Tag: environmental baseline

Third District Upholds the Department of Water Resources’ Long-Term Extensions of State Water Project Contracts under CEQA, the Delta Reform Act, and the Public Trust Doctrine

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In Planning and Conservation League v. Department of Water Resources (Cal. Ct. App., Jan. 5, 2024, No. C096304), the Third District Court of Appeal upheld an EIR prepared by the Department of Water Resources (DWR) for DWR’s approval of amendments to long-term water supply contracts with local water agencies receiving State Water Project (SWP) water. These contract amendments extended the terms of the SWP water supply contracts to 2085 and expanded DWR’s ability to use revenue bonds. In a victory for DWR and the SWP water contractors, the court upheld DWR’s EIR against an array of CEQA challenges. The court also rejected the petitioners’ claims that the amendments violated other legal requirements, including the Delta Reform Act, the Public Trust Doctrine, and the Burns-Porter Act.

By way of background, in the 1960s, DWR and 29 local government contractors entered into long-term (75-year) contracts granting the contractors rights to a portion of water from the SWP in exchange for the local agencies’ financial obligations. Each contract includes a table, “Table A,” that specifies the maximum annual water allocation, although full delivery is not guaranteed and often amounts to about half the Table A amount.

The contracts include an “evergreen clause” that allows the contractors to opt for continued service beyond the contract’s expiration by giving advanced notice. Several contractors exercised this option, leading to negotiations for long-term extensions of the contracts. The negotiations aimed to address the “debt compression problem,” where the impending contract termination limited bond maturity to 17 years, increasing the repayment costs. DWR and the contractors reached an agreement in principle to extend the contracts to 2085, which would allow for longer-term bond funding for essential capital upgrades and repairs. They also agreed to a revenue bond amendment that updates the definition of water system facilities to include post-1987 repairs and approved capital projects.

DWR prepared an EIR for the proposed amendments. The EIR concluded that the amendments would not cause environmental impacts because they would not alter the existing authority to build or modify SWP facilities, change water allocations, or create new water management measures.

After certifying the EIR, DWR filed a validation action to validate the amendments. Thereafter, several conservation groups and public agencies brought legal challenges the EIR and the validation action. The trial court ruled in favor of DWR and the petitioners appealed.

CEQA

DWR properly assumed the existence of the current contracts in the EIR’s environmental baseline.

The petitioners argued that the EIR’s impact analysis was based on an improper baseline because the baseline included the current water contracts. The court explained that to determine whether a project’s environmental impacts are significant, the agency must compare the project against existing environmental conditions—the baseline. When a project involves ongoing activities or the extension of past activities, the current levels of use and their physical impacts are part of the baseline.

The court explained that this rule is applicable to renewing permits or approvals for existing facilities, even if those facilities had not been previously assessed under CEQA. Accordingly, the court held that DWR appropriately included the existing contract conditions in the environmental baseline. DWR was not required to use a hypothetical baseline “that imagines a world” without the contracts.

DWR did not improperly piecemeal the Project in excluding a Delta conveyance facility from the project definition.

The petitioners argued that the EIR’s analysis was inadequate because it failed to consider related projects – including a future Delta conveyance facility, such as the previously proposed “California WaterFix” project – as part of the proposal, leading to an overly narrow project description and improper piecemealing.

The court explained that CEQA requires an environmental analysis to consider the whole of an action affecting the environment. An agency may not divide a larger project into smaller segments, which might individually have minimal environmental impacts but could collectively result in significant environmental damage. Further, as held in Laurel Heights Improvement Assn. v. Regents of University of California (1988) 47 Cal.3d 376 (Laurel Heights I), an EIR must analyze the environmental effects of any future expansions or actions that are a foreseeable consequence of the initial project and might alter its scope or environmental effects.

The petitioners argued that the trial court relied too heavily on the Laurel Heights I criteria, asserting that a broader “related to” test should apply and that actions that are close in time and location must be considered part of a larger project. The court rejected the petitioners’ argument, explaining that later opinions have confined such reasonings to situations in which a project legally necessitates or assumes the completion of another action, a situation that was not present here.

The court next explained that the courts have interpreted Laurel Heights I variously, with some concluding that a project is part of a larger project under CEQA if it is a “crucial element” of a larger project, such as when one project cannot proceed without the other. Other courts have held that there may be piecemealing when the project at issue is a first step or a catalyst toward another project. On the other hand, there is no piecemealing when the projects can be implemented independently.

Here, DWR properly treated the contract amendments as a stand-alone project, distinct from a future Delta conveyance facility. The record demonstrated that the amendments have separate, independent purposes from a Delta conveyance, such as addressing the bond compression issue. While the amendments may possibly aid in financing a conveyance facility, they serve broader purposes and address other challenges. Moreover, the record showed that there is considerable uncertainty as to whether a Delta conveyance facility would ever be approved or constructed. In light of these factors, DWR was not required to treat a potential, uncertain Delta conveyance as part of the same project as the contract amendments.

DWR did not need to assess the direct, indirect, and cumulative effects of projects that would benefit from the amendments’ bond funding.

The petitioners argued that the EIR should have evaluated the direct and indirect impacts of enabling a Delta conveyance project. The court found that this argument suffered from the same flaws as the petitioners’ piecemealing argument: the possibility of a Delta conveyance in the future is too speculative in terms of both its timing and scale. Lead agencies are not required to speculate about potential impacts.

The petitioners also argued that DWR should have evaluated the impacts of other capital projects financed by the amendments, such as the Oroville hydroelectric license project. Petitioners, however, failed to properly present this argument by failing to discuss these other projects or explain why their effects should be considered impacts of the amendments. Moreover, the argument was baseless. The EIR clarified that the amendments would support a variety of long-term capital projects. According to the petitioners’ logic, DWR would be obligated to predict the impacts of all of these projects in the EIR for the amendments, an expectation that is unreasonable. Further, the court noted, projects that are merely governmental funding mechanisms or fiscal activities that do not commit to any specific project that could have environmental effects are not subject to CEQA. Although these capital projects may be part of DWR’s overall plans for the SWP, their connections to the amendments is too tenuous: the amendments do not commit DWR to these projects and do not authorize revenue bonds for any of them (which would require a separate approval).

The EIR’s project description complied with CEQA and was not misleading or inconsistent.

The petitioners asserted – and the court rejected – three arguments regarding the EIR’s project description. First, the petitioners argued that depicting the Delta conveyance facility as a separate project in the EIR conflicted with statements made in earlier environmental review documents. The petitioners cited various documents to support this assertion, but failed to explain how these documents substantiated their position. Moreover, the court’s examination of the cited documents did not reveal any inconsistencies.

Second, the petitioners argued that identifying the 2085 extension date in the EIR was misleading and inaccurate because the EIR did not reveal DWR’s expectation of successive contract extensions under the existing contracts’ evergreen clauses. But petitioners failed to support this argument with any analysis or authority. Furthermore, the record demonstrated that there are clear differences between applying the evergreen clause to individual contracts and achieving a long-term extension for all contractors.

Third, the petitioners argued that the EIR incorrectly stated that the amendments would not change the authority under the current contracts to construct new or modify existing facilities. They argued that the amendments would remove limitations on revenue bond eligibility for new facilities, potentially financing new or expanded facilities. The court rejected this argument as inconsistent with the EIR’s project description, which made these facts plain by explaining that the amendments would offer enhanced funding mechanism that could fund new or expanded facilities.

The petitioners failed to show that the EIR’s range of alternatives was unreasonable.

CEQA requires an EIR to identify and evaluate a reasonable range of alternatives that could achieve most of the project’s basic objectives while avoiding or significantly reducing its adverse environmental effects. DWR’s objectives for the amendments included financing the SWP past 2035, maintaining funding reserves, simplifying the billing process, and improving financial coordination between DWR and the contractors. In addition to a no-project alternative, the EIR analyzed seven alternatives, including different contract extension lengths with or without financial amendments, bond sales extending beyond the current contract expiration, and a scenario where not all contractors agreed to the amendments. Two additional alternatives were considered, but rejected from further consideration in the EIR: reducing the “Table A” amounts and implementing new water conservation provisions.

The petitioners argued that DWR’s selection of alternatives violated CEQA in three ways. First, in a single-sentence argument, the petitioners asserted that the alternatives were not sufficiently different to constitute a reasonable range. The court summarily rejected this argument because the petitioners failed to provide any authority or analysis to support it. It was incumbent on the petitioners to show that the range of alternatives were manifestly unreasonable or identify evidence of a least one potentially feasible alternative that would meet most of the basic objectives while reducing the project’s impacts. The petitioners’ one-sentence statement did not satisfy this burden.

Second, the petitioners argued that the revenue bond amendment creates financial risk and that the EIR should have analyzed an alternative that excludes that amendment. The court rejected this argument, explaining that CEQA is not a statute for economic protection, and economic impacts alone do not qualify as significant environmental impacts. Moreover, the no-project and the extension-only alternative evaluated in the EIR sufficiently covered the exclusion of the revenue bond amendment.

Third, the petitioners challenged DWR’s rejection of alternatives to reduce Table A amounts and to implement new water conservation measures, arguing that these alternatives would reduce environmental effects and would align with other state laws and policies. The court rejected this argument, explaining that agencies are not required to analyze alternatives that would solve broader problems or add complex issues that the agencies had chosen not to address. Here, DWR deliberately limited the EIR’s scope to financial issues related to the SWP contracts and made a reasoned decision to exclude Table A amounts from the project’s scope. DWR was not required to analyze alternatives that address bigger issues than the problems DRW is trying to address.

DWR properly defined the no-project alternative as the water contracts proceeding without the amendments, rather than termination of the contracts.

An EIR is required to evaluate a “no project” alternative; the purpose of this requirement is to compare the environmental impacts of not approving the project with those that would occur if the project is approved. Here, the EIR’s no-project alternative assumed that operations and financing of the SWP would continue under existing contracts until December 31, 2035, with contract terms potentially extended beyond this date through the evergreen clause. Under this scenario, water services would continue beyond 2035 in line current financial terms, no bonds would be sold with maturity dates past 2035, and the debt compression issue would worsen. The EIR concluded that this alternative, like the amendments, would not lead to direct physical environmental impacts because it would not introduce new water management measures, change DWR’s authority to build or modify facilities, or alter water allocation in the existing contracts.

The petitioners argued that DWR should have considered, as the no-project alternative, a scenario in which the contracts are allowed to expire. According to the petitioners, relying on the evergreen clause as part of the no-project alternative is inappropriate because: (i) application of the evergreen clause might itself be a project; (ii) the evergreen clause does not guarantee an extension of all contract provisions; and (iii) the evergreen clause does not account for other future changes to the SWP that DWR has acknowledged. The petitioners further asserted that DWR’s analysis blurred the distinction between the no-project scenario and the amendments, thereby failing to provide a clear and factual analysis of maintaining the status quo.

The court rejected these arguments. The court explained that the analysis of the no-project alternative must consider current conditions and what can reasonably be expected in the foreseeable future if the project is not approved. In reviewing a no-project alternative, the court’s focus narrowly on whether the EIR adequately describes existing condition and offers a plausible vision of the foreseeable future. Here, DWR’s no-project met these standards. Given the long history of the SWP and its critical role in supplying water to the state, as well as the long-term investments of the contractors in the SWP, DWR was not required to treat termination of the contracts as the no-project alternative.

Petitioners failed to demonstrate that recirculation of the EIR was required.

CEQA requires a lead agency to recirculate an EIR for further public review and comments when the agency introduces “significant new information” to the EIR before its certification. The court held that petitioners failed to meet that burden by failing to provide any facts or analysis of the information added to the EIR was “significant” within the meaning of CEQA.

The petitioners further claimed that recirculation was required because DWR added additional information regarding the rejected “Table A amount reduction” alternative in the final EIR. The court explained, however, that the added discussion was not “significant” because it did not reveal any new environmental impact or an increase in the severity of an impact, and did not deprive the public of a meaningful opportunity to comment on a substantial adverse effect or a feasible mitigation measure or alternative that the project’s proponents declined to implement. Rather, the additional information added to the final EIR served only to clarify and amplify the conclusions of the draft EIR, and therefore did not trigger recirculation.

Delta Reform Act

Under the Delta Reform Act, any state agency planning to undertake a “covered action” must first certify in writing that the action is consistent with the Delta Plan. This certification, including detailed findings, must be submitted to the Delta Stewardship Council before the covered action is implemented. (Water Code, § 85225.) A “covered action” is defined in Water Code section 85075.5 as a plan, program, or project that meets certain criteria and is not exempt.

Here, DWR determined that the amendments were not a covered action and therefore did not prepare a certification of consistency with the Delta Plan. The petitioners, in contrast, asserted that the amendments constituted a covered action. The court agreed with DWR that the amendments were not a covered action.

The court observed that, viewing the Delta Reform Act holistically, several points stand out. First, the Act primarily targets “future developments,” rather than existing ones. Second, a covered action is defined as an action occurring within the Delta or Suisun Marsh boundaries. Third, such actions must significantly impact California’s water supply reliability or the Delta ecosystem. Fourth, routine maintenance and operation of the SWP are not included as covered actions. While the court did not delve into the exact meaning of “routine maintenance and operation,” it found it fair to say that the existing SWP is generally exempt from being a covered action.

Applying these insights, the court held that the amendments do not qualify as a covered action. The amendments merely extend existing contracts with SWP contractors and enhance DWR’s ability to finance improvements and new facilities for the SWP using revenue bonds, subject to certain approvals. They do not physically take place in the Delta, nor do they modify the developed uses of the SWP. Therefore, the DWR’s decision not to prepare a certification of consistency with the Delta Plan was not erroneous.

Public Trust Doctrine

The petitioners argued that, under the California Supreme Court’s decision in National Audubon Society v. Superior Court (1983) 33 Cal.3d 419 (National Audubon), DWR had an affirmative duty to take the public trust into account in approving the amendments. The court disagreed, reasoning that a closer reading of National Audubon indicates that the high court was specifically concerned about the approval of water diversions. This distinction is significant because DWR does not approve water diversions—that task is performed by the State Water Resources Control Board.

Furthermore, the court found that the record supported DWR’s conclusion that the amendments do not impact a public trust resource. The water rights at issue were granted by the State Water Board in 1967 and have been amended by that board several times. The contracts giving the contractors interest in those water rights “were executed in the 1960s and allow the contractors to extend their interests indefinitely.” Under this framework, it was reasonable for DWR to conclude that extending the terms of the contracts to 2085 would not have impacts on resources held in the public trust.

The court also rejected the petitioners’ argument that, under National Audubon, DWR has a “‘continuing duty to supervise’” the taking and use of the appropriated water. The court explained that petitioners took the statements in National Audubon out of context in that, in National Audubon, no agency had ever considered the public trust in relation to the challenged water diversions and their harm to Mono Lake. The court in the present case declined to translate the “continuing duty of supervision” described in National Audubon as imposing a continued duty on DWR to supervise the water rights with which it operates the SWP. In this context, DWR’s duty under the public trust doctrine is only triggered when DWR is taking an action with an impact on public trust uses. Since there is no such impact here, the duties to weigh the public trust interests or consider additional protections do not apply.

Remaining Arguments Against Validation of the Amendments

Finally, the court rejected several other arguments raised by the petitioners challenging the amendments’ validation.

The Validation Action Was Not Premature

The petitioners argued that DWR’s validation action was premature. The Court of Appeal rejected this contention, explaining that the 60-day limitation period for bringing a validation action and the public policy of a speedy determination of a public agency’s action undermined the petitioners’ claim of prematurity. Furthermore, the petitioners failed to cite any authority to support the position that prematurity is a valid defense against a validation action.

The Amendments Are Consistent with the Burns-Porter Act

Under the Burns-Porter Act, any income from the sale, delivery, or use of SWP water or power must be placed into a special fund. This fund is then used for various purposes, following a strict order of priority established by the Act. The highest priority is for funding the annual maintenance and operation costs of the SWP, including replacing any parts of the SWP as needed. The petitioners argued that the amendments – specifically the extension amendment and the revenue bond amendment – were inconsistent with this first priority requirement. The court disagreed, finding that nothing in the amendments disrupts or contravenes the established priority order for the use of funds as set forth in the Burns-Porter Act.

DWR Complied with Water Code Section 147.5

Water Code section 147.5 outlines the procedures DWR must follow when renewing or extending long-term water supply contracts. Specifically, that statute requires DWR to present details of the contract terms at an informational hearing before the Legislature at least 60 days before final approval of the contract.

The petitioners claimed that DWR failed to meet these requirements because it submitted only draft amendments, not the final version, to the Legislature. The court rejected this argument, finding that Water Code 147.5 only mandates a presentation to the Legislature 60 days before contract approval and does not specify that the contract must be in its final form at this stage. The informational hearing could lead to further amendments, and the statute not require another hearing for such changes. Moreover, the purpose of Water Code Section 147.5 is to ensure high-level oversight of the renewal or extension of SWP long-term contracts, not to involve the Legislature in overseeing the details of finalizing these contracts.

The Petitioners failed to support their argument that the amendments are unconscionable.

The petitioners argued that it was unconscionable for DWR to reauthorize the terms of the existing contracts regarding water delivery amounts because those terms are impossible or impractical to fulfill. The Court of Appeal, like the trial court before it,  declined to consider this argument because the petitioners failed to offer any legal authority to support it.

DWR acted within its authority in approving the amendments.

Lastly, the petitioners argued that validating the amendments is improper because, according to the petitioners, the amendments provide DWR “absolute power” to enter into “unbounded” contracts. The petitioners, however, failed to demonstrate how validating the amendments would give DWR absolute and unrestricted contracting authority, particularly given that the validation action is limited to contracts tied to or directly related to DWR bonds. Validating the amendments does not give DWR a “free pass” to base its decisionmaking on “paper water.”

Conclusions and Implications

At bottom, the petitioners’ CEQA arguments in this case rested on two mistaken assumptions: first, that the amendment would transform the SWP, possibly leading to expanded SWP operations and a Delta conveyance project; and second, that without the amendments, the existing SWP contracts would terminate. The court rejected these assumptions. Although future capital improvement projects within the SWP may benefit from bond funding under the amendments, such future projects are speculative and not a reasonably foreseeable consequence of the amendments. Furthermore, the court found that it is reasonable for DWR to assume that the terms of the existing contracts will continue, regardless of these particular amendments. The contracts’ evergreen provision authorizes the contractors to request the same amount of continued water service indefinitely and several contractors had already exercised that option. Furthermore, California’s residents and farms depend on continued delivery of SWP water, and the contractors have invested enormous sums in the SWP. The court agreed with DWR’s pragmatic view that it is more plausible to anticipate contract extensions than their termination.

Having rejected the underlying premises of the petitioners’ claims, the court applied straightforward analyses to the petitioners’ CEQA claims. Case law firmly establishes that when a project proposes the continuation of existing activities, the baseline includes those activities. Therefore, DWR properly included the current contracts, including current operation of the SWP, as part of the baseline. Impacts caused by the current operation of the SWP are not impacts of the proposed amendments.

The law is also clear that projects with independent utility need not be treated as part of a larger project under CEQA. Here, the amendments have utility independent of future improvements to the SWP, including a potential Delta conveyance project. Moreover, such future projects are not a consequence of the amendments, since such projects could proceed with or without the amendments. In addition, CEQA does not requires agencies to speculate about the consequences of future, uncertain activities.

– Laura M. Harris

Second District Court of Appeal Holds That Reduced Parking at National Monument is not a Direct Environmental Impact and Upholds Alternatives Analysis with Only a “No Project” Alternative.

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In Save Our Access—San Gabriel Mountains v. Watershed Conservation Authority (2021) 68 Cal.App.5th 8, the Second District Court of Appeal held that the plaintiff failed to show that reduced parking within the San Gabriel Mountains National Monument would cause any adverse physical changes in the environment, that the lead agency did not abuse its discretion in setting the baseline for parking based on aerial photography that was not included in the record, and that, based on the project’s purpose, analyzing only a “no project” alternative was a reasonable range of alternatives.

FACTUAL AND PROCEDURAL BACKGROUND

The San Gabriel Mountains National Monument was designated in 2014. The project site includes 198 acres along two and a half miles of the East fork of the San Gabriel River, including public roads, recreational facilities, and the riverbed itself. The site is significantly degraded due to heavy public use and a lack of adequate facilities. The project was proposed to improve and better manage recreation facilities along with ecological restoration and reducing environmental impacts associated with recreational use at the site.

The EIR discussed existing issues associated with parking, including the small number of designated parking spaces and the widespread practice of parking in undesignated areas, which created public safety and traffic issues throughout the site. In total, the EIR estimated that there was a total of 417 parking spaces throughout the site, of which only 48 were designated parking spaces. The estimates were based on aerial photography that was included in the EIR. The EIR also included survey data that found that average weekend use at the site from Memorial Day to Labor Day was 273 vehicles per weekend day. To address the parking and related issues, the project proposed to create a total of 270 designated car spaces and three bus spaces, and to reduce undesignated parking with a combination of signage and physical barriers.

The EIR analyzed the project’s potential impacts to recreation and concluded, based on survey data, that impacts would be less than significant because many users of the site would choose to recreate in other nearby areas if parking or other facilities were unavailable, and, given the number and variety of recreation opportunities in proximity to the site, the impacts of those users going elsewhere would be disbursed and would not be cumulatively considerable. The EIR concluded that all impacts associated with the project would be less than significant with mitigation. The alternatives analysis compared the proposed project to a “no project” alternative but did not analyze any other alternatives.

The plaintiff filed a petition for writ of mandate challenging the Watershed Conservation Authority’s certification of the EIR and approval of the project. The trial court granted the petition, in part, based on the court’s conclusion that (1) the parking baseline lacked substantial evidence support because the aerial photography the baseline relied on was not in the record; (2) the agency failed to disclose the exact number of parking spaces available in each area of the site; (3) the parking survey was unsupported by substantial evidence because of the time of day when the surveys took place; and (4) without an accurate parking baseline, the EIR failed as an informational documents because the proposed parking reduction could be significant and require mitigation.

THE COURT OF APPEAL’S DECISION

Reversing the trail court’s decision, the Court of Appeal determined that the EIR adequately discussed the project’s proposed reduction in total parking spaces and that the alleged discrepancy in total parking spaces (plaintiff alleged that there were 473 available spaces, rather than 417) was immaterial because plaintiff failed to identify any adverse physical impacts on the environment resulting from the reduced parking. The court noted that, in fact, the purpose of reducing and formalizing parking at the site was to protect and restore the environment.

The court went on to analyze two CEQA cases addressing parking issues. First, the court considered San Franciscans Upholding the Downtown Plan v. City and County of San Francisco (2002) 102 Cal.App.4th 656, which held that the inconvenience associated with “hunting” for scarce parking was not an environmental impact, but secondary effects, like traffic and air quality are. Accordingly, the court determined that an EIR need only address the adverse secondary effects of limited parking, not the social impact itself. The court also reviewed Taxpayers for Accountable School Bond Spending v. San Diego Unified School Dist. (2013) 215 Cal.App.4th 1013, which rejected the school district’s argument that a parking shortage is “never” a direct physical environmental impact. The court reasoned that each case must be decided on its facts, and that while, in some cases parking deficits may have direct physical impacts on the environment, plaintiff had not shown that the project’s parking reduction would result in direct or secondary physical impacts on the environment.

Turning to the EIR’s analysis of recreation impacts, the court found that the EIR’s analysis of nearby recreational facilities and likely impacts was adequate and that the EIR’s assumptions, based on survey data, were reasonable. The court rejected plaintiff’s speculation that, instead of leaving to recreate elsewhere, visitors to the project site would “circle and idle” until a parking space became available. Thus, the EIR’s conclusion that recreation impacts would be less than significant was supported by substantial evidence.

Regarding alternatives, the court focused on the EIR’s discussion of alternatives that were considered, but not analyzed in the EIR. The EIR explained that, through a series of workshops, three project design concepts were proposed and assessed for their ability to achieve the purposes of the project, but only one (the project), was selected for study in the EIR, along with the required “no project” alternative. The agency also considered an alternative proposed by the California Department of Fish and Wildlife but decided not to analyze it in the EIR either. The plaintiff argued that, as a matter of law, analyzing only one alternative was inadequate. The court rejected plaintiff’s argument, finding that, although CEQA and the Guidelines use the term “alternatives” (i.e., the plural form), the law is clear that the range of alternatives is subject to a rule of reason, and that each case must be evaluated on its facts. The court rejected the plaintiff’s argument that several feasible alternatives were proposed to the agency by a nearby business owner who was concerned that reduced parking at the site would impact his business. The court concluded that plaintiff had failed to show how the proposed alternatives would attain most of the basic project objectives or feasibly avoid or lessen one or more of the project’s significant impacts. The court found, on the facts of this case, that the inclusion of only a “no project” alternative was reasonable, given the purpose of the project and that the project, with mitigation, would not result in any significant impacts.

Lastly, plaintiff argued that the project was inconsistent with the Angeles National Forest Land Management Plan (LMP) and the designation creating the San Gabriel Mountains National Monument. Plaintiff’s argument centered around the reduction in parking and claimed that the corresponding reduction in access to the National Monument created inconsistencies. The court rejected this argument, finding that it elevated public access above all the other objectives and policies in the declaration. The court reasoned that the agency was required, under the proclamation and LMP, to balance public access with other concerns, including protection of the environment, and that the project did so.

– Nathan O. George