on January 16, 2015, and focuses on the biological impacts of the Project. This letter is supported by the comments of expert wildlife biologist, Dr. Shawn Smallwood, Ph.D. Dr. Smallwood’s comments are attached hereto and should be responded to separately. We incorporate by reference herein our letter dated January 16, 2015.
As discussed herein, after reviewing the Draft Environmental Impact Statement (“DEIS”) for the Project together with our expert consultants, it is evident that the document fails to comply with the California Environmental Quality Act, Public Resources Code § 21000 et seq. (“CEQA”), and contains numerous errors and omissions that continue to preclude accurate analysis of the Project.
As a result of these inadequacies, the DEIS fails as an informational document, fails to analyze all significant impacts of the Project, fails to identify and impose feasible mitigation measures to reduce the Project’s impacts, and fails to properly analyze Project alternatives and cumulative impacts.1 As a result, the Project will result in significant environmental impacts that have not been adequately addressed or mitigated as required by CEQA. LIUNA Local 1184 therefore requests that the Tribe and the City of Rancho Mirage (“City”) or the Riverside Local Agency Formation Commission (“LAFCO”) prepare and circulate a Supplemental Draft Environmental Impact Report (“SEIR”) to address the issues raised in this and other comments, and to require implementation of feasible mitigations and alternatives required by law.
1. The FEIR Fails to Adequately Analyze Impacts to Biological Resources.
It is the policy of the State of California to
Prevent the elimination of fish or wildlife species due to man’s activities, insure that fish and wildlife populations do not drop below self- perpetuating levels, and preserve for future generations representations of all plant and animal communities.
(Pub. Res. Code § 21001(c).) An EIR may not avoid studying impacts to biological resources by proposing future study or mitigation based on future studies unless the mitigation measures and performance standards are explicit in the DEIR. (San Joaquin Raptor Rescue Center v. County of Merced (2007) 149 Cal.App.4th 645, 671)
1 We reserve the right to supplement these comments at any later hearings and proceedings related to this Project. See Galante Vineyards v. Monterey Water Dist. (1997) 60 Cal. App. 4th 1109.
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As discussed by Dr. Smallwood, the DEIS fails to assess impacts to wildlife, especially sensitive species and plants. Where impacts are identified, the DEIS impermissibly relies on vague, unenforceable and deferred mitigation measures, most of which lack a foundation in science and performance standards. Consequently, the DEIS must be revised to reassess impacts to biological resources and, where appropriate, propose adequate mitigation measures with definite terms and verifiable performance standards.
a. The DEIS Fails to Describe Existing Conditions That are Necessary for a Reasonable Analysis of the Project’s
Potentially Significant Biological Impacts.
Dr. Smallwood concludes that the truncated wildlife surveys for the site ignore applicable protocols and fail to provide a proper baseline or describe the true environmental setting at the proposed Project site.
A CEQA document “must include a description of the environment in the vicinity of the project, as it exists before the commencement of the project, from both a local and a regional perspective.” (CEQA Guidelines § 15125; see Environmental Planning and Info. Council v. County of El Dorado (1982) 131 Cal.App.3d 350, 354.) This environmental setting will normally constitute the baseline physical conditions by which a Lead Agency determines whether an impact is significant.” (CEQA Guidelines § 15125.) Thus, the CEQA “baseline” is the set of environmental conditions against which to compare a project’s anticipated impacts. (Communities for a Better Environment v. So Coast Air Qual. Mgmnt. Dist. (2010) 48 Cal. 4th 310, 321.) Where a Project’s baseline is skewed by omissions or misrepresentations in the MND, it “mislead(s) the public” and “draws a red herring across the path of public input.” (San Joaquin Raptor Rescue Center v. County of Merced (2007) 149 Cal.App.4th 645, 656; Woodward Park Homeowners v. City of Fresno (2007) 150 Cal.App.4th 683, 708-711. See Save Our Peninsula Committee v. County of Monterey (2001) 87 Cal.App.4th 99, 121-23 (“the impacts of the project must be measured against the ‘real conditions on the ground,’” as opposed to hypothetical conditions).)
The failure of the DEIS and DEIS consultant to conduct wildlife surveys capable of accurately detecting burrowing owls, clapper rails, other birds of concern, or reptiles and amphibians provides no baseline in the DEIS or its attachments from which the public can evaluate potential impacts to wildlife.
Dr. Smallwood points out that a fundamental shortcoming of the DEIS is that it concludes that Section 24 is an “ecological island.” Dr. Smallwood points out this is a biased perspective to ignores the fact that “many animals can fly, walk, or crawl” on an off of the Project site. Furthermore, plant species exist on the site and successfully spread their seeds. The “ecological island” theory is 3 4
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contradicted by the plain fact that several special status species have been found on the site, including the Coachella Valley fringe-toed lizard, flat-tail horned lizard, burrowing owl, and Palm Springs ground squirrel.
Dr. Smallwood concludes that the biological surveys performed for the DEIS were inadequate and failed to conform with applicable guidance and protocols. For example, Dr. Smallwood points out that site surveys were conducted in February and March 2014, but this is a time when it is least likely to find special status species. Burrowing owls do not begin nesting until April. (Smallwood, p.3). Dr. Smallwood points out that the consultant smoothed surfaces of Section 24 and then concluded that there are no wildlife movement corridors on the site. Dr. Smallwood concludes that the soil smoothing changes animal behavior by eliminating markings that animals use to mark their paths. “Smoothing obliterates the markings of wildlife, and so disrupt the use of ‘corridors.’” (Smallwood, p.4). Thus, “The EIS had no foundation for concludes ‘no discrenable and routinely used corridors could be found.’” (Id.). Dr.
Smallwood points out that the DEIS used no accurate method for detecting bats.
Dr. Smallwood points out that desert tortoise surveys were conducted in February and March, but US Fish and Wildlife Service protocols require that surveys be conducted in April and May or September and October. Thus, the DEIS’ conclusion that desert tortoise was not found on the site lacks foundation.
The DEIS fails entirely to analyze the Project site’s importance as stop- over habitat for migratory birds.
As a result of these and other deficiencies identified by Dr. Smallwood, the DEIS fails to describe the existing environment of Section 24. A supplemental Draft EIS is necessary to accurately describe the Project site and the Project’s impacts on the existing environment.
b. The Project Has Adverse Environmental Impacts Not
Addressed in the DEIS.
Dr. Cashen concludes that the Project will have adverse impacts on wildlife movement corridors. Dr. Cashen states:
Section 24 represents a chokepoint to wildlife movement, so losing it to another residential project will block movement of wildlife along the northwest-southeast band of open spaces south of I-10. Converting Section 24 to urban housing will not only remove 577 acres of habitat of many wildlife species, but will also effectively remove the habitat capacity of at least 2,500 acres of acres of additional habitat southeast of Section
24. The additional impacts are readily apparent in Figure 1, and should not be ignored in the EIS.
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Figure 1. Google Earth imagery from 2012 shows the linkages of open space south of I-10, and how converting Section 24 (red boundary) to houses will eliminate the ability of terrestrial wildlife to move (orange arrows) into and out of >2,500 acres of open space.
This impact must be analyzed and mitigated in a supplemental DEIS.
c. The Project Has Significant Cumulative Impacts.
Dr. Smallwood points out that the DEIS contains essentially no cumulative impacts analysis – devoting a mere 19 lines of text to the subject. Dr. Smallwood concludes that the Project will have significant cumulative impacts related to habitat fragmentation together with other ongoing, proposed or likely future projects in the area. For example, Dr. Smallwood points out that according to the Desert Renewable Energy Conservation Plan (“DRECP”), 330,000 acres are likely to be converted to solar, wind, geothermal, distributed energy and transmission projects with the Mojave Desert in the near future. Dr. Smallwood concludes that the Project, together with these cumulative projects, “would eliminate most of the remaining population of burrowing owls in California, as well as large proportions of the remaining populations of desert tortoise, Coachella Valley fringe-toed lizard, flat-tail horned lizard, and Palm Springs ground squirrel, among many other special-status species.” (Smallwood, p. 6).
An EIR must discuss significant cumulative impacts. CEQA Guidelines section 15130(a). This requirement flows from CEQA section 21083, which requires a finding that a project may have a significant effect on the environment 11 12
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if “the possible effects of a project are individually limited but cumulatively considerable. . . . ‘Cumulatively considerable’ means that the incremental effects of an individual project are considerable when viewed in connection with the effects of past projects, the effects of other current projects, and the effects of probable future projects.” “Cumulative impacts” are defined as “two or more individual effects which, when considered together, are considerable or which compound or increase other environmental impacts.” CEQA Guidelines section 15355(a). “[I]ndividual effects may be changes resulting from a single project or a number of separate projects.” CEQA Guidelines section 15355(a).
“The cumulative impact from several projects is the change in the environment which results from the incremental impact of the project when added to other closely related past, present, and reasonably foreseeable probable future projects. Cumulative impacts can result from individually minor but collectively significant projects taking place over a period of time.” Communities for a Better Environment v. Cal. Resources Agency (“CBE v. CRA”), (2002) 103 Cal.App.4th 98, 117. A legally adequate cumulative impacts analysis views a particular project over time and in conjunction with other related past, present, and reasonably foreseeable probable future projects whose impacts might compound or interrelate with those of the project at hand. “Cumulative impacts can result from individually minor but collectively significant projects taking place over a period of time.” CEQA Guidelines § 15355(b).
As the court stated in CBE v. CRA, 103 Cal. App. 4th at 114:
Cumulative impact analysis is necessary because the full environmental impact of a proposed project cannot be gauged in a vacuum. One of the most important environmental lessons that has been learned is that environmental damage often occurs
incrementally from a variety of small sources. These sources appear insignificant when considered individually, but assume threatening dimensions when considered collectively with other sources with which they interact.
(Citations omitted).
In Kings County Farm Bureau v. City of Hanford, 221 Cal.App.3d at 718, the court concluded that an EIR inadequately considered an air pollution (ozone) cumulative impact. The court said: “The [ ] EIR concludes the project’s contributions to ozone levels in the area would be immeasurable and, therefore, insignificant because the [cogeneration] plant would emit relatively minor amounts of [ozone] precursors compared to the total volume of [ozone] precursors emitted in Kings County. The EIR’s analysis uses the magnitude of the current ozone problem in the air basin in order to trivialize the project’s impact.” The court concluded: “The relevant question to be addressed in the EIR 13 2.0 Responses to Comments
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is not the relative amount of precursors emitted by the project when compared with preexisting emissions, but whether any additional amount of precursor emissions should be considered significant in light of the serious nature of the ozone problems in this air basin.”2 The Kings County case was recently reaffirmed in CBE v. CRA, 103 Cal.App.4th at 116, where the court rejected cases with a narrower construction of “cumulative impacts.”
Similarly, in Friends of Eel River v. Sonoma County Water Agency, (2003) 108 Cal. App. 4th 859, the court recently held that the EIR for a project that would divert water from the Eel River had to consider the cumulative impacts of the project together with other past, present and reasonably foreseeable future projects that also divert water from the same river system. The court held that the EIR even had to disclose and analyze projects that were merely proposed, but not yet approved. The court stated, CEQA requires “the Agency to consider ‘past, present, and probable future projects producing related or cumulative impacts . . . .’ (Guidelines, § 15130, subd. (b)(1)(A).) The Agency must interpret this requirement in such a way as to ‘afford the fullest possible protection of the environment.’” Id., at 867, 869. The court held that the failure of the EIR to analyze the impacts of the project together with other proposed projects rendered the document invalid. “The absence of this analysis makes the EIR an inadequate informational document.” Id., at 872.
The court in Citizens to Preserve the Ojai v. Bd. of Supervisors, 176 Cal.App.3d 421 (1985), held that an EIR prepared to consider the expansion and modification of an oil refinery was inadequate because it failed to consider the cumulative air quality impacts of other oil refining and extraction activities combined with the project. The court held that the EIR’s use of an Air District Air Emissions Inventory did not constitute an adequate cumulative impacts analysis.
The court ordered the agency to prepare a new EIR analyzing the combined impacts of the proposed refinery expansion together with the other oil extraction projects.
The DEIS contains no list of cumulative past, present and reasonably foreseeable future projects, and contains no legally sufficient cumulative impact analysis. A supplemental DEIS is required to analyze the Project’s cumulative impacts and to propose feasible mitigation.
2 Los Angeles Unified v. City of Los Angeles, 58 Cal.App.4th at 1024-1026 found an EIR inadequate for concluding that a project's additional increase in noise level of another 2.8 to
3.3 dBA was insignificant given that the existing noise level of 72 dBA already exceeded the regulatory recommended maximum of 70 dBA. The court concluded that this "ratio theory" trivialized the project's noise impact by focusing on individual inputs rather than their collective significance. The relevant issue was not the relative amount of traffic noise resulting from the project when compared to existing traffic noise, but whether any additional amount of traffic noise should be considered significant given the nature of the existing traffic noise problem. 13 2.0 Responses to Comments
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d. The DEIS Relies on Legally Inadequate Mitigation
Measures.
Dr. Smallwood points out that the DEIS relies on legally and factually inadequate mitigation measures for the Project’s biological impacts. The primary mitigation measure is a payment to the Tribal Habitat Conservation Plan (THCP) in the amount of $2371 per disturbed acre. This mitigation measure is inadequate as a matter of law.
First, the US Fish and Wildlife Service has not yet approved the THCP. (DEIS p.2.0-23). Therefore, there can be no assurance that the THCP is adequate to mitigate Project impacts, and no calculation of the appropriate fee that would be required for mitigation. The DEIS may not rely on an unapproved TCHP as mitigation.
Second, mitigation fees are generally not adequate mitigation, unless specific measures are identified that will be paid for and implemented by the fee.
The DEIS fails to identify any specific measures. Measures may include such things as conservation easements, creation of off-site habitat, or other measures, but the DEIS fails to identify any specific measures. This renders the mitigation legally inadequate. Mitigation fees are not adequate mitigation unless the lead agency can show that the fees will fund a specific mitigation plan that will actually be implemented in its entirety. Napa Citizens for Honest Gov. v. Bd. Of Supervisors (2001) 91 CallApp.4th 342 (no evidence that impacts will be mitigated simply by paying a fee); Anderson First Coal. v. City of Anderson (2005) 130 Ca.App.4th 1173 (traffic mitigation fee is inadequate because it does not ensure that mitigation measure will actually be implemented); Kings Co. Farm Bureau v. Hanford (1990) 221 Cal.App.3d 692. But see, Save Our Peninsula Comm v. Monterey Co. (2001) 87 Cal.App.4th 99 (mitigation fee allowed when evidence in the record demonstrates that the fee will fund a specific mitigation plan that will actually be implemented in its entirety). In California Native Plant Society v. County of El Dorado et al. (2009) 170 Cal. App. 4th 1026, the court held that the fee program had to have gone through CEQA review for an agency to say that the payment of the fee alone is adequate CEQA mitigation.
Third, the mitigation fee constitutes a prohibited deferred mitigation measure. CEQA requires the specific mitigation measures to be set forth in the DEIR, so that the public may review and comment on the measures. The DEIS fails to identify any specific measures to mitigate the Project’s biological impacts.
While a payment amount is identified, the DEIS fails to identify any specific measures that will be implemented with this fee. Any specific measures will be developed at a later time. This constitutes improper deferred mitigation. Deferral of mitigation measures is prohibited under CEQA:
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Page I of I
By adopting the condition that applicant would comply with environmental standards for sludge disposal, the County effectively removed this aspect of the project from environmental review, trusting that the Regional Water Quality Control Board and the applicant would work out some solution in the future..... Having no "relevant data" pointing to a solution of the sludge disposal problem, the County evaded its duty to engage in a comprehensive environmental review by approving the use permit subject to a condition requiring future regulatory compliance. Sundstrom,202 Cal.App.3d at 309.
[R]eliance on tentative plans for future mitigation after completion of the CEQA process significantly undermines CEQA's goals of full disclosure and informed decisionmaking; and[,] consequently, these mitigation plans have been overturned on judicial review as constituting improper deferral of environmental assessment. Communities for a Better Environment v.
City of Richmond (2010) 184 Cal.App.4th at 92.
Fourth, the burrowing owl mitigation measure fails to comply with applicable guidance. MM 5.3-2 requires pre-construction surveys for burrowing owls 30 days prior t construction. However, the California Department of Fish and Game (2012) requires burrowing owl surveys 15 days prior to construction. CDFG also recommends 500 meler buffer zones between owl burrows and construction areas. The DEIS fails to incorporate these measures. The DEIS therefore fails to impose all feasible mitigation measures.
CONCLUSION
LIUNA Local Union No. 1184 believes the DEIS is legally inadequate and requires significant revision, recirculation and review. Thank you for your attention to these comments. Please include this letter and all attachments hereto in the record of proceedings for this project.
Richard T. Drury
Lozeau Drury LLP
Attorneys for Laborers'
North America (LIUNA),
lnternational Union of
Local Union No. 11 84
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K. Shawn Smallwood, Ph.D.
3108 Finch Street
Davis, CA 95616
Margaret Park, AICP
Director of Planning and Natural Resources
Agua Caliente Band of Cahuilla Indians
5401 Dinah Shore Drive
Palm Springs, CA 92264
City of Rancho Mirage
Mayor Iris Smotrich
And Honorable Member of the Rancho Mirage City Council Cindy Scott, City Clerk Steven B. Quintanilla, City Attorney Bud Kopp, Planning Manager, Rancho Mirage City Hall
69-825 Highway 111
Rancho Mirage, CA 92270
Riverside Local Agency Formation Commission
3850 Vine St, Suite 240
Riverside, CA. 92507-4277 19 January 2015
RE: Draft Environmental Impact Statement for the Proposed Section 24 Specific Plan Agua Caliente Band of Cahuilla Indians (SCH No. 2014011035)
Dear Ms. Park, Mayor Smotrich and Riverside Local Agency Formation Commission,
I write to comment on the Draft Environmental Impact Statement for the Proposed Section 24 Specific Plan Agua Caliente Band of Cahuilla Indians (“EIS”) (Meridian Consultants 2014). I have reviewed the biological resources section of the EIS and the supporting report on biological resources (Cornett 2014).
My education and experience are as follows. I earned a Ph.D. degree in Ecology from the University of California at Davis in 1990. Subsequently I worked at U.C. Davis for four years as a post-graduate researcher in the Department of Agronomy and Range Sciences. My research has been focused on animal density and distribution, habitat selection, habitat restoration, interactions between wildlife and human infrastructure and activities, conservation of rare and endangered species, and the ecology of invading species. I have authored numerous papers on special-status species issues, including “Using The Best Scientific Data For Endangered Species Conservation,” published in Environmental Management (Smallwood et al. 1998), and “Suggested Standards For Science Applied To Conservation Issues” published in the Transactions of the Western Section of The Wildlife Society (Smallwood et al. 2001). I served as Chair of the Conservation Affairs Committee for The Wildlife Society – Western Section. I am a member of The Wildlife Society and the Raptor Research Foundation, and I was a part- time lecturer at California State University, Sacramento. I was also Associate Editor of 16 2.0 Responses to Comments
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wildlife biology’s premier scientific journal, The Journal of Wildlife Management, as well as of Biological Conservation, and I was on the Editorial Board of Environmental Management.
I have performed numerous surveys for special-status species over the last 25 years, including 11 years of surveys for California red-legged frog and California tiger salamander, and 14 years for Fresno kangaroo rat, several years for salt marsh harvest mouse and California clapper rail, 16 years for burrowing owl, and 25 years for Swainson’s hawk and white-tailed kite. Based on my education and field experience, I am familiar with the ecology and habitat of wildlife species likely to occur on the project site. My CV is attached.
IMPACTS ASSESSMENT
The EIS addressed the potential impacts of converting 577 acres of plant and wildlife habitat to residential use. This 577-acre area is one of the last open spaces south of Interstate 10 in the Coachella Valley, in a region known for high species richness.
Therefore, it is important that the EIS carefully and comprehensively considers the potential project impacts and mitigation. However, this EIS inadequately described the current environmental setting, and its impact assessments and mitigation measures fell far short of what was needed.
Under CEQA,1 “[A] paramount consideration is the right of the public to be informed in such a way that it can intelligently weigh the environmental consequences of any contemplated action and have an appropriate voice in the formulation of any decision.” The public needs information that is thorough, relevant, unbiased, and honest; the public needs full disclosure of the environmental setting and possible cumulative impacts. Documents presenting information from a biased perspective will tend to include omissions, logical fallacies, internal contradictions, and unfounded responses to substantial issues. Therefore, my assessment of the EIS and of Cornett (2014) also considers omissions and bias, which bear on the sufficiency of the EIS.
As an example of bias, Cornett (2014:10) described the project site as “…nearly an ecological island bounded on all four sides by paved roadways (three of them carrying high volumes of traffic) and on two sides by residential developments.” This characterization might apply to some unnamed species that cannot cross a road, but for most animal and plant species the roadways probably do not isolate the habitat on the project site; many animals can fly, walk, or crawl across, alth0ugh many undoubtedly die in the attempt, but they also carry and disperse plant seeds and life does continue on Section 24 despite the roads. The implication of Cornett’s unfortunate site characterization is that the site is a throw-away site in terms of the local ecological resources, and so biological surveys need not consist of anything more than the cursory
1 Environmental Planning and Information Council vs. County of El Dorado (1982) 131 Cal. App. 3d 350, 354.
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surveys that were performed and satisfactory mitigation can be achieved mostly by paying a fee into a habitat conservation plan that has yet to be approved.
In fact, Section 24 is not an ecological island. If it was an ecological island, then special- status species, such as Coachella Valley fringe-toed lizard, flat-tail horned lizard, burrowing owl, and Palm Springs ground squirrel, would not have been found on site.
These species, and probably other special-status species as well, persist on the site, despite the near complete conversion of habitat to residential and commercial uses within the Coachella Valley south of Interstate 10. Had adequate surveys been performed, additional special-status species probably would have been found.
The biological surveys performed on the proposed project site were inadequate. Site visits were made by Cornett and Walter Millin for unreported periods of time on 19 days during February and March 2014, and during two nights in February (presumably involving the mammal live-traps). Cornett and Millin walked along east-west transects at 10-yard intervals during a small portion of a single season of a single year, and this time of year was, in my experience, the least likely to detect special-status species.
Burrowing owls behave cryptically during this time of year, and so are difficult to detect.
Burrowing owls do not begin nesting until April. Other special-status species are typically aestivating during this time of year. And during this time of year, migrating birds are generally not on the move.
Besides these pedestrian transects, Cornett and Millin also set 25 mammal live-traps on two nights for a mere 50 trap-nights, although the number of effective trap nights was not reported, nor were the locations of the traps or any report of trapping methods, capture success or trap mortality. The trap coverage averaged 23 acres per trap (577 acres ÷25 traps) and 0.5% of a year, and so grossly under-sampled Section 24.
Cornett (2014) monitored roadkill on roads bordering Section 24 to assess whether the site is used as a movement corridor. However, Cornett provided no details on how the roadkill surveys were performed or what was found. Without methods and results, these alleged surveys were meaningless. Furthermore, February and March is not when roadkill should be used to inform about mammalian or reptilian travel patterns. I have performed thousands of miles of roadkill surveys since 1989, so I can testify with ample confidence that most of the mammals killed by cars are killed during fall, which is the peak of dispersal and migration. There should also be lower reptile activity during February and March.
Finally, Cornett (2014) smoothed soil surfaces on portions of Section 24 to record animal tracks as a means of determining whether the site includes wildlife movement corridors. Cornett (2014) provided no details of how much area was smoothed, or in what orientation or shape the soil was smoothed. No results were reported, either.
Having developed tracking techniques since 1985, and having performed many research studies and surveys involving track counts, I can testify with ample confidence that soil smoothing changes the behaviors of the animals under survey. Wildlife that use trails or that develop routine travel routes also mark their travel paths with scent glands associated with scrapes, scats, and urine. Smoothing obliterates the markings of 18 19
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wildlife, and so disrupt the use of “corridors.” Smoothing is the last thing I would do if I was interested in detecting travel paths or corridors. The EIS (page 5.3-9) had no foundation for concluding “…no discernable and routinely used corridors could be found.”
Despite the extremely cursory nature of the surveys, Cornett (2014) detected multiple special-status species. More special-status species likely would have been detected had surveys been performed during other times of year, or had surveys been performed off site (No off-site surveys due to private property restrictions), or had surveys involved methods appropriate for the species. For example, pedestrian surveys and mammal live-trapping are unsuited for detecting bats. Bat surveys need to be performed using acoustic detectors or thermal cameras. Until appropriate surveys are performed, it is indefensible to conclude that only two species of bat potentially use Section 24. I have yet to encounter any place in California that hosts only two species of bat.
As another example, bird species will remain underrepresented until point counts are performed, and until they are performed over each season of the year. Point counts have been the standard method for detecting birds for about a century. Walking back and forth across a site is not the standard method for detecting most birds. Therefore, there was no foundation for Cornett’s (2014:13) conclusion, “In spite of severe long- term drought, it was concluded that this phenomenon did not impact the findings in this report because of evidence of sensitive species that was discovered and historical information regarding the biota of the project site.” Other than the species detections that were made despite the extremely cursory nature of the surveys, there was no support for determining that undetected species are absent from the site, and absolutely no support for making any determination about the impacts of the drought on Cornett’s findings.
According to Cornett 2014:17, “…the California Natural Diversity Database (March, 2014) has no records of the tortoise on or within one mile of the project site.” If this is the sort of historical information that Cornett referred to, as summarized in the previous paragraph, then it was unreliable. The California Natural Diversity Database (“CNDDB”) is not a scientific sampling or monitoring program; it is strictly voluntary in the reporting of special-status species by consulting and research biologists. It is inappropriate to use lack of records in CNDDB to support a conclusion that a species is absent from a site. To help get this message across, the California Department of Fish and Wildlife posts a disclaimer on its CNDDB web site: “We work very hard to keep the CNDDB and the Spotted Owl Database as current and up-to-date as possible given our capabilities and resources. However, we cannot and do not portray the CNDDB as an exhaustive and comprehensive inventory of all rare species and natural communities statewide. Field verification for the presence or absence of sensitive species will always be an important obligation of our customers.”2 Protocol-level surveys would be needed to conclude that special-status species do not occur at the project site.
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Cornett (2014) and the EIS reported that desert tortoise was not found on site.
However, the surveys performed on site were inconsistent with the US Fish and Wildlife Service protocol on desert tortoise surveys. The surveys were performed in February and March, whereas the protocol is for surveys to be performed in April and May or September and October. Also, transects should have been surveyed in a random order, but there was no indication that they were surveyed this way on Section 24. In summary, protocol-level surveys were not performed for desert tortoise. For that matter, protocol-level surveys were not performed for any special-status species potentially occurring on Section 24.
Stop-over Habitat
The EIS made no mention of the project impacts on migratory birds. The creosote scrub on Section 24 is undoubtedly used as stop-over habitat by migratory birds during migration seasons. No surveys were performed during migration seasons, and no discussion was provided of the critical importance of stop-over habitat to migratory birds. Essentially, a critical biological value of the site – its role as stop-over habitat -- was never addressed in any way.
Wildlife Movement Corridors
According to Cornett (2014:5.3-17), “The Project Site does not serve as a wildlife movement corridor. The Project Site does not connect any otherwise isolated areas of habitat; it serves more as a wildlife habitat than a wildlife corridor or linkage.
Accordingly, no significant impacts to the movement of wildlife species would result from the development of the Project.” However, these conclusions lack foundation.
Cornett did not perform surveys that would inform of whether or to what degree that Section 24 or any portion of Section 24 serves as a wildlife movement corridor. Not only were the surveys performed on site inconsistent with the types of surveys that would be needed to identify movement corridors, but methodological details and results were unreported by Cornett (2014).
Cornett (2014) and the EIS concluded that Section 24 does not serve as a wildlife movement corridor, but this conclusion represented a red herring argument. CEQA does not identify corridors as central to the environmental impact on wildlife movement. The real issue is whether the proposed project will interfere with the movement of wildlife, thereby disrupting a fundamental ecological requirement of wildlife species. The EIS did not address the real question of whether the project will interfere with the movement of any species of wildlife in the area.
That the project will interfere with wildlife movement should be obvious, given the extent of land conversions in the region and the position that Section 24 occupies on this landscape (Figure 1). Any remaining potential for terrestrial wildlife movement across the valley portion of the landscape south of I-10 has been constrained by past residential and commercial development (Figure 1). Section 24 represents a chokepoint to wildlife movement, so losing it to another residential project will block movement of wildlife along the northwest-southeast band of open spaces south of I-10. Converting 22 23
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Section 24 to urban housing will not only remove 577 acres of habitat of many wildlife species, but will also effectively remove the habitat capacity of at least 2,500 acres of acres of additional habitat southeast of Section 24. The additional impacts are readily apparent in Figure 1, and should not be ignored in the EIS.
Figure 1. Google Earth imagery from 2012 shows the linkages of open space south of I-10, and how converting Section 24 (red boundary) to houses will eliminate the ability of terrestrial wildlife to move (orange arrows) into and out of >2,500 acres of open space.
Cumulative Impacts
The EIS devoted 18 lines of text to cumulative impacts. Given such a cursory treatment of cumulative impacts, one would think that the EIS would err on the side of caution when making conclusions about cumulative impacts. After all, erring on the side of caution is the standard when making conclusions of potential impacts to sensitive resources in the face of high uncertainty (National Research Council 1986, Shrader- Frechette and McCoy 1992, O’Brien 2000). But that was not what the EIS did.
According to the EIS (page 5.3-19), “No significant unavoidable project or cumulative impacts to biological resources would result from the Project.” This conclusion was inconsistent with scientific standards, it was inconsistent with the evidence, and it was incorrect.
According to the EIS (page 2.0-24), “The Project Site does not serve as a wildlife movement corridor. The Project Site does not connect any otherwise isolated areas of habitat. Accordingly, no significant impacts to the movement of wildlife species would result from the development of the Project.” Figure 1 clearly shows that the project site does, in fact, connect otherwise isolated areas of habitat. At least 2,500 acres will be cut off from terrestrial wildlife movement should the 577 acre project area be converted to 24 25
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houses. This type of impact is what is referred to as habitat fragmentation, which is recognized as one of the most serious threats to the continued existence of terrestrial wildlife (Wilcox and Murphy 1985). Dismissing this process in the EIS was a substantial error.
Even the most simple cumulative impacts assessment was not provided in the EIS. The EIS could have tallied the number of acres of likely or potential land conversions in the Coachella Valley due to ongoing, proposed, or likely future residential, commercial and industrial projects in the foreseeable future. The EIS could have tallied the acres of proposed or anticipated land conversions to renewable energy projects within Riverside County and the larger Mojave Desert. According to the Desert Renewable Energy Conservation Plan (“DRECP”), 330,000 acres are likely to be converted to solar, wind, geothermal, distributed energy, and transmission projects within the Mojave Desert in the near future (California Energy Commission et al. 2014). These land conversions would eliminate most of the remaining population of burrowing owls in California, as well as large proportions of the remaining populations of desert tortoise, Coachella Valley fringe-toed lizard, flat-tail horned lizard, and Palm Springs ground squirrel, among many other special-status species.
MITIGATION
The core element of the mitigation plans is payment of a mitigation fee into a Habitat Conservation Plan (HCP), at the rate of $2,371 per disturbed acre. According to the EIS (page 2.0-23), “The Project would pay the development mitigation fees identified by the Tribal Habitat Conservation Plan (THCP). …In addition, the City of Rancho Mirage is a participant and permittee in the Coachella Valley Multiple Species Habitat Conservation Plan (CVMSHCP) and is coordinating with the Tribe regarding the THCP. … While the United States Fish and Wildlife Service (USFWS) has not yet approved the THCP or issued a 10(a) Permit, the Tribe has independent authority to implement the THCP to mitigate impacts to sensitive resources on Reservation lands.” However, there are two problems with this mitigation plan, as summarized in the EIS.
First, there is no approved HCP to pay into, so this portion of the mitigation amounts to deferring the formulation of the mitigation plan to an unspecified later date when one or both of the referenced HCPs might include mitigation that is acceptable to the US Fish and Wildlife Service and results in approval(s), and after any litigation over the approval has resulted in an outcome. Paying into one or both HCPs prior to approval(s) effectively prevents me and other members of the public from participating with this critical part of the environmental review, because Section 24 would have been developed prior to the circulation of the environmental review documents for one or both HCPs.
The second problem is that portion of the proposed measure that alleges the Tribe has the authority to independently implement mitigation on Reservation lands. Even if the Tribe possesses this authority (I do not know whether it does or does not), the EIS still needs to identify where habitat will be protected or where habitat restoration would occur, and it needs to prove that the promised levels of protection and restoration will be feasible. Does the Reservation have sufficient acreage of habitat to protect at 25 26
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whatever mitigation ratio is adequate? What is the mitigation ratio? Where is the like- kind habitat located? The EIS included no details on whether the Reservation has the capacity to conserve sufficient habitat to adequate mitigate the project’s impacts.
According to the EIS (page 5.3-18),“By establishing dedicated conservation areas with stringent development restrictions, the intent of the HCPs is to allow needed development to proceed elsewhere in the valley while preserving sufficient habitat for plant and wildlife species to survive. In this manner, compliance with the HCPs ensure that cumulative impacts to biological resources are mitigated to a level considered less than significant.” But again, there are no approved HCPs available. Even if there were, the EIS should identify where in the Valley conservation areas could be located. The imagery in Figure 1 indicates that there is little opportunity remaining to mitigate for the loss of 577 acres of special-status species habitat within Coachella Valley, and certainly there remains insufficient acreage to offset the loss of both the 577 acre project area and the effective loss of >2,500 acres due to habitat fragmentation.
The EIS stated that MM 5.3-2 would consist of preconstruction surveys for burrowing owls within 30 days of construction. However, this measure made no mention of passive or active relocation if owls are found; the EIS only says that grading can be halted to protect burrowing owls. More detail would be needed on mitigating impacts to burrowing owl. The same detail needs to be added for MM 5.3-3, which is the measure that is supposed to mitigate project impacts to loggerhead shrike.
Also, the California Department of Fish and Game (“CDFG”) (2012) staff recommendations on burrowing owl surveys listed minimum qualifications of survey personnel. The EIS provided no evidence that Cornett met the minimum qualifications of (1) Being familiar with burrowing owl ecology; (2) Experience conducting habitat assessments and non-breeding and breeding season surveys, or experience with these surveys conducted under the direction of an experienced surveyor; (3) Familiarity with the appropriate state and federal statutes related to burrowing owls, scientific research, and conservation; and, (4) Experience with analyzing impacts of development on burrowing owls and their habitat. Given the way the survey were performed, and the conclusions that were made about project impacts to burrowing owl and how to mitigate them, I would suggest that the survey protocol on qualifications was not met.
The CDFG staff report also identified 500 m buffer areas be maintained between burrowing owl burrows and high disturbance activities, but this buffer was not identified in the EIS. The EIS did not include a burrowing owl exclusion plan, but if it was to be revised to include such a plan, then this plan should meet the approval of CDFG. Furthermore, the EIS failed to meet any of the compensatory mitigation options listed in the CDFG staff report.
______________________
Shawn Smallwood, Ph.D.
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REFERENCES CITED
CDFG (California Department of Fish and Game). 2012. Staff Report on Burrowing Owl Mitigation. Sacramento, California.
California Energy Commission, California Department of Fish and Wildlife, U.S. Bureau of Land Management, U.S. Fish and Wildlife Service. 2014. Draft Desert Renewable Energy Conservation Plan (DRECP) and Environmental Impact Report/Environmental Impact Statement, SCH No. 2011071092 , BLM/CA/PL- 2014/025+1793, FWS–R8–ES–2014–N165. http://www.drecp.org/
Cornett, J. W. 2014. General biological resources assessment: Rancho Mirage Section 24 Specific Plan Site, Located Within SECTION 24, RANGE 5 EAST, TOWNSHIP 4 SOUTH Parcels 673-120-021, 673-120-022, 673-120-023, 673-120-024 and 673- 120-025, Riverside County, California. Report to Meridian Consultants, Westlake Village, California.
Meridian Consultants LLC. 2014. Draft Environmental Impact Statement, Section 24 Specific Plan, Agua Caliente Band of Cahuilla Indians (SCH No. 2014011035).
Prepared for Agua Caliente Band of Cahuilla Indians, Palm Springs, California.
National Research Council. 1986. Ecological knowledge and environmental problem- solving: concepts and case studies. National Academy Press, Washington, D.C.
O’Brien, M. 2000. Making better environmental decisions: an alternative to risk management. The MIT Press, Cambridge, Massachusetts.
Shrader-Frechette, K. S., and E. D. McCoy. 1992. Statistics, costs and rationality in ecological inference. Tree 7: 96-99.
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., 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.
Wilcox, B. A., and D. D. Murphy. 1985. Conservation strategy: the effects of fragmentation on extinction. American Naturalist 125:879-887.
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Comment Letter No. 8
Laborers’ International Union of North America (LIUNA), Local Union No. 1184 Richard T. Drury
Attorney, Lozeau Drury LLP
410 12th Street, Suite 250
Oakland, CA 94607
Response to Comment 8-1
The comment identifying the submittal of a comment letter on the behalf of the LIUNA, Local Union No. 1184 in regards to the Project is noted.
Response to Comment 8-2
The Draft EIS has been prepared in accordance with TEPA and CEQA, with the Tribe serving as the Lead Agency under TEPA. The Draft EIS is intended to serve as an informational document to enable the Tribe, other potential lead and/or responsible agencies under CEQA, and other interested parties to evaluate the environment impacts of the Project. Preparation of the environmental document was prepared in compliance with Section 15000 et seq. of the CEQA Guidelines, even though CEQA does not apply to any Project approvals by the Tribe. All mitigation measures, alternatives, and cumulative impacts are identified for the Project as would be required by CEQA. Significant impacts identified for the Project include construction and operation air quality impacts and construction related noise impacts. Five alternatives were analyzed to avoid or substantially reduce identified significant impacts and one alternative was chosen as the environmentally superior alternative.
Response to Comment 8-3
The comment suggests that the Draft EIS fails to properly assess the Project’s impacts to sensitive species and plants based on the opinion of Dr. Smallwood. As noted in Response to Comment 8-18, the EIS contains factual, objective and accurate information regarding the biological resources present on the Project Site and in the Coachella Valley that supports the conclusions presented on the significance of the impacts of the Project on biological resources. The Draft EIS appropriately assesses the Project’s potential biological impacts and identifies feasible mitigation measures to reduce these impacts to a level of less than significance in accordance with CEQA. As discussed in Response to Comment 8-16, Mr.
Smallwood’s experience is limited to Northern California. James W. Cornett, the ecological consultant who conducted the Biological Survey for the Project has over 40 years of expertise within the Coachella Valley and is very knowledgeable regarding the environmental and ecological conditions that are present within the Project Area.
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Response to Comment 8-4
As further discussed in detail in Response to Comment 8-20, biological surveys conducted for the Project Site were based upon the unique existing environmental conditions of the Coachella Valley. The survey pattern used has been approved by the USFWS for detecting the presence of officially listed or federally protected species. The three potential Coachella Valley sensitive species identified through these biological surveys to be found on the Project Site include the Coachella Valley milkvetch, the Coachella Valley fringe-toed lizard, and the burrowing owl. The Palm Springs Ground Squirrel was also detected on the Project Site, which is considered a Species of Special Concern by the State of California.
The identification of these sensitive species serves as the baseline within the Draft EIS of the Project’s potentially significant impacts to biological resources.
Response to Comment 8-5
As discussed in Response to Comment 8-4, several special status species have been found on the Project Site through biological surveys. The Project Site is bounded on all four sides by existing roadways and residential developments, thus acting as an isolating mechanism that presents physical barriers to plant and animal dispersal to surrounding areas. The Project Site offers no water, no shelter and no food for migratory bird species while the existing country clubs that lie along the entire western and southern boundaries of the Project Site offer more favorable conditions. Due to the lack of water, shelter and food on the Project Site, the Project Site does not serve as a potentially significant stop-over location for migratory birds. Contrary to what is suggested by the comment, the presence of these special status species on the Project Site does not diminish its existence as an ecological island. Please refer to Response to Comments 8-18 and 8-19 for further discussion.
Response to Comment 8-6
The comment suggests that the biological surveys conducted for the Project Site were inadequate.
Burrowing owls are easily detected on the valley floor because of unobstructed views, their conspicuous burrows and habitat of calling at the approach of threats. The surveys conducted were not cursory as the following maximum intensity protocols were followed: parallel transects were conducted at 10 meters apart as described for both burrowing owl and desert tortoise.7,8 Therefore, the site surveys that were conducted in February and March 2014 were adequate to record the presence of burrowing owls on the Project. As discussed in Response to Comment 8-16, Mr. Smallwood’s experience is limited
7 California Department of Fish & Game. 2012. Staff Report on Burrowing Owl Mitigation. Natural Resources Agency, State of California.
8 Preparing For Any Action That May Occur Within The Range Of The Mojave Desert Tortoise (Gopherus agassizii). United States Fish & Wildlife Service, 2010 Field Season.
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to Northern California and does not demonstrate knowledge of the unique environmental and ecological conditions present in the Coachella Valley.
Response to Comment 8-7
As discussed in further detail in Response to Comment 8-24, the Project Site does not serve part of a corridor between open space areas. The Project Site is bounded by existing roadways and residential development, thus not linking it to any vacant land that would serve as a corridor for wildlife.
Additionally, as discussed in Response to Comment 8-20, soil smoothing was conducted on the Project Site as the site contains dune sand habitat to determine if large animal corridors existed on the Project Site. In addition, sand sifting and smoothing was done in several areas, specifically within the Project Site along Ramon Road and Bob Hope Drive, so that tracks would be more prominent and identifiable.
This is a commonly conducted and accepted survey practice in sand dune habitat in the Coachella Valley.
Response to Comment 8-8
The comment is correct to note that USFWS survey protocol prefers that desert tortoise surveys be conducted between April and May or September and October. As stated in the Biological Resources Assessment (Appendix C of the Draft EIS) prepared for the Project, the CNDDB (March, 2014) has no records of the presence of the desert tortoise on or within one mile of the Project Site. The protocol also notes that surveys outside these periods may be appropriate when only presence/absence needs to be determined. No evidence of any kind (e.g. shells, bones, scutes, limbs, burrows, pallets, scats, egg shell fragments, tracks, courtship rings, drinking sites, mineral licks, etc.) was found during intensive surveys and no direct observations were made. The surveys conducted for the desert tortoise were adequate and support the conclusions reached on the presence or absence of sensitive species on the Project Site.
Therefore, the likelihood of detecting the desert tortoise on the Project Site is considered low. Please refer to Response to Comment 8-22 for further discussion. In addition, it should be noted that the Draft EIS was provided to both the USFWS and the CDFW for review and neither agency submitted comments recommending additional surveys.
Response to Comment 8-9
The Project Site consists of approximately 577 acres of vacant land with minimal existing vegetation. As also discussed in Response to Comment 8-23, the Project Site does not offer water, shelter, or food for migratory bird species. For this reason, the Project Site does not serve as a stop-over location for migratory birds.
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Response to Comment 8-10
As demonstrated by the responses to the comments in this letter, the Draft EIS properly assessed the Project’s potential impacts to biological resources. Pursuant to CEQA Guidelines Section 21166, a supplemental Draft EIS would not be required as there are no substantial new circumstances with respect to the Project, nor is there any new information that was not known upon preparation of the Draft EIS.
Response to Comment 8-11
The comment suggests that the 577 acres that comprise the Project Site serve as habitat for wildlife movement, as concluded by Dr. Cashen. As discussed in further detail within Response to Comment 8- 24, development of the Project Site would not remove the link of 2,500 acres of natural habitat located south of the Project Site due to the nature of the Project Site and the developed areas immediately adjacent to the site. Existing arterial roads and development located between the Project Site and the I- 10 to the east makes any wildlife movement traveling west across the Project Site unlikely. The biological surveys conducted in the Draft EIS conclude that the Project Site does not serve as an existing wildlife corridor within the Coachella Valley. These surveys constitute substantial evidence in support of the conclusions in the Draft EIS; whereas, this comment is based upon sheer speculation regarding wildlife movement.
Response to Comment 8-12
Pursuant to CEQA Guidelines Section 15130, the Draft EIS properly evaluated the Project’s cumulative impacts to biological resources. Any potentially significant impacts to special-status species, such as the burrowing owls, desert tortoise, Coachella Valley fringe-toed lizard, flat-tail horned lizard, and the Palm Springs ground squirrel are addressed and mitigated under the CVMSHCP and THCP, which adequately protect the critical habitat for these species. Therefore, development of the proposed Project in conjunction with other related projects would not eliminate the remaining populations of these special- status species or their habitat.
Response to Comment 8-13
Project along with related projects within the Coachella Valley are permitted by General Plans of other jurisdictions. All anticipated growth and cumulative impacts to biological resources have been analyzed by each of these jurisdictions. The CVMSHCP and THCP are intended to address the cumulative impacts on sensitive biological species posed by development throughout the Coachella Valley through the provision of mitigation for regional cumulative biological effects resulting from development within the HCP areas. The Project and all cumulative development would be subject to payment of the CVMSHCP 12-3100
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Conservation Plan Fee or Tribal HCP Conservation Fee, as applicable, in order to reduce impacts to a level of less than significance. Additionally, the Project Site is located within an area of the Coachella Valley that already contains various fragmented habitat, which is why the Project site is not designated for habitat preservation under either HCP. Please refer to Response to Comment 8-25 for further discussion.
Response to Comment 8-14
As discussed in further detail in Response to Comment 8-28, the CVMSHCP and THCP are fully approved habitat conservation plans that contain provisions for mitigation to address project-level and cumulative impacts to biological species. Mitigation Measures identified for the Project can be found on page 5.3-18 and 5.3-19 of the Draft EIS and were made available during the 60-day public comment and review period between November 20, 2014, and January 20, 2015.
Response to Comment 8-15
The comment will be reviewed by the Tribal Council in their consideration of the Record of Decision for the Project. The submitted letter will be included within this Final EIS.
Response to Comment 8-16
The comment identifying Mr. Smallwood’s professional qualification is noted, however, it is also noted that Mr. Smallwood’s experience is limited to Northern California and does not demonstrate knowledge of the unique environmental and ecological conditions present in the Coachella Valley.
Response to Comment 8-17
The comment states the Project Site represents one of the last open spaces located south of I-10 in the Coachella Valley. This characterization is not correct and demonstrates a lack of familiarity with both existing land use and environmental conditions in the Coachella Valley. Figure 1 as attached to Mr.
Smallwood’s own letter shows nearly 10,000 acres of undeveloped valley floor land south of I-10 and, in fact, there is much more than 10,000 acres. A large percentage of the open space south of the freeway is protected under the Coachella Valley Multiple Species Habitat Conservation Plan (CVMSHCP)9 a fact ignored by Smallwood. The United States Fish & Wildlife Service (USFWS) has approved the CVMSHCP (which was reviewed by dozens of professional biologists) indicating adequate valley floor habitat is protected to preserve populations of not only officially listed species but also species of concern.
9 Coachella Valley Multiple Species Habitat Conservation Plan, available online at http://www.cvmshcp.org/ . 12-3101
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This comment also states that the Coachella Valley is a region known for high species richness. It should be noted that while the greater Coachella Valley region is well known for species richness because of its extremely varied topography, the Project Site and other sand field habitats on the valley floor are not.10 Their uniformity of substrate, lack of plant form diversity and lack of topographical relief on any scale results in relatively small numbers of vascular plant, invertebrate and vertebrate species compared with most other habitat types in the region.11 While two listed species are known to occur in the Project Site (and were discussed in the Section 5.3, Biological Resources of the Draft EIS), the presence of these two species does not indicate a high level of diversity that could be characterized as high species richness.
Response to Comment 8-18
As demonstrated by the responses to the comments in this letter, the Draft EIS contains factual, objective and accurate information regarding the biological resources present on the Project Site and in the Coachella Valley that supports the conclusions presented on the significance of the impacts of the Project on biological resources.
This comment challenges the characterization of the Project Site as being nearly an ecological island bounded on all four sides by paved roadways (three of them carrying high volumes of traffic) and on two sides by residential developments. This statement accurately describes the fact that the site is bordered by existing roadways.
An isolating mechanism, whether a mountain range, river or roadway, functions to reduce or eliminate the movement of plants and animals from one parcel of land to another. This contributes to ecological isolation. This is a widely recognized biological principle that is applicable to the Project Site due to the presence of major roadways on all four edges of the site, which are physical barriers to plant and animal dispersal that surround it.
This comment also does not accurately represent the surveys conducted. For example, surveys were conducted by walking east/west transects at 10-yard intervals through the Project Site. This survey pattern used has been approved by the USFWS for determining the presence or absence of the burrowing owl and desert tortoise and represents an intensive survey effort that resulted in no officially listed or federally protected species being overlooked.
10 Zabriskie, J. 1987. Plants of Deep Canyon. University of California, Riverside. 11 Cornett, J. W. 1980. Factors affecting reptile species diversity in the Deep Canyon Transect, Colorado Desert, California.
Master’s Thesis, California State University, San Bernardino. 12-3102
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Response to Comment 8-19
The presence of threatened or endangered species in no way diminishes the existence of an ecological island. Populations of threatened or endangered species are often found trapped within isolated, island- like environments. Typically, this is why they are threatened or endangered in the first place. This concept is described in papers written by Swartz 12 and MacArthur.13 Response to Comment 8-20
This comment indicates the biological surveys performed on the Project Site were inadequate because the time of year the surveys were conducted, in Mr. Smallwood’s opinion, at a time of year least likely to result in the detection of special-status species. This opinion does not recognize the unique existing environmental conditions in the Coachella Valley.
For example, the endangered Coachella Valley milkvetch is growing and even blooming by the end of January, reaches its peak bloom in February and begins to decline in March providing there has been adequate rainfall. Young individuals of the officially threatened Coachella Valley fringe-toed lizard are active even in January on clear, calm winter days and all individuals of this species are active by early March. Burrowing owls are easily detected on the valley floor because of unobstructed views, their conspicuous burrows and habit of calling at the approach of threats. It should be noted that all three of these sensitive species were identified on the Project Site, which further demonstrates that the biological surveys were conducted at an appropriate time of year for the detection of sensitive species in the Coachella Valley.
The mammal live-trapping conducted was adequate given the habitat present on the Project Site.
Because two sensitive species might possibly be present on site, live trapping was conducted which confirmed the presence of the Palm Springs Ground Squirrel and did not confirm the presence of the Palm Springs Pocket Mouse. Neither of these two species has any federal status. Both are considered Species of Special Concern by the State of California.14 Even if it is assumed the pocket mouse is present on the site, it is a species addressed by the CVMSHCP, which will result in the preservation of sufficient land to preserve this unlisted subspecies even without inclusion of any Agua Caliente Band of Cahuilla Indians Reservation lands.15
12 Schwartz, M. W., L. R. Iverson, A. M. Prasad, S. N. Matthews, and R. J. O'Connor. 2006. Predicting extinctions as a result of climate change. Ecology 87:1611–1615.
13 MacArthur, Robert H.; Wilson, E. O. The Theory of Island Biogeography, (Princeton, New Jersey: Princeton University Press), 1967.
14 Status available at https://www.dfg.ca.gov/biogeodata/cnddb/pdfs/spanimals.pdf . 15 Coachella Valley Multiple Species Habitat Conservation Plan, available online at http://www.cvmshcp.org/ . 12-3103
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This comment offers an opinion on the effect of soil smoothing on animal movement that is not relevant to the sand habitat present in the Coachella Valley. In fact, soil smoothing is typically completed on sites that contain dune sand habitat, rather than the type of habitat found in northern California that Mr.
Smallwood is familiar with. As described in the Biological Resources Assessment (see Appendix C in the Draft EIS), in an effort to determine if large animal corridors existed on the Project Site special attention was given to observing and identifying animal tracks. In addition, sand sifting and smoothing was done in several areas so that tracks would be more prominent and identifiable. Specifically, a 100 meter long by 1 meter wide sand smoothing transect along the northwest Project Site, along Ramon Road, and a second identical transect along Bob Hope Drive near Dinah Shore Drive was conducted. No indication of wildlife departing or arriving through either transect occurred after inspection. This is a commonly conducted and accepted survey practice in sand dune habitat in the Coachella Valley.
While road kill surveys are not routinely conducted as part of a biological survey program, such surveys were conducted for the Draft EIS. Again, Mr. Smallwood’s opinion on when these surveys should have been conducted reflects his experience in Northern California, which is not applicable to the unique ecological conditions in the desert environment of the Coachella Valley.
Response to Comment 8-21
Contrary to the assertion made in this comment, the surveys conducted were not cursory as the following maximum intensity protocols were followed: parallel transects were conducted at 10 meters apart as described for both burrowing owl and desert tortoise.16,17 The point count surveys recommended in this comment are applicable for very large project sites or sites that have obstructed views. These conditions do not, however, apply to the Project Site. It should be noted that this comment does not identify a single sensitive species that was not addressed in the biological resource evaluation. Conducting surveys with acoustic detectors or thermal cameras to detect bats was not necessary because no sensitive bat species roost and hunt over the Project Site due to lack of suitable habitat for roosting or for prey species. Not one bat roost occurred within the Project Site because of the complete absence of topographical relief or large native trees or shrubs. The biological surveys recorded the bat species that were identified flying over the site.
16 California Department of Fish & Game. 2012. Staff Report on Burrowing Owl Mitigation. Natural Resources Agency, State of California.
17 Preparing For Any Action That May Occur Within The Range Of The Mojave Desert Tortoise (Gopherus agassizii). United States Fish & Wildlife Service, 2010 Field Season.
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The biological surveys conducted did not rely on the California Natural Diversity Database (CNDDB), as incorrectly stated in this comment, but instead appropriately used this database to develop the exhaustive site survey program that was conducted.
It should also be noted that road kills on surrounding paved roadways were also monitored on all site visits.
Response to Comment 8-22
This comment does not present the full guidance from the USFWS on conducting surveys to determine the presence or absence of desert tortoise. Specifically while the USFWS survey protocol states that it is preferable to conduct surveys during the tortoise’s most active periods, which are identified as April through May and September through October, if the survey area is large (over 40 acres) and if the project could affect more than 2 or 3 tortoises. The protocol also notes that surveys outside these periods may be appropriate when only presence/absence needs to be determined.
Specifically, the USFWS guidance states that surveys outside the active period may be appropriate when only a presence/absence determination is necessary and that USFWS staff bases determination of whether the results are valid on a whole suite of factors, including but not limited to the type and condition of habitat, the general location of the survey area, the experience of the surveyors, the time and weather when the survey was conducted, the nature of the year in which the survey occurred (i.e., if it rained a lot, desert tortoises are likely to have been active and are more likely to have left evidence of their presence), how much time surveyors spent at the site, and whether they were conducting a focused survey for tortoises or looking for a suite of biological and/or cultural resources. These factors are considered together to determine whether the surveyors were likely to have found whatever evidence might exist that desert tortoises were present.
As stated in the Biological Resources Assessment (Appendix C of the Draft EIS) prepared for the Project, the CNDDB (March, 2014) has no records of the tortoise on or within one mile of the Project Site. Based on this information indicating the lack of observance of the desert tortoise in the general vicinity of the site, and the location of the site and the type and condition of the habitat available, the likelihood of the desert tortoise being present on the site was considered low. Nonetheless, as reported in the Biological Resources Assessment, surveys were conducted by walking east/west transects at 10-yard intervals through the Project Site. This survey pattern used has been approved by the USFWS for determining the presence or absence of the burrowing owl and desert tortoise in the Coachella Valley and represents an intensive survey effort that resulted in no officially listed or federally protected species being overlooked. However, no evidence of any kind (e.g. shells, bones, scutes, limbs, burrows, pallets, scats, egg shell fragments, tracks, courtship rings, drinking sites, mineral licks, etc.) was found and no direct 12-3105
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observations were made. In addition, it should be noted that the Draft EIS was provided to both the USFWS and the CDFW for review and neither agency submitted comments recommending additional surveys. The surveys conducted for the desert tortoise were adequate and support the conclusions reached on the presence or absence of sensitive species on the Project Site.
Response to Comment 8-23
The Project Site offers no water, no shelter and no food for migratory bird species while the existing country clubs that lie along the entire western and southern boundaries of the Project Site offer more favorable conditions. Due to the lack of water, shelter and food on the Project Site, the Project Site does not serve as a potentially significant stop-over location for migratory birds.
Response to Comment 8-24
This comment is based on the unsupported premise that there is a band of open space located south of the I-10 that facilitates wildlife movement and also links approximately 2,500 acres of habitat area located south of the Project Site with other open space areas. Based on the existing pattern of development this is clearly not the case. As clearly shown on the aerial photograph included in Mr.
Smallwood’s letter, there are major arterial streets and a dense connected pattern of development south of the I-10. There is not 2,500 acres of natural habitat located south of the Project Site. South of Dinah Shore Drive, which is the southern boundary of Section 24 and west of Bob Hope Drive the area is completely developed. The section of land located between Gerald Ford Drive, Monterey Avenue, Frank Sinatra Drive and Bob Hope Drive is vacant but is surrounded by development and not linked to the Project Site or any other nearby undeveloped areas. The Project Site is located at the extreme southern end of the band of undeveloped land referenced in this comment and existing major arterial roads and development are located between the site and the I-10 to the east, precluding any wildlife movement from the south or east that would use the site to travel west. The intent of the HCPs is to allow development, such as the Section 24 Specific Plan Project, to proceed elsewhere in the valley while preserving sufficient habitat to assure the survival of both sensitive and common plant and wildlife species. For these reasons, as presented in the Biological Resources Assessment and in Section 5.3 of Draft EIS, the Project Site does not serve as part of a corridor between open space areas. In addition, due to the existing habitat conditions, including the lack of water, shelter or food for wildlife species, wildlife movement through the site has determined to be minimal, as documented by the biological surveys conducted.
Response to Comment 8-25
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opinion. This comment implies that the conclusion on cumulative impacts is the only information provided, when this is not the case. This conclusion is based on the information discussed on page 5.3- 18 in Section 5.3 of the Draft EIS. First, it should be noted that this discussion begins with the statement that the Project, in conjunction with other related projects in the area, as well as the additional growth permitted by the City of Rancho Mirage General Plan and the General Plans of the other jurisdictions in the Coachella Valley will result in cumulative impacts to biological resources. This discussion then addresses the comprehensive analysis and natural resource planning included in the CVMSHCP and the Agua Caliente Tribal Habitat Conservation Plan (THCP). The plans provide for mitigation of regional cumulative biological effects resulting from development within the HCP areas by establishing dedicated conservation areas with stringent development restrictions. The intent of the HCPs is to allow development, such as the Section 24 Specific Plan Project, to proceed elsewhere in the valley while preserving sufficient habitat to assure the survival of both sensitive and common plant and wildlife species. In this manner, compliance with the HCPs ensure that cumulative impacts to biological resources are mitigated to a level considered less than significant.
As discussed in the Response to Comment 8-24, the Project Site is located in a portion of the Coachella Valley where the existing pattern of development has already resulted in the type of fragmentation of habitat discussed in this comment. This is the primary reason why the CVMSHCP and THCP identify large areas of natural habitat elsewhere in the Coachella Valley that has not been fragmented by development for preservation.
Response to Comment 8-26
As stated in the Draft EIS, the THCP has been approved by the Agua Caliente Tribal Council and is being implemented by the Tribe. The THCP identifies conservation areas within the Reservation sufficient in size and habitat quality to mitigate the impact of development on other land within the Reservation.
Response to Comment 8-27
This comment is incorrect in stating the CVMSHCP and THCP are not approved. The CVMSHCP is fully approved and, as stated above, the THCP has been approved by the Agua Caliente Tribal Council.
Response to Comment 8-28
The biologist who conducted the surveys and prepared the Biological Resources Assessment has been conducting burrowing owl surveys since 1973, longer than any other actively working biological consultant in California. Furthermore, his credentials have been accepted by both the USFWS and CDFW. A curriculum vitae detailing Mr. Cornett’s credentials and expertise is attached to Appendix 4.0 of this Final EIS.
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This comment suggests that the mitigation for the burrowing owl is inadequate because does not specify relocation details in the event that burrowing owls are found during pre-construction surveys. To the contrary,the Biological Resources Study goes into detail regarding this issue on pages 20 and 21 (see Appendix C in the Draft EIS). It is up to the USFWS and the CDFW as to the disposition of any burrowing owls found during preconstruction surveys.
Response to Comment 8-29
A buffer area cannot be established until the preconstruction survey has been completed and burrowing owls are found to be present on the site. Burrowing owls, migrate, relocate and abandon burrows.
Where they are today is not necessarily an indication where they will be in the future. This is the reason the preconstruction surveys will be conducted. If burrowing owls are present, as required in Mitigation Measure MM 5.3-2, all appropriate mitigation recommended in the California Department of Fish and Game (CDFG) 2012 Staff Report on Burrowing Owl Mitigation will be applied as appropriate and necessary to avoid impacts to burrowing owls.
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Comment Letter No. 9
Union Pacific Railroad Company
Patrick R. McGill
Senior Counsel
1400 Douglas Street, Stop 1580
Omaha, Nebraska 68179
Response to Comment 9-1
located approximately 725 feet (or 0.14 miles) north/northeast of the Project Site, north of Ramon Road. The Project Site is not, therefore, adjacent to the rail line as indicated in this comment. Due to the distance of the Project Site from the UPRR transportation corridor, any increases in train volumes would not directly impact the residents/employees within the Project Site, as presented in the analysis in Section 5.9, Land Use and Planning, and Section 5.10, Noise.
Response to Comment 9-2
While the Project Site is not directly adjacent to the I-10/UPRR corridor, design of the Project considered its close proximity to the I-10/UPRR transportation corridor. The Project’s retail and resort land uses would be located along Dinah Shore Drive, Ramon Road, and Bob Hope Drive. As discussed in Section
5.9, Land Use and Planning and Section 5.10, Noise, the land uses and projected noise levels within the Project Site would be compatible with those uses along the I-10/UPRR corridor. Therefore, the combination of the Project Site’s 725 foot distance to the railroad and the proposed layout of land uses would result in compatibility with the I-10/UPRR transportation corridor.
Response to Comment 9-3
Based on the location and characteristics of the rail line in relation to the Project Site, the Project will not result in the need for train operations to reduce speed. The UPRR transportation corridor is located approximately 725 feet (or 0.14 miles) north/northeast of the Project Site. Access across the UPRR transportation corridor within the vicinity of the Project occurs via above grade, or overhead, street and sidewalk crossings. Pedestrians and vehicles associated with the Project would cross the UPPR transportation corridor via Bob Hope Drive, Ramon Road, Date Palm Drive, and Monterey Avenue and would not impact the daily operations of the Union Pacific Railroad. No at-grade crossings are in the immediate vicinity of the Project Site. No significant traffic impacts related to railroad operations were identified, and as such, no additional mitigation would be required. 12-3112
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Response to Comment 9-4
As previously noted, the Project Site is not directly adjacent to the UPRR transportation corridor and is approximately 725 feet south/southwest from the closest point to the railroad tracks. Any pedestrians associated with the Project would have to cross over the four above-grade crossings along Bob Hope Drive, Ramon Road, Date Palm Drive, and Monterey Avenue to gain access to other side of UPRR corridor. As pedestrian traffic would be directed above-grade, trespassing along the railroad tracks would be less likely. Cumulative projects located adjacent to the UPRR, such as the Section 19 Specific Plan Project, would implement similar design features such as barrier walls or block fences, to minimize the likelihood of trespassing onto the railroad right-of-way. Due to the distance of the Project from the railroad right-of-way and the adequate number of above grade crossings for pedestrians, no significant impacts would occur and no mitigation would be required.
Response to Comment 9-5
The UPRR anticipates an increase in rail operations which would result in the likely increase in noise and vibration levels along the railroad corridor. Pages 5.10-9 through 5.10-12 of Section 5.10, Noise of the Draft EIS identify that predominant ambient noise levels are attributed to roadway noise surrounding the Project Site and traffic associated with the I-10. Page 5.10-12 of Section 5.10, Noise identifies that the existing ground vibration environment within the Project vicinity would be below perceptible levels.
Noise generated by the event of a single train passing is dominated primarily by the train horn and secondarily by the train engines and cars. Train horns are required by the Federal Railroad Administration (FRA) to produce a minimum sound level of 96 dBA as measured from 100 feet from the train.18 The frequency of the trains on the UPRR tracks is estimated to be one train every 15 minutes with trains taking approximately three to five minutes to pass. The typical average noise attenuation for rail noise, a line source, is 3 dB per doubling of distance. Instantaneous noise levels at the closest edge of the Project Site would likely be 87 dBA and 84 dBA at the Active Adult Community. As discussed in Section 5.10, the sound levels from vehicle traffic along Ramon Road and Bob Hope Drive would result in a 24 hour average of 72.1 to 77.6 dBA and 74.6 to 76.3 dBA, respectively. The instantaneous noise levels from rail operations would not result in a substantial increase in the average 24 hour noise levels that would exceed the acceptable interior and exterior noise levels for the land uses proposed on the Project Site.
18 Code of Federal Regulations, Title 49, Part 229.129(a) – Railroad Locomotive Safety Standards. 12-3113
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The proposed land use plan would ensure that compatible land uses would be located adjacent to one another and that noise sensitive land uses such as residential would be protected from noise impacts by locating them away from high noise sources such as the I-10/UPRR corridor and traffic along the adjacent major arterials (Dinah Shore Drive and Bob Hope Drive). For example, retail and resort land uses have been located along Dinah Shore Drive, Ramon Road, and Bob Hope Drive for maximum exposure, but also because these uses would be more compatible with the vehicular noise levels along these roadways. Placing the retail and resort land uses along the major roadway frontages would also provide a noise buffer for the residential uses that would be developed in the Mixed Use Core and Residential Planning Areas.
The FTA criteria for frequent vibration events from transit is 72 VdB.19 Freight trains traveling at 50 miles per hour can generate vibration levels of 90 VdB at 25 feet. Vibration levels only attributed to train operations would not be noticeable as a result of the distance from the Project Site to the railroad right- of-way. Therefore, no vibration impacts would occur and no mitigation would be necessary.
Refer to Section 5.10, Noise, for a detailed noise analysis and the Project’s Design Features and Mitigation Measures that would reduce noise level impacts at the Project Site.
Response to Comment 9-6
The Tribe will provide notice to the Union Pacific Railroad Company of public meetings to consider this Project as requested.
19 U.S. Department of Transportation, Federal Railroad Administration, High-Speed Ground Transportation Noise and Vibration Impact Assessment, https://www.fra.dot.gov/Elib/Document/2680 , (September 2012). 12-3114
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Letter No. 10
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Comment Letter No. 10
Mira Vista Homeowners
Carol Trentacosta
Board Member
98 Via Bella
Rancho Mirage, CA 92270
Response to Comment 10-1
As discussed in Section 3.0, Project Description, the Project is anticipated to be developed in two phases. The Active Adult Community is estimated to start construction in late fourth quarter of 2015 and would require six to eight years to complete, with an estimated completion date for 2022. The second phase of construction involves the development of the Tribal Planning Areas. While there is currently no established timeframe, buildout of the Tribal Planning Areas is projected for 2035.
Response to Comment 10-2
The construction entrance would initially be from Los Alamos Road. Dinah Shore is heavily travelled and access is not currently available from Ramon Road or Bob Hope Drive. As discussed in Section 5.14, Traffic and Transportation of the Draft EIS Mitigation Measure MM 5.14-1 requires that each individual project proponent prepare and submit a detailed construction traffic management plan to the Tribe, City, and/or County for review and approval, as applicable. The construction traffic management plan would be required to identify construction entrances and measures to maximize traffic flow conditions around the Project Site. As discussed throughout the Draft EIS, construction hours would conform to the appropriate jurisdiction’s Municipal Code, either the City (7:00 AM to 7:00 PM except on Sundays) or the County of Riverside Municipal Code (7:00 AM to 7:00 PM weekdays and 8:00 AM to 5:00 PM on Saturdays). As the Project is built out, the project proponent would explore other feasible opportunities for construction access to the Project Site.
Response to Comment 10-3
The scope and timing of the ultimate buildout of Los Alamos Road would be outlined within the conditions of approval for the Project tentative map. These conditions of approval would be prepared by the governing agency, either the Tribe, the City, and/or the County, as part of the map approval process.
Response to Comment 10-4
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point to the Project Site and would account for approximately 43 percent of the traffic generated by the Active Adult Community. The primary access point would be from Dinah Shore Drive, opposite the existing signalized access to the Westin Mission Hills Golf Resort, with secondary access to Bob Hope Drive via Casino Drive. As discussed in Section 5.14 of the Draft EIS, the intersection at Los Alamos Road at Via Bella would operate at a Level of Service (LOS) A during both peak hours for the major street left turn and LOS B during both peak hours for the minor street approach under Full Project Development conditions. A traffic signal warrant analysis was performed for all proposed intersections, and due to the projected LOS at this intersection, signalization of the intersection is not warranted (see Appendix 4 of the Traffic Study [Appendix G of the Draft EIS]).
Response to Comment 10-5
Please refer to Response 10-4 above regarding the access point to the Project Site at Los Alamos Road.
As it has been determined that the intersection of Los Alamos Road at Via Bella would operate at acceptable conditions for both the major street left turn and minor street approach (LOS A and B, respectively) with full development of the Project, a traffic control signal would not be necessary.
C. PUBLIC MEETING COMMENTS AND RESPONSES
The following subsection contains the comments, identified in Table 2.0-1, collected from the public meeting that was held by the Indian Planning Commission on December 17, 2014, at the Agua Caliente Casino Resort Spa Cahuilla Room B, located at 32-250 Hope Drive in Rancho Mirage. The individual comments have been bracketed and numbered for ease of reference. The comments are followed by written responses to the comments numbered to correspond to the numbered comment.
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Public Comment No. 1
Mira Vista Homeowners
Carol Trentacosta
Board Member
98 Via Bella
Rancho Mirage, CA 92270
Response to Public Comment 1
The comment identifying the representation of Carol Trentacosta on behalf of the Mira Vista Homeowners Association (HOA) in regards to the Project is noted. The information in the EIS, including this comment in support of the Project as proposed, will be reviewed and considered by the Tribal Council.
Response to Public Comment 2
The comment suggests that a signalized intersection at Los Alamos Road at Via Bella (Intersection 8) would be necessary upon buildout of the Active Adult Community. Access to the Project Site was addressed in the Draft EIS in Section 5.14, on page 5.14-21. This intersection is located across directly across the street from the main entrance to the Mira Vista HOA and currently features a stop sign for traffic control. As discussed in detail in Response to Comment 10-4, the traffic signal warrant analysis performed for this intersection identified that a traffic signal is not warranted (see Appendix 4 of the Traffic Study [Appendix G of the Draft EIS]).
Response to Public Comment 3
As stated in Response to Comment 10-3, the scope and timing of the ultimate buildout of Los Alamos Road would be outlined within the conditions of approval for the Project tentative map. These conditions of approval would be prepared by the governing agency, the Tribe, the City, and/or the County, as part of the map approval process.
Response to Public Comment 4
As discussed in detail in Response to Comment 10-2, the construction entrance for the Project would initially be from Los Alamos Road. Individual project proponents would prepare and submit a detailed construction traffic management plan to the Tribe, City, and/or County for review and approval, as applicable. The construction traffic management plan would be required to identify construction entrances and measures to maximize traffic flow conditions around the Project Site. The Project’s potential access impacts to the adjacent residential uses were identified as less than significant. 12-3119
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Response to Public Comment 5
As discussed in Section 3.0, Project Description, the Project is anticipated to be developed in two phases. The Active Adult Community is estimated to start construction in late fourth quarter of 2015 and would require six to eight years to complete, with an estimated completion date for 2022. The second phase of construction involves the development of the Tribal Planning Areas. While there is currently no established timeframe, buildout of the Tribal Planning Areas is projected for 2035.
Response to Public Comment 6
The Tribe acknowledges the concerns of the Mira Vista HOA in regards to implementation of the Project.
These concerns are addressed by the responses to the comments from the public meeting, as well as Comment Letter No. 10, and will be reviewed and considered by the Tribal Council.
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Public Comment No. 2
Rod Pennycook
31 Via Bella
Rancho Mirage, CA 92270
Response to Public Comment 7
The Tribe acknowledges the concerns Rod Pennycook has regarding the Project. These concerns are similar to those presented by Carol Trentacosta on behalf of the Mira Vista Homeowners Association (HOA) within Public Comment No. 1. Please refer to Responses to Public Comment No. 1 above for additional information.
Response to Public Comment 8
The comment suggests concern over the Project’s construction schedule and specifically the noise impacts that would result. As stated in Response to Comment 10-1, the Project is anticipated to be developed in two phases. The Active Adult Community is estimated to start construction in late fourth quarter of 2015 and would require six to eight years to complete, with an estimated completion date for 2022. The second phase of construction involves the development of the Tribal Planning Areas. While there is currently no established timeframe, buildout of the Tribal Planning Areas is projected for 2035.
With respect to construction access to the site, Section 5.14, Traffic and Transportation of the Draft EIS identifies Mitigation Measure MM 5.14-1, which requires that each individual project proponent prepare and submit a detailed construction traffic management plan to the Tribe, City, and/or County for review and approval, as applicable. Therefore, construction activities would comply with the appropriate jurisdiction’s regulations and requirements, as appropriate, to ensure construction access impacts are less than significant. As the Project is built out, the project proponent would explore other feasible opportunities for construction access to the Project Site.
As the Project would be developed in various phases through 2035, noise impacts related to construction activities would vary in location, intensity, duration. As discussed throughout the Draft EIS, construction hours would conform to the appropriate jurisdiction’s Municipal Code, either the City (7:00 AM to 7:00 PM except on Sundays) or the County of Riverside Municipal Code (7:00 AM to 7:00 PM weekdays and 8:00 AM to 5:00 PM on Saturdays), as appropriate..
Response to Public Comment 9
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previously described above, would be required from each individual project proponent to identify construction entrances and measures to maximize traffic flow conditions around the Project Site. Haul trucks traveling to and from the site would operate under those conditions identified within the construction traffic management plan, as approved by the appropriate jurisdiction. As the Project is built out, the project proponent would explore other feasible opportunities for construction access to the Project Site. Impacts to the adjacent residential communities would be less than significant.
Response to Public Comment 10
The responses to these comments are demonstrated above. This Final EIS for the Project will be made available to those potentially impacted or interested parties prior to the Record of Decision made by the Tribal Council. The comments presented by Mr. Pennycook are noted by the Tribe. 12-3123
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3.0 REVISIONS TO THE DRAFT EIS
The Tribe, acting as the Lead Agency for the planning and environmental review of this Project, under Agua Caliente Tribal Environmental Policy Act (TEPA) (Tribal Ordinance No. 28), has also decided to prepare this Environmental Impact Statement (EIS) in compliance with the California Environmental Quality Act (CEQA). In accordance with the CEQA Guidelines § 15132 (a), this Section of the Final EIS provides changes to the Draft EIS that have been made to clarify, correct or supplement the environmental impact analysis for the Project. Such changes are a result of recognition of inadvertent errors or omissions as well as public and agency comments received in response to the Draft EIS. The changes described in this section do not result in any new or increased significant environmental impacts that would result from the Project.
Provided below are corrections and additions to the Draft EIS, including where appropriate, the associated technical appendices. Changes are identified below by the corresponding Draft EIS section and subsection, if applicable, and the page number. Additions are underlined and deletions are shown in strikethrough (strikethrough) format.
Section 1.0.B.1 Introduction
The following revision has been made to clarify language and proper characterization.
Page Revision
1.0-3 The NOI also provided notice of the public scoping meetings the Tribe held on February 1412, 2014, at 4:00 PM and 7:00 PM, at the Agua Caliente Casino Resort Spa, located at 32-250 Bob Hope Drive in Rancho Mirage.
Section 2.0.F Summary
The following revision has been made to clarify language and proper characterization.
Page Revision
2.0-26 MM 5.4-1 Prior to the start of any ground disturbing activities within the Project Site the Agua Caliente Band of Cahuilla Indians (Tribe) Tribal Historic Preservation Officer (THPO) shall be notified of the pending activities. A qualified archaeologist shall coordinate with the THPO during the drafting for the archaeological monitoring plan and the plan shall allow for the archaeologist in consultation with the THPO to determine the 12-3124
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timing of when monitoring is no longer necessary. During earth moving disturbances that involve excavation activities, if there is any evidence of Native American resources (significant or otherwise), the THPO will be notified and construction activities modified in accordance with the archaeological monitoring plan.
The following revision has been made to reflect the changes made in Section 5.6, Greenhouse Gases.
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2.0-33 Project operational GHG emissions for the Active Adult Community, Tribal Planning Areas, and Combined Development would be 8,879.398,882.84, 39,326.09, and 45,899.9446,480.7 metric tons of carbon dioxide equivalents (MTCO2e) per year, respectively.
The following revision has been made to address a minor and necessary text edit within the Section subtitle within Table 2.0-1.
Page Revision
2.0-64 Project Design Feature 5.15.1-4 will ensure that all future wells developed on-site would be constructed consistent with the CVWD Development Design Manual, and if groundwater testing for total chromium prior to installation indicates that the groundwater exceeds US Environmental Protection Agency (USEPA) Maximum Contaminant Level (MCL), the water wells would provide treatment to reduce the level of chromium below the USEPA MCL.
Section 3.C.6 Project Description
The following revision has been made to clarify the Project Site’s proposed water wells.
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3.0-20 The seven proposed wells would be constructed consistent with the CVWD Development Design Manual. Groundwater testing for total chromium will be undertaken prior to construction to determine if the groundwater exceeds USEPA MCL, and if the USEPA MCL is exceeded, the wells will provide treatment to reduce the level of chromium below the EPA MCL.
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Section 3.D Project Description
The following revision has been made to clarify language and proper characterization.
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Table 3.0-2
Intended Uses of the EIS
Potential Lead and/or Lead Agency under TEPA Potential Action Agua Caliente Band of Cahuilla Indians • Record of Decision of EIS • Approval of the Section 24 Specific Plan
• Adoption of the Section 24 Specific Plan
• Parcel Map to Reconfigure Allottee Parcels
• Consent to Annexation
• Approval of Tentative Tract Maps and permits for
future project development in the Tribal Planning
Areas (Planning Areas 1 through 7)
Potential Lead and/or Responsible Agencies Potential Action City of Rancho Mirage • Certification of EIS
• Adoption of the Section 24 Specific Plan
• Approve Request for Annexation
• Approval of Tentative Tract Maps and permits for
future project development in the Active Adult
Community (Planning Area 8)
Local Agency Formation of Riverside County • Approve Annexation of the Project Site into the City of Rancho Mirage
Coachella Valley Water District • Approve Construction and Specifications Plans for CVWD service infrastructure
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Section 5.2.B.4 Air Quality
The following revision has been made to update the calculations for construction emissions related to implementation of the Active Adult Community.
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Table 5.2-6
Active Adult Community Construction Emissions
Pollutant (pounds/day)
Source VOC NOx CO SOx PM10 PM2.5
Year 2015
Maximum 1.091.07 20.4120.43 39.3739.13 0.060.06 6.806.80 3.76 SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2016
Maximum 3.644.06 29.7237.54 59.2670.08 0.100.12 3.483.82 1.531.62 SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2017
Maximum 72.9673.07 1.571.57 7.056.13 0.010.01 0.240.24 0.08 SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2018
Maximum 73.0372.93 1.52 6.575.73 0.01 0.24 0.08
SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2019
Maximum 73.0072.90 1.49 6.215.43 0.01 0.24 0.08
SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2020
Maximum 73.9873.89 11.35 22.68 0.040.03 0.32 0.13
SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2021
Maximum 73.9673.87 11.33 23.3022.49 0.040.03 0.32 0.13
SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
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Pollutant (pounds/day)
Source VOC NOx CO SOx PM10 PM2.5
Year 2022
Maximum 72.9472.86 1.42 5.544.87 0.01 0.24 0.08
SCAQMD threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Source: Refer to the data sheets in Appendix 3.0XXB, Air Quality Air Quality – Supplemental Emission Modeling Information and Greenhouse Gas Emissions ModelingXXXX.
Abbreviations: CO = carbon monoxide; NOx = nitrogen oxide; PM10 = particulate matter less than 10 microns; PM2.5 = particulate matter less than 2.5 microns; VOC = volatile organic compound; SCAQMD = South Coast Air Quality Management District; SOX = sulfur oxide.
The following revision has been made to update the calculations for operational emissions related to implementation of the Active Adult Community.
Page Revision
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Table 5.2-7
Active Adult Community Operational Emissions
Pollutant (pounds/day)
Source VOC NOx CO SOx PM10 PM2.5
Maximum 106.84 102.78 49.98 309.80 0.430.41 26.19 8.74 SCAQMD threshold 75 100 550 150 150 55
Threshold exceeded? Yes No No No No No
Source: Refer to the data sheets in Appendix B3.0, Air Quality – Supplemental Emission Modeling Informationand Greenhouse Gas Emissions Modeling.
The following revision has been made to update the calculations for construction emissions related to implementation of both the Active Adult Community and Tribal Planning Areas.
Page Revision
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Table 5.2-10
Combined Construction Emissions
Pollutant (pounds/day)
Source VOC NOx CO SOx PM10 PM2.5
Year 2015
Maximum 1.099 20.43 39.3737 0.06 6.916.80 3.783.76
SCAQMD 75 100 550 150 150 55
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Pollutant (pounds/day)
Source VOC NOx CO SOx PM10 PM2.5
threshold
Threshold
Exceeded? No No No No No No
Year 2016
Maximum 9.9516.83 36.6372.18 131.31236.37 0.190.34 12.667.23 3.732.85 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? No No No No No No
Year 2017
Maximum 259.64278.94 6.2282.06 54.84326.90 0.090.53 7.7111.70 2.084.26 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Year 2018
Maximum 259.23276.77 5.7877.86 50.00302.85 0.090.53 7.7111.66 2.084.22 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Year 2019
Maximum 258.91275.13 5.4274.31 46.37284.92 0.090.52 7.7111.62 2.084.19 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Year 2020
Maximum 260.21273.64 15.0369.95 61.06268.62 0.120.52 7.8711.57 2.154.15 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Year 2021
Maximum 260.02263.03 14.8221.49 59.01100.22 0.120.21 7.874.62 2.151.53 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Year 2022
Maximum 258.31261.18 4.7711.30 39.5279.01 0.090.18 7.714.54 2.081.48 SCAQMD
threshold 75 100 550 150 150 55
Threshold
Exceeded? Yes No No No No No
Note: Refer to the data sheets in Appendix 3.0B, Air Quality – Supplemental Emission Modeling Informationand Greenhouse Gas Emissions Modeling.
Abbreviations: CO = carbon monoxide; NOx = nitrogen oxide; PM10 = particulate matter less than 10 microns; PM2.5 = particulate matter less than 2.5 microns; VOC = volatile organic compounds; SCAQMD = South Coast Air Quality Management District; SOX = sulfur oxide.
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Section 5.4.C Cultural Resources
The following revision has been made to clarify language and proper characterization of MM 5.4-1.
Page Revision
5.4-18 MM 5.4-1 Prior to the start of any ground disturbing activities within the Project Site, the Agua Caliente Band of Cahuilla Indians (Tribe) Tribal Historic Preservation Officer (THPO) shall be notified of the pending activities. A qualified archaeologist shall coordinate with the THPO during the drafting for the archaeological monitoring plan and the plan shall allow for the archaeologist in consultation with the THPO to determine the timing of when monitoring is no longer necessary. During earth moving disturbances that involve excavation activities, if there is any evidence of Native American resources (significant or otherwise), the THPO will be notified and construction activities modified in accordance with the archaeological monitoring plan.
Section 5.5.C Geology and Soils
The following revisions has been made to clarify language and proper characterization.
Page Revision
5.5-18 MM 5.5-1 As part of final design development, a detailed geotechnical and soils investigation shall be conducted by a registered engineering geologist for review and approval by the City of Rancho Mirage Building and Safety Division, if annexed into the City, the Tribe Tribal Engineer, or the County Engineer as applicable, prior to the issuance of grading and building permits.
The following revisions has been made to clarify language and proper characterization.
Page Revision
5.5-19 MM 5.5-2 All grading and earthwork recommendations from the Project geotechnical and soils reports, including any updates, must be incorporated into the final Project design, including the final grading, drainage and erosion control plans, or other plans deemed necessary by the City of Rancho Mirage Building and Safety Division, if annexed into 12-3130
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the City, the Tribal Engineer, or the County Engineer as applicable, and must ensure they meet the City’s Building Code requirements set forth in the City Municipal Code, the Tribe Tribal Land Use Ordinance, or the County Municipal Code as applicable. All grading activities must be supervised by a certified engineering geologist: Final grading, drainage, and erosion control plans must be reviewed and approved by the City of Rancho Mirage Building and Safety Division before the City issues a grading permit, by the Tribal Engineer, or the County Engineer, as applicable.
Section 5.6.B.4 Greenhouse Gases
The following revision has been made to update the CalEEMod calculations for construction GHG emissions related to the Active Adult Community.
Page Revision
5.6-23 As presented in Table 5.6-3, Active Adult Community Construction GHG Emissions, construction activities associated with the Active Adult Community would generate 4,770.86 1,559.45 MTCO2e GHG emissions.
The following revision has been made to update the CalEEMod calculations for construction GHG emissions related to the Active Adult Community.
Page Revision
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Table 5.6-3
Active Adult Community Construction GHG Emissions
Year
CO2e Emissions
(Metric Tons per Year)
2015 111.68
2016 654.88 758.55
2017 84.43
2018 109.92
2019 107.04
2020 134.37
2021 196.81
2022 56.65
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Year
CO2e Emissions
(Metric Tons per Year)
Total Construction GHG Emissions* 1,455.78 1,559.45
Annualized over Project Lifetime 48.53 51.98
Source: CalEEMod Emissions calculations are provided in Appendix 3.0B, Air Quality and Greenhouse Gas Emissions Modeling – Supplemental Emission Modeling Information.
Note: Totals in table may not appear to add exactly due to rounding in the computer model calculations.
Abbreviations: MTCO2e = metric tons of carbon dioxide emissions. *N2O emissions account for 0.06 MTCO2e/year.
The following revision has been made to update the CalEEMod calculations for operational GHG emissions related to the Active Adult Community.
Page Revision
5.6-24
Table 5.6-4
Active Adult Community Operational GHG Emissions
GHG Emissions Source
Emissions
(MTCO2e/year)
Construction (amortized) 48.5351.98
Operational (mobile) sources* 3,223.21
Area sources 329.60
Energy 4,054.66
Waste 109.18
Water 1,114.21
Annual Total 8,879.398,882.84
Source: CalEEMod Emissions calculations are provided in Appendix 3.0B, Air Quality – Supplemental Emission Modeling Information and Greenhouse Gas Emissions Modeling.
Notes: Totals in table may not appear to add exactly due to rounding in the computer model calculations.
Abbreviations: MTCO2e = metric tons of carbon dioxide emissions. *N2O emissions account for 0.1317 MTCO2e/year.
The following revision has been made to revise the Active Adult Community’s operational GHG emissions based upon the updated CalEEMod calculations.
Page Revision
5.6-24 As shown in Table 5.6-4, the operational GHG emissions for the Active Adult Community with Project Design Features and Mitigation Measures would be 8,879.39 8,882.84 MTCO2e per year.
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The following revision has been made to revise the GHG emissions for the Active Adult Community that would result from the business as usual scenario.
Page Revision
5.6-25 The business as usual scenario would result in GHG emissions (without Title 24 efficiencies, Project Design Features, or Mitigation Measures) of 11,763.65 11,767.14 MTCO2e per year.25 As indicated in Table 5.6-4, the Active Adult Community portion of the Project would result in 8,879.39 8,882.84 MTCO2e per year with Project Design Features and Mitigation Measures. The Project Design Features and Mitigation Measures would reduce GHG emissions by 2,884.26 MTCO2e per year, approximately
24.52 24.51percent, from the business as usual scenario.
25 11,714.99 MTCO2e per year BAU + 48.53 51.98 MTCO2e per year BAU Construction + 0.13 0.17 MTCO2e per year N2O = 11,763.65 11,767.14 MTCO2e per year BAU.
The following revision has been made to revise the combined construction GHG emissions.
Page Revision
5.6-28
Table 5.6-7
Combined Construction GHG Emissions
Year
CO2e Emissions
(Metric Tons per Year)a
2015 111.68
2016 746.381,171.62
2017 629.654,693.40
2018 811.484,974.29
2019
782.244,828.24
2020 784.644,366.22
2021 835.061,573.41
2022 406.01810.97
Total Construction GHG Emissions 5,107.1422,529.88
Annualized over Project Lifetime 170.24751.00
Source: CalEEMod Emissions calculations are provided in Appendix 3.0B, Air Quality – Supplemental Emission Modeling Informationand Greenhouse Gas Emissions Modeling. *N2O emissions account for 0.21 MTCO2e per year.
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The following revision has been made to revise the combined operational GHG emissions.
Page Revision
5.6-29
Table 5.6-8
Combined Operational GHG Emissions
GHG Emissions Source
Emissions
(MTCO2e/year)
Construction (amortized) 170.24751.00
Operational (mobile) sources* 19,860.16
Area sources 661.06
Energy 21,432.25
Waste 547.13
Water 3,229.10
Annual Total 45,899.9446,480.7
Source: CalEEMod Emissions calculations are provided in Appendix 3.0B, Air Quality – Supplemental Emission Modeling Information and Greenhouse Gas Emissions Modeling.
Note: Totals in table may not appear to add exactly due to rounding in the computer model calculations.
Abbreviations: MTCO2e = metric tons of carbon dioxide emissions. * N2O emissions account for 0.81 MTCO2e per year.
The following revision has been made to revise the combined business as usual scenario.
Page Revision
5.6-29 The combined business as usual scenario GHG emissions (without Title 24 efficiencies, Project Design Features, or mMitigation mMeasures) would be 82,065.58 82,646.10 MTCO2e per year.27 As indicated in Table 5.6-8, the Project Design Features and Mitigation Measures would reduce GHG emissions for the entire Project by 36,165.4064 MTCO2e per year to 45,899.9446,480.70 MTCO2e per year, a reduction of approximately 44.07 43.76 percent.
27 81,894.53 MTCO2e per year BAU + 170.24751.00 MTCO2e per year Construction BAU + 0.81 0.57 MTCO2e per year N2O emissions = 82,065.58 MTCO2e per year BAU emissions.
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Section 5.6.C Greenhouse Gases
The following revision has been made to clarify language and proper characterization.
Page Revision
5.6-34 MM 5.6-7 Prior to the issuance of each building permit, the applicant shall provide evidence to the appropriate Planning Department of the use of water efficient irrigation systems and devices, such as soil-based irrigation controls and use water-efficient irrigation methods consistent with measures recommended in the Voluntary Green Building Program, and any other green building standards adopted by the Tribe or City, and the Coachella Valley Water District water efficiency goals. In accordance with the appropriate program, the applicant shall provide evidence that building is consistent with the following Specific Plan-wide water conservation measures and/or does not prevent or conflict with the Specific Plan’s ability to meet the following water conservation measures:
• 90 100 percent of all builder-installed plumbing devices in each residential buildings shall be low-flow and water-efficient. • 90 100 percent of all builder-installed plumbing devices in each non- residential buildings shall be low-flow and water-efficient. • Turf shall not exceed 20 percent of the total landscaped area of each lot, with the exception of parks and recreation centers. • 80 percent of public and common landscape areas shall use smart irrigation systems per project.
• 80 percent of public and common landscape areas shall use drought-tolerant, native, and/or water-efficient plant materials per project.
Section 5.6.D Greenhouse Gases
The following revision has been made to clarify language and proper characterization.
Page Revision
5.6-35 D. Level of Significance of After Mitigation
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Section 5.8.A.1 Hydrology and Water Quality
The following revision has been made to clarify beneficial uses of the downstream receiving waters of Whitewater River, Coachella Valley Storm Water Channel, and Salton Sea.
Page Revision
5.8-7 The beneficial uses of the downstream receiving waters (Whitewater River, Coachella Valley Storm Water Channel, and Salton Sea) of the Project include but are not limited to agriculture supply, water-contact recreation, and warm fresh water habitat.
Section 5.8.A.2 Hydrology and Water Quality
The following revision has been made to incorporate County of Riverside regulatory information in regards to the design of flood hazard protection facilities.
Page Revision
5.8-14 Riverside County Ordinance No. 458
The County of Riverside adopted Ordinance No. 458 to specifically regulate development within FEMA-designated flood hazard areas, or also known as the 100- year flood hazard areas. This oOrdinance was adopted by the County as its participation in the National Flood Insurance Program (NFIP) of FEMA.34
34 Code of Federal Regulations, Title 44, Section 65.
The following revision has been made to incorporate Coachella Valley Water District (CVWD) regulatory information in regards to the design of flood hazard protection facilities.
Page Revision
5.8-16 Coachella Valley Water District Ordinance No. 1234.1 CVWD requires conditions of approval for development in flood hazard areas within the CVWD Stormwater Unit Boundary.36 The key provisions of this ordinance are as follows:
• Whitewater River/Coachella Valley Stormwater Channel: Designed and constructed utilizing the Standard Project Storm/Standard Project Flood (SPS/SPF) design standard. The SPS/SPF design standard will continue to be utilized for this facility, and for the analyses addressing impacts associated with lands adjacent to 12-3136
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this facility. The Whitewater River/Coachella Valley Stormwater Channel can be owned, operated, and maintained by CVWD or by a private entity that has an existing regional stormwater facilities agreement with CVWD. • Existing Tributary Regional Facilities: Designed and constructed utilizing the SPS/SPF design standard. The SPS/SPF design standard will continue to be utilized for these facilities and adjacent lands. These existing tributary regional facilities can be owned, operated, and maintained by CVWD or by a private entity that has an existing regional stormwater facilities agreement with CVWD. • Existing Tributary Regional Facilities (100-Year Storm/100-Year Flood): Designed and constructed utilizing the 100-Year Storm/100-Year Flood design standard. The 100-Year Storm/100-Year Flood design standard shall continue to be utilized for these facilities and for analyses addressing impacts associated with land adjacent to these facilities. These facilities will continue to be owned, operated, and maintained by an entity or party other than CVWD.
• Proposed Tributary Regional Stormwater Facilities: Design shall be based on the 100-Year Storm/100-Year Flood design standard. CVWD shall assume operation and maintenance of proposed 100-year tributary regional stormwater facilities unless the developer specifically requests to assume the operation and maintenance responsibility.
36 Coachella Valley Water District, Ordinance 1234.1, Guideline K-7, March 25, 2013.
The following information is added after the first full paragraph on page 5.8-29 to the discussion under the heading Otherwise substantially degrade water quality to address potential water quality impacts associated with the proposed water wells.
Page Revision
5.8-29 Furthermore, Project Design Feature 5.15.1-4 will ensure that all future wells developed on site would be constructed consistent with the CVWD Development Design Manual, and if groundwater testing for total chromium prior to installation indicates that the groundwater exceeds USEPA MCL, the water wells would provide treatment to reduce the level of chromium below USEPA MCL. Accordingly, water quality provided to 12-3137
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residents and employees in the Project Site would meet USEPA MCL standards under the Safe Drinking Water Act and water quality impacts would be less than significant.
Section 5.15.1.A.1 Water Supply
The following revision has been made to clarify language and proper characterization.
Page Revision
5.15.1-2 CVWD has been recycling reclaimed wastewater since 1967 and operates six WRPs, three of which currently provide recycled water for reuse.
The following revision has been made to clarify language and proper characterization within Section
5.15.1, Water Service.
Page Revision
5.15.1-3 The primary source of water supply for the Coachella Valley is the Coachella Valley Groundwater Basin, which is recharged by other sources of water such as Colorado River water, reclaimed irrigation return water, SWP supplies and potentially desalinated agricultural drain water.
The following revision has been made to clarify language and proper characterization.
Page Revision
5.15.1-6 Since 2010, groundwater levels in the eastern portion of the Coachella Valley have risenrose due to groundwater management activities, which include recharge of Colorado River water at the Thomas E. Levy Recharge Facility, and changes in private landowner water use practices.
The following revision has been made to modify the title for Table 5.15.1-9.
Page Revision
5.15.1-29 Table 5.15.1-9, Summary of Historical and Projected Average Water Suppliesy, shows the actual water supplies in 2010 as well as the projected water supplies from 1995 2010 through 2035.
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The following revision has been made to reflect Table 4-1, Projected Water Supplies in the CVWD 2010 Urban Water Management Plan within Table 5.15.1-9.
Page Revision
5.15.1-30
Table 5.15.1-9
Summary of Historical and Projected Average Water Suppliesy Year
Groundwater
Supply1
Treated Colorado
River Water
Supply2
SWP Exchange
WaterUntreated
Colorado River Water3
Recycled
Water
Desalinated
Drain Water Total Supply
1995 66,600 285,929 45,214 11,100 -- 408,843
1996 50,700 289,726 100,376 11,520 -- 452,322
1997 52,400 281,179 83,407 12,550 -- 429,536
1998 71,100 281,714 99,729 13,657 -- 466,200
1999 53,800 282,021 70,446 13,397 -- 419,664
2000 71,000 282,781 56,161 13,289 -- 423,231
2001 73,000 272,741 3,242 12,923 -- 361,906
2002 76,500 280,845 26,912 13,289 -- 397,546
2003 78,600 245,069 3,177 13,903 -- 340,749
2004 73,400 238,456 16,167 14,831 -- 342,854
2005 85,100 282,000 46,000 15,300 -- 428,400
2010 106,700109,488 318,0000 62,0000 23,100 4,0000 513,800109,488 2015 123,100118,700 342,0005,700 70,6001,300 25,100 8,0000 568,800125,800 2020 123,700125,600 379,00019,300 70,10011,100 26,500 8,0000 607,300156,100 2025 124,200129,900 404,00031,400 68,10026,300 27,600 11,0000 634,900187,700 2030 123,200133,500 429,00039,500 66,50039,000 28,300 11,0000 658,000212,000 2035 128,700 49,100 54,800 10,000 242,700
Source: CVWD, 2010 Urban Water Management Plan (July 2011) Table 4-1. 1 CVWD Share of net groundwater inflow to Whitewater and Mission Creek Subbasins, shared with DWA Service Area and private pumpers. 2 Net water deliveries to Coachella Valley, excluding conveyance losses.
Anticipated average availability assuming MWD calls-back 50 percent of the time in dry years.
Modified version of CVWD UWMP 2010 Update to account for advanced deliveries, DWR SWP 2013 Draft Reliability Report, and reductions to associate with Longfin Smelt and other issues
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Section 5.15.1.A.2 Water Supply
The following revision has been made to clarify language and proper characterization.
Page Revision
5.15.1-38 Safe DrinkingClean Water Act
The following revision has been made to clarify the Project Site’s proposed water wells.
Page Revision
5.15.1-52 PDF 5.15.1-4 All proposed water wells to be constructed within the Project Site shall be consistent with the CVWD Development Design Manual, and if groundwater testing for total chromium prior to installation indicates that the groundwater exceeds USEPA MCL, the water wells shall provide treatment to reduce the level of chromium below the USEPA MCL. The USEPA MCL is different from the California EPA MCL, in that the California EPA MCL only tests for one isotope of chromium, not total chromium.
The following revision has been made to clarify the Project Site’s proposed water wells.
Page Revision
5.15.1-54 Project Design Feature 5.15.1-4 will ensure that all future wells developed on site would be constructed consistent with the CVWD Development Design Manual, and if groundwater testing for total chromium prior to installation indicates that the groundwater exceeds USEPA MCL, the water wells would provide treatment to reduce the level of chromium below the USEPA MCL.
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APPENDIX 1.0
Mitigation Monitoring and Reporting Program
12-3141
Mitigation Monitoring and Enforcement Program
Section 24 Specific Plan
Agua Caliente Band of Cahuilla Indians
Adopted by:
Agua Caliente Band of Cahuilla Indians
5401 Dinah Shore Drive
Palm Springs, California 92264
February 2015
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Agua Caliente Band of Cahuilla Indians i Section 24 Specific Plan Project MMEP February 2015
TABLE OF CONTENTS
Section Page
1.0 Introduction ..................................................................................................................................... 1
1.1 Monitoring Authority ....................................................................................................................... 1
1.2 Enforcement Responsibility ............................................................................................................. 1
1.3 Monitoring Compliance Responsibility ............................................................................................ 2
1.4 General Monitoring Procedures ...................................................................................................... 2
1.5 Mitigation Monitoring Table ............................................................................................................ 3 12-3143
Agua Caliente Band of Cahuilla Indians 1 Section 24 Specific Plan Project MMEP February 2015
MITIGATION MONITORING PROGRAM
1.0 INTRODUCTION
As the Lead Agency under the Agua Caliente Tribal Environmental Policy Act (TEPA) (Tribal Ordinance No. 28), the Agua Caliente Band of Cahuilla Indians (“Tribe”) has decided to prepare the Environmental Impact Statement (EIS) for the Section 24 Specific Plan (“Project”) in accordance with TEPA, as well as to prepare this EIS in compliance with the substantive and procedural requirements of the California Environmental Quality Act (CEQA). The Tribe will adopt a program for reporting, enforcing, and monitoring the implementation of mitigation measures adopted for the Project, to ensure that the adopted mitigation measures are implemented as defined in the Final EIS and/or Record of Decision for the Project.
As set forth in TEPA, the Tribal Council of the Agua Caliente Band of Cahuilla Indians (“Tribal Council”) will make a final decision, in the form of a Record of Decision, with respect to the Project’s requested actions after review and consideration of this EIS. As part of the Record of Decision, the Tribe has adopted a monitoring and enforcement program and summarized all applicable mitigation in this Section, as defined under the Code of Federal Regulations (CFR), Title 40, Chapter 5, Part 1505.2(c) (Record of decision in cases requiring EIS).
While compliance with CEQA is not required at this time, the Lead Agency responsibility to adopt such a program originates in Public Resources Code section 21081.6(a) (Findings), and the State CEQA Guidelines sections 15091(d) (Findings), and 15097 (Mitigation Monitoring or Reporting).
Projects, activities, and decisions implemented under the Project would be overseen by the agencies having jurisdiction over affected lands and resources. Lead, Responsible, and Cooperating Agencies having approval or oversight responsibilities for some aspect of the Project would consider each applicable measure identified in the EIS at a project level, making any necessary adjustments in the measures to account for the specific nature and location of the project proponent and its impacts. The agencies would ensure that issues identified in the EIS are adequately considered and addressed as part of the Project implementation. This responsibility would apply to all actions within the scope of this EIS that are subject to further TEPA or CEQA review.
1.1 MONITORING AUTHORITY
The purpose of a Mitigation Monitoring and Enforcement Program (MMEP) is to ensure that measures adopted to mitigate or avoid significant impacts are implemented. A MMEP can be a working guide to facilitate not only the implementation of mitigation measures by individual project proponents, but also the monitoring, compliance/enforcement and reporting activities of the appropriate jurisdiction, in this 12-3144
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Agua Caliente Band of Cahuilla Indians 2 Section 24 Specific Plan Project MMEP February 2015
case either the Tribe, the County of Riverside (County), the City of Rancho Mirage (City), the Riverside Local Agency Formation Commission (LAFCo), or the Coachella Valley Water District (CVWD).
The appropriate jurisdiction may delegate duties and responsibilities for monitoring to other environmental monitors or consultants as deemed necessary, and some monitoring responsibilities may be assumed by responsible agencies, such as affected jurisdictions and cities, and state agencies. The number of monitors assigned to the Project will depend on the number of concurrent operation activities and their locations. The Tribe’s Chief Planning and Development Officer (or equivalent position or appropriate agency representative) or his/her designee(s), however, will ensure that each person delegated duties or responsibilities are qualified to monitor compliance and enforcement. It is the responsibility of the environmental monitor assigned to each measure to ensure that appropriate agency reviews and approvals are obtained.
1.2 ENFORCEMENT RESPONSIBILITY
The project proponent is responsible for successfully implementing all of the adopted mitigation measures in the MMEP. The MMEP guides implementation of mitigation measures and specifies the type of compliance, monitoring, and reporting required with regard to those measures.
Any assigned environmental monitor shall note problems with monitoring, notify appropriate agencies or individuals about any problems, and report the problems to the Tribes’ Chief Planning and Development Officer (or equivalent position for the applicable agency representative) or his/her designee. The Tribes’ Chief Planning and Development Officer (or equivalent position for the applicable agency representative) or his/her designee will also ensure that any deviation from the procedures identified under the monitoring program is approved by the Tribes’ Chief Planning and Development Officer (or equivalent position for the applicable agency representative).
1.3 MITIGATION COMPLIANCE RESPONSIBILITY
The Tribe, County, City, or CVWD, as appropriate for the applicable jurisdiction, will be responsible for enforcing the procedures adopted for monitoring the implementation of each mitigation measure.
Standards for successful mitigation are included in some of the adopted mitigation measures. Additional mitigation success thresholds may be established by applicable agencies with jurisdiction through the permit process and through the review and approval of specific plans for the implementation of mitigation measures.
1.4 CHANGES TO MITIGATION MEASURES
Any substantive change in the monitoring and reporting plan made by the applicable jurisdiction shall be reported in writing to the Tribe’s Chief Planning and Development Officer (or equivalent position for the 12-3145
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applicable agency representative) or his/her designee(s). Reference to such changes shall be made in the monthly/yearly Environmental Mitigation Monitoring and Enforcement Report prepared by the appropriate jurisdiction. Modifications to the mitigation measures may be made by the appropriate jurisdiction subject to one of the following findings, documented by evidence included in the record:
(a) The mitigation measure included in the Final EIS and/or Record of Decision and the MMEP is no longer required because the significant environmental impact identified in the Final EIS has been found not to exist, or to occur at a level which makes the impact less than significant as a result of changes in the project, changes in conditions of the environment, or other factors.
OR
(b) The modified or substitute mitigation measure to be included in the MMEP provides a level of environmental protection equal to or greater than that afforded by the mitigation measure included in the Final EIS and/or Record of Decision and the MMEP.
The modified or substitute mitigation measure does not have significant adverse effects on the environment in addition to or greater than that which was considered by the responsible hearing bodies in their decisions on the Final EIS and the proposed project.
The modified or substitute mitigation measure is feasible, and the appropriate jurisdiction, through measures included in the MMEP or other agency procedures, can assure its implementation.
1.5 MITIGATION MONITORING TABLE
Table 1, Mitigation Monitoring and Enforcement Program – Section 24 Specific Plan, presents the mitigation monitoring requirements for each adopted mitigation measure.
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APPENDIX 2.0
Traffic Report—Highway Capacity Software Calculation Worksheets 12-3177
12-3178
12-3179
12-3180
12-3181
12-3182
12-3183
12-3184
12-3185
12-3186
12-3187
12-3188
12-3189
12-3190
12-3191
12-3192
12-3193
APPENDIX 3.0
Air Quality—Supplemental Emission Modeling Information
12-3194
Appendix 3.0-a
Updated CalEEMod Files
12-3195
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