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1998 CEQA Guidelines Revisions: What Every CEQA Practitioner Needs to Know Prepared by Maureen F. Gorsen General Counsel, California Resources Agency October 1998 October 26, 1998 marks the conclusion of a five year effort by the Governor Wilsonss Office of Planning and Research and the California Resources Agency to update the CEQA Guidelines to reflect statutory and case law revisions and to provide guidance on some of the more knotty issues presented to decisionmakers in following the CEQA process.1 Such issues include the following: what point in time to choose for the baseline for measuring the significance of environmental effects whether there are effects that could be considered "de minimis" in a cumulatively impacted environment at what point a projects incremental impacts are "cumulatively considerable" when to rely on prior EIRs analysis of cumulative impacts whether the re-permitting of a facility falls within the existing facilities exemption or is a new project what are the role of regulatory standards in detemining significance how to analyze impacts on historical resources. They are designed to assist lead agencies in making these and other difficult discretionary determinations required by the CEQA process. And with one exception, they are due to be effective at the end of October 1998.2 The latest revisions are the third set to be proposed and adopted by the Resources Agency since 1993. Over the past five years, over 120 sections to the CEQA Guidelines have been revised and updated. This latest set revises approximately sixty (60) sections. This article highlights the twenty (20) or so of those revisions which have received the most attention during the public comment period and which are likely to be of most immediate interest to CEQA practitioners. They are grouped by topic: determining significance, determining the scope of priate analysis in an EIR, exempting environmentally beneficial activities, and improving CEQAs roadmap. DETERMINING SIGNIFICANCE No subject addressed in the CEQA Guidelines over the past few years has been more controversial than the revisions assisting lead agencies in the job of determining the significance of effects which may be caused by projects they are reviewing. Arguably, the two most important discretionary determinations that a lead agency must make in the CEQA process are whether the environmental consequences of the project are "potentially significant" and whether the environmental consequences of the project are, in fact, "significant" on the basis of the information in the environmental impact report ["EIR"]. And, it is easy to see why these two issues are so debated and so controversial. Both decisions affect the timing and cost of projects and the amount of environmental protection, either by requiring the preparation of an environmental impact report ["EIR" } and/or by requiring the project to avoid or mitigate those effects found significant. Guidance to lead agencies in making these critical determinations is found in several sections of the Guidelines. Section 15064 provides the basic guidance to lead agencies in determining the significance of a projects effects. Section 15065 provides the conditions for which lead agencies are mandated to determine significance and thus, require preparation of an EIR or require mitigation to reduce the effect to less than significant in order to prepare a mitigated negative declaration. Appendices G and I provide optional tools to assist lead agencies in determining the significance of particular effects. In current form, these sections have been criticized for "insufficient guidance on how to determine when an environmental effect is significant" and the "[c]onfusion, delay and uncertainty," that result when different and conflicting approaches to the same issues are taken by the lead agency in the EIR and other agencies under their regulatory programs." 3 The State Bar Environmental Law Section recommended that "[t]o increase certainty in significance determinations, the Guidelines should be amended to provide clearer guidance on impact significance."4 The UC Berkeley California Policy Seminar similarly called for the development and adoption of standardized thresholds of significance.5 The CEQA Workgroup of the Bay Area Economic Forum also recommended the inclusion of state and federal significance criteria.6Responding to this criticism and in a modest attempt to fulfill the recommendations of these expert commentators, the latest revisions: (1) clarify the role of regulatory standards in determining significance; (2) add a section to encourage lead agencies to develop and publish cognizable thresholds of significance; (3) assist lead agencies in the threshold determination of whether a projects impact is cumulatively considerable; (4) merge and enhance Appendices G and I to provide a better tool to lead agencies in determining the level at which an effect is significant; and (5) add a section to address impacts to historical and archeological resources. Clarifying the Role of Regulatory Standards in Determining Significance (New 15064(i)) 7Effective August 24, 1998, subsection (i) of 15064 is revised to guide lead agencies to rely on the vast body of regulatory standards have been adopted over the past few decades establishing levels at which impacts to a particular resource is a substantial or potentially substantial adverse effect on a particular environmental resource. The change to §15064(i) is intended only to direct lead agencies to consistently and predictably refer to standards in their significance determination under CEQA. It is important to note that subsection (i) only applies to the extent that there exists a standard for a particular effect being examined by the lead agency and that standard has undergone rigorous public review and otherwise meets the conditions of the subsection. Encouraging Thresholds of Significance (New §15064.7) In addition to encouraging more predictable reliance on existing regulatory standards, new section 15064.7 attempts to stimulate more certainty and consistency by encouraging lead agencies to develop and publish the thresholds that the agency uses in determining the significance of environmental effects caused by projects under its review. Lead agencies, under current statute and guidelines, are required to determine whether a project may cause a significant effect on the environment. 8 The addition of this section merely encourages lead agencies to identify the criteria they use to make this determination and to develop such criteria though a public review process supported by substantial evidence. In so doing, all interested and expert persons would be able to present scientific data and standards, the validity of which would be openly debated by conflicting experts. This revision opens up this secretive decision to the public where a lead agencys decision can be subjected to and compared with the best scientific data and standards.9Additionally, once a threshold of significance has been published, any interested party may be able to ascertain the standard of significance for a particular resource in a certain community. By knowing the standard in advance, thresholds may likely encourage increased use of alternative designs and locations to substantially lessen the potential significant environmental impact of projects. At a minimum, it provides public agencies with a method of putting in place a degree of predictability in their significance determination process. Determining when a Projects Incremental Impact is Cumulatively Considerable (New 15064(j) 10/15130)New subsection 156064(j), together with additions to section 15130, make clear the difference between the cumulative impacts analysis required in an initial study and that required in an EIR. Current section 15064 does not provide any guidance to lead agencies in determining at what level a projects incremental impact, although individually insignificant, may be "cumulatively considerable".11 The additions to 15064 make clear that the question of whether a projects effects are "cumulatively considerable" is different than the question of whether a project has "significant cumulative effects." The former is governed by Guidelines sections 15064 and 15065 while the latter is governed by section 15130 and 15355. The focus in the initial study is on the projects incremental impact. An agency considers the effects of other projects only as a context for determining whether the incremental effects of the project under review are "considerable."12 This revision makes clear, consistent with CEQAs statutory scheme, that the need for an EIR turns on the impacts of the project under review, not the impacts of other past, present or future projects. This subsection also provides a definition of a "de minimis" impact as an incremental contribution where the environmental conditions would be essentially the same whether or not the proposed project is implemented and explains that such minimal impacts do not trigger the need to prepare an EIR. It also permits lead agencies, similar to section 15064(i) for individual significance, to determine that an incremental effect is not cumulatively considerable where the project complies with the requirements of a previously approved plan or program that will avoid or mitigate the cumulative problem. Enhanced/ Integrated Appendix G - a tool for assisting lead agencies in determining just when an environmental effect is significant Existing Appendix G lists a broad range of project consequences that serve as examples of "potentially significant" effects on the environment. The current Appendix G was drafted 25 years ago at a time when CEQA was a new law and the question of what is a "significant effect on the environment" was unknown and unclear. Twenty-five years later, lead agencies have a better idea of what consequences are generally considered a significant environmental effect and the Appendix has outlived its usefulness. More importantly, as many commentators have noted, the current Appendix G offers no specific direction on how to determine the level at which an environmental effect is "significant."13 The proposed new Appendix G (consolidated with Appendix I) is designed to remedy this deficiency by replacing the current vague list with an enhanced initial study checklist, organized by resource topic and referencing federal, state and local laws and regulations containing precise qualitative and quantitative standards that are commonly used thresholds in practice. In addition to providing more clear criteria to lead agencies in determining the significance of particular impacts, the new checklist integrates references to the numerous statutes dealing with specific environmental impacts (e.g. California Endangered Species Act) and standards developed by numerous regulatory bodies focused on particular environmental problems (e.g. San Francisco Bay Conservation and Development Commission, South Coast Air Quality Management District) in dealing with environmental impacts to certain important resources. In so doing, the Guidelines achieve the important statutory goal of integrating the requirements of CEQA with the environmental requirements of other laws. 14 Several new and notable questions are added to the new Appendix G. Lead agencies are asked to consider impacts to candidate, sensitive and species of special concern under the biological resources heading. Questions regarding effects to water efficient or fire resistent landscaping, and other drought and flood impacted areas are added to the checklist. A new heading is added grouping questions related to impacts to agricultural resources. Lead agencies are asked to consider a broader array of impacts on agricultural resources and the existing requirement to consider "prime" farmland is expanded to include "unique" farmland and "farmland of statewide importance." Lastly, as required by a recent revision to the statute, the new Appendix G incorporates the Land Evaluation Site Assessment model prepared by the Department of Conservation as an optional model for determining when conversions of farmland are significant. Determining the Significance of Impacts to Archeological and Historical Resources, Mitigating for Those Impacts and Protecting Those Resources (New §§15064.5/15126.4/15331) The addition of these sections was made necessary by revisions to the statute made in the early 1990s and the woefully inadequate and outdated guidance provided in existing Appendix K. 15 Appendix K has been deleted and the still relevant guidance it contained was moved into the body of the Guidelines in new sections 15064.5 and 15126.4. In order to resolve the conflict between the narrow and limiting statutory provision for mitigation of archeological resources and the broadly protective statutory provision for determining the significance of historical resources, section 15064.5(c) provides that to the extent an archeological resource is also an historical resource, the provisions regarding historical resources apply.These revisions are precedent-setting in their endorsement of the first set of standardized mitigation measures for historic resources. The new sections provide that projects following the Secretary of the Interiors Standards for Treatment of Historic Properties shall be considered as mitigated to a level of less than significant. Among other provisions, they put lead agencies on notice that, in many circumstances, the very popular method of mitigating impacts on historical resources by way of documentation (e.g. historic narrative, photographs or architectural drawings) will not mitigate the effects to a point where clearly no significant effect on the environment would occur. Additionally, a new categorical exemption, section 15331, is added for projects limited to restoration or rehabilitation of historical resources consistent with the Secretary of the Interiors Standards.
DETERMINING THE SCOPE OF ANALYSIS IN AN EIR CEQA sets out a process by which public agencies inform themselves of the environmental consequences of their actions or the actions over which they have decision-making authority. Unfortunately, over the past two decades, the terms and concepts of CEQAs information requirements have grown, more to stave off threats of litigation than to foster informed decision-making. In its 1995 report, the California Policy Seminar found that "[a]lthough the idea of analyzing alternatives, cumulative impacts and growth-inducing impacts may be good in theory, in practice such analyses are usually incomplete, poorly done, and confusing to the decisionmaking process ... Rather than focusing on how best to mitigate the adverse impacts of realistic alternatives, the DEIR commenting process then becomes one of choosing among nonexistent and unfeasible alternatives." 16 The Legislative Analyst's report identified as CEQAs weakness the "complexity and unpredictability of the CEQA process, the costs of compliance, and the ease for legal challenges... " and observed that this growing open-endedness was leading to analyses which "contribute little to the decision-making of public agencies."17Several revisions in Article 9 of the CEQA Guidelines, entitled "Contents of EIRs," are an effort to restore CEQA and the EIR as an information document that can lead to better decisions and decisions which more accurately reflect the environmental consequences of projects over which the public agency has decision-making authority. These revisions provide a clear description of the environmental setting, a definition of the baseline, and provide guidance on how to discuss the no project alternative, on the scope of cumulative impact analysis and the focus of a responsible agencys review of a draft EIR. Determining the Environmental Setting and the Baseline The Guidelines require a description of the environmental setting "before the commencement of the project" in order to examine and analyze the effects of the physical change in the environment after the project is commenced and completed. "Before the commencement of the project" has been one of those unfortunate terms which has been subjected to much debate and a near infinite variety of interpretations over the past twenty years. Many have interpreted this to require an EIR to reconstruct a past setting (e.g. pre-CEQA) or a future setting (e.g. post-traffic or infrastructure improvements). Efforts spent on EIRs describing and predicting historical or future conditions may be interesting and intellectually-challenging to the preparer, but they are costly, time-consuming and, more importantly, they don't describe the environment which actually exists "before the commencement of the project." In 1994, the Legislature amended the statute to make clear that CEQA review is required for activities which may cause a physical change in the environment. 18CEQA review is therefore required to focus on changes in the physical environment and therefore an EIR need describe the environmental setting so that the changes can be seen in context. The revisions to section 15125 make clear that the existing environmental setting is the baseline physical conditions that exist "before the commencement of the project," meaning right before the commencement of the project, or as the guideline will now read, "at the time the notice of preparation is published, or if no notice of preparation is published, at the time environmental analysis is commenced." They also make clear the purpose of providing a description of the existing setting in an EIR, that is, to provide meaningful context to examine the physical changes from the project, by explicitly defining it as the "baseline" for measuring the significance of a projects effects.Determining the Difference Between the Baseline and the No Project Alternative Whereas the existing environmental setting or baseline is the physical conditions before a project commences, the no project alternative is the physical conditions likely to occur if the project is not approved. It may be the same as the baseline or status quo, but more often it is not. New section 15126.6 expands on the guidance previously found in 15126(d)(4) and discusses the different methods for analyzing the no project alternative. 19 Importantly, this revision urges lead agencies and EIR preparers to identify the practical result of a projects non-approval and not create or analyze a set of artificial assumptions that would be required to preserve the existing physical environment.Determining the Scope of Cumulative Impacts Analysis Section 15130 has been amended to include much of the same criteria found in new subsection 15064(j) for determining the significance of a cumulative impact. Guidance has been added to assist lead agencies in determining the scope of analysis. Subsection (b)(1)(B)3 encourages lead agencies to adopt a standardized approach regarding the geographic range for analyses. Subsection (b)(1)(B)2 defines the scope of probable future projects by providing a list of projects that are reasonable to anticipate, such as projects for which an application has been received, projects included in adopted capital improvement programs or public projects for which money has been budgeted. The California Policy Seminar reported: If there is one thing upon which everyone who has studied CEQA agrees, it is that effective large-scale impact mitigation cannot be undertaken on a piecemeal or project-by-project basis. Although the CEQA Guidelines have been broadened to require the identification of cumulative impacts, none of the communities we examined has been able effectively to mitigate cumulative impacts. The difficulties inherent in cumulative impact assessment are not just analytical. Mitigations that represent the best practice at the project level may actually be counterproductive at the community or regional level. CEQAs emphasis on project-by-project reviews, and its resulting inability to promote cumulative impact mitigation and environmental enhancement, is its single biggest failure. Acknowledging, as the California Policy Seminar report found that "project by project review of impacts is not adequate for identifying and mitigating cumulative development impacts," and "[e]ven when cumulative impacts are properly identified, there is usually very little that can be done at the (specific) project approval stage to ameliorate them," subsections (d) and (e) of 15130 encourage broader regional planning to avoid and/or mitigate cumulative impacts. Here and elsewhere, the revisions encourage an expanded use of tiering from specific, area, redevelopment and general plans for identification, analysis and mitigation of localized cumulative environmental impacts. See sections 15152, 15183 and Appendix J - the new graphic guide to tiering. Determining the Focus of Review in an EIR Revisions to section 15204 emphasize that CEQA requires a good faith disclosure but not an exhaustive, bulletproofing exercise where every research or study or information requested or suggested is required. It asks reviewers to base their comments on facts and opinions supported by facts. It requires responsible and trustee agencies to base their comments on information germane to its expertise and to provide as much detailed information as it can about how the lead agency can mitigate significant effects identified by them. These revisions, with others in Article 9, aspire to restore the EIR as an information tool to assist public agencies in understanding the actual environmental consequences of activities they undertake or approve.
EXEMPTING ENVIRONMENTALLY BENEFICIAL ACTIVITIES Public Resources Code §21084 authorizes the Secretary of the Resources Agency to prepare lists of classes of projects which have been determined not to have a significant effect on the environment and hence be exempt from CEQA. As with all the current categorical exemptions, for example, new construction of small structures (15303) or minor additions to schools (15314), the Secretary defines a subset of projects with conditions that as a class do not have a significant effect on the environment. These revisions create three new categorical exemptions for activities which are environmentally beneficial (15330, 15331, 15332), clarify and update three existing categorical exemptions (15301, 15316, 15325), and make complete the list of exceptions to use of a categorical exemption (15300.2). Facilitating Clean Up of Hazardous Waste Of the new categorical exemptions, only two received much public comment. The third, section 15331, for projects restoring or rehabilitating historic structures, was previously addressed in this article. 20 Section 15330 creates an exemption for minor clean up actions to minimize or eliminate the release or threat of release of hazardous substances. The request for this addition came from the Department of Toxic Substances Control. Currently, negative declarations are prepared for these minor clean up actions which delays these important and environmentally beneficial actions for three months. While many public commentors had concern that some waste removal actions could have significant environmental effects, theAgency dealt with each concern by adding a restriction to eliminate the possibility raised by the commentor. The restrictions included are very clear and limit the application of this section (i.e. exemption cannot be relied upon if the action requires on-site use of a hazardous waste incinerator, involves the relocation of persons or business or potential release of volatile organic compounds) so that the potential for the occurrence of a significant effect is eliminated. Further, any actions relying on this exemption must be consistent with state and local environmental permitting requirements. Delineated examples, such as construction of temporary surface caps, are included. Preserving Agricultural Land and Preventing Urban Sprawl The other notable new exemption creates an incentive to prevent urban sprawl and preserve agricultural land by exempting a narrow class of infill development projects without some of the restrictions that have made the statutory infill exemptions unworkable. According to practitioners and others involved in CEQA practice, the comparable statutory exemptions are of little practical value given the plethora of restrictions attached to their use. The result is that developers look elsewhere other than urban, previously developed areas to develop. Those areas usually happen to be agricultural lands, open space, etc. at the fringe of the urban limits where land is plentiful and cheap. Proposed section 15333 attempts to prevent that from occurring by encouraging development in previously developed areas, with restrictions to ensure that the Secretary can make the requisite finding of no significant effect, but not as many restrictions as contained in statute to ensure practical application. Promote Preservation of Habitat, Open Space, Parks and Historic Resources Two existing categorical exemptions are expanded to promote local efforts to preserve and expand habitat areas and open space and provide incentives to create ownership interests in land for open space and habitat. Sections 15325 expands the existing exemption for transfers of land to preserve open space to "habitat" and "historic resources." It also expands the methods for such transfers from acquisition to "acquisition, sale or other transfer" to give proper recognition of the fact that public agencies may not only acquire but transfer rights to another agency, non-profit entity, land trust, or individual for purposes of preservation or restoration. Section 15316 has similarly been expanded to permit innovative transactions in order to establish a park. Clarify and Update Existing Categorical Exemption While the above two expansions were well-received, the clarification to the existing facilities exemption, which more properly belongs in the "improving the roadmap" section below, met with some opposition. The revisions make clear that "permitting, leasing, and licensing" of a project which will involve negligible or no expansion of use beyond that previously existing, are included in the term "operation" consistent with case law interpreting this issue. 21 This is declaratory of existing law and does not exempt any projects that are currently subject to CEQA.An activity which involves no physical change in the environment does not meet the definition of "project" under CEQA. 22 The definition of "project" includes permitting, leasing and licensing activities to the extent that they have the potential to result in a direct physical change in the environment or a reasonably foreseeable indirect physical change in the environment.23 Public Resources Code §21068 defines "significant effect on the environment" as substantial adverse change. The emphasis in the statute is on change and the requirements for analysis are for physical change. This revision adds language to clarify that the focus on the applicability of this exemption shall be the measure of "negligible or no expansion of use" of an existing facility.
IMPROVING THE ROADMAP The primary mandate that these revisions fulfill is to provide objectives, criteria and guidelines for the orderly evaluation of projects and the preparation of EIRs and negative declarations consistent with CEQA.24 In short, these revisions seek to improve the roadmap for lead agencies to follow. In addition to all the improvements discussed above, some of the other important roadmap improvements are outlined below. Sections 15073.5 and 15088.5 advise lead agencies how to handle public comments when recirculation is required, especially where there are duplicative comments or comments as to a portion of the first EIR which has been made obsolete after recirculation. Section 15004(b)(3)(A - C) advises lead agencies on the appropriate timing of environmental review. As recommended in the State Bar, Environmental Law Section report, the revisions instruct lead agencies not to take actions (such as committing funding or entering land acquisition agreements) that would foreclose meaningful choice of alternatives or mitigation measures. Section 15124(d) is intended to better integrate CEQAs requirements with related federal, state and local environmental requirements. Sections 15041 and 15126.4 provide standards for good mitigation measures and new Appendix G encourages upfront identification of mitigation measures. Section 15097 provides guidance on what is an adequate mitigation monitoring and reporting program to ensure that prior measures adopted to minimize environmental effects are enforced and completed to provide the intended environmental protection. Lastly, many revisions recognize that public input and access is a hallmark of CEQA and a vital component of its effectiveness as a force for environmental protection. The revisions encourage public agencies to use the Internet for all of their notice and posting requirements and direct public agencies to submit environmental documents in electronic form, where available, to the Office of Planning and Research. (Sections 15062, 15075, 15085, 15202 and sections 15205, 15206, respectively.)
CONCLUSION This third, most comprehensive, and ambitious revision to the CEQA Guidelines during the Wilson Administration reflects the thinking that has developed since the 1991 Ueberoth report and in subsequent reports of the Little Hoover Commission, the Legislative Analyst Office, the Bay Area Economic Forum, the State Bar and Associations of Planners and Environmental Professionals on the problem areas in CEQA. It reflects the thoughtful comments received by the public in over seven (7) solicitations for written comments and oral comments made at over ten (10) public hearings in the past five years. In addition, it reflects upon other natural resources policy goals that have marked Doug Wheelers tenure as Secretary of the Resources Agency, such as agricultural land conservation, historical resource protection, ecosystem habitat planning and the creative and innovative ways his Agency has pursued these goals. These revisions restore a degree of certainty, predictability and rationality to the regulations that are the roadmap to public agencies in implementing CEQA. They more accurately reflect the complex and interrelated universe of environmental laws and regulations that has matured with the CEQA process in addition to resolving the problems identified and studied since the last revision of the Guidelines in 1986. The revisions bring definition and clarity to the many vague and subjective standards such as "significant effect," "substantial evidence," "probable future projects", and the scope and requirements of alternatives analysis and cumulative effects analysis. These revisions also provide a much needed update to the Guidelines to bring greater comprehension to reflect recent statutory changes and case law. And, it is hoped that in so doing, these regulatory accomplishments will have helped restore CEQA to its primary purpose of informing decision-makers of the environmental consequences of their actions and, more importantly, will have increased the ability of public agencies to make on-the-ground, substantive environmental protection.
Maureen F. Gorsen is the General Counsel for the California Resources Agency. Her responsibilities include review of all significant legal matters relating to the laws and programs of the Resources Agency. Among other duties, she is responsible for reform and revisions to the California Environmental Quality Act and issues relating to the California Endangered Species Act. For questions regarding this article or related issues, she can be reached at maureen@resources.ca.gov or 916-653-5656. Acknowledgement must be given to many for this accomplishment. To Governor Pete Wilson, for his leadership. To Secretary Douglas P. Wheeler, for his vision. To my predecessor, James T. Burroughs, for commencing and designing the blueprint of the five year effort. To Antero Rivasplata, Chief Planner for the Governors Office of Planning & Research, for drafting the text and contributing to it his scrupulous, encyclopedic knowledge of the law and practice of CEQA. To the Resources Agencys two Assistant General Counsels, Steve Greene and Matthew Francois, and many law clerks, for the long hours, hard work, commitment to and enthusiasm for the subject. To all the editorial advisors, for the expert advice and experience they generously lent to the effort. The addition of 15064(i) clarifying the role of regulatory standards in the significance determination was proposed and adopted separately in its own rulemaking pursuant to the Administrative Procedure Act. It became effective August 24, 1998. It can be viewed at the CEQA homepage [ http://www.ceres.ca.gov/ceqa]. Streamlining CEQA: An Action Agenda, CEQA Task Force, California Chapter, APA/AEP, pp. ES-5, 5-1 (March 12, 1993). Task Force on the Relationship of Government Operations and Regulations to Economic Competitiveness, Report of the CEQA Work Group, Bay Area Economic Forum, p. 7 (November 1995). The California Environmental Quality Act: Assessment and Recommendations, State Bar of California, Environmental Law Section, p. 30 (January 21, 1995). Landis, et al., Fixing CEQA: Options and Opportunities for Reforming CEQA, California Policy Seminar (1995). Task Force on the Relationship of Government Operations and Regulations to Economic Competitiveness, Report of the CEQA Work Group, Bay Area Economic Forum, p. 5-2, 7 (November 1995). This subsection will be relettered (h) upon approval by the Office of Administrative Law of the deletion of subsection (e). Proposed subsection (j) will be relettered (i). Approval is expected in late October 1998. Public Resources Code §21080. Public Resources Code §21082 requires all public agencies to adopt "objectives, criteria, and procedures for the evaluation of projects and the preparation of environmental impact reports and negative declarations." In Fixing CEQA, the authors state that "the fundamental problem with CEQA is that it fails to encourage fairness and consistency in the review process or in required impact mitigations". (p.180). They note a "tremendous variation in the types, quantity, and quality of environmental impact mitigation." (Id.) This "significance surprise" - where significance of impacts is determined behind closed doors by a few persons on a project-by-project basis - is the cause for the lack of certainty and predictability that plagues the CEQA process. Interestingly, the authors note that it is the same stakeholders who decry lack of fairness and consistency that often support maximum flexibility in the CEQA process. "Although many actors in the local CEQA review process decry its lack of fairness and consistency, the same players who complain about unpredictable reviews also often support maximum flexibility in the development approval process. Developers often benefit from local flexibility, because in most case local governments do not require them to complete EIRs. . . . Local decisionmakers value flexibility because they like to make decisions based on immediate political concerns, including re-election. Planning staff value flexibility because it often allows them to dispense with procedural requirements they consider unnecessary and sometimes grants them bargaining power within the development process that they would otherwise lack." (p.180) The State Bar, Environmental Law Section report echoed that "project proponents and the public are not aware of what level of CEQA review will occur until an Initial Study is prepared, or even later . . ." and attributed it to the fact that "project proponents have no reliable standards to use in planning their projects in advance to avoid significant effects." (State Bar, p.27) To escape this chaos and subversion of the CEQA process, the authors of Fixing CEQA recommend that local governments be required to develop and adopt standardized thresholds of significance and that state and regional agencies play a predictable role in local reviews. To be relettered (i), if approval by OAL to delete subsection (e) is granted. Public Resources Code §21083(b). "Cumulatively considerable" means that incremental effects of an individual project are considerable when viewed in connection with the effects of other current projects, and the effects of probably future projects." Public Resources Code §21083(b); San Joaquin Raptor/Wildlife Rescue Center v. County of Stanislaus (1996) 32 Cal.App.4th 608. The California Environmental Quality Act: Assessment and Recommendations, State Bar of California, Environmental Law Section, p. 30 (January 21, 1995).Public Resources Code §21003. Public Resources Code §21084.1. [Added.Chapter 1375, Statutes of 1992]; Public Resources Code §21083.2. [Amended. Chapter 375, Statutes of 1993]. UC Berkeley California Policy Seminar Report at page 179. It should be noted that revisions to the CEQA Guidelines proposed in 1993 and effective in 1994 established the "rule of reason" and "feasibility" as key factors in alternatives analysis, incorporating the reasoning in the Laurel Heights and Goleta cases. Laurel Heights Improvement Association v. Regents of the University of California (1993) 6 Cal. 4th 1112; Citizens of Goleta Valley v. Board of Supervisors (1990) 52 Cal.3d 553. CEQA: Making It Work Better, Legislative Analyst Office, page 10, (March 20, 1997). Public Resources Code §21065. [Amended, Chapter 1230, Statutes of 1994]. As section 15126, entitled "Consideration and Discussion of Environmental Impacts" had become unwieldy, it was been divided into four sections, an overview section outlining the requirements for the content of an EIR (new §15126), and then breaking out the rest of old 15126 into three sections, providing guidance on the requirements for consideration and discussion of significant environmental impacts (15126.2), mitigation measure proposed to minimize significant effects (15126.4), and alternatives to the proposed project (15126.6). See discussion under heading entitled Determining the Significance of Impacts to Archeological and Historical Resources, Mitigating for Those Impacts and Protecting Those Resources (New §§15064.5/15126.4/15331) on page 6. Bloom v. McGurk (1994) 26 Cal. App.4th 1307. Public Resources Code §21065. 14 California Code of Regulations §15378. Public Resources Code §21083.
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