suitable habitat (this term is nonsensical, as there is no such thing as unsuitable habitat; for a given species, a place either supports habitat or it does not).
This concerns me, because having performed research on burrowing owls over many years (Smallwood et al. 2013, Smallwood and Morrison 2018), I have found that burrowing owls often make use of environmental conditions that other biologists assume is not habitat. I have watched survey personnel walk right past nest sites
14 without looking at them because they assumed burrowing owls would not occur there. I have found burrowing owls nesting in very tall vegetation, and twice I found them nesting under trees. I am concerned that Rincon’s biologists might have disregarded portions of the project site based on preconceived erroneous notions about what qualifies as burrowing owl habitat.
Back to Response to Comment No. O6-48
Which referred me to Response to Comment No. O6-8.
Reply: State and federal agencies spent a lot of time and effort to develop survey protocols for special-status species. In the case of the burrowing owl protocol, many experts on burrowing owls had a part in formulating it. Based on more recent findings, I believe the burrowing owl survey protocol should be revised, but on the whole the protocol is excellent. In my own studies, I treat the CDFW (2012) survey guidelines as minimal levels of effort, and so I vastly exceed them. Where the CDFW (2012) guidelines recommend 4 surveys spaced by 3 weeks each, I survey my study sites many times throughout the breeding season, including prior to the earliest date recommend by CDFW and well after the last date recommended by CDFW. In my experience, failing to achieve the minimum standards of the guidelines can easily result in false negative findings. That a survey should be completed after June 15th has been proven multiple times in my own surveys when I found pairs of burrowing owls starting nest attempts after this date. I once found chicks just emerged from a nest in early October, which means that nest attempt began well after June 15. For the reasons stated, a survey effort that fell short of the CDFW (2012) guidelines cannot support an absence determination.
Response to Comment No. O6-49a
The comment states that an important part of documenting a site’s environmental setting is a desktop review, which includes literature and database review and consultation with local experts to inform and augment reconnaissance surveys and to help determine which protocol-level detection surveys should be conducted. The commenter suggests that the Draft EIR’s desktop review is incomplete and flawed because it neglected readily available species occurrence databases and provides no evidence that any local experts were consulted. The commenter indicates that Dr.
Smallwood conducted an independent database review and a Project Site visit, which resulted in the identification of 122 special status wildlife species occurring near enough to the Project Site to warrant analysis of their occurrence potential. This comment is substantially similar to Comment No. O6-9. Please refer to Response to Comment No.
O6-9 above.
Reply: The response refers me to an earlier response, this time to 06-9.
Response to Comment No. O6-9a
The comment states that an important part of documenting a site’s environmental setting is a desktop review, which includes literature and database review and consultation with local experts to inform and augment reconnaissance surveys and to help determine which protocol-level detection surveys should be conducted. The comment suggests that the Draft EIR’s desktop review is incomplete and flawed because
15 it neglected readily available species occurrence databases and provided no evidence that any local experts were consulted. The comment indicates that Dr. Smallwood conducted an independent database review and the various Project Site visits, which resulted in the identification of 122 special status wildlife species occurring near enough to the Project Site to warrant analysis of their occurrence potential.
However, the comment does not mention which of the 122 species they believe could potentially occur on the Project Site.
Reply: The short answer is that all or nearly all of the 122 species in my Table 2 could occur at the project site, but some more fleetingly than others, and others more often.
The City seems to expect that I should engage in the same type of speculative determinations of occurrence likelihoods that its consultant undertook. I suggest that this approach if fraught with problems. The first problem is the implication that the analyst has perfect understanding of the habitat associations of each species, but this is far from the truth (Smallwood 2002). A second problem is the lack of definition of what an occurrence means, both to the analyst and to the species at issue. Does the occurrence mean permanent residence? Periodic home range patrol? Migratory stopover? Occasional stopover such as every decade or so? The City provides no scale of occurrence by which to interpret what it means by its occurrence likelihood determinations of none, low, moderate or high.
Rincon (2023) describes its occurrence likelihood determinations as based on two factors. With the first factor, Rincon (2023) judges whether the site has none, few, some or all of the “habitat components” required by a species, hence contributing to determinations of no potential, low, medium and high potential. This factor would either require perfect knowledge of the habitat components required by each species, which is unrealistic, or imperfect knowledge, which would mean the determinations of occurrence likelihood should include uncertainty (error) statements. Rincon (2023) presents its occurrence likelihood determinations as if they are based on perfect knowledge; it certainly provides no uncertainty statements about the habitat components that are relied on. And as I commented in my letter of 19 May 2023, Rincon pigeon-holes species into unrealistically narrow portions of the environment, which is the same as saying that not all of the habitat components used by the species are identified in Rincon (2023).
With the second factor, Rincon (2023) relies on the probability of the species being found on site. But what does this mean? The probability of a species being found on a site is a product of both the true likelihood of occurrence at the time a survey is underway (which goes to the topic of the preceding paragraph) and the survey detection probability. The latter probability goes to the ability of survey personnel to detect a particular species, and it varies a great deal by survey duration and survey start time, season, species’ body size and behavior, terrain, vegetation structure, the behavior of the investigator, and the skill of the investigator. It is a complex probability that for most species and most types of survey, researchers are still trying to quantify (Green and Young 1993, Thompson 2002, Hutto 2016, Smallwood and Neher 2017). In short, Rincon’s second factor is incompletely characterized and is of dubious validity.
16 Response to Comment No. O6-9b
Rather, the list of species presented in Table 4 of Dr. Smallwood’s report identifies those species that occur “In region” “Nearby”, “Very close”, and “On site”. Of the 122 species included in Dr. Smallwood’s Table 4 identified as “On site”, all are common in the region and non-listed species that include Allen’s hummingbird, turkey vulture, red-tailed hawk, Cooper’s hawk, California thrasher, and Southern California rufous-crowned sparrow.
Reply: The species listed in the response are special-status species. Not all special- status species are listed; in fact, most are not. And to say these species are common in the region is also a bit misleading, because the response does not clarify what it means by “common.” Commonness can express a level of spatial distribution or it can express population density, the latter of which is a function of the spatial scale of examination (Smallwood 1999). In terms of density, Cooper’s hawks are not nearly as common as Allen’s hummingbirds where the species co-occur, but in terms of spatial coverage over a defined area, Cooper’s might or might not be regarded as more common than Allen’s hummingbird. It would help to avoid confusion if the City would clarify what it means.
Response to Comment No. O6-9c
With the exception of Allen’s hummingbird, all of these species were documented in the Biological Assessment Report (included in Appendix D of the Draft EIR).
Reply: The response is in error. Rincon (2023) also fails to include another three species including Costa’s hummingbird, sharp-shinned hawk, and Bullock’s oriole.
Response to Comment No. O6-9d
Additionally, many of the 122 species included in Mr. Smallwood’s report that are not included in the Draft EIR are derived from unconfirmed sources in eBird (https://eBird.org) and iNaturalist (https://www.inaturalist.org) and include species that require habitat that is not present on, or in the vicinity of, the Project Site.
Examples include numerous coastal species, such as Laughing gull, Heermann’s gull, western gull, willet, long-billed curlew, whimbrel, California least tern, gull-billed tern, black tern, American white pelican, and California brown pelican, as well as species that are dependent on perennial water sources, such as lakes and ocean, including least bittern, common loon, double-breasted cormorant, white-faced ibis, and osprey. Mr.
Smallwood incorrectly alleges that some of these species are “Nearby”, which is unsubstantiated and inaccurate.
Reply: The response dismisses eBird and iNaturalist as unconfirmed sources, but again it is difficult to understand what the City means. It begs the question of what is a confirmed source. Similar to CNDDB, eBird and iNaturalist records are scrutinized by experts, but whereas CNBDDB records are scrutinized by CDFW staff biologists, eBird records are scrutinized by some of the most respected ornithologists in the world at Cornell University Lab of Ornithology, and this is only after the new records have gone through eBird’s data filters. Further unlike CNDDB records, eBird and iNaturalist records are scrutinized by other participants. Feedback on questionable records is
17 common. eBird and iNaturalist records also often include photos of the animals, or comments about the observation to help the user of the records decide on their veracity.
One such eBird record I took seriously, as an example, was that of the yellow warbler reported on the project site by the Michael Baker International biologist who detected it incidentally to a site visit intended for another purpose. The date and the consulting firm matched exactly the reporting of the observation in Rincon (2023).
The City points out species whose inclusion in Table 2 of my comment letter are unlikely to occur at the project site. But these species met my standard of inclusion in an analysis, because my standard was solely based on distance domains from the project site. California brown pelican is identified as having occurred in the region, and this identification is based on numerous records between 4 and 30 miles of the project site.
One of these records comes from Kimball Garrett, whose ability to identify a California brown pelican ought to go unquestioned (Collections Manager in Ornithology at the Museum of Natural History of Los Angeles until 2022). Are California brown pelicans likely to land on the project site? Probably not, but they likely do fly through the project site’s airspace.
The City points out double-crested cormorant as another species that depends on a perennial body of water, but which the project site lacks. eBird includes numerous records of double-crested cormorants that are between 1.5 and 4 miles of the project site. To the question about confirmation of source material, one can examine a photo by Tina Tan taken on 14 February 2023 to see that she was indeed looking at a double- crested cormorant at Bridgeport Lake. To the City’s argument that this species needs water, I agree, but I must add that this species also needs unobstructed airspace to travel between bodies of water, and sometimes they need substrate that is suitable for nest colonies, which are not always immediately adjacent to bodies of water.
The City points out western gull as another species that it would not include on a list of potentially occurring species. If its the source that is the problem for the City, then I refer the City to Judy Matsuoka’s photo taken on 19 November 2022 at Bridgeport Lake.
The subject of her photo looks to me like a western gull. Bobby Walsh has another photo on eBird that looks like a western gull, this one taken on 2 January 2021 in Santa Clarita CBC Area 5 (“Old Valencia”). There are numerous additional records of western gulls in the area.
The City points out osprey, as well. I have many times documented osprey foraging or traveling far from perennial bodies of water, including many observations of them on the expansive annual grasslands of the Altamont Pass Wind Resource Area. Osprey mainly hunt for fish, but they can take other types of prey. But I have also noticed that osprey are very selective about their flight paths between bodies of water, as they almost always fly over the available open space; that is, the spaces that are not covered by anthropogenic structures. One of the osprey seen near the project site was reported by Kimball Garrett (see above).
The City views habitat as something that occurs at ground level and can be put onto a two-dimensional map. But as I commented on 19 May 2023, habitat of volant wildlife
18 includes that portion of the aerosphere that they use. The airspace that would be taken by the project’s buildings is also habitat of many species of wildlife, including those species the City believes should not have been included in Table 2 of my comment letter.
My standard of inclusion is a distance standard for sound reasons. The City’s standards of inclusion are vague and misleading.
Response to Comment No. O6-9e
As indicated in the Draft EIR and the Biological Resources Assessment Report (included in Appendix D of the Draft EIR), the majority of the Project Site consists of non-native wild oat-annual brome grassland. In addition to other disturbed areas on the Project Site, off-highway vehicle trails and other disturbances (e.g., encampments and trash) on the site are evident in the native vegetation communities that are present. Moreover, the Project Site is generally fragmented from intact native habitats in the region and surrounded by development and urban sprawl. Finally, the database reviews performed by Rincon were standard and appropriate for performing Project-level analysis under CEQA. These resources included queries of the USFWS Information for Planning and Consultation online project planning tool (2022), USFWS Planning and Conservation System (2022), CDFW California Natural Diversity Database (2022), and the California Native Plant Society Online Inventory of Rare, Threatened and Endangered Plants of California (2022) to obtain comprehensive information regarding state- and federally- listed species, as well as other special-status species considered to have potential to occur within a 9- USGS quadrangle map search area that included the Newhall, California USGS 7.5-minute topographic quadrangle and the surrounding eight quadrangles (Whitaker Peak, Warm Springs Mountain, Green Valley, Val Verde, Mint Canyon, Santa Susana, Oat Mountain, and San Fernando). In addition, the following resources were reviewed for information about the Project Site: · Aerial photographs (Google Earth Pro 2022) · Newhall, California USGS 7.5-minute topographic quadrangle · U.S. Department of Agriculture (USDA), Natural Resources Conservation Service (NRCS) Web Soil Survey · USFWS Critical Habitat Portal · USFWS National Wetland Inventory (NWI) · United States Geological Survey (USGS) National Hydrography Dataset (NHD) The aforementioned resources are intended to provide a list of special-status species that have been recorded in the region and were accompanied by field assessments performed by qualified biologists, including several focused wildlife and plant surveys performed between 2015 and 2022 in accordance with agency standards.
Reply: Left unexplained is how the occurrence likelihood of a particular special-status species would be determined by examining most of the resources listed above, including the USFWS Information for Planning and Consultation online project planning tool (2022), USFWS Planning and Conservation System (2022), Aerial photographs (Google Earth Pro 2022), Newhall, California USGS 7.5-minute topographic quadrangle, U.S.
Department of Agriculture (USDA), Natural Resources Conservation Service (NRCS) Web Soil Survey, USFWS Critical Habitat Portal, USFWS National Wetland Inventory (NWI), United States Geological Survey (USGS) National Hydrography Dataset (NHD).
None of these resources would have been helpful, and the response provides not a single example of how any of these resources contributed to a determination of species occurrence likelihood. The only resource that would have contributed to the occurrence
19 likelihood determinations of wildlife species was CNDDB. As I commented on 19 May 2023, the City misused CNDDB.
Back to Response to Comment No. O6-49a
Which referred me to Response to Comment No. O6-9.
Reply: The City did not make use of all the resources it had available to analyze occurrence likelihoods of special-status species. It made no use of eBird and iNaturalist, nor did it consult any local experts. Likewise, Rincon failed to utilize eBird, iNaturalist and local experts. Instead of making use of the resources that it should have, the City attempts to defend an unsound approach to determining the occurrence likelihoods of special-status species. In its defense, the City criticizes my approach, which is much simpler and its sole contributing factor is distance domains between the project site and the nearest occurrence records. My approach better manages the uncertainty associated with species occurrences.
In fact, the City’s approach is highly uncertain but its product is presented as highly certain. This is one reason why it is misleading. It also follows from an inceptive flaw in the very selection of special-status species for inclusion in the analysis. Rincon (2023) explains that occurrence likelihoods were determined by the number of “habitat components” required by a species and the probability of the species being found on site. However, CNDDB records queries do not take these factors into consideration.
CNDDB records inform only of where and when reporters observed members of species that carried special-status at the time of the observations. In other words, Rincon (2023) predetermines the species to be considered per the factors Rincon identifies when Rincon queries CNDDB for occurrence records. By including in the analysis of species’ occurrence likelihoods only those species whose documented occurrences within the nearest CNDDB quadrangles, Rincon (2023) screens out many special-status species from further consideration. As I commented on 19 May 2023, this is not how CNDDB is intended to be used.
eBird and iNaturalist records are actually more suitable for the approach taken by the City, because special-status at the time of observation is not required of records for submission to the database. This is important for all those species that only recently were assigned special-status, as they are treated in these databases more equally to those species that have long been special-status species.
Response to Comment No. O6-49b
The comment reiterates the assertion that detection likelihoods of most special-status species are low during reconnaissance-level survey and maintains that additional surveys are needed. Please refer to Response to Comment No. O6-41, which explains why additional surveys are not necessary.
Reply: The main point of Response to Comment No. 06-41 is that the reconnaissance survey conducted by Rincon was not intended to be a comprehensive inventory of all species that inhabit the Project Site, and that Rincon’s biologists were able to draw inferences “about the potential for special-status wildlife to occur based upon known
20 ranges, habitat preferences for the species, species occurrence records from scientific database queries, previous reports for the Project Site, and the results of surveys of the Project Site.” Please see my replies to Response to Comment Nos. 06-41 and 06-49a.
Rincon’s approach is confused. Its inceptive error was its misuse of CNDDB to derive an unrealistically short list of special-status species. And then it minimalizes the use of the most effective method known to biologists for assessing habitat, which is field surveys to detect as many species as reasonably possible. Instead of appropriately looking for special-status species on the project site, Rincon’s approach assigns occurrence likelihoods to the species on its unrealistically short list. These assignments are reportedly based on the number of habitat components required by a species and the probability of the species being found on site, but these bases are vague, potentially highly complex, and highly unlikely to have actually been quantified. No examples are provided. No uncertainty statements are provided, either, which leaves the approach looking unscientific.
Response to Comment No. O6-50
The comment states that it is inappropriate to assign low likelihoods of occurrence to special-status species of wildlife simply because the biologist did not detect the species during a single reconnaissance survey. The Rincon BRA did not exclude the potential for special-status wildlife species to occur based on failure to detect the species during the reconnaissance survey. As described in Response to Comment No. O6-41, additional factors were considered, such as availability and quality of habitat to support the species, known ranges, species occurrence records from scientific database queries, previous reports for the Project Site, and the results of surveys of the Project Site.
Reply: By definition, a determination of low likelihood does not exclude the potential for special-status species to occur. This part of the response makes little sense to me.
The rest of the response and adds confusion about how special-status species were assigned occurrence likelihoods. This response explains that habitat availability and habitat quality were the factors that contributed to determinations of occurrence likelihoods. Habitat availability can be likened to the number of habitat components that the City earlier identified as a contributing factor to determinations of occurrence likelihoods, but this is a conflation of terms, because habitat availability and habitat components carry different meanings. Habitat quality is entirely a different term, and one that had not been used before as a factor contributing to determinations of occurrence likelihood. Habitat quality is typically represented by productivity metrics such as fecundity and nest success. Rincon (2023) did not measure habitat quality on the project site.
Response to Comment No. O6-51 The comment states that more special-status species occur at the Project Site than those that were identified in the Draft EIR and by Rincon and that the Draft EIR incorrectly characterized the wildlife community at the Project Site. The comment also suggests that additional surveys would result in the detection of more species. These issues have been addressed in Response to Comment Nos. O6-7, O6-9, and O6-41. Response to Comment No. O6-7 and O6-9 explain the discrepancies between the species detected by Ms. Smallwood and those that were
21 reported by Rincon. Response to Comment No. O6-41 explains why additional surveys are not necessary.
Reply: The referenced responses were wrong. The difference in the numbers of species detected by Rincon and Noriko Smallwood was not due to seasonality, and no evidence was brought to bear that it was. That more surveys are needed is evident in Figures 1 and 2 of my comment letter. Wildlife surveys are the most effective method for determining occurrence likelihoods. They are far more effective than the flawed approach implemented by Rincon (2023) (see my comments in my letter of 19 May 2023 and my replies that precede this one).
Response to Comment No. O6-52 The comment claims that there are three types of impacts that are likely to result from the Project, two of which are not analyzed in the Draft EIR. According to the comment, the one impact that is addressed in the Draft EIR is only mentioned and concluded to be of no significance. The comment correctly cites the Draft EIR’s characterization of the Project Site as a relatively flat, undeveloped piece of land with low, ruderal plants and gravel driveways that has been cleared of the majority of its natural vegetation and disturbed by past uses. The presence of 16 coast live oak and valley oak trees within the context of the largely disturbed Project Site is also accurately cited. The comment provides no specifics on the three types of impact.
As such, this comment is noted, and no additional response is required.
Reply: My introductory paragraphs did not warrant a response.
Response to Comment No. O6-53
The comment states that the Draft EIR failed to analyze the Project Site’s capacity to support wildlife and estimates the loss of 1,924 bird nests as a result of the Project’s development. The comment states that the Draft EIR must be revised to analyze the Project’s impacts to wildlife caused by habitat loss and habitat fragmentation. This comment is similar to Comment No. O6- 16 but cites studies from 1948 and 1982 to support the bird nesting densities and calculations summarized in Comment No. O6-16.
Please refer to Response to Comment No. O6-16 above.
Reply: The response refers me to Response to Comment No. O6-16.
Response to Comment No. O6-16a
Most of the vegetation on the Project Site is non-native, consisting of non-native wild oat-annual brome grassland, and much of the site has been disturbed by off-highway vehicle trails and other disturbances (e.g., encampments and trash), including within the native vegetation communities.
Reply: The response continues the DEIR’s characterization of the site as a highly disturbed, trash-filled site that does not warrant serious consideration as wildlife habitat. Yet the wildlife are there. Sixty species have already been documented at the site based solely on surveys completed by wildlife biologists. Species occurrence databases indicate that even more species of wildlife have been documented there. Wildlife are
22 present because, despite the City’s characterization of the site as a site in miserable condition, there are 16 oaks on site, large tracts of big sagebrush scrub and scale broom scrub, three species of willows along a streambed and perhaps elsewhere on the project site, and other natural resources upon which wildlife depend. The City’s characterization of the project site does not comport with the number of species of wildlife already known to be using it.
Response to Comment No. O6-16b
The comment suggests that the Project would contribute further to habitat fragmentation by the loss of one of the region’s last patches of undeveloped open space; however, based on review of aerial imagery, the Project Site is isolated and already fragmented from intact native habitats in the region and is surrounded by development.
Reply: Please see the definition of habitat fragmentation (Smallwood 2015). That the site is isolated by development is the epitome of habitat fragmentation, consistent with my comments of 19 May 2023. The loss of this large, isolated fragment of habitat would be even more devastating to wildlife than would the loss of any similar-sized fragment of habitat around the periphery of Santa Clarita, because it would prevent the escape of many of the terrestrial wildlife on the site and it would remove the last remaining stopover opportunity of volant wildlife.
Response to Comment No. O6-16c
The comment states that their independent biologist predicts the loss of 1,924 bird nests as a result of the Project’s development. This prediction is not supported by any rationale that considers the current state of the Project Site and the condition habitat for nesting birds. For example, the majority of the Project Site consists of low-growing herbaceous vegetation, and few bird species in the region are ground nesters that would nest in this habitat, such as mourning dove (Zenaida macroura) and killdeer (Charadrius vociferus). Therefore, few bird nests are expected to occur within the non- native grassland areas of the Project Site that would be disturbed. The oak trees and native vegetation on the Project Site provide habitat for nesting birds but are not expansive when considering the amount of area that is covered by native plants/suitable bird nesting habitat. It is expected that birds currently nest within the trees and shrubs that would be disturbed by the Project but not nearly the amount alleged in the comment (estimated by Rincon’s professional biologists to be likely less than 5 percent of the 1,924 nests predicted in the comment).
Reply: The response misrepresents my comment by claiming that I made no account of the current state of habitat on the project site. In fact, I did. I assumed the project site would support 60% of the nesting density measured at the referenced study sites. But even if I am wrong in my accounting, and a more accurate assumption is 40%, then the annual number of birds denied to California would still be 4,234, which is still a very large number.
The City reports that Rincon’s biologists estimate the project site’s total nesting density at <5% of my prediction, which is <115 nests per year, or <1.23 nest sites per acre per year. However, this estimate does not appear to be based on any methodology other
23 than a guess. It is also quite absurd, as Franzeb (1978) estimated a total nest density of
0.45 per acre in the extremely xeric, sparsely-vegetated Algodones Dunes in the southern Mojave Desert. Kozma and Mathews (1997) estimated total bird nesting density at o.667 nests/acre in another desert environment – the Chihuahuan Desert of New Mexico. But the project site is not a desert environment, and has to be much more productive to birds than are the Algodones Dunes and Chihuahuan Desert. A total nest density of <1.23 nests per acre is not believable.
This spring I surveyed a study site for the purpose of estimating total nest density. This site would be closer in habitat and habitat condition to the project site than were the other two study sites I cited. I believe I just completed my last or perhaps second to last survey to achieve my objective, so I have not yet fully analyzed my data. I did analyze the data I had collected through mid-May, and at the time I had about 9 nests per acre.
Since that time, I would estimate the total nest density had risen to about 15 nests per acre, or about 44% of the mean between the two studies I cited. Considering this preliminary study outcome, I would estimate that the total nest density at the project site is somewhere between what I predicted in my comment letter and what I predicted herein.
Response to Comment No. O6-16c
The comment suggests that the Draft EIR lacked “any” analysis and mitigation for loss of nesting bird habitat. Federal and State regulations, including the federal Migratory Bird Treaty Act of 1918 and the California Department of Fish and Game Code, prohibit a project from impacting an active bird nest. Therefore, Mitigation Measure MM-BIO-3 presented in Section 4.3, Biological Resources, of the Draft EIR includes avoidance of bird nests during construction activities. Furthermore, the majority of the native habitat on-site occurs within and along Placerita Creek, which would largely be preserved in place by the Project. Of the 5.39 acres of sensitive natural communities on the Project Site, only 1.392 acres would be permanently impacted, with 0.57 acre temporarily impacted during construction. Mitigation Measure MM-BIO- 4 further requires restoration/replacement of this habitat at a minimum 1:1 ratio, thereby further reducing the Project’s long-term impacts on habitat and its use by wildlife.
Reply: The loss of nesting bird habitat is not necessarily the same thing as impacting an active bird nest. My comments went to the loss of breeding capacity as a project impact. This part of the response that conflates lost breeding capacity with impacts to active nests is off-base.
The response also argues that 3.998 acres (5.39 acres – 1.392 acres) of the 93.5-acre project site would be preserved along Placerita Creek, implying I suppose that the breeding capacity would not be lost to the degree that I predict. Preserving <4 acres between large studio buildings might support a few bird nests, but realistically this number would be small.
Response to Comment No. O6-54 The comment states that the Draft EIR purported to analyze whether the Project would interfere substantially with the movement of any wildlife species or with established wildlife corridors but only
24 addresses interference with wildlife corridors and ignores interference with movement of wildlife species. This comment is similar to Comment No. O6-17. Please refer to Response to Comment No. O6-17 above.
Reply: The response refers me to Response to Comment No. O6-17.
Response to Comment No. O6-17a
The comment states that the Draft EIR seemed to analyze whether the Project would interfere substantially with the movement of any wildlife species or with established wildlife corridors but only addressed interference with wildlife corridors and ignored interference with movement of wildlife species. The Project Site represents a relatively small amount of undeveloped space in the vicinity and the region. Not only does most of the Project Site consist of non-native grassland, but it is isolated and already fragmented from intact native habitats in the region and is surrounded by development that limits opportunities for wildlife movement, both locally and regionally. The comment alleges that the Project would cut off such wildlife from one of the last remaining stopover and staging opportunities in the Project area, forcing ever increasing travel between remaining stopover sites. However, this statement is inaccurate, especially when considering the large tracts of open space to the north and east of the Project Site, including the Quigley Canyon Open Space located approximately one mile to the east and the Angeles National Forest just east of SR-14.
Reply: The response is silent on my comment that the DEIR relies on false CEQA standard as the basis of its conclusion. The project site need not serve as a wildlife corridor to be important to wildlife movement in the region. The response also ignores the basis of my comment, which is that the highly fragmented nature of the project site is the very reason that it would attract stopover by volant wildlife moving through the region. Just as Hawaii is often used as a stopover for travelers crossing the Pacific, so too is the project site used as stopover by migratory wildlife.
The response asserts that my comment is inaccurate about the site’s use as stopover during long-distance movement. However, the City’s assertion is based on no attempt to measure wildlife movement on or across the project site. Rincon (2023) did nothing to measure wildlife movement or to sample wildlife in a manner that would support inference about wildlife movement. The birds that were seen on site were not even reported with attributes that would help to characterize what the birds were doing there.
There was no program of observation to characterize wildlife movement. The City lacks evidence in support of its assertion that my comment is inaccurate.
Response to Comment No. O6-17b
Lastly, the comment suggests that the Project could result in traffic-caused wildlife mortality and bird mortality from window collisions. Although the Project would increase vehicle trips, vehicle circulation is generally already high on Railroad Avenue immediately to the west of the Project Site, as well as on Wiley Canyon Road to the north and Lyons Avenue to the south. The Project Site is not within a local or regional wildlife movement corridor, and wildlife are not expected to travel through the Project Site and across Railroad Avenue because of the development that currently exists
25 immediately to the west. Therefore, wildlife collisions along Railroad Avenue immediately to the west of the Project Site are currently low and would be expected to remain low during the operation of the Project due to the vast amount of development that currently exists. In addition, the Project Site is not located within a local or regional bird migration corridor or flyway, and the Project would not introduce significant barriers or windows in the vicinity when considering the vast amount of existing development that is in the immediate vicinity and throughout the City. The scale and type of building construction proposed on site is similar to multiple other commercial and business park developments in the Project vicinity and throughout the Santa Clarita Valley, none of which have resulted in significant bird strike issues. Potential Project impacts to birds due to window collisions would not be significant given the extensive existing development surrounding the Project Site. The incorporation of alternative types of glass or alternative window layouts as suggested in the comment is not necessary to mitigate Project impacts to biological resources; therefore, incorporation of this recommendation in the Draft EIR is not required under CEQA. However, this comment is noted for the administrative record and will be forwarded to the decision- makers for review and consideration.
Reply: The response represents a raft of speculation that does not seriously address my comments. The road mortality I predict would be for all roads used by project-generated traffic, and not just Railroad Avenue, which oddly is the focus of the response regarding wildlife-automobile collision mortality.
That bird-window collision mortality is not recognized by the City as a significant issue in Santa Clarita might be due to a lack of fatality monitoring at existing structures. I posit that if the City introduced scientific monitoring to a sample of structures in Santa Clarita, the City would discover an alarming high collision fatality rate is ongoing.
Otherwise, the responses assertions that project-generated traffic and the large glass windows of the project’s buildings will not kill wildlife is conclusory and contrary to the evidence collected from where studies have been completed on these types of wildlife mortality.
Response to Comment No. O6-55
While the study that the comment cites is not publicly available, Vasco Road is a two- lane road that bisects relatively undeveloped open spaces. Accordingly, the comment’s estimated number of traffic-related wildlife fatalities that may result from Project development is not accurate when considering the existing high vehicle circulation on Railroad Avenue immediately to the west of the Project Site, as well as on Wiley Canyon Road to the north and Lyons Avenue to the south. The Project Site is not within a local or regional wildlife movement corridor and wildlife are not expected to travel through the Project Site and across Railroad Avenue due to the development that currently exists immediately to the west. Therefore, wildlife collisions along Railroad Avenue immediately to the west of the Project Site are currently low and would be expected to remain low during the operation of the Project due to the vast amount of development that currently exists.
26 Reply: See my replies to Response to Comment 06-17. The Mendelsohn et al. (2009) study was not in a wildlife movement corridor, either. And Railroad Avenue is just one of many roads that would be used by project-generated traffic. Some of the roads that would be used by this traffic are likely two-lane roads.
Response to Comment No. O6-56 The comment states that the Project could result in bird mortality from window collisions, and recommends exploration of alternative window layouts or alternative types of glass to minimize bird-window collisions. The comment cites numerous bird fatality and collision studies, which provide fatality estimates to support the claim. These estimates are noted in the administrative record and will be forwarded to the decision-makers for review and consideration. Please refer to Response to Comment No. O6-17, which concludes that potential Project impacts to birds due to window collisions would not be significant given the extensive existing development surrounding the Project Site. The comment’s recommendations for the use of alternative types of glass or alternative window layouts is not necessary to mitigate Project impacts to biological resources; however, these recommendations are noted in the administrative record and will be forwarded to the decision-makers for review and consideration.
Reply: Please see my replies to Response to Comment No. 06-17. The response is conclusory and not well reasoned. It is not factual. It is essentially a “comment noted” type of response.
Response to Comment No. O6-57a
The comment states that the Draft EIR lacked an adequate analysis of the Project’s cumulative impacts on wildlife, references certain sections of the CEQA Guidelines that provide guidance on how to analyze cumulative impacts, and provides commentary on approaches to evaluating cumulative impacts.
Reply: No, the comment states that the DEIR provide any analysis of cumulative impacts. I wrote, “the DEIR effectively provides no cumulative effects analysis.”
Response to Comment No. O6-57b
However, the comment does not identify any significant cumulative impacts that would be caused by the Project or that the Project would contribute to in a considerable manner.
Reply: Not true. I wrote, “the DEIR acknowledges that the project would contribute to cumulative impacts because “there would be less habitat available for protected species.”” Habitat loss and habitat fragmentation would be the principal cumulative impacts to which the project would contribute. The City knows this, and I know this.
Response to Comment No. O6-57c
As discussed in the Draft EIR, the loss of habitat caused by the Project is not a significant impact either on a Project-level or cumulative. The majority of the Project Site is covered in nonnative grasses. The habitat areas of the Project Site, including Placerita Creek and the northern ridgeline would be largely preserved in place. Given
27 the limited acreage of habitat impacts of the Project and the vast tracks of protected open spaces in the Project vicinity (e.g., Quigley Canyon Open Space, Whitney Canyon Park, Golden Valley Ranch Open Space, Saddletree Open Space, Gates King Open Space, Wildwood Canyon Open Space, and the Angeles National Forest), the Project’s contributions to the cumulative loss of open space and potential habitat would not be cumulatively considerable. Please also refer to Response to Comment No. O6-18 above.
Reply: The response is nothing more than speculation in favor of the notion that the project would cause no direct or cumulative impacts to biological resources. The speculation is based on no supporting evidence. No regional monitoring plan is cited.
And the speculation is not credible. The loss of 93.5 acres, or even if it is only 90 acres, would result in a substantial loss of birds and other wildlife, no matter how we estimate the loss (so long as the method is defensible). The site is one of the richest in number of species per hour of survey that Noriko Smallwood and I have surveyed within California (see Figure 1 of my 19 May 2023 comment letter). The avian breeding capacity of the region would be diminished, and migratory birds would lose an important stopover opportunity. The project would contribute to collision mortality in the region caused by windows and automobiles. The cumulative impacts would be significant. But the DEIR does not seriously analyze cumulative impacts.
Response to Comment No. O6-58a
As detailed in Response to Comment Nos. O6-17 and O6-19, Project impacts due to nesting bird and special-status species habitat loss, habitat fragmentation, wildlife collisions, and bird window strikes would be less than significant, and additional mitigation is not warranted.
Reply: These conclusions are indefensible. Sixty species of vertebrate wildlife have been documented on the project site, and my analysis predicts that at least 163 species occur there, including at least 24 special-status species of wildlife. Wildlife are breeding on the project site. The project cannot take 93.5 acres of wildlife habitat, while also severely fragmenting what is left of wildlife habitat in the region, and not have significant impacts to wildlife. The project cannot generate so much traffic nor insert so many large windows into the aerosphere without causing significant impacts to wildlife. The response lays bare the fundamental flaw in the mitigation plan of the project, as it reveals the City’s baseless claim that impacts would be less than significant.
Response to Comment No. O6-58b
Mitigation Measures MMBIO- 4 and MM-BIO-5 establish minimum compensatory mitigation requirements for impacts to sensitive natural communities and jurisdictional areas and require the preparation of a Restoration Plan to identify specifically how the replacement habitat would be acquired/restored. Mitigation Measure MM-BIO-4 identifies the minimum content requirements for the Restoration Plan and Mitigation Measures MM-BIO-4 and MM-BIO-5 collectively require the Restoration Plan be approved by CDFW, the U.S. Army Corps of Engineers, and the Los Angeles Regional Water Quality Control Board prior to initiating construction or any site disturbance. As the mitigation measures included in the Draft EIR commit the Project to mitigating the potentially significant impacts and include specific performance standards that must be
28 achieved, a security deposit is not appropriate or required. In addition, as discussed in Response to Comment No. A1-8, Mitigation Measures MM-BIO-1 has been revised to further ensure that impacts to biological resources would be less than significant. The comment’s recommended revisions are not warranted but are noted for the administrative record and will be forwarded to the decision-makers for review and consideration.
Reply: When formulation of mitigation is deferred, such as the formulation of these measures are deferred, the agency must adopt specific performance standards the deferred mitigation will achieve, and it must identify potential action(s) that can feasibly achieve the performance standard (CEQA Guidelines section 15126.4(a)(1)(B)). The very performance standards of these measures are deferred.
The response fails to address my comments on MM-BIO-2 and MM-BIO-3.
Response to Comment No. O6-59
The commenter provides recommended measures for protocol surveys for burrowing owl, California gnatcatcher, and special-status bats; pest control to prohibit rodenticides and avicides; Bird-Safe Guidelines; and additional compensatory mitigation for road mortality and window strikes. The commenter also recommends using California native plants for landscaping. As stated in Response to Comment No. O6-58, Project impacts to biological resources would be less than significant, and additional mitigation is not warranted. Therefore, incorporation of the comment’s recommended measures in the Draft EIR is not required under CEQA. However, the recommended measures are noted for the administrative record and will be forwarded to the decision-makers for review and consideration.
Reply: see my reply to Response to Comment Nol. 06-58a. The City’s premise for its conclusions is wrong.
Letter A1 from the California Department of Fish and Wildlife, 22 May 2023
Response to Comment No. A1-3
The comment summarizes the Project Description but does not address the adequacy of the Draft EIR. Accordingly, the comment is noted, and no additional response is warranted.
Reply: The comment actually does point out a deficiency of the DEIR. It points out that the majority of the existing oaks would be removed from the landscape, and that the mitigation measure of planting many replacement oaks and non-oaks on the campus could not possibly replace the biological values that would be lost. The DEIR considers the planted new trees as equivalent in value to the existing trees that live on the existing environment, but there is no equivalence. The existing trees undoubtedly include many cavities in which birds and other wildlife nest and roost (Photos 1 and 2). Photo 18 of my comment letter shows a white-breasted nuthatch delivering food to its chicks in just such a cavity on the project site. And even by the time the replacement trees mature,
29 their existence on the campus could not possibly resemble the existing environment in which the birds that rely on tree cavities can find sufficient food for their chicks.
Photos 1 and 2. Western screech-
owl within a cavity of an old-growth
walnut (above), and an ash-
throated flycatcher entering a nest
cavity of another old-growth walnut
(right). Old oaks similarly provide
many cavities for wildlife roosting
and cavity-nesting birds including
American kestrel, oak titmouse,
Nuttall’s woodpecker and many
additional special-status species.
30 Response to Comment No. A1-4
The comment is an introductory statement to specific comments on the analysis of biological resources presented in the Draft EIR. The comment does not address the adequacy of the Draft EIR. Accordingly, the comment is noted, and no additional response is warranted.
Reply: The response ignores the recommendation by CDFW to revise the DEIR to include scientific monitoring of biological resources as part of an adaptive management plan. CDFW’s recommendation is sound, as adaptive management was first formulated in 1978 (Holling 1978, Walters 1986, Walters and Holling 1990) and has since been given a great deal of scientific development and actual implementation.
Response to Comment No. A1-5a
The candidacy status of Crotch’s bumble bee was reinstated by the California Fish and Game Commission on September 30, 2022. The literature review for the Biological Resources Assessment report was conducted on January 18, 2022, when Crotch’s bumble bee was not a candidate to be considered a special status species. The Notice of Preparation (NOP) for the Draft EIR was published on March 29, 2022, and the baseline conditions for biological resources were established at that time (per CEQA Guidelines Section 15125). While the majority of the Project Site is disturbed or vegetated with non- native grasslands with few floral resources, the City acknowledges that upland scrub habitats within the Project Site might arguably provide potentially suitable nesting and foraging habitat for Crotch’s bumble bee.
Reply: In the spirit and intent of CEQA, the appropriate action was to require a detection survey for Crotch’s bumblebee, because the City was aware that both the project site could support Crotch’s bumblebee and the species was being considered for listing. The lead agency is not required to survey only for listed species, but rather to meet CEQA’s objectives of minimizing harm to the environment. At a time when other lead agencies were requiring surveys for Crotch’s bumblebee, City of Santa Clarita did not. In my own experience, Crotch’s bumblebee has been an issue in CEQA review since at least December 2021.
CDFW commented that Crotch’s bumblebee records exist throughout Los Angeles County. As my comment letter of 19 May 2023 reports, there are Crotch’s bumblebee records between 1.5 and 4 miles of the project site. With Crotch’s bumblebee occurring so close by, and considering the vegetation and soils on the project site appear suitable to the species, a decision to not survey for Crotch’s bumblebee to the standards summarized in CDFW’s comment letter would be indefensible.
Response to Comment No. A1-5b
Accordingly, the Draft EIR was revised to discuss the potential for the species to occur, evaluate potential project impacts, and provide species-specific avoidance and minimization measures in accordance with the comment’s recommendation.
Specifically, Mitigation Measure MM-BIO-6 requiring presence/ absence surveys conducted by a qualified biologist was added. If Crotch’s bumble bee is detected and cannot be feasibly avoided, the Applicant is required to seek an Incidental Take Permit
31 from CDFW. Mitigation Measures MM-BIO-7, MM-BIO-8, and MM-BIO-9 would require the application for such take authorization, establishment of a buffer zone around any active nest, and replacement of any floral resource associated with Crotch’s bumble bee that is removed or damaged. If Crotch’s bumblebee is present within the Project Site, implementation of Mitigation Measures MM-BIO-7 through MM-BIO-9 would reduce potential impacts to the species to a less-than- significant level.
Reply: As CDFW recommended, the detection surveys for Crotch’s bumblebee should be completed prior to finalization of the CEQA review. The DEIR should be withdrawn, and not recirculated until after it has been updated with the results of a project-wide detection survey for Crotch’s bumblebee.
Response to Comment No. A1-6a
...the likelihood for mountain lion to be present within the Project Site is low due to a variety of factors: the Project Site is not within a natural landscape block; the nearest blocks are within the Santa Susana Mountains southwest of I-5 and the San Gabriel Mountains east of SR- 14.2 The CDFW mountain lion habitat suitability dataset predicts relatively low probability of use within the Project Site, similar to the urban center of Santa Clarita.3 The Project Site is bounded to the southwest and southeast by commercial development, and to the east by residential development. While Placerita Creek may provide local movement pathways for mobile species, such as mule deer and coyote, on a broader landscape scale, Placerita Creek and its surrounding open spaces (including Quigley Canyon Open Space) are cut off from suitable mountain lion habitat linkages and corridors by SR-14, approximately 2 miles to the east. A review of iNaturalist shows that mountain lions or their sign (e.g., scat, tracks) were not documented within the Santa Clarita Valley in the area bounded by I-5, SR-14, and the Santa Clara River. Newhall Creek, situated downstream of the Project Site, is heavily constrained on both sides by intensive residential and commercial development.
Accordingly, the potential for mountain lion occurrence is low, and Placerita Creek is not likely to function as regional movement pathway for mountain lions, which require extensive home ranges. Due to the extensive development surrounding the Project Site discussed above, human presence from the surrounding land uses is already at a high level, and development of the Project would not represent a significant change in this condition.
Reply: The analysis is speculative and begins from a flawed premise. The response argues that the likelihood of occurrence of mountain lion on the project site is low, but it fails to acknowledge that the rare occurrence of mountain lion is also a critically important occurrence to the persistence of the species in southern California. The greatest threat to mountain lions in southern California is the species’ loss of connectivity.
My four decades of research on mountain lions began with a review of news stories of mountain lions occurring at just the sort of places that the response speculates mountain lions would not occur. I found numerous stories going back a century of mountain lions ending up in places like Chico, Redding, Oroville, Sacramento, Fresno and Bakersfield. I saw one in Davis, California just before she and her cub was
32 euthanized in Woodland after having preyed on deer that were enclosed at UC Davis as part of a research study. The many occurrences of mountain lions in urban places, which continues to this day, reflect the need of young mountain lions to disperse from their natal home ranges. Many of their traditional travel routes, such along streams, have been encroached by urbanization, but this encroachment has not stopped mountain lions from attempting to disperse along the long-used routes.
I have detected mountain lions on the outskirts of Santa Clarita numerous times during my studies dating to 1985 (Smallwood and Fitzhugh 1995, Smallwood 1997). One reliable location for detecting this species has been along a transect I use just uphill from the Placerita Creek headwaters. Another reliable transect location is upstream along Bouquet Canyon. I would expect mountain lions originating from either location to cross through Santa Clarita heading to or from the Transverse Range to the west. And contrary to the assertion made in the response, mountain lions often cross roads, including the busiest highways, but not always successfully. In recent years, at least several mountain lions have been killed on Highway 14 and Interstate 5 at and near Santa Clarita.
The project site is not going to be part of a mountain lion home range, so the response’s speculation about mountain lions requiring larger home ranges is a bit misleading. The question is whether a mountain lion would use Placerita Creek as a movement corridor and whether along the way they might stopover on the project site. My answer, based on my experience with tracking this species over many years, is yes.
CDFW’s comments were relevant and justified. The text added to the EIR is misleading and addresses the wrong issue of occurrence likelihood. The DEIR should be revised in response to CDFW’s comments.
Response to Comment No. A1-6b
The Project would comply with all applicable herbicide and rodenticide regulations.
Reply: This response does not go far enough. Compliance with existing regulations is still resulting with too much use of rodenticides to the detriment of Mammalian Carnivores throughout California. As I recommended in my comments of 19 May 2023, “The project should commit to no use of rodenticides and avicides. It should commit to no placement of poison bait stations outside the building.”
Response to Comment No. A1-9a
The injury or death of limited individuals of SSC, if present, due to Project construction activities would not contribute to a loss of population viability of these species and would not result in impacts that would meet this threshold of significance. As a result, additional mitigation measures requiring focused surveys for SSC species are not necessary to reduce Project impacts to a less-than-significant level.
Reply: The response is purely speculative, and completely unsubstantiated by evidence.
Not for one SSC species has the City presented any evidence that the project’s takings of members of that species would results in no significant impacts to the population.
33 Response to Comment No. A1-9b
Nevertheless, as shown above, to be responsive to the commenter’s concerns, Mitigation Measure MM-BIO-1 has been revised to include a relocation and avoidance plan, worker awareness training, and additional details regarding biological monitoring responsibilities and protocols, even though their inclusion is not necessary to reduce Project impacts to a less-than-significant level.
Reply: A relocation plan brings additional risks of harm to wildlife at the receiving sites. Displacement by relocation often results in the deaths of animals undergoing relocation or the deaths of others in the areas receiving translocated plants or animals (Griffith et al. 1989, Dodd and Seigel 1991, Schulz 1997). Conspecifics outside the project area can be injured or killed or starved as a result of competition with desperate animals that are translocated from the project. In one study of relocated burrowing owls (an SSC), for example, many of the translocated owls collided with windows and automobiles soon after release (Schulz 1997). The process of translocation appears to be traumatic for the translocated individuals, as it probably also is for the conspecifics having to deal with the translocated animals released into their territories.
Rather than revise the DEIR to include a relocation plan that would further jeopardize wildlife, I recommend that the City take seriously the recommended mitigation measures of CDFW.
Thank you for your consideration,
______________________
Shawn Smallwood, Ph.D.
LITERATURE CITED
CDFW (California Department of Fish and Wildlife). 2012. Staff Report on Burrowing Owl Mitigation. Sacramento, California.
Dodd, C. K. and R. A. Seigel. 1991. Relocation, repatriation and translocation of amphibians and reptiles: Are they conservation strategies that work? Herpetologica 47:336-350.
Franzeb, K. E. 1978. Breeding bird densities, species composition, and bird species diversity of the Algodones Dunes. Western Birds 9:9-20.
Green, R. H., and R. C. Young. 1993. Sampling to detect rare species. Ecological Applications 3:351-356.
34 Griffith, B., J.M. Scott, J.W. Carpenter, and C. Reed. 1989. Translocation as a Species Conservation Tool: Status and Strategy. Science 245:477-480
Holling, C.S. (ed.). 1978. Adaptive environmental assessment and management. John Wiley & Sons, New York.
Hutto. R. L. 2016. Should scientists be required to use a model-based solution to adjust for possible distance-based detectability trials? Ecological Applications 26:1287- 1294.
Kozma, J. M. and N. E. Mathews. 1997. Breeding bird communities and nest plant selection in Chihuahuan Desert habitats in south-central New Mexico. Wilson Bulletin 109:424-436.
Rincon. 2023. Shadowbox Studios Project Biological Resources Assessment. Prepared for Shadowbox Studios, Atlanta, Georgia.
Schulz, T. A. 1997. Observations, resightings, and encounters of rehabilitated, orphaned, and relocated burrowing owls. Journal of Raptor Research Reports 9:128-131.
Smallwood, K. S. 1997. Interpreting puma (Puma concolor) density estimates for theory and management. Environmental Conservation 24(3):283-289.
Smallwood, K. S. 1999. Scale domains of abundance among species of Mammalian Carnivora. Environmental Conservation 26:102-111.
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. 2015. Habitat fragmentation and corridors. Pages 84-101 in M. L.
Morrison and H. A. Mathewson, Eds., Wildlife habitat conservation: concepts, challenges, and solutions. John Hopkins University Press, Baltimore, Maryland.
Smallwood, K. S. 2022. Utility-scale solar impacts to volant wildlife. Journal of Wildlife Management: e22216. https://doi.org/10.1002/jwmg.22216
Smallwood, K. S. and E. L. Fitzhugh. 1995. A track count for estimating mountain lion Felis concolor californica population trend. Biological Conservation 71:251-259
Smallwood, K. S., and L. Neher. 2017. Comparing bird and bat use data for siting new wind power generation. Report CEC-500-2017-019, California Energy Commission Public Interest Energy Research program, Sacramento, California. http://www.energy.ca.gov/2017publications/CEC-500-2017-019/CEC-500-2017-
35 019.pdf and http://www.energy.ca.gov/2017publications/CEC-500-2017-019/CEC- 500-2017-019-APA-F.pdf
Smallwood, K. S. and M. L. Morrison. 2018. Nest-site selection in a high-density colony of burrowing owls. Journal of Raptor Research 52:454-470.
Smallwood, K. S., L. Neher, J. Mount, and R. C. E. Culver. 2013. Nesting burrowing owl abundance in the Altamont Pass Wind Resource Area, California. Wildlife Society Bulletin: 37:787-795.
Strusis-Timmer, M. 2009 Habitat associations and nest survival of Yellow Warblers in California. Master's Theses. 3682. DOI: https://doi.org/10.31979/etd.sb3f-z3a6 https://scholarworks.sjsu.edu/etd_theses/3682
Thompson, W. L. 2002. Towards reliable bird surveys: Accounting for individuals present by not detected. The Auk 119:18-25.
Timmer, M., D. L. Suddjian, S. Lambrecht, and S. Bros-Seemann. 2011. Nesting success of the yellow warbler in a disturbed riparian forest in coastal California. Western Birds 42:96–102.
U.S. Fish and Wildlife Service. 1997. Coastal California Gnatcatcher (Polioptila californica californica) presence/absence survey guidelines, February 28, 1997.
Carlsbad Fish and Wildlife Office, Carlsbad, California.
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1 Kenneth Shawn Smallwood
Curriculum Vitae
3108 Finch Street Born May 3, 1963 in
Davis, CA 95616 Sacramento, California.
Phone (530) 756-4598 Married, father of two.
Cell (530) 601-6857
[email protected]
Ecologist
Expertise
Finding solutions to controversial problems related to wildlife interactions with human industry, infrastructure, and activities;
Wildlife monitoring and field study using GPS, thermal imaging, behavior surveys;
Using systems analysis and experimental design principles to identify meaningful ecological patterns that inform management decisions.
Education
Ph.D. Ecology, University of California, Davis. September 1990.
M.S. Ecology, University of California, Davis. June 1987.
B.S. Anthropology, University of California, Davis. June 1985.
Corcoran High School, Corcoran, California. June 1981.
Experience
480 professional publications, including:
83 peer reviewed publications
24 in non-reviewed proceedings
371 reports, declarations, posters and book reviews
8 in mass media outlets
87 public presentations of research results
Editing for scientific journals: Guest Editor, Wildlife Society Bulletin, 2012-2013, of invited papers representing international views on the impacts of wind energy on wildlife and how to mitigate the impacts. Associate Editor, Journal of Wildlife Management, March 2004 to 30 June 2007.
Editorial Board Member, Environmental Management, 10/1999 to 8/2004. Associate Editor, Biological Conservation, 9/1994 to 9/1995.
Member, Alameda County Scientific Review Committee (SRC), August 2006 to April 2011. The five-member committee investigated causes of bird and bat collisions in the Altamont Pass Wind Resource Area, and recommended mitigation and monitoring measures. The SRC Smallwood CV
2 reviewed the science underlying the Alameda County Avian Protection Program, and advised the County on how to reduce wildlife fatalities.
Consulting Ecologist, 2004-2007, California Energy Commission (CEC). Provided consulting services as needed to the CEC on renewable energy impacts, monitoring and research, and produced several reports. Also collaborated with Lawrence-Livermore National Lab on research to understand and reduce wind turbine impacts on wildlife.
Consulting Ecologist, 1999-2013, U.S. Navy. Performed endangered species surveys, hazardous waste site monitoring, and habitat restoration for the endangered San Joaquin kangaroo rat, California tiger salamander, California red-legged frog, California clapper rail, western burrowing owl, salt marsh harvest mouse, and other species at Naval Air Station Lemoore; Naval Weapons Station, Seal Beach, Detachment Concord; Naval Security Group Activity, Skaggs Island; National Radio Transmitter Facility, Dixon; and, Naval Outlying Landing Field Imperial Beach.
Part-time Lecturer, 1998-2005, California State University, Sacramento. Instructed Mammalogy, Behavioral Ecology, and Ornithology Lab, Contemporary Environmental Issues, Natural Resources Conservation.
Senior Ecologist, 1999-2005, BioResource Consultants. Designed and implemented research and monitoring studies related to avian fatalities at wind turbines, avian electrocutions on electric distribution poles across California, and avian fatalities at transmission lines.
Chairman, Conservation Affairs Committee, The Wildlife Society--Western Section, 1999-2001.
Prepared position statements and led efforts directed toward conservation issues, including travel to Washington, D.C. to lobby Congress for more wildlife conservation funding.
Systems Ecologist, 1995-2000, Institute for Sustainable Development. Headed ISD’s program on integrated resources management. Developed indicators of ecological integrity for large areas, using remotely sensed data, local community involvement and GIS.
Associate, 1997-1998, Department of Agronomy and Range Science, University of California, Davis. Worked with Shu Geng and Mingua Zhang on several studies related to wildlife interactions with agriculture and patterns of fertilizer and pesticide residues in groundwater across a large landscape.
Lead Scientist, 1996-1999, National Endangered Species Network. Informed academic scientists and environmental activists about emerging issues regarding the Endangered Species Act and other environmental laws. Testified at public hearings on endangered species issues.
Ecologist, 1997-1998, Western Foundation of Vertebrate Zoology. Conducted field research to determine the impact of past mercury mining on the status of California red-legged frogs in Santa Clara County, California.
Senior Systems Ecologist, 1994-1995, EIP Associates, Sacramento, California. Provided consulting services in environmental planning, and quantitative assessment of land units for their Smallwood CV
3 conservation and restoration opportunities basedon ecological resource requirements of 29 special-status species. Developed ecological indicators for prioritizing areas within Yolo County to receive mitigation funds for habitat easements and restoration.
Post-Graduate Researcher, 1990-1994, Department of Agronomy and Range Science, U.C. Davis.
Under Dr. Shu Geng’s mentorship, studied landscape and management effects on temporal and spatial patterns of abundance among pocket gophers and species of Falconiformes and Carnivora in the Sacramento Valley. Managed and analyzed a data base of energy use in California agriculture. Assisted with landscape (GIS) study of groundwater contamination across Tulare County, California.
Work experience in graduate school: Co-taught Conservation Biology with Dr. Christine Schonewald, 1991 & 1993, UC Davis Graduate Group in Ecology; Reader for Dr. Richard Coss’s course on Psychobiology in 1990, UC Davis Department of Psychology; Research Assistant to Dr. Walter E. Howard, 1988-1990, UC Davis Department of Wildlife and Fisheries Biology, testing durable baits for pocket gopher management in forest clearcuts; Research Assistant to Dr. Terrell P. Salmon, 1987-1988, UC Wildlife Extension, Department of Wildlife and Fisheries Biology, developing empirical models of mammal and bird invasions in North America, and a rating system for priority research and control of exotic species based on economic, environmental and human health hazards in California. Student Assistant to Dr. E.
Lee Fitzhugh, 1985-1987, UC Cooperative Extension, Department of Wildlife and Fisheries Biology, developing and implementing statewide mountain lion track count for long-term monitoring.
Fulbright Research Fellow, Indonesia, 1988. Tested use of new sampling methods for numerical monitoring of Sumatran tiger and six other species of endemic felids, and evaluated methods used by other researchers.
Projects
Repowering wind energy projects through careful siting of new wind turbines using map-based collision hazard models to minimize impacts to volant wildlife. Funded by wind companies (principally NextEra Renewable Energy, Inc.), California Energy Commission and East Bay Regional Park District, I have collaborated with a GIS analyst and managed a crew of five field biologists performing golden eagle behavior surveys and nocturnal surveys on bats and owls. The goal is to quantify flight patterns for development of predictive models to more carefully site new wind turbines in repowering projects. Focused behavior surveys began May 2012 and continue.
Collision hazard models have been prepared for seven wind projects, three of which were built.
Planning for additional repowering projects is underway.
Test avian safety of new mixer-ejector wind turbine (MEWT). Designed and implemented a before- after, control-impact experimental design to test the avian safety of a new, shrouded wind turbine developed by Ogin Inc. (formerly known as FloDesign Wind Turbine Corporation). Supported by a $718,000 grant from the California Energy Commission’s Public Interest Energy Research program and a 20% match share contribution from Ogin, I managed a crew of seven field biologists who performed periodic fatality searches and behavior surveys, carcass detection trials, nocturnal behavior surveys using a thermal camera, and spatial analyses with the collaboration of a GIS Smallwood CV
4 analyst. Field work began 1 April 2012 and ended 30 March 2015 without Ogin installing its MEWTs, but we still achieved multiple important scientific advances.
Reduce avian mortality due to wind turbines at Altamont Pass. Studied wildlife impacts caused by 5,400 wind turbines at the world’s most notorious wind resource area. Studied how impacts are perceived by monitoring and how they are affected by terrain, wind patterns, food resources, range management practices, wind turbine operations, seasonal patterns, population cycles, infrastructure management such as electric distribution, animal behavior and social interactions.
Reduce avian mortality on electric distribution poles. Directed research toward reducing bird electrocutions on electric distribution poles, 2000-2007. Oversaw 5 founds of fatality searches at 10,000 poles from Orange County to Glenn County, California, and produced two large reports.
Cook et al. v. Rockwell International et al., No. 90-K-181 (D. Colorado). Provided expert testimony on the role of burrowing animals in affecting the fate of buried and surface-deposited radioactive and hazardous chemical wastes at the Rocky Flats Plant, Colorado. Provided expert reports based on four site visits and an extensive document review of burrowing animals. Conducted transect surveys for evidence of burrowing animals and other wildlife on and around waste facilities. Discovered substantial intrusion of waste structures by burrowing animals. I testified in federal court in November 2005, and my clients were subsequently awarded a $553,000,000 judgment by a jury.
After appeals the award was increased to two billion dollars.
Hanford Nuclear Reservation Litigation. Provided expert testimony on the role of burrowing animals in affecting the fate of buried radioactive wastes at the Hanford Nuclear Reservation, Washington. Provided three expert reports based on three site visits and extensive document review.
Predicted and verified a certain population density of pocket gophers on buried waste structures, as well as incidence of radionuclide contamination in body tissue. Conducted transect surveys for evidence of burrowing animals and other wildlife on and around waste facilities. Discovered substantial intrusion of waste structures by burrowing animals.
Expert testimony and declarations on proposed residential and commercial developments, gas-fired power plants, wind, solar and geothermal projects, water transfers and water transfer delivery systems, endangered species recovery plans, Habitat Conservation Plans and Natural Communities Conservation Programs. Testified before multiple government agencies, Tribunals, Boards of Supervisors and City Councils, and participated with press conferences and depositions. Prepared expert witness reports and court declarations, which are summarized under Reports (below).
Protocol-level surveys for special-status species. Used California Department of Fish and Wildlife and US Fish and Wildlife Service protocols to search for California red-legged frog, California tiger salamander, arroyo southwestern toad, blunt-nosed leopard lizard, western pond turtle, giant kangaroo rat, San Joaquin kangaroo rat, San Joaquin kit fox, western burrowing owl, Swainson’s hawk, Valley elderberry longhorn beetle and other special-status species.
Conservation of San Joaquin kangaroo rat. Performed research to identify factors responsible for the decline of this endangered species at Lemoore Naval Air Station, 2000-2013, and implemented habitat enhancements designed to reverse the trend and expand the population.
Smallwood CV
5 Impact of West Nile Virus on yellow-billed magpies. Funded by Sacramento-Yolo Mosquito and Vector Control District, 2005-2008, compared survey results pre- and post-West Nile Virus epidemic for multiple bird species in the Sacramento Valley, particularly on yellow-billed magpie and American crow due to susceptibility to WNV.
Workshops on HCPs. Assisted Dr. Michael Morrison with organizing and conducting a 2-day workshop on Habitat Conservation Plans, sponsored by Southern California Edison, and another 1- day workshop sponsored by PG&E. These Workshops were attended by academics, attorneys, and consultants with HCP experience. We guest-edited a Proceedings published in Environmental Management.
Mapping of biological resources along Highways 101, 46 and 41. Used GPS and GIS to delineate vegetation complexes and locations of special-status species along 26 miles of highway in San Luis Obispo County, 14 miles of highway and roadway in Monterey County, and in a large area north of Fresno, including within reclaimed gravel mining pits.
GPS mapping and monitoring at restoration sites and at Caltrans mitigation sites. Monitored the success of elderberry shrubs at one location, the success of willows at another location, and the response of wildlife to the succession of vegetation at both sites. Also used GPS to monitor the response of fossorial animals to yellow star-thistle eradication and natural grassland restoration efforts at Bear Valley in Colusa County and at the decommissioned Mather Air Force Base in Sacramento County.
Mercury effects on Red-legged Frog. Assisted Dr. Michael Morrison and US Fish and Wildlife Service in assessing the possible impacts of historical mercury mining on the federally listed California red-legged frog in Santa Clara County. Also measured habitat variables in streams.
Opposition to proposed No Surprises rule. Wrote a white paper and summary letter explaining scientific grounds for opposing the incidental take permit (ITP) rules providing ITP applicants and holders with general assurances they will be free of compliance with the Endangered Species Act once they adhere to the terms of a “properly functioning HCP.” Submitted 188 signatures of scientists and environmental professionals concerned about No Surprises rule US Fish and Wildlife Service, National Marine Fisheries Service, all US Senators.
Natomas Basin Habitat Conservation Plan alternative. Designed narrow channel marsh to increase the likelihood of survival and recovery in the wild of giant garter snake, Swainson’s hawk and Valley Elderberry Longhorn Beetle. The design included replication and interspersion of treatments for experimental testing of critical habitat elements. I provided a report to Northern Territories, Inc.
Assessments of agricultural production system and environmental technology transfer to China.
Twice visited China and interviewed scientists, industrialists, agriculturalists, and the Directors of the Chinese Environmental Protection Agency and the Department of Agriculture to assess the need and possible pathways for environmental clean-up technologies and trade opportunities between the US and China.
Yolo County Habitat Conservation Plan. Conducted landscape ecology study of Yolo County to spatially prioritize allocation of mitigation efforts to improve ecosystem functionality within the Smallwood CV
6 County from the perspective of 29 special-status species of wildlife and plants. Used a hierarchically structured indicators approach to apply principles of landscape and ecosystem ecology, conservation biology, and local values in rating land units. Derived GIS maps to help guide the conservation area design, and then developed implementation strategies.
Mountain lion track count. Developed and conducted a carnivore monitoring program throughout California since 1985. Species counted include mountain lion, bobcat, black bear, coyote, red and gray fox, raccoon, striped skunk, badger, and black-tailed deer. Vegetation and land use are also monitored. Track survey transect was established on dusty, dirt roads within randomly selected quadrats.
Sumatran tiger and other felids. Upon award of Fulbright Research Fellowship, I designed and initiated track counts for seven species of wild cats in Sumatra, including Sumatran tiger, fishing cat, and golden cat. Spent four months on Sumatra and Java in 1988, and learned Bahasa Indonesia, the official Indonesian language.
Wildlife in agriculture. Beginning as post-graduate research, I studied pocket gophers and other wildlife in 40 alfalfa fields throughout the Sacramento Valley, and I surveyed for wildlife along a 200 mile road transect since 1989 with a hiatus of 1996-2004. The data are analyzed using GIS and methods from landscape ecology, and the results published and presented orally to farming groups in California and elsewhere. I also conducted the first study of wildlife in cover crops used on vineyards and orchards.
Agricultural energy use and Tulare County groundwater study. Developed and analyzed a data base of energy use in California agriculture, and collaborated on a landscape (GIS) study of groundwater contamination across Tulare County, California.
Pocket gopher damage in forest clear-cuts. Developed gopher sampling methods and tested various poison baits and baiting regimes in the largest-ever field study of pocket gopher management in forest plantations, involving 68 research plots in 55 clear-cuts among 6 National Forests in northern California.
Risk assessment of exotic species in North America. Developed empirical models of mammal and bird species invasions in North America, as well as a rating system for assigning priority research and control to exotic species in California, based on economic, environmental, and human health hazards.
Peer Reviewed Publications
Smallwood, K. S. and M. L. Morrison. 2018. Nest-site selection in a high-density colony of burrowing owls. Journal of Raptor Research 52:454-470.
Smallwood, K. S., D. A. Bell, E. L. Walther, E. Leyvas, S. Standish, J. Mount, B. Karas. 2018.
Estimating wind turbine fatalities using integrated detection trials. Journal of Wildlife Management 82:1169-1184.
Smallwood, K. S. 2017. Long search intervals under-estimate bird and bat fatalities caused by Smallwood CV
7 wind turbines. Wildlife Society Bulletin 41:224-230.
Smallwood, K. S. 2017. The challenges of addressing wildlife impacts when repowering wind energy projects. Pages 175-187 in Köppel, J., Editor, Wind Energy and Wildlife Impacts:
Proceedings from the CWW2015 Conference. Springer. Cham, Switzerland.
May, R., Gill, A. B., Köppel, J. Langston, R. H.W., Reichenbach, M., Scheidat, M., Smallwood, S., Voigt, C. C., Hüppop, O., and Portman, M. 2017. Future research directions to reconcile wind turbine–wildlife interactions. Pages 255-276 in Köppel, J., Editor, Wind Energy and Wildlife Impacts: Proceedings from the CWW2015 Conference. Springer. Cham, Switzerland.
Smallwood, K. S. 2017. Monitoring birds. M. Perrow, Ed., Wildlife and Wind Farms - Conflicts and Solutions, Volume 2. Pelagic Publishing, Exeter, United Kingdom. www.bit.ly/2v3cR9Q
Smallwood, K. S., L. Neher, and D. A. Bell. 2017. Siting to Minimize Raptor Collisions: an example from the Repowering Altamont Pass Wind Resource Area. M. Perrow, Ed., Wildlife and Wind Farms - Conflicts and Solutions, Volume 2. Pelagic Publishing, Exeter, United Kingdom. www.bit.ly/2v3cR9Q
Johnson, D. H., S. R. Loss, K. S. Smallwood, W. P. Erickson. 2016. Avian fatalities at wind energy facilities in North America: A comparison of recent approaches. Human–Wildlife Interactions 10(1):7-18.
Sadar, M. J., D. S.-M. Guzman, A. Mete, J. Foley, N. Stephenson, K. H. Rogers, C. Grosset, K. S.
Smallwood, J. Shipman, A. Wells, S. D. White, D. A. Bell, and M. G. Hawkins. 2015. Mange Caused by a novel Micnemidocoptes mite in a Golden Eagle (Aquila chrysaetos). Journal of Avian Medicine and Surgery 29(3):231-237.
Smallwood, K. S. 2015. Habitat fragmentation and corridors. Pages 84-101 in M. L. Morrison and H. A. Mathewson, Eds., Wildlife habitat conservation: concepts, challenges, and solutions. John Hopkins University Press, Baltimore, Maryland, USA.
Mete, A., N. Stephenson, K. Rogers, M. G. Hawkins, M. Sadar, D. Guzman, D. A. Bell, J. Shipman, A. Wells, K. S. Smallwood, and J. Foley. 2014. Emergence of Knemidocoptic mange in wild Golden Eagles (Aquila chrysaetos) in California. Emerging Infectious Diseases 20(10):1716- 1718.
Smallwood, K. S. 2013. Introduction: Wind-energy development and wildlife conservation.
Wildlife Society Bulletin 37: 3-4.
Smallwood, K. S. 2013. Comparing bird and bat fatality-rate estimates among North American wind-energy projects. Wildlife Society Bulletin 37:19-33. + Online Supplemental Material.
Smallwood, K. S., L. Neher, J. Mount, and R. C. E. Culver. 2013. Nesting Burrowing Owl Abundance in the Altamont Pass Wind Resource Area, California. Wildlife Society Bulletin:
37:787-795.
Smallwood CV
8 Smallwood, K. S., D. A. Bell, B. Karas, and S. A. Snyder. 2013. Response to Huso and Erickson Comments on Novel Scavenger Removal Trials. Journal of Wildlife Management 77: 216-225.
Bell, D. A., and K. S. Smallwood. 2010. Birds of prey remain at risk. Science 330:913.
Smallwood, K. S., D. A. Bell, S. A. Snyder, and J. E. DiDonato. 2010. Novel scavenger removal trials increase estimates of wind turbine-caused avian fatality rates. Journal of Wildlife Management 74: 1089-1097 + Online Supplemental Material.
Smallwood, K. S., L. Neher, and D. A. Bell. 2009. Map-based repowering and reorganization of a wind resource area to minimize burrowing owl and other bird fatalities. Energies 2009(2):915- 943. http://www.mdpi.com/1996-1073/2/4/915
Smallwood, K. S. and B. Nakamoto. 2009. Impacts of West Nile Virus Epizootic on Yellow-Billed Magpie, American Crow, and other Birds in the Sacramento Valley, California. The Condor 111:247-254.
Smallwood, K. S., L. Rugge, and M. L. Morrison. 2009. Influence of Behavior on Bird Mortality in Wind Energy Developments: The Altamont Pass Wind Resource Area, California. Journal of Wildlife Management 73:1082-1098.
Smallwood, K. S. and B. Karas. 2009. Avian and Bat Fatality Rates at Old-Generation and Repowered Wind Turbines in California. Journal of Wildlife Management 73:1062-1071.
Smallwood, K. S. 2008. Wind power company compliance with mitigation plans in the Altamont Pass Wind Resource Area. Environmental & Energy Law Policy Journal 2(2):229-285.
Smallwood, K. S., C. G. Thelander. 2008. Bird Mortality in the Altamont Pass Wind Resource Area, California. Journal of Wildlife Management 72:215-223.
Smallwood, K. S. 2007. Estimating wind turbine-caused bird mortality. Journal of Wildlife Management 71:2781-2791.
Smallwood, K. S., C. G. Thelander, M. L. Morrison, and L. M. Rugge. 2007. Burrowing owl mortality in the Altamont Pass Wind Resource Area. Journal of Wildlife Management 71:1513- 1524.
Cain, J. W. III, K. S. Smallwood, M. L. Morrison, and H. L. Loffland. 2005. Influence of mammal activity on nesting success of Passerines. J. Wildlife Management 70:522-531.
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.
Morrison, M. L., K. S. Smallwood, and L. S. Hall. 2002. Creating habitat through plant relocation:
Lessons from Valley elderberry longhorn beetle mitigation. Ecological Restoration 21: 95-100.
Smallwood CV
9 Zhang, M., K. S. Smallwood, and E. Anderson. 2002. Relating indicators of ecological health and integrity to assess risks to sustainable agriculture and native biota. Pages 757-768 in D.J.
Rapport, W.L. Lasley, D.E. Rolston, N.O. Nielsen, C.O. Qualset, and A.B. Damania (eds.), Managing for Healthy Ecosystems, Lewis Publishers, Boca Raton, Florida USA.
Wilcox, B. A., K. S. Smallwood, and J. A. Kahn. 2002. Toward a forest Capital Index. Pages 285- 298 in D.J. Rapport, W.L. Lasley, D.E. Rolston, N.O. Nielsen, C.O. Qualset, and A.B. Damania (eds.), Managing for Healthy Ecosystems, Lewis Publishers, Boca Raton, Florida USA.
Smallwood, K.S. 2001. The allometry of density within the space used by populations of Mammalian Carnivores. Canadian Journal of Zoology 79:1634-1640.
Smallwood, K.S., and T.R. Smith. 2001. Study design and interpretation of Sorex density estimates. Annales Zoologi Fennici 38:141-161.
Smallwood, K.S., A. Gonzales, T. Smith, E. West, C. Hawkins, E. Stitt, C. Keckler, C. Bailey, and K. Brown. 2001. Suggested standards for science applied to conservation issues. Transactions of the Western Section of the Wildlife Society 36:40-49.
Geng, S., Yixing Zhou, Minghua Zhang, and K. Shawn Smallwood. 2001. A Sustainable Agro- ecological Solution to Water Shortage in North China Plain (Huabei Plain). Environmental Planning and Management 44:345-355.
Smallwood, K. Shawn, Lourdes Rugge, Stacia Hoover, Michael L. Morrison, Carl Thelander. 2001.
Intra- and inter-turbine string comparison of fatalities to animal burrow densities at Altamont Pass. Pages 23-37 in S. S. Schwartz, ed., Proceedings of the National Avian-Wind Power Planning Meeting IV. RESOLVE, Inc., Washington, D.C.
Smallwood, K.S., S. Geng, and M. Zhang. 2001. Comparing pocket gopher (Thomomys bottae) density in alfalfa stands to assess management and conservation goals in northern California.
Agriculture, Ecosystems & Environment 87: 93-109.
Smallwood, K. S. 2001. Linking habitat restoration to meaningful units of animal demography.
Restoration Ecology 9:253-261.
Smallwood, K. S. 2000. A crosswalk from the Endangered Species Act to the HCP Handbook and real HCPs. Environmental Management 26, Supplement 1:23-35.
Smallwood, K. S., J. Beyea and M. Morrison. 1999. Using the best scientific data for endangered species conservation. Environmental Management 24:421-435.
Smallwood, K. S. 1999. Scale domains of abundance among species of Mammalian Carnivora.
Environmental Conservation 26:102-111.
Smallwood, K.S. 1999. Suggested study attributes for making useful population density estimates.
Transactions of the Western Section of the Wildlife Society 35: 76-82.
Smallwood CV
10 Smallwood, K. S. and M. L. Morrison. 1999. Estimating burrow volume and excavation rate of pocket gophers (Geomyidae). Southwestern Naturalist 44:173-183.
Smallwood, K. S. and M. L. Morrison. 1999. Spatial scaling of pocket gopher (Geomyidae) density. Southwestern Naturalist 44:73-82.
Smallwood, K. S. 1999. Abating pocket gophers (Thomomys spp.) to regenerate forests in clearcuts. Environmental Conservation 26:59-65.
Smallwood, K. S. 1998. Patterns of black bear abundance. Transactions of the Western Section of the Wildlife Society 34:32-38.
Smallwood, K. S. 1998. On the evidence needed for listing northern goshawks (Accipter gentilis) under the Endangered Species Act: a reply to Kennedy. J. Raptor Research 32:323-329.
Smallwood, K. S., B. Wilcox, R. Leidy, and K. Yarris. 1998. Indicators assessment for Habitat Conservation Plan of Yolo County, California, USA. Environmental Management 22: 947-958.
Smallwood, K. S., M. L. Morrison, and J. Beyea. 1998. Animal burrowing attributes affecting hazardous waste management. Environmental Management 22: 831-847.
Smallwood, K. S, and C. M. Schonewald. 1998. Study design and interpretation for mammalian carnivore density estimates. Oecologia 113:474-491.
Zhang, M., S. Geng, and K. S. Smallwood. 1998. Nitrate contamination in groundwater of Tulare County, California. Ambio 27(3):170-174.
Smallwood, K. S. and M. L. Morrison. 1997. Animal burrowing in the waste management zone of Hanford Nuclear Reservation. Proceedings of the Western Section of the Wildlife Society Meeting 33:88-97.
Morrison, M. L., K. S. Smallwood, and J. Beyea. 1997. Monitoring the dispersal of contaminants by wildlife at nuclear weapons production and waste storage facilities. The Environmentalist 17:289-295.
Smallwood, K. S. 1997. Interpreting puma (Puma concolor) density estimates for theory and management. Environmental Conservation 24(3):283-289.
Smallwood, K. S. 1997. Managing vertebrates in cover crops: a first study. American Journal of Alternative Agriculture 11:155-160.
Smallwood, K. S. and S. Geng. 1997. Multi-scale influences of gophers on alfalfa yield and quality. Field Crops Research 49:159-168.
Smallwood, K. S. and C. Schonewald. 1996. Scaling population density and spatial pattern for terrestrial, mammalian carnivores. Oecologia 105:329-335.
Smallwood CV
11 Smallwood, K. S., G. Jones, and C. Schonewald. 1996. Spatial scaling of allometry for terrestrial, mammalian carnivores. Oecologia 107:588-594.
Van Vuren, D. and K. S. Smallwood. 1996. Ecological management of vertebrate pests in agricultural systems. Biological Agriculture and Horticulture 13:41-64.
Smallwood, K. S., B. J. Nakamoto, and S. Geng. 1996. Association analysis of raptors on an agricultural landscape. Pages 177-190 in D.M. Bird, D.E. Varland, and J.J. Negro, eds., Raptors in human landscapes. Academic Press, London.
Erichsen, A. L., K. S. Smallwood, A. M. Commandatore, D. M. Fry, and B. Wilson. 1996. White- tailed Kite movement and nesting patterns in an agricultural landscape. Pages 166-176 in D. M.
Bird, D. E. Varland, and J. J. Negro, eds., Raptors in human landscapes. Academic Press, London.
Smallwood, K. S. 1995. Scaling Swainson's hawk population density for assessing habitat-use across an agricultural landscape. J. Raptor Research 29:172-178.
Smallwood, K. S. and W. A. Erickson. 1995. Estimating gopher populations and their abatement in forest plantations. Forest Science 41:284-296.
Smallwood, K. S. and E. L. Fitzhugh. 1995. A track count for estimating mountain lion Felis concolor californica population trend. Biological Conservation 71:251-259
Smallwood, K. S. 1994. Site invasibility by exotic birds and mammals. Biological Conservation 69:251-259.
Smallwood, K. S. 1994. Trends in California mountain lion populations. Southwestern Naturalist 39:67-72.
Smallwood, K. S. 1993. Understanding ecological pattern and process by association and order.
Acta Oecologica 14(3):443-462.
Smallwood, K. S. and E. L. Fitzhugh. 1993. A rigorous technique for identifying individual mountain lions Felis concolor by their tracks. Biological Conservation 65:51-59.
Smallwood, K. S. 1993. Mountain lion vocalizations and hunting behavior. The Southwestern Naturalist 38:65-67.
Smallwood, K. S. and T. P. Salmon. 1992. A rating system for potential exotic vertebrate pests.
Biological Conservation 62:149-159.
Smallwood, K. S. 1990. Turbulence and the ecology of invading species. Ph.D. Thesis, University of California, Davis.
Smallwood CV
12 Peer-reviewed Reports
Smallwood, K. S., and L. Neher. 2017. Comparing bird and bat use data for siting new wind power generation. Report CEC-500-2017-019, California Energy Commission Public Interest Energy Research program, Sacramento, California. http://www.energy.ca.gov/2017publications/CEC- 500-2017-019/CEC-500-2017-019.pdf and http://www.energy.ca.gov/2017publications/CEC- 500-2017-019/CEC-500-2017-019-APA-F.pdf
Smallwood, K. S. 2016. Bird and bat impacts and behaviors at old wind turbines at Forebay, Altamont Pass Wind Resource Area. Report CEC-500-2016-066, California Energy Commission Public Interest Energy Research program, Sacramento, California. http://www.energy.ca.gov/publications/displayOneReport.php? pubNum=CEC-500- 2016-066
Sinclair, K. and E. DeGeorge. 2016. Framework for Testing the Effectiveness of Bat and Eagle Impact-Reduction Strategies at Wind Energy Projects. S. Smallwood, M. Schirmacher, and M.
Morrison, eds., Technical Report NREL/TP-5000-65624, National Renewable Energy Laboratory, Golden, Colorado.
Brown, K., K. S. Smallwood, J. Szewczak, and B. Karas. 2016. Final 2012-2015 Report Avian and Bat Monitoring Project Vasco Winds, LLC. Prepared for NextEra Energy Resources, Livermore, California.
Brown, K., K. S. Smallwood, J. Szewczak, and B. Karas. 2014. Final 2013-2014 Annual Report Avian and Bat Monitoring Project Vasco Winds, LLC. Prepared for NextEra Energy Resources, Livermore, California.
Brown, K., K. S. Smallwood, and B. Karas. 2013. Final 2012-2013 Annual Report Avian and Bat Monitoring Project Vasco Winds, LLC. Prepared for NextEra Energy Resources, Livermore, California. http://www.altamontsrc.org/alt_doc/p274_ventus_vasco_winds_2012_13_avian_ bat_monitoring_report_year_1.pdf
Smallwood, K. S., L. Neher, D. Bell, J. DiDonato, B. Karas, S. Snyder, and S. Lopez. 2009. Range Management Practices to Reduce Wind Turbine Impacts on Burrowing Owls and Other Raptors in the Altamont Pass Wind Resource Area, California. Final Report to the California Energy Commission, Public Interest Energy Research – Environmental Area, Contract No.
CEC-500-2008-080. Sacramento, California. 183 pp. http://www.energy.ca.gov/ 2008publications/CEC-500-2008-080/CEC-500-2008-080.PDF
Smallwood, K. S., and L. Neher. 2009. Map-Based Repowering of the Altamont Pass Wind Resource Area Based on Burrowing Owl Burrows, Raptor Flights, and Collisions with Wind Turbines. Final Report to the California Energy Commission, Public Interest Energy Research – Environmental Area, Contract No. CEC-500-2009-065. Sacramento, California. http:// www.energy.ca.gov/publications/displayOneReport.php?pubNum=CEC-500-2009-065
Smallwood, K. S., K. Hunting, L. Neher, L. Spiegel and M. Yee. 2007. Indicating Threats to Birds Posed by New Wind Power Projects in California. Final Report to the California Energy Smallwood CV
13 Commission, Public Interest Energy Research – Environmental Area, Contract No. Pending.
Sacramento, California.
Smallwood, K. S. and C. Thelander. 2005. Bird mortality in the Altamont Pass Wind Resource Area, March 1998 – September 2001 Final Report. National Renewable Energy Laboratory, NREL/SR-500-36973. Golden, Colorado. 410 pp.
Smallwood, K. S. and C. Thelander. 2004. Developing methods to reduce bird mortality in the Altamont Pass Wind Resource Area. Final Report to the California Energy Commission, Public Interest Energy Research – Environmental Area, Contract No. 500-01-019. Sacramento, California. 531 pp. http://www.energy.ca.gov/reports/500-04-052/2004-08-09_500-04-052.PDF
Thelander, C.G. S. Smallwood, and L. Rugge. 2003. Bird risk behaviors and fatalities at the Altamont Pass Wind Resource Area. Period of Performance: March 1998—December 2000.
National Renewable Energy Laboratory, NREL/SR-500-33829. U.S. Department of Commerce, National Technical Information Service, Springfield, Virginia. 86 pp.
Thelander, C.G., S. Smallwood, and L. Rugge. 2001. Bird risk behaviors and fatalities at the Altamont Wind Resource Area – a progress report. Proceedings of the American Wind Energy Association, Washington D.C. 16 pp.
Non-Peer Reviewed Publications
Smallwood, K. S., D. Bell, and S. Standish. 2018. Skilled dog detections of bat and small bird carcasses in wind turbine fatality monitoring. Report to East Bay Regional Park District, Oakland, California.
Smallwood, K. S. 2009. Methods manual for assessing wind farm impacts to birds. Bird Conservation Series 26, Wild Bird Society of Japan, Tokyo. T. Ura, ed., in English with Japanese translation by T. Kurosawa. 90 pp.
Smallwood, K. S. 2009. Mitigation in U.S. Wind Farms. Pages 68-76 in H. Hötker (Ed.), Birds of Prey and Wind Farms: Analysis of problems and possible solutions. Documentation of an International Workshop in Berlin, 21st and 22nd October 2008. Michael-Otto-Instiut im NABU, Goosstroot 1, 24861 Bergenhusen, Germany. http://bergenhusen.nabu.de/forschung/greifvoegel/
Smallwood, K. S. 2007. Notes and recommendations on wildlife impacts caused by Japan’s wind power development. Pages 242-245 in Yukihiro Kominami, Tatsuya Ura, Koshitawa, and Tsuchiya, Editors, Wildlife and Wind Turbine Report 5. Wild Bird Society of Japan, Tokyo.
Thelander, C.G. and S. Smallwood. 2007. The Altamont Pass Wind Resource Area's Effects on Birds: A Case History. Pages 25-46 in Manuela de Lucas, Guyonne F.E. Janss, Miguel Ferrer Editors, Birds and Wind Farms: risk assessment and mitigation. Madrid: Quercus.
Neher, L. and S. Smallwood. 2005. Forecasting and minimizing avian mortality in siting wind turbines. Energy Currents. Fall Issue. ESRI, Inc., Redlands, California.
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14 Jennifer Davidson and Shawn Smallwood. 2004. Laying plans for a hydrogen highway.
Comstock’s Business, August 2004:18-20, 22, 24-26.
Jennifer Davidson and Shawn Smallwood. 2004. Refined conundrum: California consumers demand more oil while opposing refinery development. Comstock’s Business, November 2004:26-27, 29-30.
Smallwood, K.S. 2002. Review of “The Atlas of Endangered Species.” By Richard Mackay.
Environmental Conservation 30:210-211.
Smallwood, K.S. 2002. Review of “The Endangered Species Act. History, Conservation, and Public Policy.” By Brian Czech and Paul B. Krausman. Environmental Conservation 29: 269- 270.
Smallwood, K.S. 1997. Spatial scaling of pocket gopher (Geomyidae) burrow volume. Abstract in Proceedings of 44th Annual Meeting, Southwestern Association of Naturalists. Department of Biological Sciences, University of Arkansas, Fayetteville.
Smallwood, K.S. 1997. Estimating prairie dog and pocket gopher burrow volume. Abstract in Proceedings of 44th Annual Meeting, Southwestern Association of Naturalists. Department of Biological Sciences, University of Arkansas, Fayetteville.
Smallwood, K.S. 1997. Animal burrowing parameters influencing toxic waste management.
Abstract in Proceedings of Meeting, Western Section of the Wildlife Society.
Smallwood, K.S, and Bruce Wilcox. 1996. Study and interpretive design effects on mountain lion density estimates. Abstract, page 93 in D.W. Padley, ed., Proceedings 5th Mountain Lion Workshop, Southern California Chapter, The Wildlife Society. 135 pp.
Smallwood, K.S, and Bruce Wilcox. 1996. Ten years of mountain lion track survey. Page 94 in D.W. Padley, ed. Abstract, page 94 in D.W. Padley, ed., Proceedings 5th Mountain Lion Workshop, Southern California Chapter, The Wildlife Society. 135 pp.
Smallwood, K.S, and M. Grigione. 1997. Photographic recording of mountain lion tracks. Pages 75-75 in D.W. Padley, ed., Proceedings 5th Mountain Lion Workshop, Southern California Chapter, The Wildlife Society. 135 pp.
Smallwood, K.S., B. Wilcox, and J. Karr. 1995. An approach to scaling fragmentation effects.
Brief 8, Ecosystem Indicators Working Group, 17 March, 1995. Institute for Sustainable Development, Thoreau Center for Sustainability – The Presidio, PO Box 29075, San Francisco, CA 94129-0075.
Wilcox, B., and K.S. Smallwood. 1995. Ecosystem indicators model overview. Brief 2, Ecosystem Indicators Working Group, 17 March, 1995. Institute for Sustainable Development, Thoreau Center for Sustainability – The Presidio, PO Box 29075, San Francisco, CA 94129- 0075.
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15 EIP Associates. 1996. Yolo County Habitat Conservation Plan. Yolo County Planning and Development Department, Woodland, California.
Geng, S., K.S. Smallwood, and M. Zhang. 1995. Sustainable agriculture and agricultural sustainability. Proc. 7th International Congress SABRAO, 2nd Industrial Symp. WSAA.
Taipei, Taiwan.
Smallwood, K.S. and S. Geng. 1994. Landscape strategies for biological control and IPM. Pages 454-464 in W. Dehai, ed., Proc. International Conference on Integrated Resource Management for Sustainable Agriculture. Beijing Agricultural University, Beijing, China.
Smallwood, K.S. and S. Geng. 1993. Alfalfa as wildlife habitat. California Alfalfa Symposium 23:105-8.
Smallwood, K.S. and S. Geng. 1993. Management of pocket gophers in Sacramento Valley alfalfa.
California Alfalfa Symposium 23:86-89.
Smallwood, K.S. and E.L. Fitzhugh. 1992. The use of track counts for mountain lion population census. Pages 59-67 in C. Braun, ed. Mountain lion-Human Interaction Symposium and Workshop. Colorado Division of Wildlife, Fort Collins.
Smallwood, K.S. and E.L. Fitzhugh. 1989. Differentiating mountain lion and dog tracks. Pages 58-63 in Smith, R.H., ed. Proc. Third Mountain Lion Workshop. Arizona Game and Fish Department, Phoenix.
Fitzhugh, E.L. and K.S. Smallwood. 1989. Techniques for monitoring mountain lion population levels. Pages 69-71 in Smith, R.H., ed. Proc. Third Mountain Lion Workshop. Arizona Game and Fish Department, Phoenix.
Reports to or by Alameda County Scientific Review Committee (Note: all documents linked to SRC website have since been removed by Alameda County)
Smallwood, K. S. 2014. Data Needed in Support of Repowering in the Altamont Pass WRA. http://www.altamontsrc.org/alt_doc/p284_smallwood_data_needed_in_support_of_repowering_ in_the_altamont_pass_wra.pdf
Smallwood, K. S. 2013. Long-Term Trends in Fatality Rates of Birds and Bats in the Altamont Pass Wind Resource Area, California. http://www.altamontsrc.org/alt_doc/r68_smallwood _altamont_fatality_rates_longterm.pdf
Smallwood, K. S. 2013. Inter-annual Fatality rates of Target Raptor Species from 1999 through 2012 in the Altamont Pass Wind Resources Area. http://www.altamontsrc.org/alt_doc/p268_ smallwood_inter_annual_comparison_of_fatality_rates_1999_2012.pdf
Smallwood, K. S. 2012. General Protocol for Performing Detection Trials in the FloDesign Study of the Safety of a Closed-bladed Wind Turbine. http://www.altamontsrc.org/alt_doc/p246_ smallwood_flodesign_detection_trial_protocol.pdf
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16 Smallwood, K. S., l. Neher, and J. Mount. 2012. Burrowing owl distribution and abundance study through two breeding seasons and intervening non-breeding period in the Altamont Pass Wind Resource Area, California. http://www.altamontsrc.org/alt_doc/p245_smallwood_et_al_ burrowing_owl density_2012.pdf
Smallwood, K. S 2012. Draft study design for testing collision risk of Flodesign wind turbine in former AES Seawest wind projects in the Altamont Pass Wind Resource Area (APWRA). http://www.altamontsrc.org/alt_doc/p238_smallwood_floeesign_draft_study_design_april_2012 .pdf
Smallwood, L. Neher, and J. Mount. 2012. Winter 2012 update on burrowing owl distribution and abundance study in the Altamont Pass Wind Resource Area, California. http://www. altamontsrc.org/alt_doc/p232_smallwood_et_al_winter_owl_survey_update.pdf
Smallwood, S. 2012. Status of avian utilization data collected in the Altamont Pass Wind Resource Area, 2005-2011. http://www.altamontsrc.org/alt_doc/p231_smallwood_apwra _use_data_2005_2011.pdf
Smallwood, K. S., L. Neher, and J. Mount. 2011. Monitoring Burrow Use of Wintering Burrowing Owls. http://www.altamontsrc.org/alt_doc/p229_smallwood_et_al_progress_monitoring_ burrowing_owl_burrow_use.pdf
Smallwood, K. S., L. Neher, and J. Mount. 2011. Nesting Burrowing Owl Distribution and Abundance in the Altamont Pass Wind Resource Area, California. http://www.altamontsrc.org/alt_doc/p228_smallwood_et_al_for_nextera_burrowing_owl_distrib ution_and_abundance_study.pdf
Smallwood, K. S. 2011. Draft Study Design for Testing Collision Risk of Flodesign Wind Turbine in Patterson Pass Wind Farm in the Altamont Pass Wind Resource Area (APWRA). http://www.altamontsrc.org/alt_doc/p100_src_document_list_with_reference_numbers.pdf
Smallwood, K. S. 2011. Sampling Burrowing Owls Across the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_doc/p205_smallwood_neher_progress_on_sampling _burrowing_owls_across_apwra.pdf
Smallwood, K. S. 2011. Proposal to Sample Burrowing Owls Across the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_doc/p198_smallwood_proposal_to_sample_ burrowing_owls_across_apwra.pdf
Smallwood, K. S. 2010. Comments on APWRA Monitoring Program Update. http://www.altamontsrc.org/alt_doc/p191_smallwood_comments_on_apwra_monitoring_progra m_update.pdf
Smallwood, K. S. 2010. Inter-turbine Comparisons of Fatality Rates in the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_doc/p189_smallwood_report_of_ apwra_fatality_rate_patterns.pdf
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17 Smallwood, K. S. 2010. Review of the December 2010 Draft of M-21: Altamont Pass Wind Resource Area Bird Collision Study. http://www.altamontsrc.org/alt_doc/p190_smallwood _review_of_december_2010_monitoring_report.pdf
Alameda County SRC (Shawn Smallwood, Jim Estep, Sue Orloff, Joanna Burger, and Julie Yee).
Comments on the Notice of Preparation for a Programmatic Environmental Impact Report on Revised CUPs for Wind Turbines in the Alameda County portion of the Altamont Pass. http://www.altamontsrc.org/alt_doc/p183_src_integrated_comments_on_nop.pdf
Smallwood, K. S. 2010. Review of Monitoring Implementation Plan. http://www.altamontsrc.org/alt_doc/p180_src_comments_on_dip.pdf
Burger, J., J. Estep, S. Orloff, S. Smallwood, and J. Yee. 2010. SRC Comments on CalWEA Research Plan. http://www.altamontsrc.org/alt_doc/p174_smallwood_review_of_calwea_ removal_study_plan.pdf
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). SRC Comments on Monitoring Team’s Draft Study Plan for Future Monitoring. http://www.altamontsrc.org/alt_doc/p168_src_comments_on_m53_mt_draft_study_plan_for_fut ure_monitoring.pdf
Smallwood, K. S. 2010. Second Review of American Kestrel-Burrowing owl (KB) Scavenger Removal Adjustments Reported in Alameda County Avian Monitoring Team’s M21 for the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_doc/p171_smallwood _kb_removal_rates_follow_up.pdf
Smallwood, K. S. 2010. Assessment of Three Proposed Adaptive Management Plans for Reducing Raptor Fatalities in the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_ doc/p161_smallwood_assessment_of_amps.pdf
Smallwood, K. S. and J. Estep. 2010. Report of additional wind turbine hazard ratings in the Altamont Pass Wind Resource Area by Two Members of the Alameda County Scientific Review Committee. http://www.altamontsrc.org/alt_doc/p153_smallwood_estep_additional_ hazard_ratings.pdf
Smallwood, K. S. 2010. Alternatives to Improve the Efficiency of the Monitoring Program. http://www.altamontsrc.org/alt_doc/p158_smallwood_response_to_memo_on_monitoring_costs .pdf
Smallwood, S. 2010. Summary of Alameda County SRC Recommendations and Concerns and Subsequent Actions. http://www.altamontsrc.org/alt_doc/p147_smallwood_summary_of_src_ recommendations_and_concerns_1_11_10.pdf
Smallwood, S. 2010. Progress of Avian Wildlife Protection Program & Schedule. http://www.altamontsrc.org/alt_doc/p148_smallwood_progress_of_avian_wildlife_protection_p rogram_1_11_10.pdf
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18 Smallwood, S. 2010. Old-generation wind turbines rated for raptor collision hazard by Alameda County Scientific Review Committee in 2010, an Update on those Rated in 2007, and an Update on Tier Rankings. http://www.altamontsrc.org/alt_doc/p155_smallwood_src_ turbine_ratings_and_status.pdf
Smallwood, K. S. 2010. Review of American Kestrel-Burrowing owl (KB) Scavenger Removal Adjustments Reported in Alameda County Avian Monitoring Team’s M21 for the Altamont Pass Wind Resource Area. http://www.altamontsrc.org/alt_doc/p154_smallwood_kb_removal_ rates_041610.pdf
Smallwood, K. S. 2010. Fatality Rates in the Altamont Pass Wind Resource Area 1998-2009.
Alameda County SRC document P-145.
Smallwood, K. S. 2010. Comments on Revised M-21: Report on Fatality Monitoring in the Altamont Pass Wind Resource Area. P144 SRC Comments on 2009 Draft Monitoring Report M21.
Smallwood, K. S. 2009. http://www.altamontsrc.org/alt_doc/p129_smallwood_search_ interval_summaries_supplemental_to_m39.pdf
Smallwood, K. S. 2009. Smallwood’s review of M32. Alameda County SRC document P-111. 6 pp. http://www.altamontsrc.org/alt_doc/p111_smallwoods_review_of_m32.pdf
Smallwood, K. S. 2009. 3rd Year Review of 16 Conditional Use Permits for Windworks, Inc. and Altamont Infrastructure Company, LLC. Comment letter to East County Board of Zoning Adjustments. 10 pp + 2 attachments.
Smallwood, K. S. 2008. Weighing Remaining Workload of Alameda County SRC against Proposed Budget Cap. Alameda County SRC document not assigned. 3 pp.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). 2008. SRC comments on August 2008 Fatality Monitoring Report, M21. Alameda County SRC document P-107. 21 pp. http://www.altamontsrc.org/alt_doc/p107_smallwood_review_of_july_2008_ monitoring_report_m21.pdf
Smallwood, K. S. 2008. Burrowing owl carcass distribution around wind turbines. Alameda County SRC document 106. 8 pp. http://www.altamontsrc.org/alt_doc/p106_smallwood_ burrowing_owl_carcass_distribution_around_wind_turbines.pdf
Smallwood, K. S. 2008. Assessment of relocation/removal of Altamont Pass wind turbines rated as hazardous by the Alameda County SRC. Alameda County SRC document P-103. 10 pp. http://www.altamontsrc.org/alt_doc/p103_assessment_of_src_recommendations_to_ relocate_rated_turbines.pdf
Smallwood, K. S. and L. Neher. 2008. Summary of wind turbine-free ridgelines within and around the APWRA. Alameda County SRC document P-102. 4 pp.
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19 Smallwood, K. S. and B. Karas. 2008. Comparison of mortality estimates in the Altamont Pass Wind Resource Area when restricted to recent fatalities. Alameda County SRC document P- 101.
Smallwood, K. S. 2008. On the misapplication of mortality adjustment terms to fatalities missed during one search and found later. Alameda County SRC document P-97. 3 pp.
Smallwood, K. S. 2008. Relative abundance of raptors outside the APWRA. Alameda County SRC document P-88. 6 pp.
Smallwood, K. S. 2008. Comparison of mortality estimates in the Altamont Pass Wind Resource Area. Alameda County SRC document P-76. 19 pp
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). 2010.
Guidelines for siting wind turbines recommended for relocation to minimize potential collision- related mortality of four focal raptor species in the Altamont Pass Wind Resource Area.
Alameda County SRC document P-70.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). December 11, 2007. SRC selection of dangerous wind turbines. Alameda County SRC document P-67. 8 pp.
Smallwood, S. October 6, 2007. Smallwood’s answers to Audubon’s queries about the SRC’s recommended four month winter shutdown of wind turbines in the Altamont Pass. Alameda County SRC document P-23.
Smallwood, K. S. October 1, 2007. Dissenting opinion on recommendation to approve of the AWI Blade Painting Study. Alameda County SRC document P-60.
Smallwood, K. S. July 26, 2007. Effects of monitoring duration and inter-annual variability on precision of wind-turbine caused mortality estimates in the Altamont Pass Wind Resource Area, California. SRC Document P44.
Smallwood, K. S. July 26, 2007. Memo: Opinion of some SRC members that the period over which post-management mortality will be estimated remains undefined. SRC Document P43.
Smallwood, K. S. July 19, 2007. Smallwood’s response to P24G. SRC Document P41, 4 pp.
Smallwood, K. S. April 23, 2007. New Information Regarding Alameda County SRC Decision of 11 April 2007 to Grant FPLE Credits for Removing and Relocating Wind Turbines in 2004.
SRC Document P26.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, and J. Burger [J. Yee abstained]).
April 17, 2007. SRC Statement in Support of the Monitoring Program Scope and Budget.
Smallwood, K. S. April 15, 2007. Verification of Tier 1 & 2 Wind Turbine Shutdowns and Relocations. SRC Document P22.
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20 Smallwood, S. April 15, 2007. Progress of Avian Wildlife Protection Program & Schedule.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). April 3, 2007.
Alameda County Scientific Review Committee replies to the parties’ responses to its queries and to comments from the California Office of the Attorney General. SRC Document S20.
Smallwood, S. March 19, 2007. Estimated Effects of Full Winter Shutdown and Removal of Tier I & II Turbines. SRC Document S19.
Smallwood, S. March 8, 2007. Smallwood’s Replies to the Parties’ Responses to Queries from the SRC and Comments from the California Office of the Attorney General. SRC Document S16.
Smallwood, S. March 8, 2007. Estimated Effects of Proposed Measures to be Applied to 2,500 Wind Turbines in the APWRA Fatality Monitoring Plan. SRC Document S15.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). February 7, 2007. Analysis of Monitoring Program in Context of 1/1//2007 Settlement Agreement.
Smallwood, S. January 8, 2007. Smallwood’s Concerns over the Agreement to Settle the CEQA Challenges. SRC Document S5.
Alameda County SRC (Smallwood, K. S., S. Orloff, J. Estep, J. Burger, and J. Yee). December 19, 2006. Altamont Scientific Review Committee (SRC) Recommendations to the County on the Avian Monitoring Team Consultants’ Budget and Organization.
Reports to Clients
Smallwood, K. S. 2018. Addendum to Comparison of Wind Turbine Collision Hazard Model Performance: One -year Post -construction Assessment of Golden Eagle Fatalities at Golden Hills. Report to Audubon Society, NextEra Energy, and the California Attorney General.
Smallwood, K. S., and L. Neher. 2018 . Siting wind turbines to minimize raptor collisions at Rooney Ranch and Sand Hill Repowering Project, Altamont Pass Wind Resourc e Area. Report to S-Power, Salt Lake City, Utah.
Smallwood, K. S. 2017. Summary of a burrowing owl conservation workshop . Report to Santa Clara Valley Habitat Agency, Morgan Hill, California.
Smallwood, K. S., and L. Neher. 2017. Comparison of wind turbine collision hazard model performance prepared for repowering projects in the Altamont Pass Wind Resources Area.
Report to NextEra Energy Resources, Inc., Office of the California Attorney General, Audubon Society, East Bay Regional Park District.
Smallwood, K. S., and L. Neher. 2016. Siting wind turbines to minimize raptor collisions at Summit Winds Repowering Project, Altamont Pass Wind Resource Area. Report to Salka, Inc., Washington, D.C.
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21 Smallwood, K. S., L. Neher, and D. A. Bell. 2017. Mitigating golden eagle impacts from repowering Altamont Pass Wind Resource Area and expanding Los Vaqueros Reservoir.
Report to East Contra Costa County Habitat Conservation Plan Conservancy and Contra Costa Water District.
Smallwood, K. S. 2016. Report of Altamont Pass research as Vasco Winds mitigation. Report to NextEra Energy Resources, Inc., Office of the California Attorney General, Audubon Society, East Bay Regional Park District.
Smallwood, K. S., and L. Neher. 2016. Siting Wind Turbines to Minimize Raptor collisions at Sand Hill Repowering Project, Altamont Pass Wind Resource Area. Report to Ogin, Inc., Waltham, Massachusetts.
Smallwood, K. S., and L. Neher. 2015a. Siting wind turbines to minimize raptor collisions at Golden Hills Repowering Project, Altamont Pass Wind Resource Area. Report to NextEra Energy Resources, Livermore, California.
Smallwood, K. S., and L. Neher. 2015b. Siting wind turbines to minimize raptor collisions at Golden Hills North Repowering Project, Altamont Pass Wind Resource Area. Report to NextEra Energy Resources, Livermore, California.
Smallwood, K. S., and L. Neher. 2015c. Siting wind turbines to minimize raptor collisions at the Patterson Pass Repowering Project, Altamont Pass Wind Resource Area. Report to EDF Renewable Energy, Oakland, California.
Smallwood, K. S., and L. Neher. 2014. Early assessment of wind turbine layout in Summit Wind Project. Report to Altamont Winds LLC, Tracy, California.
Smallwood, K. S. 2015. Review of avian use survey report for the Longboat Solar Project. Report to EDF Renewable Energy, Oakland, California.
Smallwood, K. S. 2014. Information needed for solar project impacts assessment and mitigation planning. Report to Panorama Environmental, Inc., San Francisco, California.
Smallwood, K. S. 2014. Monitoring fossorial mammals in Vasco Caves Regional Preserve, California: Report of Progress for the period 2006-2014. Report to East Bay Regional Park District, Oakland, California.
Smallwood, K. S. 2013. First-year estimates of bird and bat fatality rates at old wind turbines, Forebay areas of Altamont Pass Wind Resource Area. Report to FloDesign in support of EIR.
Smallwood, K. S. and W. Pearson. 2013. Neotropical bird monitoring of burrowing owls (Athene cunicularia), Naval Air Station Lemoore, California. Tierra Data, Inc. report to Naval Air Station Lemoore.
Smallwood, K. S. 2013. Winter surveys for San Joaquin kangaroo rat (Dipodomys nitratoides) and Smallwood CV
22 burrowing owls (Athene cunicularia) within Air Operations at Naval Air Station, Lemoore.
Report to Tierra Data, Inc. and Naval Air Station Lemoore.
Smallwood, K. S. and M. L. Morrison. 2013. San Joaquin kangaroo rat (Dipodomys n. nitratoides) conservation research in Resource Management Area 5, Lemoore Naval Air Station: 2012 Progress Report (Inclusive of work during 2000-2012). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California.
Smallwood, K. S. 2012. Fatality rate estimates at the Vantage Wind Energy Project, year one.
Report to Ventus Environmental, Portland, Oregon.
Smallwood, K. S. and L. Neher. 2012. Siting wind turbines to minimize raptor collisions at North Sky River. Report to NextEra Energy Resources, LLC.
Smallwood, K. S. 2011. Monitoring Fossorial Mammals in Vasco Caves Regional Preserve, California: Report of Progress for the Period 2006-2011. Report to East Bay Regional Park District.
Smallwood, K. S. and M. L. Morrison. 2011. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2011 Progress Report (Inclusive of work during 2000-2011). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California.
Smallwood, K. S. 2011. Draft study design for testing collision risk of FloDesign Wind Turbine in Patterson Pass, Santa Clara, and Former AES Seawest Wind Projects in the Altamont Pass Wind Resource Area (APWRA). Report to FloDesign, Inc.
Smallwood, K. S. 2011. Comments on Marbled Murrelet collision model for the Radar Ridge Wind Resource Area. Report to EcoStat, Inc., and ultimately to US Fish and Wildlife Service.
Smallwood, K. S. 2011. Avian fatality rates at Buena Vista Wind Energy Project, 2008-2011.
Report to Pattern Energy.
Smallwood, K. S. and L. Neher. 2011. Siting repowered wind turbines to minimize raptor collisions at Tres Vaqueros, Contra Costa County, California. Report to Pattern Energy.
Smallwood, K. S. and M. L. Morrison. 2011. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2010 Progress Report (Inclusive of work during 2000-2010). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California.
Smallwood, K. S. 2010. Wind Energy Development and avian issues in the Altamont Pass, California. Report to Black & Veatch.
Smallwood, K. S. and L. Neher. 2010. Siting repowered wind turbines to minimize raptor collisions at the Tres Vaqueros Wind Project, Contra Costa County, California. Report to the East Bay Regional Park District, Oakland, California.
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23 Smallwood, K. S. and L. Neher. 2010. Siting repowered wind turbines to minimize raptor collisions at Vasco Winds. Report to NextEra Energy Resources, LLC, Livermore, California.
Smallwood, K. S. 2010. Baseline avian and bat fatality rates at the Tres Vaqueros Wind Project, Contra Costa County, California. Report to the East Bay Regional Park District, Oakland, California.
Smallwood, K. S. and M. L. Morrison. 2010. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2009 Progress Report (Inclusive of work during 2000-2009). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 86 pp.
Smallwood, K. S. 2009. Mammal surveys at naval outlying landing field Imperial Beach, California, August 2009. Report to Tierra Data, Inc. 5 pp
Smallwood, K. S. 2009. Mammals and other Wildlife Observed at Proposed Site of Amargosa Solar Power Project, Spring 2009. Report to Tierra Data, Inc. 13 pp
Smallwood, K. S. 2009. Avian Fatality Rates at Buena Vista Wind Energy Project, 2008-2009.
Report to members of the Contra Costa County Technical Advisory Committee on the Buena Vista Wind Energy Project. 8 pp.
Smallwood, K. S. 2009. Repowering the Altamont Pass Wind Resource Area more than Doubles Energy Generation While Substantially Reducing Bird Fatalities. Report prepared on behalf of Californians for Renewable Energy. 2 pp.
Smallwood, K. S. and M. L. Morrison. 2009. Surveys to Detect Salt Marsh Harvest Mouse and California Black Rail at Installation Restoration Site 30, Military Ocean Terminal Concord, California: March-April 2009. Report to Insight Environmental, Engineering, and Construction, Inc., Sacramento, California. 6 pp.
Smallwood, K. S. 2008. Avian and Bat Mortality at the Big Horn Wind Energy Project, Klickitat County, Washington. Unpublished report to Friends of Skamania County. 7 pp.
Smallwood, K. S. 2009. Monitoring Fossorial Mammals in Vasco Caves Regional Preserve, California: report of progress for the period 2006-2008. Unpublished report to East Bay Regional Park District. 5 pp.
Smallwood, K. S. and M. L. Morrison. 2008. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2008 Progress Report (Inclusive of work during 2000-2008). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 84 pp.
Smallwood, K. S. and M. L. Morrison. 2008. Habitat Assessment for California Red-Legged Frog at Naval Weapons Station, Seal Beach, Detachment Concord, California. Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 48 Smallwood CV
24 pp.
Smallwood, K. S. and B. Nakamoto 2008. Impact of 2005 and 2006 West Nile Virus on Yellow- billed Magpie and American Crow in the Sacramento Valley, California. 22 pp.
Smallwood, K. S. and M. L. Morrison. 2008. Former Naval Security Group Activity (NSGA), Skaggs Island, Waste and Contaminated Soil Removal Project (IR Site #2), San Pablo Bay, Sonoma County, California: Re-Vegetation Monitoring. Report to U.S. Navy, Letter Agreement – N68711-04LT-A0045. Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 10 pp.
Smallwood, K. S. and M. L. Morrison. 2008. Burrowing owls at Dixon Naval Radio Transmitter Facility. Report to U.S. Navy. Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 28 pp.
Smallwood, K. S. and M. L. Morrison. 2008. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2007 Progress Report (Inclusive of work during 2001-2007). Naval Facilities Engineering Command, Southwest, Desert Integrated Products Team, San Diego, California. 69 pp.
Smallwood, K. S. and M. L. Morrison. 2007. A Monitoring Effort to Detect the Presence of the Federally Listed Species California Clapper Rail and Salt Marsh Harvest Mouse, and Wetland Habitat Assessment at the Naval Weapons Station, Seal Beach, Detachment Concord, California. Installation Restoration (IR) Site 30, Final Report to U.S. Navy, Letter Agreement – N68711-05LT-A0001. U.S. Navy Integrated Product Team (IPT), West, Naval Facilities Engineering Command, San Diego, California. 8 pp.
Smallwood, K. S. and M. L. Morrison. 2007. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2006 Progress Report (Inclusive of work during 2001-2006). U.S. Navy Integrated Product Team (IPT), West, Naval Facilities Engineering Command, Southwest, Daly City, California. 165 pp.
Smallwood, K. S. and C. Thelander. 2006. Response to third review of Smallwood and Thelander (2004). Report to California Institute for Energy and Environment, University of California, Oakland, CA. 139 pp.
Smallwood, K. S. 2006. Biological effects of repowering a portion of the Altamont Pass Wind Resource Area, California: The Diablo Winds Energy Project. Report to Altamont Working Group. Available from Shawn Smallwood, [email protected] . 34 pp.
Smallwood, K. S. 2006. Impact of 2005 West Nile Virus on Yellow-billed Magpie and American Crow in the Sacramento Valley, California. Report to Sacramento-Yolo Mosquito and Vector Control District, Elk Grove, CA. 38 pp.
Smallwood, K. S. and M. L. Morrison. 2006. San Joaquin kangaroo rat (Dipodomys n. nitratoides) Conservation Research in Resource Management Area 5, Lemoore Naval Air Station: 2005 Progress Report (Inclusive of work during 2001-2005). U.S. Navy Integrated Product Team Smallwood CV
25 (IPT), West, Naval Facilities Engineering Command, South West, Daly City, California. 160 pp.
Smallwood, K. S. and M. L. Morrison. 2006. A monitoring effort to detect the presence of the federally listed species California tiger salamander and California red-legged frog at the Naval Weapons Station, Seal Beach, Detachment Concord, California. Letter agreements N68711- 04LT-A0042 and N68711-04LT-A0044, U.S. Navy Integrated Product Team (IPT), West, Naval Facilities Engineering Command, South West, Daly City, California. 60 pp.
Smallwood, K. S. and M. L. Morrison. 2006. A monitoring effort to detect the presence of the federally listed species California Clapper Rail and Salt Marsh Harvest Mouse, and wetland habitat assessment at the Naval Weapons Station, Seal Beach, Detachment Concord, California.
Sampling for rails, Spring 2006, Installation Restoration (IR) Site 1. Letter Agreement – N68711-05lt-A0001, U.S. Navy Integrated Product Team (IPT), West, Naval Facilities Engineering Command, South West, Daly City, California. 9 pp.
Morrison, M. L. and K. S. Smallwood. 2006. Final Report: Station-wide Wildlife Survey, Naval Air Station, Lemoore. Department of the Navy Integrated Product Team (IPT) West, Naval Facilities Engineering Command Southwest, 2001 Junipero Serra Blvd., Suite 600, Daly City, CA 94014-1976. 20 pp.
Smallwood, K. S. and M. L. Morrison. 2006. Former Naval Security Group Activity (NSGA), Skaggs Island, Waste and Contaminated Soil Removal Project, San Pablo Bay, Sonoma County, California: Re-vegetation Monitoring. Department of the Navy Integrated Product Team (IPT) West, Naval Facilities Engineering Command Southwest, 2001 Junipero Serra Blvd., Suite 600, Daly City, CA 94014-1976. 8 pp.
Dorin, Melinda, Linda Spiegel and K. Shawn Smallwood. 2005. Response to public comments on the staff report entitled Assessment of Avian Mortality from Collisions and Electrocutions (CEC-700-2005-015) (Avian White Paper) written in support of the 2005 Environmental Performance Report and the 2005 Integrated Energy Policy Report. California Energy Commission, Sacramento. 205 pp.
Smallwood, K. S. 2005. Estimating combined effects of selective turbine removal and winter-time shutdown of half the wind turbines. Unpublished CEC staff report, June 23. 1 p.
Erickson, W. and S. Smallwood. 2005. Avian and Bat Monitoring Plan for the Buena Vista Wind Energy Project Contra Costa County, California. Unpubl. report to Contra Costa County, Antioch, California. 22 pp.
Lamphier-Gregory, West Inc., Shawn Smallwood, Jones & Stokes Associates, Illingworth & Rodkin Inc. and Environmental Vision. 2005. Environmental Impact Report for the Buena Vista Wind Energy Project, LP# 022005. County of Contra Costa Community Development Department, Martinez, California.
Morrison, M. L. and K. S. Smallwood. 2005. A monitoring effort to detect the presence of the federally listed species California clapper rail and salt marsh harvest mouse, and wetland habitat assessment at the Naval Weapons Station, Seal Beach, Detachment Concord, California.
Smallwood CV
26 Targeted Sampling for Salt Marsh Harvest Mouse, Fall 2005 Installation Restoration (IR) Site
30. Letter Agreement – N68711-05lt-A0001, U.S. Department of the Navy, Naval Facilities Engineering Command Southwest, Daly City, California. 6 pp.
Morrison, M. L. and K. S. Smallwood. 2005. A monitoring effort to detect the presence of the federally listed species California clapper rail and salt marsh harvest mouse, and wetland habitat assessment at the Naval Weapons Station, Seal Beach, Detachment Concord, California. Letter Agreement – N68711-05lt-A0001, U.S. Department of the Navy, Naval Facilities Engineering Command Southwest, Daly City, California. 5 pp.
Morrison, M. L. and K. S. Smallwood. 2005. Skaggs Island waste and contaminated soil removal projects, San Pablo Bay, Sonoma County, California. Report to the U.S. Department of the Navy, Naval Facilities Engineering Command Southwest, Daly City, California. 6 pp.
Smallwood, K. S. and M. L. Morrison. 2004. 2004 Progress Report: San Joaquin kangaroo rat (Dipodomys nitratoides) Conservation Research in Resources Management Area 5, Lemoore Naval Air Station. Progress report to U.S. Department of the Navy, Lemoore, California. 134 pp.
Smallwood, K. S. and L. Spiegel. 2005a. Assessment To Support An Adaptive Management Plan For The APWRA. Unpublished CEC staff report, January 19. 19 pp.
Smallwood, K. S. and L. Spiegel. 2005b. Partial Re-assessment of An Adaptive Management Plan For The APWRA. Unpublished CEC staff report, March 25. 48 pp.
Smallwood, K. S. and L. Spiegel. 2005c. Combining biology-based and policy-based tiers of priority for determining wind turbine relocation/shutdown to reduce bird fatalities in the APWRA. Unpublished CEC staff report, June 1. 9 pp.
Smallwood, K. S. 2004. Alternative plan to implement mitigation measures in APWRA.
Unpublished CEC staff report, January 19. 8 pp.
Smallwood, K. S., and L. Neher. 2005. Repowering the APWRA: Forecasting and minimizing avian mortality without significant loss of power generation. California Energy Commission, PIER Energy-Related Environmental Research. CEC-500-2005-005. 21 pp. [Reprinted (in Japanese) in Yukihiro Kominami, Tatsuya Ura, Koshitawa, and Tsuchiya, Editors, Wildlife and Wind Turbine Report 5. Wild Bird Society of Japan, Tokyo.]
Morrison, M. L., and K. S. Smallwood. 2004. Kangaroo rat survey at RMA4, NAS Lemoore.
Report to U.S. Navy. 4 pp.
Morrison, M. L., and K. S. Smallwood. 2004. A monitoring effort to detect the presence of the federally listed species California clapper rails and wetland habitat assessment at Pier 4 of the Naval Weapons Station, Seal Beach, Detachment Concord, California. Letter Agreement N68711-04LT-A0002. 8 pp. + 2 pp. of photo plates.
Smallwood, K. S. and M. L. Morrison. 2003. 2003 Progress Report: San Joaquin kangaroo rat Smallwood CV
27 (Dipodomys nitratoides) Conservation Research at Resources Management Area 5, Lemoore Naval Air Station. Progress report to U.S. Department of the Navy, Lemoore, California. 56 pp. + 58 figures.
Smallwood, K. S. 2003. Comparison of Biological Impacts of the No Project and Partial Underground Alternatives presented in the Final Environmental Impact Report for the Jefferson- Martin 230 kV Transmission Line. Report to California Public Utilities Commission. 20 pp.
Morrison, M. L., and K. S. Smallwood. 2003. Kangaroo rat survey at RMA4, NAS Lemoore.
Report to U.S. Navy. 6 pp. + 7 photos + 1 map.
Smallwood, K. S. 2003. Assessment of the Environmental Review Documents Prepared for the Tesla Power Project. Report to the California Energy Commission on behalf of Californians for Renewable Energy. 32 pp.
Smallwood, K. S., and M. L. Morrison. 2003. 2002 Progress Report: San Joaquin kangaroo rat (Dipodomys nitratoides) Conservation Research at Resources Management Area 5, Lemoore Naval Air Station. Progress report to U.S. Department of the Navy, Lemoore, California. 45 pp. + 36 figures.
Smallwood, K. S., Michael L. Morrison and Carl G. Thelander 2002. Study plan to test the effectiveness of aerial markers at reducing avian mortality due to collisions with transmission lines: A report to Pacific Gas & Electric Company. 10 pp.
Smallwood, K. S. 2002. Assessment of the Environmental Review Documents Prepared for the East Altamont Energy Center. Report to the California Energy Commission on behalf of Californians for Renewable Energy. 26 pp.
Thelander, Carl G., K. Shawn Smallwood, and Christopher Costello. 2002 Rating Distribution Poles for Threat of Raptor Electrocution and Priority Retrofit: Developing a Predictive Model.
Report to Southern California Edison Company. 30 pp.
Smallwood, K. S., M. Robison, and C. Thelander. 2002. Draft Natural Environment Study, Prunedale Highway 101 Project. California Department of Transportation, San Luis Obispo, California. 120 pp.
Smallwood, K.S. 2001. Assessment of ecological integrity and restoration potential of Beeman/Pelican Farm. Draft Report to Howard Beeman, Woodland, California. 14 pp.
Smallwood, K. S., and M. L. Morrison. 2002. Fresno kangaroo rat (Dipodomys nitratoides) Conservation Research at Resources Management Area 5, Lemoore Naval Air Station. Progress report to U.S. Department of the Navy, Lemoore, California. 29 pp. + 19 figures.
Smallwood, K.S. 2001. Rocky Flats visit, April 4th through 6th, 2001. Report to Berger & Montaque, P.C. 16 pp. with 61 color plates.
Smallwood, K.S. 2001. Affidavit of K. Shawn Smallwood, Ph.D. in the matter of the U.S. Fish and Smallwood CV
28 Wildlife Service’s rejection of Seatuck Environmental Association’s proposal to operate an education center on Seatuck National Wildlife Refuge. Submitted to Seatuck Environmental Association in two parts, totaling 7 pp.
Magney, D., and K.S. Smallwood. 2001. Maranatha High School CEQA critique. Comment letter submitted to Tamara & Efren Compeán, 16 pp.
Smallwood, K.S. 2001. Preliminary Comments on the Proposed Blythe Energy Project. Submitted to California Energy Commission on March 15 on behalf of Californians for Renewable Energy (CaRE). 14 pp.
Smallwood, K. S. and D. Mangey. 2001. Comments on the Newhall Ranch November 2000 Administrative Draft EIR. Prepared for Ventura County Counsel regarding the Newhall Ranch Specific Plan EIR. 68 pp.
Magney, D. and K. S. Smallwood. 2000. Newhall Ranch Notice of Preparation Submittal. Prepared for Ventura County Counsel regarding our recommended scope of work for the Newhall Ranch Specific Plan EIR. 17 pp.
Smallwood, K. S. 2000. Comments on the Preliminary Staff Assessment of the Contra Costa Power Plant Unit 8 Project. Submitted to California Energy Commission on November 30 on behalf of Californians for Renewable Energy (CaRE). 4 pp.
Smallwood, K. S. 2000. Comments on the California Energy Commission’s Final Staff Assessment of the MEC. Submitted to California Energy Commission on October 29 on behalf of Californians for Renewable Energy (CaRE). 8 pp.
Smallwood, K. S. 2000. Comments on the Biological Resources Mitigation Implementation and Monitoring Plan (BRMIMP). Submitted to California Energy Commission on October 29 on behalf of Californians for Renewable Energy (CaRE). 9 pp.
Smallwood, K. S. 2000. Comments on the Preliminary Staff Assessment of the Metcalf Energy Center. Submitted to California Energy Commission on behalf of Californians for Renewable Energy (CaRE). 11 pp.
Smallwood, K. S. 2000. Preliminary report of reconnaissance surveys near the TRW plant south of Phoenix, Arizona, March 27-29. Report prepared for Hagens, Berman & Mitchell, Attorneys at Law, Phoenix, AZ. 6 pp.
Morrison, M.L., K.S. .Smallwood, and M. Robison. 2001. Draft Natural Environment Study for Highway 46 compliance with CEQA/NEPA. Report to the California Department of Transportation. 75 pp.
Morrison, M.L., and K.S. Smallwood. 1999. NTI plan evaluation and comments. Exhibit C in W.D. Carrier, M.L. Morrison, K.S. Smallwood, and Vail Engineering. Recommendations for NBHCP land acquisition and enhancement strategies. Northern Territories, Inc., Sacramento.
Smallwood CV
29 Smallwood, K. S. 1999. Estimation of impacts due to dredging of a shipping channel through Humboldt Bay, California. Court Declaration prepared on behalf of EPIC.
Smallwood, K. S. 1998. 1998 California Mountain Lion Track Count. Report to the Defenders of Wildlife, Washington, D.C. 5 pages.
Smallwood, K.S. 1998. Draft report of a visit to a paint sludge dump site near Ridgewood, New Jersey, February 26th, 1998. Unpublished report to Consulting in the Public Interest.
Smallwood, K.S. 1997. Science missing in the “no surprises” policy. Commissioned by National Endangered Species Network and Spirit of the Sage Council, Pasadena, California.
Smallwood, K.S. and M.L. Morrison. 1997. Alternate mitigation strategy for incidental take of giant garter snake and Swainson’s hawk as part of the Natomas Basin Habitat Conservation Plan. Pages 6-9 and iii illustrations in W.D. Carrier, K.S. Smallwood and M.L. Morrison, Natomas Basin Habitat Conservation Plan: Narrow channel marsh alternative wetland mitigation. Northern Territories, Inc., Sacramento.
Smallwood, K.S. 1996. Assessment of the BIOPORT model's parameter values for pocket gopher burrowing characteristics. Report to Berger & Montague, P.C. and Roy S. Haber, P.C., Philadelphia. (peer reviewed).
Smallwood, K.S. 1997. Assessment of plutonium releases from Hanford buried waste sites. Report Number 9, Consulting in the Public Interest, 53 Clinton Street, Lambertville, New Jersey, 08530.
Smallwood, K.S. 1996. Soil Bioturbation and Wind Affect Fate of Hazardous Materials that were Released at the Rocky Flats Plant, Colorado. Report to Berger & Montague, P.C., Philadelphia.
Smallwood, K.S. 1996. Second assessment of the BIOPORT model's parameter values for pocket gopher burrowing characteristics and other relevant wildlife observations. Report to Berger & Montague, P.C. and Roy S. Haber, P.C., Philadelphia.
Smallwood, K.S., and R. Leidy. 1996. Wildlife and Their Management Under the Martell SYP.
Report to Georgia Pacific, Corporation, Martel, CA. 30 pp.
EIP Associates. 1995. Yolo County Habitat Conservation Plan Biological Resources Report. Yolo County Planning and Development Department, Woodland, California.
Smallwood, K.S. and S. Geng. 1995. Analysis of the 1987 California Farm Cost Survey and recommendations for future survey. Program on Workable Energy Regulation, University-wide Energy Research Group, University of California.
Smallwood, K.S., S. Geng, and W. Idzerda. 1992. Final report to PG&E: Analysis of the 1987 California Farm Cost Survey and recommendations for future survey. Pacific Gas & Electric Company, San Ramon, California. 24 pp.
Smallwood CV
30 Fitzhugh, E.L. and K.S. Smallwood. 1987. Methods Manual – A statewide mountain lion population index technique. California Department of Fish and Game, Sacramento.
Salmon, T.P. and K.S. Smallwood. 1989. Final Report – Evaluating exotic vertebrates as pests to California agriculture. California Department of Food and Agriculture, Sacramento.
Smallwood, K.S. and W. A. Erickson (written under supervision of W.E. Howard, R.E. Marsh, and R.J. Laacke). 1990. Environmental exposure and fate of multi-kill strychnine gopher baits. Final Report to USDA Forest Service –NAPIAP, Cooperative Agreement PSW-89-0010CA.
Fitzhugh, E.L., K.S. Smallwood, and R. Gross. 1985. Mountain lion track count, Marin County, 1985. Report on file at Wildlife Extension, University of California, Davis.
Comments on Environmental Documents
I was retained or commissioned to comment on environmental planning and review documents, including:
The Villages of Lakeview EIR (2017; 28 pp);
Notes on Proposed Study Options for Trail Impacts on Northern Spotted Owl (2017; 4 pp); San Gorgonio Crossings EIR (2017; 22 pp);
Replies to responses on Jupiter Project IS and MND (2017; 12 pp); MacArthur Transit Village Project Modified 2016 CEQA Analysis (2017; 12 pp); Central SoMa Plan DEIR (2017; 14 pp);
Colony Commerce Center Specific Plan DEIR (2016; 16 pp); Fairway Trails Improvements MND (2016; 13 pp);
Review of Avian-Solar Science Plan (2016; 28 pp);
Replies to responses on Initial Study for Pyramid Asphalt (2016; 5 pp); Initial Study for Pyramid Asphalt (2016; 4 pp);
Agua Mansa Distribution Warehouse Project Initial Study (2016; 14 pp); Santa Anita Warehouse IS and MND (2016; 12 pp);
CapRock Distribution Center III DEIR (2016: 12 pp);
Orange Show Logistics Center Initial Study and MND (2016; 9 pp); City of Palmdale Oasis Medical Village Project IS and MND (2016; 7 pp); Comments on proposed rule for incidental eagle take (2016, 49 pp); Grapevine Specific and Community Plan FEIR (2016; 25 pp); Grapevine Specific and Community Plan DEIR (2016; 15 pp); Clinton County Zoning Ordinance for Wind Turbine siting (2016); Hallmark at Shenandoah Warehouse Project Initial Study (2016; 6 pp); Tri-City Industrial Complex Initial Study (2016; 5 pp); Hidden Canyon Industrial Park Plot Plan 16-PP-02 (2016; 12 pp); Kimball Business Park DEIR (2016; 10 pp);
Jupiter Project IS and MND (2016; 9 pp);
Revised Draft Giant Garter Snake Recovery Plan of 2015 (2016, 18 pp); Palo Verde Mesa Solar Project Draft Environmental Impact Report (2016; 27 pp); Smallwood CV
31 Reply Witness Statement on Fairview Wind Project, Ontario, Canada (2016; 14 pp); Fairview Wind Project, Ontario, Canada (2016; 41 pp); Supplementary Reply Witness Statement Amherst Island Wind Farm, Ontario (2015, 38 pp); Witness Statement on Amherst Island Wind Farm, Ontario (2015, 31 pp); Second Reply Witness Statement on White Pines Wind Farm, Ontario (2015, 6 pp); Reply Witness Statement on White Pines Wind Farm, Ontario (2015, 10 pp); Witness Statement on White Pines Wind Farm, Ontario (2015, 9 pp); Proposed Section 24 Specific Plan Agua Caliente Band of Cahuilla Indians DEIS (2015, 9 pp);
Replies to comments 24 Specific Plan Agua Caliente Band of Cahuilla Indians FEIS (2015, 6 pp);
Willow Springs Solar Photovoltaic Project DEIR (2015; 28 pp); Sierra Lakes Commerce Center Project DEIR (2015, 9 pp); Columbia Business Center MND (2015; 8 pp);
West Valley Logistics Center Specific Plan DEIR (2015, 10 pp); World Logistic Center Specific Plan FEIR (2015, 12 pp); Bay Delta Conservation Plan EIR/EIS (2014, 21 pp);
Addison Wind Energy Project DEIR (2014, 32 pp);
Response to Comments on the Addison Wind Energy Project DEIR (2014, 15 pp); Addison and Rising Tree Wind Energy Project FEIR (2014, 12 pp); Alta East Wind Energy Project FEIS (2013, 23 pp);
Blythe Solar Power Project Staff Assessment, California Energy Commission (2013, 16 pp); Clearwater and Yakima Solar Projects DEIR (2013, 9 pp); Cuyama Solar Project DEIR (2014, 19 pp);
Draft Desert Renewable Energy Conservation Plan (DRECP) EIR/EIS (2015, 49 pp); Kingbird Solar Photovoltaic Project EIR (2013, 19 pp); Lucerne Valley Solar Project Initial Study & Mitigated Negative Declaration (2013, 12 pp); Palen Solar Electric Generating System Final Staff Assessment of California Energy Commission, (2014, 20 pp);
Rebuttal testimony on Palen Solar Energy Generating System (2014, 9 pp); Rising Tree Wind Energy Project DEIR (2014, 32 pp);
Response to Comments on the Rising Tree Wind Energy Project DEIR (2014, 15 pp); Soitec Solar Development Project Draft PEIR (2014, 18 pp); Comment on the Biological Opinion (08ESMF-00-2012-F-0387) of Oakland Zoo expansion on Alameda whipsnake and California red-legged frog (2014; 3 pp); West Antelope Solar Energy Project Initial Study and Negative Declaration (2013, 18 pp); Willow Springs Solar Photovoltaic Project DEIR (2015, 28 pp); Alameda Creek Bridge Replacement Project DEIR (2015, 10 pp); Declaration on Tule Wind project FEIR/FEIS (2013; 24 pp); Sunlight Partners LANDPRO Solar Project Mitigated Negative Declaration (2013; 11 pp); Declaration in opposition to BLM fracking (2013; 5 pp); Rosamond Solar Project Addendum EIR (2013; 13 pp);
Pioneer Green Solar Project EIR (2013; 13 pp);
Reply to Staff Responses to Comments on Soccer Center Solar Project Mitigated Negative Smallwood CV
32 Declaration (2013; 6 pp);
Soccer Center Solar Project Mitigated Negative Declaration (2013; 10 pp); Plainview Solar Works Mitigated Negative Declaration (2013; 10 pp); Reply to the County Staff’s Responses on comments to Imperial Valley Solar Company 2 Project (2013; 10 pp);
Imperial Valley Solar Company 2 Project (2013; 13 pp); FRV Orion Solar Project DEIR (PP12232) (2013; 9 pp);
Casa Diablo IV Geothermal Development Project (3013; 6 pp); Reply to Staff Responses to Comments on Casa Diablo IV Geothermal Development Project (2013; 8 pp);
FEIS prepared for Alta East Wind Project (2013; 23 pp); Metropolitan Air Park DEIR, City of San Diego (2013; ); Davidon Homes Tentative Subdivision Map and Rezoning Project DEIR (2013; 9 pp); Analysis of Biological Assessment of Oakland Zoo Expansion Impacts on Alameda Whipsnake (2013; 10 pp);
Declaration on Campo Verde Solar project FEIR (2013; 11pp); Neg Dec comments on Davis Sewer Trunk Rehabilitation (2013; 8 pp); Declaration on North Steens Transmission Line FEIS (2012; 62 pp); City of Lancaster Revised Initial Study for Conditional Use Permits 12-08 and 12-09, Summer Solar and Springtime Solar Projects (2012; 8 pp); J&J Ranch, 24 Adobe Lane Environmental Review (2012; 14 pp); Reply to the County Staff’s Responses on comments to Hudson Ranch Power II Geothermal Project and the Simbol Calipatria Plant II (2012; 8 pp); Hudson Ranch Power II Geothermal Project and the Simbol Calipatria Plant II (2012; 9 pp); Desert Harvest Solar Project EIS (2012; 15 pp);
Solar Gen 2 Array Project DEIR (2012; 16 pp);
Ocotillo Sol Project EIS (2012; 4 pp);
Beacon Photovoltaic Project DEIR (2012; 5 pp);
Declaration on Initial Study and Proposed Negative Declaration for the Butte Water District 2012 Water Transfer Program (2012; 11 pp);
Mount Signal and Calexico Solar Farm Projects DEIR (2011; 16 pp); City of Elk Grove Sphere of Influence EIR (2011; 28 pp); Comment on Sutter Landing Park Solar Photovoltaic Project MND (2011; 9 pp); Statement of Shawn Smallwood, Ph.D. Regarding Proposed Rabik/Gudath Project, 22611 Coleman Valley Road, Bodega Bay (CPN 10-0002) (2011; 4 pp); Declaration of K. Shawn Smallwood on Biological Impacts of the Ivanpah Solar Electric Generating System (ISEGS) (2011; 9 pp);
Comments on Draft Eagle Conservation Plan Guidance (2011; 13 pp); Comments on Draft EIR/EA for Niles Canyon Safety Improvement Project (2011; 16 pp); Declaration of K. Shawn Smallwood, Ph.D., on Biological Impacts of the Route 84 Safety Improvement Project (2011; 7 pp);
Rebuttal Testimony of Witness #22, K. Shawn Smallwood, Ph.D, on Behalf of Intervenors Friends of The Columbia Gorge & Save Our Scenic Area (2010; 6 pp); Prefiled Direct Testimony of Witness #22, K. Shawn Smallwood, Ph.D, on Behalf of Smallwood CV
33 Intervenors Friends of the Columbia Gorge & Save Our Scenic Area. Comments on Whistling Ridge Wind Energy Power Project DEIS, Skamania County, Washington (2010; 41 pp);
Evaluation of Klickitat County’s Decisions on the Windy Flats West Wind Energy Project (2010; 17 pp);
St. John's Church Project Draft Environmental Impact Report (2010; 14 pp.); Initial Study/Mitigated Negative Declaration for Results Radio Zone File #2009-001 (2010; 20 pp);
Rio del Oro Specific Plan Project Final Environmental Impact Report (2010;12 pp); Answers to Questions on 33% RPS Implementation Analysis Preliminary Results Report (2009: 9 pp);
SEPA Determination of Non-significance regarding zoning adjustments for Skamania County, Washington. Second Declaration to Friends of the Columbia Gorge, Inc. and Save Our Scenic Area (Dec 2008; 17 pp);
Comments on Draft 1A Summary Report to CAISO (2008; 10 pp); County of Placer’s Categorical Exemption of Hilton Manor Project (2009; 9 pp); Protest of CARE to Amendment to the Power Purchase and Sale Agreement for Procurement of Eligible Renewable Energy Resources Between Hatchet Ridge Wind LLC and PG&E (2009; 3 pp);
Tehachapi Renewable Transmission Project EIR/EIS (2009; 142 pp); Delta Shores Project EIR, south Sacramento (2009; 11 pp + addendum 2 pp); Declaration of Shawn Smallwood in Support of Care’s Petition to Modify D.07-09-040 (2008; 3 pp);
The Public Utility Commission’s Implementation Analysis December 16 Workshop for the Governor’s Executive Order S-14-08 to implement a 33% Renewable Portfolio Standard by 2020 (2008; 9 pp);
The Public Utility Commission’s Implementation Analysis Draft Work Plan for the Governor’s Executive Order S-14-08 to implement a 33% Renewable Portfolio Standard by 2020 (2008; 11 pp);
Draft 1A Summary Report to California Independent System Operator for Planning Reserve Margins (PRM) Study (2008; 7 pp.);
SEPA Determination of Non-significance regarding zoning adjustments for Skamania County, Washington. Declaration to Friends of the Columbia Gorge, Inc. and Save Our Scenic Area (Sep 2008; 16 pp);
California Energy Commission’s Preliminary Staff Assessment of the Colusa Generating Station (2007; 24 pp);
Rio del Oro Specific Plan Project Recirculated Draft Environmental Impact Report (2008:
66 pp);
Replies to Response to Comments Re: Regional University Specific Plan Environmental Impact Report (2008; 20 pp);
Regional University Specific Plan Environmental Impact Report (2008: 33 pp.); Clark Precast, LLC’s “Sugarland” project, Negative Declaration (2008: 15 pp.); Cape Wind Project Draft Environmental Impact Statement (2008; 157 pp.); Yuba Highlands Specific Plan (or Area Plan) Environmental Impact Report (2006; 37 pp.); Replies to responses to comments on Mitigated Negative Declaration of the proposed Smallwood CV
34 Mining Permit (MIN 04-01) and Modification of Use Permit 96-02 at North Table Mountain (2006; 5 pp);
Mitigated Negative Declaration of the proposed Mining Permit (MIN 04-01) and Modification of Use Permit 96-02 at North Table Mountain (2006; 15 pp); Windy Point Wind Farm Environmental Review and EIS (2006; 14 pp and 36 Powerpoint slides in reply to responses to comments);
Shiloh I Wind Power Project EIR (2005; 18 pp);
Buena Vista Wind Energy Project Notice of Preparation of EIR (2004; 15 pp); Negative Declaration of the proposed Callahan Estates Subdivision (2004; 11 pp); Negative Declaration of the proposed Winters Highlands Subdivision (2004; 9 pp); Negative Declaration of the proposed Winters Highlands Subdivision (2004; 13 pp); Negative Declaration of the proposed Creekside Highlands Project, Tract 7270 (2004; 21 pp);
On the petition California Fish and Game Commission to list the Burrowing Owl as threatened or endangered (2003; 10 pp);
Conditional Use Permit renewals from Alameda County for wind turbine operations in the Altamont Pass Wind Resource Area (2003; 41 pp);
UC Davis Long Range Development Plan of 2003, particularly with regard to the Neighborhood Master Plan (2003; 23 pp);
Anderson Marketplace Draft Environmental Impact Report (2003: 18 pp + 3 plates of photos);
Negative Declaration of the proposed expansion of Temple B’nai Tikyah (2003: 6 pp); Antonio Mountain Ranch Specific Plan Public Draft EIR (2002: 23 pp); Response to testimony of experts at the East Altamont Energy Center evidentiary hearing on biological resources (2002: 9 pp);
Revised Draft Environmental Impact Report, The Promenade (2002: 7 pp); Recirculated Initial Study for Calpine’s proposed Pajaro Valley Energy Center (2002: 3 pp); UC Merced -- Declaration of Dr. Shawn Smallwood in support of petitioner’s application for temporary restraining order and preliminary injunction (2002: 5 pp); Replies to response to comments in Final Environmental Impact Report, Atwood Ranch Unit III Subdivision (2003: 22 pp);
Draft Environmental Impact Report, Atwood Ranch Unit III Subdivision (2002: 19 pp + 8 photos on 4 plates);
California Energy Commission Staff Report on GWF Tracy Peaker Project (2002: 17 pp + 3 photos; follow-up report of 3 pp);
Initial Study and Negative Declaration, Silver Bend Apartments, Placer County (2002: 13 pp);
UC Merced Long-range Development Plan DEIR and UC Merced Community Plan DEIR (2001: 26 pp);
Initial Study, Colusa County Power Plant (2001: 6 pp); Comments on Proposed Dog Park at Catlin Park, Folsom, California (2001: 5 pp + 4 photos);
Pacific Lumber Co. (Headwaters) Habitat Conservation Plan and Environmental Impact Report (1998: 28 pp);
Final Environmental Impact Report/Statement for Issuance of Take authorization for listed Smallwood CV
35 species within the MSCP planning area in San Diego County, California (Fed. Reg. 62 (60):
14938, San Diego Multi-Species Conservation Program) (1997: 10 pp); Permit (PRT-823773) Amendment for the Natomas Basin Habitat Conservation Plan, Sacramento, CA (Fed. Reg. 63 (101): 29020-29021) (1998); Draft Recovery Plan for the Giant Garter Snake (Thamnophis gigas). (Fed. Reg. 64(176):
49497-49498) (1999: 8 pp);
Review of the Draft Recovery Plan for the Arroyo Southwestern Toad (Bufo microscaphus californicus) (1998);
Ballona West Bluffs Project Environmental Impact Report (1999: oral presentation); California Board of Forestry’s proposed amended Forest Practices Rules (1999); Negative Declaration for the Sunset Skyranch Airport Use Permit (1999); Calpine and Bechtel Corporations’ Biological Resources Implementation and Monitoring Program (BRMIMP) for the Metcalf Energy Center (2000: 10 pp); California Energy Commission’s Final Staff Assessment of the proposed Metcalf Energy Center (2000);
US Fish and Wildlife Service Section 7 consultation with the California Energy Commission regarding Calpine and Bechtel Corporations’ Metcalf Energy Center (2000: 4 pp); California Energy Commission’s Preliminary Staff Assessment of the proposed Metcalf Energy Center (2000: 11 pp);
Site-specific management plans for the Natomas Basin Conservancy’s mitigation lands, prepared by Wildlands, Inc. (2000: 7 pp);
Affidavit of K. Shawn Smallwood in Spirit of the Sage Council, et al. (Plaintiffs) vs. Bruce Babbitt, Secretary, U.S. Department of the Interior, et al. (Defendants), Injuries caused by the No Surprises policy and final rule which codifies that policy (1999: 9 pp).
Comments on other Environmental Review Documents:
Proposed Regulation for California Fish and Game Code Section 3503.5 (2015: 12 pp); Statement of Overriding Considerations related to extending Altamont Winds, Inc.’s Conditional Use Permit PLN2014-00028 (2015; 8 pp);
Draft Program Level EIR for Covell Village (2005; 19 pp); Bureau of Land Management Wind Energy Programmatic EIS Scoping document (2003: 7 pp.);
NEPA Environmental Analysis for Biosafety Level 4 National Biocontainment Laboratory (NBL) at UC Davis (2003: 7 pp);
Notice of Preparation of UC Merced Community and Area Plan EIR, on behalf of The Wildlife Society—Western Section (2001: 8 pp.);
Preliminary Draft Yolo County Habitat Conservation Plan (2001; 2 letters totaling 35 pp.); Merced County General Plan Revision, notice of Negative Declaration (2001: 2 pp.); Notice of Preparation of Campus Parkway EIR/EIS (2001: 7 pp.); Draft Recovery Plan for the bighorn sheep in the Peninsular Range (Ovis candensis) (2000); Draft Recovery Plan for the California Red-legged Frog (Rana aurora draytonii), on behalf of The Wildlife Society—Western Section (2000: 10 pp.); Sierra Nevada Forest Plan Amendment Draft Environmental Impact Statement, on behalf of The Wildlife Society—Western Section (2000: 7 pp.);
Smallwood CV
36 State Water Project Supplemental Water Purchase Program, Draft Program EIR (1997); Davis General Plan Update EIR (2000);
Turn of the Century EIR (1999: 10 pp);
Proposed termination of Critical Habitat Designation under the Endangered Species Act (Fed. Reg. 64(113): 31871-31874) (1999);
NOA Draft Addendum to the Final Handbook for Habitat Conservation Planning and Incidental Take Permitting Process, termed the HCP 5-Point Policy Plan (Fed. Reg. 64(45):
11485 - 11490) (1999; 2 pp + attachments);
Covell Center Project EIR and EIR Supplement (1997).
Position Statements I prepared the following position statements for the Western Section of The Wildlife Society, and one for nearly 200 scientists:
Recommended that the California Department of Fish and Game prioritize the extermination of the introduced southern water snake in northern California. The Wildlife Society-- Western Section (2001);
Recommended that The Wildlife Society—Western Section appoint or recommend members of the independent scientific review panel for the UC Merced environmental review process (2001);
Opposed the siting of the University of California’s 10th campus on a sensitive vernal pool/grassland complex east of Merced. The Wildlife Society--Western Section (2000); Opposed the legalization of ferret ownership in California. The Wildlife Society--Western Section (2000);
Opposed the Proposed “No Surprises,” “Safe Harbor,” and “Candidate Conservation Agreement” rules, including permit-shield protection provisions (Fed. Reg. Vol. 62, No. 103, pp. 29091-29098 and No. 113, pp. 32189-32194). This statement was signed by 188 scientists and went to the responsible federal agencies, as well as to the U.S. Senate and House of Representatives.
Posters at Professional Meetings
Leyvas, E. and K. S. Smallwood. 2015. Rehabilitating injured animals to offset and rectify wind project impacts. Conference on Wind Energy and Wildlife Impacts, Berlin, Germany, 9-12 March 2015.
Smallwood, K. S., J. Mount, S. Standish, E. Leyvas, D. Bell, E. Walther, B. Karas. 2015. Integrated detection trials to improve the accuracy of fatality rate estimates at wind projects. Conference on Wind Energy and Wildlife Impacts, Berlin, Germany, 9-12 March 2015.
Smallwood, K. S. and C. G. Thelander. 2005. Lessons learned from five years of avian mortality research in the Altamont Pass WRA. AWEA conference, Denver, May 2005.
Neher, L., L. Wilder, J. Woo, L. Spiegel, D. Yen-Nakafugi, and K.S. Smallwood. 2005. Bird’s eye view on California wind. AWEA conference, Denver, May 2005.
Smallwood, K. S., C. G. Thelander and L. Spiegel. 2003. Toward a predictive model of avian Smallwood CV
37 fatalities in the Altamont Pass Wind Resource Area. Windpower 2003 Conference and Convention, Austin, Texas.
Smallwood, K.S. and Eva Butler. 2002. Pocket Gopher Response to Yellow Star-thistle Eradication as part of Grassland Restoration at Decommissioned Mather Air Force Base, Sacramento County, California. White Mountain Research Station Open House, Barcroft Station.
Smallwood, K.S. and Michael L. Morrison. 2002. Fresno kangaroo rat (Dipodomys nitratoides) Conservation Research at Resources Management Area 5, Lemoore Naval Air Station. White Mountain Research Station Open House, Barcroft Station.
Smallwood, K.S. and E.L. Fitzhugh. 1989. Differentiating mountain lion and dog tracks. Third Mountain Lion Workshop, Prescott, AZ.
Smith, T. R. and K. S. Smallwood. 2000. Effects of study area size, location, season, and allometry on reported Sorex shrew densities. Annual Meeting of the Western Section of The Wildlife Society.
Presentations at Professional Meetings and Seminars
Repowering the Altamont Pass. Altamont Symposium, The Wildlife Society – Western Section, 5 February 2017.
Developing methods to reduce bird mortality in the Altamont Pass Wind Resource Area, 1999- 2007. Altamont Symposium, The Wildlife Society – Western Section, 5 February 2017.
Conservation and recovery of burrowing owls in Santa Clara Valley. Santa Clara Valley Habitat Agency, Newark, California, 3 February 2017.
Mitigation of Raptor Fatalities in the Altamont Pass Wind Resource Area. Raptor Research Foundation Meeting, Sacramento, California, 6 November 2015.
From burrows to behavior: Research and management for burrowing owls in a diverse landscape.
California Burrowing Owl Consortium meeting, 24 October 2015, San Jose, California.
The Challenges of repowering. Keynote presentation at Conference on Wind Energy and Wildlife Impacts, Berlin, Germany, 10 March 2015.
Research Highlights Altamont Pass 2011-2015. Scientific Review Committee, Oakland, California, 8 July 2015.
Siting wind turbines to minimize raptor collisions: Altamont Pass Wind Resource Area. US Fish and Wildlife Service Golden Eagle Working Group, Sacramento, California, 8 January 2015.
Evaluation of nest boxes as a burrowing owl conservation strategy. Sacramento Chapter of the Western Section, The Wildlife Society. Sacramento, California, 26 August 2013.
Predicting collision hazard zones to guide repowering of the Altamont Pass. Conference on wind Smallwood CV
38 power and environmental impacts. Stockholm, Sweden, 5-7 February 2013.
Impacts of Wind Turbines on Wildlife. California Council for Wildlife Rehabilitators, Yosemite, California, 12 November 2012.
Impacts of Wind Turbines on Birds and Bats. Madrone Audubon Society, Santa Rosa, California, 20 February 2012.
Comparing Wind Turbine Impacts across North America. California Energy Commission Staff Workshop: Reducing the Impacts of Energy Infrastructure on Wildlife, 20 July 2011.
Siting Repowered Wind Turbines to Minimize Raptor Collisions. California Energy Commission Staff Workshop: Reducing the Impacts of Energy Infrastructure on Wildlife, 20 July 2011.
Siting Repowered Wind Turbines to Minimize Raptor Collisions. Alameda County Scientific Review Committee meeting, 17 February 2011
Comparing Wind Turbine Impacts across North America. Conference on Wind energy and Wildlife impacts, Trondheim, Norway, 3 May 2011.
Update on Wildlife Impacts in the Altamont Pass Wind Resource Area. Raptor Symposium, The Wildlife Society—Western Section, Riverside, California, February 2011.
Siting Repowered Wind Turbines to Minimize Raptor Collisions. Raptor Symposium, The Wildlife Society - Western Section, Riverside, California, February 2011.
Wildlife mortality caused by wind turbine collisions. Ecological Society of America, Pittsburgh, Pennsylvania, 6 August 2010.
Map-based repowering and reorganization of a wind farm to minimize burrowing owl fatalities.
California burrowing Owl Consortium Meeting, Livermore, California, 6 February 2010.
Environmental barriers to wind power. Getting Real About Renewables: Economic and Environmental Barriers to Biofuels and Wind Energy. A symposium sponsored by the Environmental & Energy Law & Policy Journal, University of Houston Law Center, Houston, 23 February 2007.
Lessons learned about bird collisions with wind turbines in the Altamont Pass and other US wind farms. Meeting with Japan Ministry of the Environment and Japan Ministry of the Economy, Wild Bird Society of Japan, and other NGOs Tokyo, Japan, 9 November 2006.
Lessons learned about bird collisions with wind turbines in the Altamont Pass and other US wind farms. Symposium on bird collisions with wind turbines. Wild Bird Society of Japan, Tokyo, Japan, 4 November 2006.
Responses of Fresno kangaroo rats to habitat improvements in an adaptive management framework.
California Society for Ecological Restoration (SERCAL) 13th Annual Conference, UC Santa Smallwood CV
39 Barbara, 27 October 2006.
Fatality associations as the basis for predictive models of fatalities in the Altamont Pass Wind Resource Area. EEI/APLIC/PIER Workshop, 2006 Biologist Task Force and Avian Interaction with Electric Facilities Meeting, Pleasanton, California, 28 April 2006.
Burrowing owl burrows and wind turbine collisions in the Altamont Pass Wind Resource Area. The Wildlife Society - Western Section Annual Meeting, Sacramento, California, February 8, 2006.
Mitigation at wind farms. Workshop: Understanding and resolving bird and bat impacts. American Wind Energy Association and Audubon Society. Los Angeles, CA. January 10 and 11, 2006.
Incorporating data from the California Wildlife Habitat Relationships (CWHR) system into an impact assessment tool for birds near wind farms. Shawn Smallwood, Kevin Hunting, Marcus Yee, Linda Spiegel, Monica Parisi. Workshop: Understanding and resolving bird and bat impacts.
American Wind Energy Association and Audubon Society. Los Angeles, CA. January 10 and 11, 2006.
Toward indicating threats to birds by California’s new wind farms. California Energy Commission, Sacramento, May 26, 2005.
Avian collisions in the Altamont Pass. California Energy Commission, Sacramento, May 26, 2005.
Ecological solutions for avian collisions with wind turbines in the Altamont Pass Wind Resource Area. EPRI Environmental Sector Council, Monterey, California, February 17, 2005.
Ecological solutions for avian collisions with wind turbines in the Altamont Pass Wind Resource Area. The Wildlife Society—Western Section Annual Meeting, Sacramento, California, January 19, 2005.
Associations between avian fatalities and attributes of electric distribution poles in California. The Wildlife Society - Western Section Annual Meeting, Sacramento, California, January 19, 2005.
Minimizing avian mortality in the Altamont Pass Wind Resources Area. UC Davis Wind Energy Collaborative Forum, Palm Springs, California, December 14, 2004.
Selecting electric distribution poles for priority retrofitting to reduce raptor mortality. Raptor Research Foundation Meeting, Bakersfield, California, November 10, 2004.
Responses of Fresno kangaroo rats to habitat improvements in an adaptive management framework.
Annual Meeting of the Society for Ecological Restoration, South Lake Tahoe, California, October 16, 2004.
Lessons learned from five years of avian mortality research at the Altamont Pass Wind Resources Area in California. The Wildlife Society Annual Meeting, Calgary, Canada, September 2004.
The ecology and impacts of power generation at Altamont Pass. Sacramento Petroleum Association, Smallwood CV
40 Sacramento, California, August 18, 2004.
Burrowing owl mortality in the Altamont Pass Wind Resource Area. California Burrowing Owl Consortium meeting, Hayward, California, February 7, 2004.
Burrowing owl mortality in the Altamont Pass Wind Resource Area. California Burrowing Owl Symposium, Sacramento, November 2, 2003.
Raptor Mortality at the Altamont Pass Wind Resource Area. National Wind Coordinating Committee, Washington, D.C., November 17, 2003.
Raptor Behavior at the Altamont Pass Wind Resource Area. Annual Meeting of the Raptor Research Foundation, Anchorage, Alaska, September, 2003.
Raptor Mortality at the Altamont Pass Wind Resource Area. Annual Meeting of the Raptor Research Foundation, Anchorage, Alaska, September, 2003.
California mountain lions. Ecological & Environmental Issues Seminar, Department of Biology, California State University, Sacramento, November, 2000.
Intra- and inter-turbine string comparison of fatalities to animal burrow densities at Altamont Pass.
National Wind Coordinating Committee, Carmel, California, May, 2000.
Using a Geographic Positioning System (GPS) to map wildlife and habitat. Annual Meeting of the Western Section of The Wildlife Society, Riverside, CA, January, 2000.
Suggested standards for science applied to conservation issues. Annual Meeting of the Western Section of The Wildlife Society, Riverside, CA, January, 2000.
The indicators framework applied to ecological restoration in Yolo County, California. Society for Ecological Restoration, September 25, 1999.
Ecological restoration in the context of animal social units and their habitat areas. Society for Ecological Restoration, September 24, 1999.
Relating Indicators of Ecological Health and Integrity to Assess Risks to Sustainable Agriculture and Native Biota. International Conference on Ecosystem Health, August 16, 1999.
A crosswalk from the Endangered Species Act to the HCP Handbook and real HCPs. Southern California Edison, Co. and California Energy Commission, March 4-5, 1999.
Mountain lion track counts in California: Implications for Management. Ecological & Environmental Issues Seminar, Department of Biological Sciences, California State University, Sacramento, November 4, 1998.
“No Surprises” -- Lack of science in the HCP process. California Native Plant Society Annual Conservation Conference, The Presidio, San Francisco, September 7, 1997.
Smallwood CV
41 In Your Interest. A half hour weekly show aired on Channel 10 Television, Sacramento. In this episode, I served on a panel of experts discussing problems with the implementation of the Endangered Species Act. Aired August 31, 1997.
Spatial scaling of pocket gopher (Geomyidae) density. Southwestern Association of Naturalists 44th Meeting, Fayetteville, Arkansas, April 10, 1997.
Estimating prairie dog and pocket gopher burrow volume. Southwestern Association of Naturalists 44th Meeting, Fayetteville, Arkansas, April 10, 1997.
Ten years of mountain lion track survey. Fifth Mountain Lion Workshop, San Diego, February 27, 1996.
Study and interpretive design effects on mountain lion density estimates. Fifth Mountain Lion Workshop, San Diego, February 27, 1996.
Small animal control. Session moderator and speaker at the California Farm Conference, Sacramento, California, Feb. 28, 1995.
Small animal control. Ecological Farming Conference, Asylomar, California, Jan. 28, 1995.
Habitat associations of the Swainson’s Hawk in the Sacramento Valley’s agricultural landscape. 1994 Raptor Research Foundation Meeting, Flagstaff, Arizona.
Alfalfa as wildlife habitat. Seed Industry Conference, Woodland, California, May 4, 1994.
Habitats and vertebrate pests: impacts and management. Managing Farmland to Bring Back Game Birds and Wildlife to the Central Valley. Yolo County Resource Conservation District, U.C. Davis, February 19, 1994.
Management of gophers and alfalfa as wildlife habitat. Orland Alfalfa Production Meeting and Sacramento Valley Alfalfa Production Meeting, February 1 and 2, 1994.
Patterns of wildlife movement in a farming landscape. Wildlife and Fisheries Biology Seminar Series: Recent Advances in Wildlife, Fish, and Conservation Biology, U.C. Davis, Dec. 6, 1993.
Alfalfa as wildlife habitat. California Alfalfa Symposium, Fresno, California, Dec. 9, 1993.
Management of pocket gophers in Sacramento Valley alfalfa. California Alfalfa Symposium, Fresno, California, Dec. 8, 1993.
Association analysis of raptors in a farming landscape. Plenary speaker at Raptor Research Foundation Meeting, Charlotte, North Carolina, Nov. 6, 1993.
Landscape strategies for biological control and IPM. Plenary speaker, International Conference on Integrated Resource Management and Sustainable Agriculture, Beijing, China, Sept. 11, 1993.
Smallwood CV
42 Landscape Ecology Study of Pocket Gophers in Alfalfa. Alfalfa Field Day, U.C. Davis, July 1993.
Patterns of wildlife movement in a farming landscape. Spatial Data Analysis Colloquium, U.C.
Davis, August 6, 1993.
Sound stewardship of wildlife. Veterinary Medicine Seminar: Ethics of Animal Use, U.C. Davis.
May 1993.
Landscape ecology study of pocket gophers in alfalfa. Five County Grower's Meeting, Tracy, California. February 1993.
Turbulence and the community organizers: The role of invading species in ordering a turbulent system, and the factors for invasion success. Ecology Graduate Student Association Colloquium, U.C. Davis. May 1990.
Evaluation of exotic vertebrate pests. Fourteenth Vertebrate Pest Conference, Sacramento, California. March 1990.
Analytical methods for predicting success of mammal introductions to North America. The Western Section of the Wildlife Society, Hilo, Hawaii. February 1988.
A state-wide mountain lion track survey. Sacramento County Dept Parks and Recreation. April 1986.
The mountain lion in California. Davis Chapter of the Audubon Society. October 1985.
Ecology Graduate Student Seminars, U.C. Davis, 1985-1990: Social behavior of the mountain lion; Mountain lion control; Political status of the mountain lion in California.
Other forms of Participation at Professional Meetings
Scientific Committee, Conference on Wind energy and Wildlife impacts, Berlin, Germany, March 2015.
Scientific Committee, Conference on Wind energy and Wildlife impacts, Stockholm, Sweden, February 2013.
Workshop co-presenter at Birds & Wind Energy Specialist Group (BAWESG) Information sharing week, Bird specialist studies for proposed wind energy facilities in South Africa, Endangered Wildlife Trust, Darling, South Africa, 3-7 October 2011.
Scientific Committee, Conference on Wind energy and Wildlife impacts, Trondheim, Norway, 2-5 May 2011.
Chair of Animal Damage Management Session, The Wildlife Society, Annual Meeting, Reno, Nevada, September 26, 2001.
Smallwood CV
43 Chair of Technical Session: Human communities and ecosystem health: Comparing perspectives and making connection. Managing for Ecosystem Health, International Congress on Ecosystem Health, Sacramento, CA August 15-20, 1999.
Student Awards Committee, Annual Meeting of the Western Section of The Wildlife Society, Riverside, CA, January, 2000.
Student Mentor, Annual Meeting of the Western Section of The Wildlife Society, Riverside, CA, January, 2000.
Printed Mass Media
Smallwood, K.S., D. Mooney, and M. McGuinness. 2003. We must stop the UCD biolab now. Op- Ed to the Davis Enterprise.
Smallwood, K.S. 2002. Spring Lake threatens Davis. Op-Ed to the Davis Enterprise.
Smallwood, K.S. Summer, 2001. Mitigation of habitation. The Flatlander, Davis, California.
Entrikan, R.K. and K.S. Smallwood. 2000. Measure O: Flawed law would lock in new taxes. Op-Ed to the Davis Enterprise.
Smallwood, K.S. 2000. Davis delegation lobbies Congress for Wildlife conservation. Op-Ed to the Davis Enterprise.
Smallwood, K.S. 1998. Davis Visions. The Flatlander, Davis, California.
Smallwood, K.S. 1997. Last grab for Yolo’s land and water. The Flatlander, Davis, California.
Smallwood, K.S. 1997. The Yolo County HCP. Op-Ed to the Davis Enterprise.
Radio/Television
PBS News Hour,
FOX News, Energy in America: Dead Birds Unintended Consequence of Wind Power Development, August 2011.
KXJZ Capital Public Radio -- Insight (Host Jeffrey Callison). Mountain lion attacks (with guest Professor Richard Coss). 23 April 2009;
KXJZ Capital Public Radio -- Insight (Host Jeffrey Callison). Wind farm Rio Vista Renewable Power. 4 September 2008;
KQED QUEST Episode #111. Bird collisions with wind turbines. 2007;
Smallwood CV
44 KDVS Speaking in Tongues (host Ron Glick), Yolo County HCP: 1 hour. December 27, 2001;
KDVS Speaking in Tongues (host Ron Glick), Yolo County HCP: 1 hour. May 3, 2001;
KDVS Speaking in Tongues (host Ron Glick), Yolo County HCP: 1 hour. February 8, 2001;
KDVS Speaking in Tongues (host Ron Glick & Shawn Smallwood), California Energy Crisis: 1 hour. Jan. 25, 2001;
KDVS Speaking in Tongues (host Ron Glick), Headwaters Forest HCP: 1 hour. 1998;
Davis Cable Channel (host Gerald Heffernon), Burrowing owls in Davis: half hour. June, 2000;
Davis Cable Channel (hosted by Davis League of Women Voters), Measure O debate: 1 hour.
October, 2000;
KXTV 10, In Your Interest, The Endangered Species Act: half hour. 1997.
Reviews of Journal Papers (Scientific journals for whom I’ve provided peer review) Journal Journal
American Naturalist Journal of Animal Ecology
Journal of Wildlife Management Western North American Naturalist Auk Journal of Raptor Research
Biological Conservation National Renewable Energy Lab reports Canadian Journal of Zoology Oikos
Ecosystem Health The Prairie Naturalist
Environmental Conservation Restoration Ecology
Environmental Management Southwestern Naturalist
Functional Ecology The Wildlife Society--Western Section Trans.
Journal of Zoology (London) Proc. Int. Congress on Managing for Ecosystem Health Journal of Applied Ecology Transactions in GIS
Ecology Tropical Ecology
Wildlife Society Bulletin Peer J
Biological Control The Condor
Committees
Scientific Review Committee, Alameda County, Altamont Pass Wind Resource Area Ph.D. Thesis Committee, Steve Anderson, University of California, Davis MS Thesis Committee, Marcus Yee, California State University, Sacramento
Smallwood CV
45 Other Professional Activities or Products
Testified in Federal Court in Denver during 2005 over the fate of radio-nuclides in the soil at Rocky Flats Plant after exposure to burrowing animals. My clients won a judgment of $553,000,000. I have also testified in many other cases of litigation under CEQA, NEPA, the Warren-Alquist Act, and other environmental laws. My clients won most of the cases for which I testified.
Testified before Environmental Review Tribunals in Ontario, Canada regarding proposed White Pines, Amherst Island, and Fairview Wind Energy projects.
Testified in Skamania County Hearing in 2009 on the potential impacts of zoning the County for development of wind farms and hazardous waste facilities.
Testified in deposition in 2007 in the case of O’Dell et al. vs. FPL Energy in Houston, Texas.
Testified in Klickitat County Hearing in 2006 on the potential impacts of the Windy Point Wind Farm.
Memberships in Professional Societies
The Wildlife Society
Raptor Research Foundation
Honors and Awards
Fulbright Research Fellowship to Indonesia, 1987
J.G. Boswell Full Academic Scholarship, 1981 college of choice Certificate of Appreciation, The Wildlife Society—Western Section, 2000, 2001 Northern California Athletic Association Most Valuable Cross Country Runner, 1984 American Legion Award, Corcoran High School, 1981, and John Muir Junior High, 1977 CIF Section Champion, Cross Country in 1978
CIF Section Champion, Track & Field 2 mile run in 1981
National Junior Record, 20 kilometer run, 1982
National Age Group Record, 1500 meter run, 1978
Community Activities
District 64 Little League Umpire, 2003-2007
Dixon Little League Umpire, 2006-07
Davis Little League Chief Umpire and Board member, 2004-2005 Davis Little League Safety Officer, 2004-2005
Davis Little League Certified Umpire, 2002-2004
Davis Little League Scorekeeper, 2002
Davis Visioning Group member
Petitioner for Writ of Mandate under the California Environmental Quality Act against City of Woodland decision to approve the Spring Lake Specific Plan, 2002 Served on campaign committees for City Council candidates
Smallwood CV
46 Representative Clients/Funders
Law Offices of Stephan C. Volker EDF Renewables
Blum Collins, LLP National Renewable Energy Lab
Eric K. Gillespie Professional Corporation Altamont Winds LLC Law Offices of Berger & Montague Salka Energy
Lozeau | Drury LLP Comstocks Business (magazine)
Law Offices of Roy Haber BioResource Consultants
Law Offices of Edward MacDonald Tierra Data
Law Office of John Gabrielli Black and Veatch
Law Office of Bill Kopper Terry Preston, Wildlife Ecology Research Center Law Office of Donald B. Mooney EcoStat, Inc.
Law Office of Veneruso & Moncharsh US Navy
Law Office of Steven Thompson US Department of Agriculture Law Office of Brian Gaffney US Forest Service
California Wildlife Federation US Fish & Wildlife Service Defenders of Wildlife US Department of Justice
Sierra Club California Energy Commission
National Endangered Species Network California Office of the Attorney General Spirit of the Sage Council California Department of Fish & Wildlife The Humane Society California Department of Transportation Hagens Berman LLP California Department of Forestry
Environmental Protection Information Center California Department of Food & Agriculture Goldberg, Kamin & Garvin, Attorneys at Law Ventura County Counsel Californians for Renewable Energy (CARE) County of Yolo Seatuck Environmental Association Tahoe Regional Planning Agency Friends of the Columbia Gorge, Inc. Sustainable Agriculture Research & Education Program Save Our Scenic Area Sacramento-Yolo Mosquito and Vector Control District Alliance to Protect Nantucket Sound East Bay Regional Park District Friends of the Swainson’s Hawk County of Alameda
Alameda Creek Alliance Don & LaNelle Silverstien
Center for Biological Diversity Seventh Day Adventist Church California Native Plant Society Escuela de la Raza Unida Endangered Wildlife Trust Susan Pelican and Howard Beeman and BirdLife South Africa Residents Against Inconsistent Development, Inc.
AquAlliance Bob Sarvey
Oregon Natural Desert Association Mike Boyd
Save Our Sound Hillcroft Neighborhood Fund
G3 Energy and Pattern Energy Joint Labor Management Committee, Retail Food Industry Emerald Farms Lisa Rocca
Pacific Gas & Electric Co. Kevin Jackson
Southern California Edison Co. Dawn Stover and Jay Letto Georgia-Pacific Timber Co. Nancy Havassy
Northern Territories Inc. Catherine Portman (for Brenda Cedarblade) David Magney Environmental Consulting Ventus Environmental Solutions, Inc.
Wildlife History Foundation Panorama Environmental, Inc.
NextEra Energy Resources, LLC Adams Broadwell Professional Corporation Ogin, Inc.
Smallwood CV
47 Representative special-status species experience
Common name Species name Description
Field experience
California red-legged frog Rana aurora draytonii Protocol searches; Many detections Foothill yellow-legged frog Rana boylii Presence surveys; Many detections Western spadefoot Spea hammondii Presence surveys; Few detections California tiger salamander Ambystoma californiense Protocol searches; Many detections Coast range newt Taricha torosa torosa Searches and multiple detections Blunt-nosed leopard lizard Gambelia sila Detected in San Luis Obispo County California horned lizard Phrynosoma coronatum frontale Searches; Many detections Western pond turtle Clemmys marmorata Searches; Many detections San Joaquin kit fox Vulpes macrotis mutica Protocol searches; detections Sumatran tiger Panthera tigris Track surveys in Sumatra Mountain lion Puma concolor californicus Research and publications Point Arena mountain beaver Aplodontia rufa nigra Remote camera operation Giant kangaroo rat Dipodomys ingens Detected in Cholame Valley San Joaquin kangaroo rat Dipodomys nitratoides Monitoring & habitat restoration Monterey dusky-footed woodrat Neotoma fuscipes luciana Non-target captures and mapping of dens Salt marsh harvest mouse Reithrodontomys raviventris Habitat assessment, monitoring Salinas harvest mouse Reithrodontomys megalotus
distichlus
Captures; habitat assessment
Bats Thermal imaging surveys
California clapper rail Rallus longirostris Surveys and detections Golden eagle Aquila chrysaetos Numerical & behavioral surveys Swainson’s hawk Buteo swainsoni Numerical & behavioral surveys Northern harrier Circus cyaeneus Numerical & behavioral surveys White-tailed kite Elanus leucurus Numerical & behavioral surveys Loggerhead shrike Lanius ludovicianus Large area surveys Least Bell’s vireo Vireo bellii pusillus Detected in Monterey County Willow flycatcher Empidonax traillii extimus Research at Sierra Nevada breeding sites Burrowing owl Athene cunicularia hypugia Numerical & behavioral surveys Valley elderberry longhorn
beetle
Desmocerus californicus
dimorphus
Monitored success of relocation and habitat
restoration
Analytical
Arroyo southwestern toad Bufo microscaphus californicus Research and report.
Giant garter snake Thamnophis gigas Research and publication Northern goshawk Accipiter gentilis Research and publication Northern spotted owl Strix occidentalis Research and reports Alameda whipsnake Masticophis lateralis
euryxanthus
Expert testimony
EXHIBIT D
1 794 Sawnee Bean Road
Thetford Center VT 05075
Norman Marshall, President
(802) 356-2969
[email protected]
July 17, 2023
Richard M. Franco
Adams Broadwell Joseph & Cardozo
601 Gateway Blvd., Suite 1000
South San Francisco, CA 94080
Subject: Responses to the Shadowbox Studio Project Draft Final EIR Dear Mr. Franco,
The Shadowbox Studio Project Draft Final Environmental Impact Report (“DFEIR”) includes responses to my comment letter dated concerning the vehicle miles traveled (“VMT”) impacts of the proposed project as presented in the DEIR (May 19, 2023). In my previous comments, I stated:
The DEIR’s assertion that the project is in a VMT-efficient location is based on an outdated transportation model with a base year of 2012 that is known to underestimate commute VMT. Census data indicate that the actual average commute distances of workers employed in the project area is 2.8 times as great as asserted in the DEIR. The DEIR must be revised to include a realistic estimate of VMT impacts.
The DFEIR does not address the substantive problem with the project VMT analysis raised in this comment – that the significance threshold and Project VMT estimate were derived from an outdated model known to underestimate VMT– but instead offers as a defense that the analysis is an “apples-to- apples” comparison (DFEIR, p. 2-1012). While “apples-to-apples” comparisons are generally of value, they are not when both “apples” are rotten. In this case, it is just a mindless exercise of comparing one inaccurate number with another inaccurate number. As I pointed out in my comments, the 2020 model incorporates census data (which was not used in the 2016 model) to “calibrate the tail of the trip length distribution, because there were few observations of these long commute patterns captured in the [California Household Travel Survey (CHTS) data].” As I also explained, the census data showed average
2 commute lengths 65% higher than the average in the CHTS date used to calibrate the outdate model.
None of these facts are addressed or refuted in the FEIR.
VMT efficiency has not been adequately demonstrated for this proposed project, and additional VMT mitigation is required.
The DFEIR makes two false claims about my VMT estimate: The first false claim is that I incorrectly calculated work VMT per employee as including round trip commuting because the “State” definition is “VMT per employee is a one-way trip distance” (DFEIR, p. 2-1012). This is false. There is no such “State” definition. The Office of Policy Research’s Technical Advisory on Evaluating Transportation Impacts in CEQA (December 2018) includes the phrase “VMT per employee” three but the phrase is not defined.
The plain meaning of VMT per employee per day is roundtrip VMT.
Most documents related to SB 743 fail to spell out that VMT per employee includes both directions assuming the plain language interpretation is understood, but here are two examples from Fehr and Peers (the firm that has done a lion’s share of SB 743 VMT analysis) that does.
Daily Home-Based Work VMT per Worker – weekday VMT generated by each worker for trips to or from the workplace and the worker’s home.1
Home-based work VMT includes only vehicle trips directly between work and home or home and work.2
The second false claim is that I ignored carpool, transit, bike and walk trips (DFEIR, p. 2-1012) which are clearly accounted for on page 7 of my May letter.
Despite the DFEIR providing no evidence that the model can accurately estimate average commute distances, it assumes that the model can magically account for the unusual characteristics of the workforce for the proposed project. The DFEIR states:
The calculation of work VMT per employee is based on the residential location of the worker and the mode split of the employee travel to the Project Site. There is nothing in the calculation of work VMT per employee that is affected by the length of the employee’s tenure on-site. The regional travel demand forecast model used to predict the geographic distribution of Project employees takes into account the regional distribution of both residential and employment land uses and estimates the most likely distribution of employees based on the regional pattern of employment opportunities.
Accordingly, the calculation of work VMT is made independent of the temporary vs. short-term vs. permanent employment status. (DFEIR, p. 2-1030) Yes, this excerpt describes a problem that I raised in my comments – that the VMT estimate does not consider whether short-term employees might have longer average commutes than
1 Mila, Ronald, Fehr and Peers. VMT in CEQA: Changes in Transportation Analysis. Presented to Town of Los Gatos, October 8, 2019
2 Fehr and Peers. SB 743 Implementation Decisions – Prepared for City/County of Governments (C/CAG) of San Mateo County and its Member Agencies, p. 15. September 29, 2021. 3 permanent employees. As the model cannot assess this issue, analysis must be done outside the model.
In my previous comments, I stated:
The project’s greenhouse gas (“GHG”) emissions are also underestimated in the DEIR. The number of daily vehicle trips assumed in the air quality analysis is less than the number of trips reported in the transportation analysis. The default average trip lengths used in the air quality analysis are lower than the distances calculated from Census data. After VMT is calculated correctly, the GHG analysis should be redone with the corrected VMT.
The DFEIR addresses the first part of this comment by making a small adjustment in CalEEMod (DFEIR, Table 4.7-2, p. 2-1032) to make the number of trips consistent between the transportation and air quality analyses, but the second part of the comment is not addressed. The VMT underestimation translates directly to underestimated emissions, including greenhouse gas emissions.
Sincerely,
Norman L. Marshall
4 Resume
NORMAN L. MARSHALL, PRESIDENT
[email protected]
EDUCATION:
Master of Science in Engineering Sciences, Dartmouth College, Hanover, NH, 1982 Bachelor of Science in Mathematics, Worcester Polytechnic Institute, Worcester, MA, 1977 PROFESSIONAL EXPERIENCE: (32 Years, 18 at Smart Mobility, Inc.) Norm Marshall helped found Smart Mobility, Inc. in 2001. Prior to this, he was at RSG for 14 years where he developed a national practice in travel demand modeling. He specializes in analyzing the relationships between the built environment and travel behavior and doing planning that coordinates multi-modal transportation with land use and community needs.
Regional Land Use/Transportation Scenario Planning
Portland Area Comprehensive Transportation System (PACTS) – the Portland Maine Metropolitan Planning Organization. Updating regional travel demand model with new data (including AirSage), adding a truck model, and multiclass assignment including differentiation between cash toll and transponder payments.
Loudoun County Virginia Dynamic Traffic Assignment – Enhanced subarea travel demand model to include Dynamic Traffic Assignment (Cube). Model being used to better understand impacts of roadway expansion on induced travel.
Vermont Agency of Transportation-Enhanced statewide travel demand model to evaluate travel impacts of closures and delays resulting from severe storm events. Model uses innovate Monte Carlo simulations process to account for combinations of failures.
California Air Resources Board – Led team including the University of California in $250k project that reviewed the ability of the new generation of regional activity-based models and land use models to accurately account for greenhouse gas emissions from alternative scenarios including more compact walkable land use and roadway pricing. This work included hands-on testing of the most complex travel demand models in use in the U.S. today.
Climate Plan (California statewide) – Assisted large coalition of groups in reviewing and participating in the target setting process required by Senate Bill 375 and administered by the California Air Resources Board to reduce future greenhouse gas emissions through land use measures and other regional initiatives.
Chittenden County (2060 Land use and Transportation Vision Burlington Vermont region) – led extensive public visioning project as part of MPO’s long-range transportation plan update.
Flagstaff Metropolitan Planning Organization – Implemented walk, transit and bike models within regional travel demand model. The bike model includes skimming bike networks including on-road and off-road bicycle facilities with a bike level of service established for each segment.
Chicago Metropolis Plan and Chicago Metropolis Freight Plan (6-county region)— developed alternative transportation scenarios, made enhancements in the regional travel demand model, and used the enhanced 5 model to evaluate alternative scenarios including development of alternative regional transit concepts.
Developed multi-class assignment model and used it to analyze freight alternatives including congestion pricing and other peak shifting strategies.
Municipal Planning
City of Grand Rapids – Michigan Street Corridor – developed peak period subarea model including non- motorized trips based on urban form. Model is being used to develop traffic volumes for several alternatives that are being additional analyzed using the City’s Synchro model
City of Omaha - Modified regional travel demand model to properly account for non-motorized trips, transit trips and shorter auto trips that would result from more compact mixed-use development. Scenarios with different roadway, transit, and land use alternatives were modeled.
City of Dublin (Columbus region) – Modified regional travel demand model to properly account for non- motorized trips and shorter auto trips that would result from more compact mixed-use development. The model was applied in analyses for a new downtown to be constructed in the Bridge Street corridor on both sides of an historic village center.
City of Portland, Maine – Implemented model improvements that better account for non-motorized trips and interactions between land use and transportation and applied the enhanced model to two subarea studies.
City of Honolulu – Kaka’ako Transit Oriented Development (TOD) – applied regional travel demand model in estimating impacts of proposed TOD including estimating internal trip capture.
City of Burlington (Vermont) Transportation Plan – Led team that developing Transportation Plan focused on supporting increased population and employment without increases in traffic by focusing investments and policies on transit, walking, biking and Transportation Demand Management.
Transit Planning
Regional Transportation Authority (Chicago) and Chicago Metropolis 2020 – evaluated alternative 2020 and 2030 system-wide transit scenarios including deterioration and enhance/expand under alternative land use and energy pricing assumptions in support of initiatives for increased public funding.
Capital Metropolitan Transportation Authority (Austin, TX) Transit Vision – analyzed the regional effects of implementing the transit vision in concert with an aggressive transit-oriented development plan developed by Calthorpe Associates. Transit vision includes commuter rail and BRT.
Bus Rapid Transit for Northern Virginia HOT Lanes (Breakthrough Technologies, Inc and Environmental Defense.) – analyzed alternative Bus Rapid Transit (BRT) strategies for proposed privately-developing High Occupancy Toll lanes on I-95 and I-495 (Capital Beltway) including different service alternatives (point-to-point services, trunk lines intersecting connecting routes at in-line stations, and hybrid).
Roadway Corridor Planning
I-30 Little Rock Arkansas – Developed enhanced version of regional travel demand model that integrates TransCAD with open source Dynamic Traffic Assignment (DTA) software, and used to model I-30 alternatives.
Freeway bottlenecks are modeled much more accurately than in the base TransCAD model. 6 South Evacuation Lifeline (SELL) – In work for the South Carolina Coastal Conservation League, used Dynamic Travel Assignment (DTA) to estimate evaluation times with different transportation alternatives in coastal South Caroline including a new proposed freeway.
Hudson River Crossing Study (Capital District Transportation Committee and NYSDOT) – Analyzing long term capacity needs for Hudson River bridges which a special focus on the I-90 Patroon Island Bridge where a microsimulation VISSIM model was developed and applied.
PUBLICATIONS AND PRESENTATIONS (partial list)
DTA Love: Co-leader of workshop on Dynamic Traffic Assignment at the June 2019 Transportation Research Board Planning Applications Conference.
Forecasting the Impossible: The Status Quo of Estimating Traffic Flows with Static Traffic Assignment and the Future of Dynamic Traffic Assignment. Research in Transportation Business and Management 2018.
Assessing Freeway Expansion Projects with Regional Dynamic Traffic Assignment. Presented at the August 2018 Transportation Research Board Tools of the Trade Conference on Transportation Planning for Small and Medium Sized Communities.
Vermont Statewide Resilience Modeling. With Joseph Segale, James Sullivan and Roy Schiff. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
Assessing Freeway Expansion Projects with Regional Dynamic Traffic Assignment. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
Pre-Destination Choice Walk Mode Choice Modeling. Presented at the May 2017 Transportation Research Board Planning Applications Conference.
A Statistical Model of Regional Traffic Congestion in the United States, presented at the 2016 Annual Meeting of the Transportation Research Board.
MEMBERSHIPS/AFFILIATIONS
Associate Member, Transportation Research Board (TRB)
Member and Co-Leader Project for Transportation Modeling Reform, Congress for the New Urbanism (CNU)
SCOPE SCOPE SCOPE SCOPE
Santa Clarita Organization for Planning and the Environment
TO PROMOTE, PROTECT AND PRESERVE THE ENVIRONMENT, ECOLOGY
AND QUALITY OF LIFE IN THE SANTA CLARITA VALLEY
POST OFFICE BOX 1182, SANTA CLARITA, CA 91386
www.scope.org
7-12-23
Erika Iverson, Planning
City of Santa Clarita
23920 Valencia Blvd.
Santa Clarita, CA 91355
Sent via email to [email protected]
Re: Newhall Studio Project 21-109 draft FEIR initial comments Please copy to all members of the Planning Commission
Dear Ms. Iverson and Planning Commission Members
SCOPE is a planning and conservation non-profit group now celebrating its 35 th year of work in the Santa Clarita Valley.
These comments are made on the FEIR for this project. We continue to assert that the DEIR is inadequate in several areas. Our concerns were not addressed in the response to comments as detailed below.
The draft FEIR has added new and substantive revisions to the “Final EIR” as “error” or an “inadvertent omission” from the DEIR. This seems to be an attempt to circumvent the recirculation of the EIR. We request that an additional hearing beyond the July 18 th hearing be
added and the EIR recirculated to include such important deficiencies as leaving out the So. Cal.
Mountain lion along with its usage of the Placerita Creek as a wildlife corridor.
Overall Inadequacy of the DEIR.
The purpose of an EIR is to inform the public and its responsible officials of the environmental consequences of decisions before they are made. (Laurel Heights Improvement Assn. v. Regents of University of California (1993) 6 Cal.4th 1112 , 1123, 26 Cal.Rptr.2d 231, 864 P.2d 502.)
The Notice of Preparation for this lists many areas of concern and finds the majority of them as potentially significant (see Appendix A). CEQA requires that each area of significance be analyzed so that mitigation can be ascertained. Instead this EIR for the most part (with the exception of biological, tribal and paleontological impacts) found major impacts described by the community and agencies to be non-existent. We re-iterate, this is absurd on its face. A huge 24/7 industrial project that will require some 2500 parking spaces, massively increase the allowable building heights beyond current City Standards in an area that is currently vacant land will have a major impact on noise, light, aesthetics, traffic, GHG and air quality as well as other areas.
By failing to inform the public, as required by law, and provide mitigation measures, it deprives the public and decision makers of the assurance that proposed improvements will really come to pass.
General Plan Inconsistency
Our General Plan was updated in 2012. It did not include a large industrial project on this property, but instead the area is zoned for the much-needed housing. Thus, a general plan
SCOPE Comments on Project 21-109 Page 2
amendment is needed. Therefore, this project is not currently consistent with our General Plan.
However, the document brazenly states multiple times that is consistent in all areas even though it will not be consistent until numerous permits to allow this inconsistency are granted. This constitutes a failure to disclose the real and major impacts of this proposal.
The response to this comment is that all that is needed to build studios is a conditional use permit. Even the draft FEIR contradicts this statement on page 1-2 where it describes the number of planning approvals that will be necessary to approve this project.
Further, an industrial building is NOT a mixed-use development. According to the City Codes the MNX zone is defined thus: “This zone is intende d for mixed use development, which is encouraged in order to create neighborhoods that integrate residential uses with complementary commercial services, including retail and office uses.” 1 Where are the residential uses? This
project is NOT an MNX qualified project as it contains no housing. It is a commercial project. A plan amendment to commercial is needed to comply with the General Plan.
Inconsistency with emergency planning required in the Circulation Plan - Fire Evacuation
o Objective C 2.5: Consider the needs for emergency access in transportation planning. Policy C 2.5.2: Ensure that new development is provided with adequate emergency and/or secondary access for purposes of evacuation and emergency response; require two points of ingress and egress for every subdivision or phase thereof, except as otherwise approved for small business subdivisions where physical constraints preclude a second access point.
Threshold 4.8(g): Expose people or structures, either directly or indirectly, to a significant risk of loss, injury or death involving wildland fires.
The response to comments states “As discussed in Response to Comment No. O8-25, the Draft EIR included an FPP that evaluated the Project’s po tential to ignite new fires and an extensive evacuation modeling analysis that accounted for Project employees and existing adjacent residents (see Appendix N of the Draft EIR)” There is no stated evacuation Plan in Appendix N.
This section describes hazard reduction, but not a plan of how people would be moved out of the area. It does evaluate various times for evacuation of the area as defined as being bounded by the area south of Parvin Drive on the north, In general, the Evacuation Shed is bounded by the area south of Parvin Drive on the north, Quigley Canyon Road and Melody Movie Ranch on the east, The Master’s University campus and Placerita Canyon Road on the south, and Railroad Avenue on the west” and “assumed that this evacuation she d would require a total of 1,340 cars to evacuate the area based on one vehicle per dwelling unit plus vehicles associated with students and faculty/staff at The Master’s University.”
2 First, no map is included for this area, so it is indeterminable whether “bounded by” means “including” or “adjacent to”. Second, the 2500 cars and additional vehicles on the site are not included in this evaluation. Third, the evaluation included only half of Placerita Canyon. It seems to assume that half the Canyon will evacuate in a different direction. This will not be possible if a fire sweeps in from the east, moving west through the canyon.
1 17.35.020 Mixed Use Neighborhood (MXN) Zone
2 Gibson Report, Appendix N
SCOPE Comments on Project 21-109 Page 3
Thus, we continue to assert that:
The EIR must describe an evacuation plan for its employees and the existing adjacent residents. This is a deficiency. It is also inconsistent with the General Plan.
This Plan is inconsistent with the Open Space and Conservation Element of the General Plan. The combined Conservation and Open Space Element establishes a policy framework for the designation and long-term preservation of open space within the planning area and addresses community benefits derived from open space, such as providing land for park and recreational facilities, habitat preservation, scenic views, and water recharge and watershed protection. The Conservation and Open Space Element states that rivers and streams located within the valley’s canyons “provide scenic visual relief from urbanization”. Placerita Creek transects the northern portion of the Project Site, and is a tributary to the south fork of the Santa Clara River. It’s floodplain also provides ground water recharge and a wildlife corridor for animals to access the Santa Clara River, and a major wildlife connection between the San Gabriel, Santa Susana and San Padres mountain ranges which the DEIR failed to discuss and to mitigate impacts on it.3
The response to our comments was that we provided no proof. The plain meaning and definition of the open space element and the fact the Placerita Creek is a creek, speaks for itself as a fact. Further, the Biology section of the DEIR should have monitored animal movement along Placerita Creek. It failed to do so.
Greenhouse Gases and Climate Change
The EIR fails to acknowledge or discuss the City’s 2012 Climate Action Plan that requires returning to a baseline 0f 2006 emissions.
The response to this statement was that the developer did not have to abide by the CAP because the planning cycle ended in 2020. While the City has not updated its Plan to extend it beyond 2020, that does not mean that the developer is not required to abided by it. Further, the Plan requires an additional 12% reduction in GHG for any projects that were not in the original 2021 CAP. This project was not in the 2012 CAP Therefore GHS emissions must be reduced an additional 13% to comply with the Plan.
Failure to Provide a Real Project Alternatives
During the staff report for the June 20 th meeting, starting at approximately minute 22 of the meeting recording, staff member Erica Iverson, made the statement that Alternative 3 would not really reduce impacts as it was purported to do in the DEIR, that it was only there as a pro forma requirement of CEQA. We ask that the DEIR include real and viable alternatives for the decisionmakers and the public to review as required by law.
Conclusion
As the courts have explained , a prejudicial abuse of discretion occurs “if the fa ilure to include relevant information precludes informed decision-making and informed public participation, thereby thwarting the statutory goals of the EIR process.” 4 An inadequate under DEIR under
3 Mitigation must include setbacks, riparian re—vege tation for cover, light glare reduction, and any other mitigation that the Fish and Wildlife Dept. would suggest.
4 Berkeley Jets , 91 Cal.App.4th at p. 1355; see also San Joaquin Raptor/Wildlife Rescue Center v.
County of Stanislaus (1994) 27 Cal.App.4th 713, 722 (error is prejudicial if the failure to include relevant information precludes informed decision ma king and informed public participation, thereby SCOPE Comments on Project 21-109 Page 4
CEQA must be revised to provide legally adequate analysis of, and mitigation for, all of the Project’s potentially significant impacts. These revisions will necessarily require that the DEIR be recirculated for additional public review. Until the DEIR has been revised and recirculated, to address the insufficiencies described in our May 22 letter and this correspondence, along with those described by others which we hereby incorporate by reference, the City may not lawfully approve the Project.
Thank you for your careful evaluation of this matter.
Sincerely,
Lynne Plambeck,
thwarting the statutory goals of the EIR process); Galante Vineyards , 60 Cal.App.4th at p. 1117 (decision to approve a project is a nullity if based upon an EIR that does not provide decision-makers and the public with information about the project a s required by CEQA); County of Amador v. El Dorado County Water Agency (1999) 76 Cal.App.4th 931, 946 (prejudicial abuse o f discretion results where agency fails to comply with information discl osure provisions of CEQA). 1 F r i e n d s o f t h e S a n t a C l a r a R i v e r PO Box 7713Ventura, California 93006 (805) 628-2250 www.fscr.org
7-12-23
Erika Iverson, Planning
City of Santa Clarita
23920 Valencia Blvd.
Santa Clarita, CA 91355
Sent via email to [email protected]
Re: Newhall Studio Project 21-109 FEIR comments
Please copy to all members of the Planning Commission
Dear Ms. Iverson and Planning Commission Members
Friends of the Santa Clara River (FSCR) was formed in 1993 to provide public oversight and demand protection for the Santa Clara River and its tributaries. The Placerita Creek and its floodplain are tributaries to the Santa Clara River. Thus, we continue to participate in this process to advocate for the stewardship and preservation of the river and its water resources.
The Santa Clara River provides water supply and habitat for humans and other species, including many endangered and fully protected species, along its reaches. Without careful stewardship, these resources will not exist for future generations. We continue to have concerns that this project will significantly impact this important natural resource.
Inadequate Response to comments
The response to comments (pdf page 2-1039, 2-1039) claims that ARk storms and rainfall in excess of FEMA COLMAR letters 50 and 100 year floods don’t have to be addressed. Yet, as we stated, this area has already recently exceeded such rainfall years due to ARk storms (atmospheric rivers)
1 as predicted by USGS 2 to occur as a result of global warming. Please see local rainfall data provided by the LA Almanac 3 derived from data provided by the Western Regional Climate Center. ARk storms and atmospheric rivers cause excessive amounts of rainfall in specific locations and are not accounted for in FEMA 50 and 100 year flood predictions. The
1 An ARkStorm (for Atmospheric River 1,000) is a "megastorm" pro posed scenario based on repeated historical occurrences of atmospheric rivers and ot her major rain events first developed and published by the Multi-Hazards Demonstration Project (MHDP) of t he United States Geological Survey (USGS) in 2010 and updated as ARkStorm 2.0 in 2022
2 https://www.usgs.gov/centers/western-geographic-sc ience-center/science/arkstorm 3 http://www.laalmanac.com/weather/we134aa.php
2 floodplain of Placerita creek has acted to protect up and down stream residents from such new phenomena by allowing the creek to spread out across the flood plain.
Contrary to the response to comments stating that we provided no data to substantiate these statements, we included both references and diagrams. We provided a quote, along with reference documentation from the State Climatologist, Michael Anderson, Ph.D., P.E. at California Department of Water Resources Division of Flood Management who said 4:
“Variability in annual precipitation statewide and across the regions of the state has increased since the early 1980s, peaking in the late 1990s for most climate divisions (Figure 3) 5 (He & Guatam, 2016). This shows that dry and wet precipitation extremes have become more frequent.”
The US EPA has also reported that the best way to protect communities from flooding is to protect the floodplain 6, as indicated by the citation provided in our DEIR comments
We re-iterate our concern that the DEIR contains no study relating to loss of ground water re- charge, but only the conclusionary statement that that water will be returned to the creek and therefore, no significant impact will occur 7. We note that the creek area is substantially smaller than the 12 acres of flood plain and will therefore not be able to provide the same amount of groundwater recharge as the flood plain. Two other comment letters plus the comment letter from the Santa Clarita Valley Water Agency also raised this concern.
We therefore continue to assert that this EIR is deficient in its failure to asses loss of ground water recharge from impermeable surfaces and that a mitigation requirement to address this issue must be provided..
This project proposes to riprap and narrow the streambed (in violation of the Placerita Community Standards District). Yet we cannot know exactly how much this will affect the flood plain because no mapping of the jurisdictional waters has been provided in the DEIR. Again the DEIR and the response to comments makes the conclusionary statement that no significant impacts will occur. We do not agree. The CA Dept. of Fish and Wildlife, along with ourselves and several other commentors, noted this impact as being siggnificant, and suggested various mitigation proposals that might reduce such impacts. However, these comments weere ignored.
The Decifiencies in this EIR Require Re-noticing and Recirculation
The project proponent attempts to remedy some deficiencies (although not those indicated above) by providing new data in a section titled “ERRATA AND CLARIFICATIONS TO THE DRAFT EIR”. This section does not provide sufficient disclosure to address such important issues as the omission of certain species, including the mountain lion, failure to discuss the creek’s function as a wildlife corridor and substantial additional disclosure to the GHG section. These impacts should have been disclosed and discussed in the DEIR.
4 https://oehha.ca.gov/climate-change/report/2018-rep ort-indicators-climate-change-california , p.89 5 Ibid, https://oehha.ca.gov/climate-change/report/2018-rep ort-indicators-climate-change-california , https://oehha.ca.gov/media/epic/downloads/cc_precip itation2018.pdf 6 https://www.epa.gov/green-infrastructure/manage-fl ood-risk 7 DEIR, ES-19 and re-iterated in the FEIR as stated above. 3 CEQA requires public agencies to avoid or reduce environmental damage when “feasible” by requiring consideration of environmentally superior alternatives and adoption of all feasible mitigation measures. 8 The EIR serves to provide agencies and the public with information about the environmental impacts of a proposed project and to “identify ways that environmental damage can be avoided or significantly reduced.” 9 These important functions of CEQA, which protect both our environment and our communities, cannot be provided when a project proponent obfuscates or omits information regarding significant impacts, fails to disclose other impacts or tries to disclose them as “errata” in the FEIR. Significant impacts cannot be addressed and mitigated if they are not disclosed in the first place. The DEIR must be re-circulated, impacts must be adequately disclosed and real mitigation (not “project design features”), provided so the public can be assured that this project is the best it can be.
Thank you for your time and attention to these issues.
Sincerely,
James M. Danza, MS, AICP
Chair, Friends of the Santa Clara River
8 CEQA Guidelines § 15002(a)(2), (3); see also Berkeley Jets , 91 Cal.App.4th at 1354; Citizens of Goleta Valley , 52 Cal.3d at p. 564
9 CEQA Guidelines § 15002(a)(2).
P: (626) 314-3821
F: (626) 389-5414
E: [email protected]
Mitchell M. Tsai
Attorney At Law
139 South Hudson Avenue
Suite 200
Pasadena, California 91101
VIA E-MAIL
July 17, 2023
Erika Iverson
Planner
City of Santa Clarita
23920 Valencia Boulevard, Suite 302
Santa Clarita, CA 91355
Em: [email protected]
RE: City of Santa Clarita’s Shadowbox Studios FEIR Comment Letter Dear Erika Iverson,
On behalf of the Southwest Mountain States Regional Council of Carpenters (“Southwest Carpenters” or “SWMSRCC”), our office is submitting these comments for the City of Santa Clarita’s (the “City”) Shadowbox Studios project (the “Project”) and its Final Environmental Impact Report (“FEIR”), to be considered on the July 18, 2023 Planning Commissions hearing.
The Southwest Mountain States Carpenters is a labor union representing 63,000 union carpenters in 10 states, including California, and has a strong interest in well-ordered land use planning and in addressing the environmental impacts of development projects. Individual members of the Southwest Carpenters live, work, and recreate in the City and surrounding communities and would be directly affected by the Project’s environmental impacts.
The Southwest Carpenters expressly reserves the right to supplement these comments at or prior to hearings on the Project, and at any later hearing and proceeding related to this Project. California Government Code (“Gov. Code”) § 65009, subd. (b); Public Resources Code (“Pub. Res. Code”) § 21177, subd. (a); see Bakersfield Citizens for Local Control v. Bakersfield (2004) 124 Cal.App.4th 1184, 1199-1203; see also Galante Vineyards v. Monterey Water Dist. (1997) 60 Cal.App.4th 1109, 1121.
The Southwest Carpenters incorporates by reference all comments raising issues regarding the Project or its EIR submitted before the close of the public hearing on City of Santa Clarita – Shadowbox Studios Project
July 17, 2023