Majority
When ARB adopted the original LCFS regulations in 2009, it violated the California Environmental Quality Act (CEQA; Pub. Resources Code, § 21000 et seq.[1] ). In 2013, we identified those violations and directed the issuance of a writ of mandate compelling ARB to take corrective action. ( POET, LLC v. State Air Resources Bd. (2013) 218 Cal.App.4th 681 , 160 Cal.Rptr.3d 69 ( Poet I ).) Now, we consider whether ARB's actions satisfied that writ and corrected one of its CEQA violations. The specific question presented is whether ARB's disclosures about the project's effects on biodiesel consumption, and the related increases in nitrogen oxide (NOx) emissions, satisfied paragraph 3 of the writ of mandate.
The writ provisions were drafted by this court. Therefore, we interpret paragraph 3 of the writ without deference to the trial court or ARB. We used the term "project" in paragraph 3 of the writ in the same way it is used in CEQA, the Guidelines[2] and CEQA case law. Stated generally, "project" includes the whole of an activity directly undertaken by a public agency. More specifically, when the agency's activity involves a regulation (as compared to building a physical structure, such as a road or power plant), the whole of the activity constituting the "project" includes the enactment, implementation and enforcement of the regulation. Here, the term "project" includes the whole of ARB's activity in promulgating and enforcing (1) the regulations originally adopted in 2009 and (2) the replacement regulations adopted in 2015 in response to the writ of mandate issued pursuant to Poet I .
Consequently, ARB's view that the "project" included only the regulations adopted in 2015 was wrong and explains why it incorrectly chose 2014 NOx emissions as the baseline. The proper baseline for a project normally is the conditions existing when the environmental review of the project is commenced. Here, ARB's review commenced before the regulations were first approved in 2009. Thus, ARB's use of 2014 NOx emissions as the baseline was improper and generated flawed results when that baseline was plugged into the formula for calculating environmental change. Specifically, NOx emissions in 2014 were higher than the NOx emissions prior to the 2009 approval of the LCFS regulations, which caused ARB's most recent calculations of the yearly changes in NOx emissions to be too low and thus misleading. ARB's flawed analysis of NOx emissions did not cure the CEQA violation identified in Poet I or comply with paragraph 3 of the writ.
1 All unlabeled statutory references are to the Public Resources Code.
2 "Guidelines" refers to the regulations promulgated to implement CEQA, which are set forth in California Code of Regulations, title 14, section 15000 et seq. (§ 21083, subds. (a), (f) ["Office of Planning and Research shall prepare and develop proposed guidelines" and "Secretary of the Resources Agency shall certify and adopt guidelines"].)
Most providers of petroleum and biofuels in California are subject to the reporting and carbon intensity value requirements
In December 2009, plaintiffs POET, LLC and James M. Lyons filed this litigation to challenge the LCFS regulations, alleging violations of CEQA and California's Administrative Procedure Act (APA; Gov. Code, § 11340 et seq. ). In November 2011, the trial court denied plaintiffs' petition for writ of mandate and filed a judgment in favor of ARB. Plaintiffs appealed.
In May 2013, oral argument was held in the appeal. In June 2013, this court issued an order requesting input from counsel regarding the terms of the disposition and attached a tentative disposition. We asked counsel to make certain assumptions, including that certain CEQA violations had occurred and the LCFS regulations would be allowed to continue to operate. We stated our preference for a disposition "drafted so the superior court can take the language from the disposition and insert it into the peremptory writ of mandate" and asked counsel to take this into account when proposing changes or alternatives to the tentative disposition. Our order sought input on six topics of interest, including (1) maintaining the status quo and whether the 2014 standards should have been allowed to go into effect and (2) the framework for ARB's analysis of NOx emissions on remand.
On July 15, 2013, our opinion in Poet I was filed. We reversed the denial of plaintiffs' petition for writ of mandate and remanded for the issuance of a writ directing ARB to correct its CEQA and APA violations. In August 2013, we denied ARB's
Corrective Action Relating to NOx Emissions
The portion of the February 2014 writ relevant to this appeal concerns the deficiencies in ARB's analysis of NOx emissions and mitigation measures for any significant adverse environmental impact resulting from increased NOx emissions. ARB's actions to comply with the writ and remedy its CEQA violations are described in part I.D, post .
ARB's Return, Discharge Order, Stay Requests and Appeal
In November 2015, ARB filed its return to the February 2014 writ. (See pt. I.D.4, post .) In January 2016, the trial court issued an order discharging the writ. (See pt. I.D.5, post .) On February 5, 2016, plaintiffs filed a motion to stay the order discharging the writ pending an appeal. On February 29, 2016, the trial court's order denying the motion for a stay was served on the parties without holding a hearing.
On March 4, 2016, plaintiffs filed a notice of appeal from the order discharging the writ and the order denying their motion for stay pending appeal. Plaintiffs then filed a petition for writ of supersedeas requesting a stay of the order discharging the writ pending a decision in this appeal. We denied the writ and request for a stay, even though plaintiffs established a strong
6 Our concern about the overall impact of suspending the LCFS regulations can be described as the-baby-with-the-bathwater problem. In other words, we were concerned that suspending the LCFS regulations might result in a loss of the baby (i.e., the reduction of various greenhouse gases) to resolve the problem of dirty bathwater (i.e., an improper CEQA analysis of NOx emissions).
3. Interpreting the February 2014 Writ
The parties' dispute over ARB's compliance with the February 2014 writ is primarily a conflict about how to interpret the writ's provisions. We drafted the language in the writ that is the subject of the present dispute and, more fundamentally, we identified the CEQA violations the language was designed to remedy. Thus, we
ARB's 2009 draft environmental disclosure document did not ignore the question of "whether the substitution of biodiesel for petroleum-based diesel would increase emissions of NOx." ( Poet I , supra , 218 Cal.App.4th at p. 704, 160 Cal.Rptr.3d 69 .) Instead, ARB sidestepped and never reached the question of whether any increase would constitute a " 'significant effect on the environment.' " (§ 21083, subd.
8 Unless the context requires otherwise, subsequent references in this opinion to the significance of an effect on the environment include significance based on the three conditions listed in section 21083, subdivision (b). Thus, the references to whether an increase in NOx emissions is significant includes whether the incremental increase attributable to the project is "cumulatively considerable" for purposes of section 21083, subdivision (b)(2). (See Guidelines, §§ 15130 [discussion of cumulative impacts], 15355 [definition of cumulative impacts].)
C. The Disposition from Poet I
Our decision in Poet I dealt with the foregoing CEQA violation involving NOx emissions from biodiesel and with other CEQA violations. It (1) reversed the judgment denying plaintiffs' writ petition; (2) remanded the matter for further proceedings; (3) directed to trial court to grant plaintiffs' petition and issue a writ of mandate; and (4) specified terms to be included in the writ of mandate. ( Poet I , supra , 218 Cal.App.4th at p. 766, 160 Cal.Rptr.3d 69 .) The terms in the writ required ARB to set aside its approval of the LCFS regulations.[10] ( Ibid . ) In addition, ARB was required to select a single decision maker to complete the project's environmental review before reapproving the LCFS regulations or approving a modified version of the regulations. ( Id . at pp. 765, 767, 160 Cal.Rptr.3d 69 .) The third numbered paragraph in the disposition compelled ARB to:
"Address whether the project will have a significant adverse effect on the environment as a result of increased NOx emissions, make findings (supported by substantial evidence) regarding the potential
10 Setting aside an approval is different from setting aside (i.e., suspending or invalidating) the regulations.
regarding the potential adverse environmental effect of increased NOx emissions, and adopt mitigation measures in the event the environmental effects are found to be significant."
Whether ARB complied with the paragraph 3 and what appellate relief is appropriate if ARB did not comply are the two main issues in the appeal.
D. ARB's Actions to Comply with Writ
1. ARB's Modified Regulations
ARB's attempts to comply with the February 2014 writ (which included preparing a revised analysis of NOx emissions from biodiesel) preceded its approval of a modified version of the LCFS regulations, rather than a reapproval of the original version without changes. The possibility of modification was recognized in Poet I , where we stated that ARB might exercise its discretion on remand by "reapproving the LCFS regulations or a modified version of those regulations." ( Poet I , supra , 218 Cal.App.4th at p. 765, 160 Cal.Rptr.3d 69 .) Before our decision in Poet I was filed, ARB was holding public workshops to discuss regulatory changes and amendments to the LCFS regulations.
From 2013 through September 2015, ARB's staff held five overarching workshops to discuss the LCFS regulations as a whole and 16 topic-specific workshops to discuss proposed revisions. On December 30, 2014, an initial statement of reasons was released to the public in support of ARB's staff's proposal to readopt the LCFS regulations. Attached as an appendix was a draft Environmental Analysis of (1) the proposed LCFS regulations and (2) newly proposed regulations addressing alternative diesel fuels (ADF).[11] After a 45-day comment period and a public hearing in February 2015, the Board directed modifications be made to the proposed regulations. After another comment period, the Board held a public hearing on September 24, 2015, and continued its consideration of the proposed LCFS and ADF regulations until the next day.
On September 25, 2015, the Board adopted resolutions that finalized its rulemaking determinations. The Board certified the final Environmental Analysis for the proposed LCFS regulations and ADF regulations, stating it met the requirements of CEQA. Based on the final Environmental Analysis (which is described in the next section of this opinion), the Board adopted (1) a set of findings and statement of overriding considerations and (2) the
11 The ADF regulations are set forth in sections 2293 through 2293.9 of title 13 of the California Code of Regulations and their purpose is "to establish a comprehensive, multi-stage process governing the commercialization of alternative diesel fuels (ADF) in California." (Cal. Code of Regs., tit. 13, § 2293 ; see pt. II.F.3, post .)
The final Environmental Analysis's reference to biodiesel's "feedstock" as a factor affecting NOx emissions might encompass both the source of the organic matter (e.g., soybean, cottonseed, tallow, restaurant
The final Environmental Analysis attempted to justify its use of the 2014 baseline for analyzing NOx emissions by discussing the possibility of comparing project NOx emissions to conditions existing in 2009-the year ARB prepared and adopted the original LCFS regulations. The final Environmental Analysis stated:
"In the interest of public disclosure, ARB staff examined the current and expected future emissions of NOx from biodiesel relative to the NOx emissions from biodiesel that were occurring prior to the adoption of the original LCFS (2009). In 2009, there were few [new technology diesel engines], no renewable diesel, and little biodiesel in California, so the NOx emissions from biodiesel were minimal. Staff re-evaluated the 2009 data and determined that NOx emissions were approximately 0.3 [tons per day] greater than reported in the Draft ISOR and E[nvironmental Analysis]. However, since 2009, NOx emissions from biodiesel have increased with the increased use of biodiesel resulting from multiple incentives related to biodiesel since 2009. Thus, it is unclear and impossible to determine what portion of the increase in use is attributable to the original LCFS." (Underlining omitted.)
This discussion continued with a description of the incentives created by federal regulations for fuel standards and federal tax incentives. The final Environmental Analysis stated the view of ARB's staff that the economic incentives in the federal measures were more instrumental than the LCFS regulations in bringing biodiesel to California post-2009. The final Environmental Analysis stated California's proportionate share of the national supply of fuel
Another place where NOx emissions were addressed is the public comments to the draft Environmental Analysis and ARB's responses. Those comments included a challenge to ARB's use of a 2014 baseline to analyze the impacts of the 2015 LCFS regulations. One comment asserted an earlier baseline should have been used and an assessment made of the environmental changes between the adoption of the original LCFS regulations and the adoption of the 2015 LCFS regulations. ARB's response to the comment stated that an environmental baseline predating the beginning of the 2015 administrative proceedings (1) would be misleading, (2) was not required by law, and (3) was not required by Poet I . ARB's response stated it did not agree that an earlier "baseline would yield meaningful information for environmental analysis."
Another comment interpreted the information provided in the draft Environmental Analysis to mean the readoption of the LCFS regulations would result in additional NOx emissions of 1.29 tons per day. ARB's response explained that the figure of 1.29 tons per day for 2015 appearing in its disclosure documents represented the NOx emissions attributable to the use of biodiesel blends. The figure was higher than the NOx emissions that would have occurred if only conventional diesel was used to fulfill diesel fuel demand in California. As biodiesel was already used in 2015 to fulfill California's diesel fuel demand, ARB's response stated:
"[T]he emissions the commenter refers to are already occurring as part of the current conditions. [¶] Thus, the 2014 and 2015 NOx emissions (1.35 [tons per day] in 2014 and 1.29 [tons per day] in 2015) associated with biodiesel use are not NOx increases resulting from the implementation of the proposed regulation starting in 2016, but are estimated emissions associated with current conditions. For purposes of the E[nvironmental Analysis], ARB analyzed impacts against 2014 conditions, the time when the environmental analysis began. ARB staff's analysis of NOx emissions from 2014 through 2023 (displayed in Table B-1), shows that NOx emissions would decrease over time with the implementation of the regulatory proposal."
In other words, the 1.29 tons per day of NOx emissions referred to in the comment were not incremental NOx emissions caused in 2015 by the LCFS regulations operating at that time. When the total of 1.29 tons per day was compared to the 1.35 tons per day from 2014, it showed NOx emissions were decreasing.
The public's comments and ARB's responses to the comments were appended to the environmental analysis and were considered by the Board at its hearings in September 2015.
4. ARB's Return to the Writ
In November 2015, ARB filed its return to the February 2014 writ together with the final Environmental Analysis, ARB's responses to comments, and other supporting documents. The return explained ARB's attempt to comply with paragraph 3 by stating "[t]he Board addressed whether the project (the proposed LCFS and Alternative Diesel Fuel ('ADF') regulations) will have a significant adverse effect on the environment as a result of increased NOx emission." The return then set forth findings about NOx emissions caused by short-term construction projects for new or modified facilities built to satisfy the fuel demands incentivized by ARB's regulations. The return next addressed the emissions caused by using biodiesel, stating ARB found:
"[1] that use of biodiesel can increase NOx emissions in some engines, depending in part on feedstock and blend level;
"[2] that total NOx emissions from biodiesel will decline from the 2014 baseline level under the proposed LCFS and ADF regulations; and
"[3] that the use of biodiesel consistent with the proposed regulations will not result in a significant adverse impact to air quality.
"(Exhibit C at pp. 4-5, 14; see also Exhibit A at p. 4 [adopting findings].) Overall, ARB found that the LCFS and ADF regulations and the compliance responses to those regulations would result in long-term beneficial impacts to air quality through reductions in criteria pollutants (which include NOx emissions). (Exh. C at p. 1.) These findings are supported by substantial evidence. (E.g, Exhibit D at p. 30-31, 56-63, 127-130 [excerpts of EA]; Exhibit E [ADF ISOR Appendix B].) This satisfies paragraph 3 of the peremptory writ."
Plaintiffs objected to ARB's return, contending ARB had not complied with paragraph 3. Plaintiffs argued ARB had failed to consider the original
The terms "activity" and "activities" appear throughout CEQA and the Guidelines, but they are not defined. The Guidelines' definition of "[p]roject," however, substitutes the phrase "the whole of an action" for the statutory phrase "[a]n activity." (Guidelines, § 15378, subd. (a).) Thus, courts routinely state the term "project" means the whole of an action. (E.g. North Coast Rivers Alliance v. Westlands Water Dist. (2014) 227 Cal.App.4th 832 , 858, 174 Cal.Rptr.3d 229 ; San Joaquin Raptor/Wildlife Rescue Center v. County of Stanislaus (1994) 27 Cal.App.4th 713 , 730, 32 Cal.Rptr.2d 704 .)
The broad interpretation of "project" to encompass "the whole of an action" (Guidelines, § 15378, subd. (a)) is designed to provide the fullest possible protection of the environment within the reasonable scope of CEQA's statutory language. ( Tuolumne County Citizens for Responsible Growth, Inc. v. City of Sonora (2007) 155 Cal.App.4th 1214 , 1222, 66 Cal.Rptr.3d 645 ( Tuolumne CCRG ); Friends of the Sierra Railroad v. Tuolumne Park & Recreation Dist. (2007) 147 Cal.App.4th 643 , 653, 54 Cal.Rptr.3d 500 ["CEQA's conception of a project is broad"]; Guidelines, § 15003, subd. (f).)
In Poet I , there was no dispute that the adoption of the original LCFS regulations was a "project" for purposes of CEQA. More precisely, the "activity" constituting the "project" was ARB's action in enacting the regulations plus its actions in implementing of the regulations (which includes enforcement activity). The concept of "activity" is not central to the parties' dispute over what paragraph 3 meant when it used the term "project." Instead, that dispute can be phrased as what constitutes "the whole of [ARB's] action." (Guidelines, § 15378, subd. (a).)
4. Legal Test for Determining Which Acts Are Part of the Whole
Answering the question about what constitutes the whole of ARB's action involves two steps. The first step identifies the legal test for determining the acts or activities that constitute the whole CEQA project. The second step applies that test to the facts of this case.
We discussed the scope of the activity constituting a project in Tuolumne CCRG , supra , 155 Cal.App.4th at pages 1222 through 1227, 66 Cal.Rptr.3d 645 , and the appropriate legal test for determining which acts to include in, or exclude from, the project. Tuolumne CCRG involved physical structures-a proposed road realignment and a proposed Lowe's home improvement center-that would become part of the physical environment, rather than the adoption of an ordinance or regulation. Despite the differences between physical construction projects and legislative action, we conclude the same test applies when determining what constitutes the whole of the action. In Tuolumne CCRG , the test we adopted and applied was whether the acts in question were " 'related to each other.' " ( Tuolumne CCRG , supra , 155 Cal.App.4th at p. 1225, 66 Cal.Rptr.3d 645 , quoting Plan for Arcadia, Inc. v. City Council of Arcadia (1974) 42 Cal.App.3d 712 , 726, 117 Cal.Rptr. 96 .)
We described the reach of this test by stating there are different ways actions can be related to (i.e., connected with) each other. ( Tuolumne CCRG , supra , 155 Cal.App.4th at pp. 1226-1227, 66 Cal.Rptr.3d 645 .) For instance, the two actions could be "related in (1) time, (2) physical location and (3) the entity undertaking the action." ( Id . at p. 1227, 66 Cal.Rptr.3d 645 .) We also examined how closely related the acts were to the overall objective of the project, stating: "The relationship between the particular act and the remainder of the project is sufficiently close when the proposed physical act is among the 'various steps
A simple way to conceptualize the goal of the writ is to consider the information that would have been provided if ARB had complied with CEQA in the first place. ARB's failure to comply with CEQA meant ARB's first set of environmental disclosure documents failed to provide all of the information required by CEQA. Paragraph 3 sought to remedy that informational deficit
To summarize, interpreting paragraph 3's use of the term "project" to include the original LCFS regulations, the 2015 LCFS regulations, and the ADF regulations (1) addresses the CEQA defects that paragraph 3 was designed to correct, (2) implements the intention of this court, and (3) is how "project" would be interpreted by an objectively reasonable attorney familiar with CEQA, the Guidelines, published CEQA decisions discussing the term "project," and the CEQA violation to be remedied.
F. Baseline
1. Parties' Contentions
Plaintiffs contend that the 2014 baseline for NOx emissions adopted by ARB in its analysis of the project's impact was a "regulatory sleight of hand [that] conceals the fact that California will continue to experience increased NOx emissions caused by the original LCFS regulation until at least 2021."[16] In response, ARB supports its use
16 This argument is based in part on the final Environmental Analysis's prediction that biodiesel-related NOx emissions in California ultimately will decrease to 2009 levels by 2023, which logically implies that NOx emissions from biodiesel in each year before 2023 will be greater than the NOx emissions from biodiesel in 2009. Thus, plaintiffs' statement about increased NOx emissions is accurate. However, their statement that the increases are caused by the original LCFS regulations is not accurate because it goes beyond facts and findings in the record. Specifically, ARB has yet to resolve the causation questions and how much of each year's increased NOx emissions was or will be caused by the project, rather than other factors.
Our Supreme Court has recognized that to achieve CEQA's goal of informing decision makers and the public of any significant environmental effects a project is likely to have, the environmental disclosure document (such as an EIR) "must delineate environmental conditions prevailing absent the project, defining a baseline against which predicted effects can be described and quantified." ( Neighbors for Smart Rail, supra, 57 Cal.4th at p. 447, 160 Cal.Rptr.3d 1 , 304 P.3d 499 .) Thus, the concept of a baseline is a key component in identifying and quantifying a project's environmental effects. CEQA does not use or define the term "baseline," but Guidelines section 15125, subdivision (a) provides in part:
"An EIR must include a description of the physical environmental conditions in the vicinity of the project, as they exist at the time the notice of preparation is published, or if no notice of preparation is published, at the time environmental analysis is commenced , from both a local and regional perspective. This environmental setting will normally constitute the baseline physical conditions by which a lead agency determines whether an impact is significant." (Italics added.)
In Communities for a Better Environment v. South Coast Air Quality Management Dist. (2010) 48 Cal.4th 310 , 106 Cal.Rptr.3d 502 , 226 P.3d 985 , the court relied on this provision and case law "for the principle that the baseline for an agency's primary environmental analysis under CEQA must ordinarily be the actually existing physical conditions rather than hypothetical conditions that could have existed under applicable permits and regulations." ( Neighbors for Smart Rail , supra , 57 Cal.4th at p. 448, 160 Cal.Rptr.3d 1 , 304 P.3d 499 , citing Communities for a Better Environment , supra , at pp. 320-322, 106 Cal.Rptr.3d 502 , 226 P.3d 985 .) The court addressed the problem of defining an existing conditions baseline in circumstances where the existing conditions themselves change or fluctuate over time. ( Communities for a Better Environment , supra , at pp. 327-328, 106 Cal.Rptr.3d 502 , 226 P.3d 985 .) The court resolved this problem by concluding a single, uniform rule for determining existing conditions was not appropriate. ( Id. at p. 328, 106 Cal.Rptr.3d 502 , 226 P.3d 985 .) Instead, the court interpreted CEQA and the Guidelines as giving the agency "the discretion to decide, in the first instance, exactly how the existing physical conditions without the project can most realistically be measured." ( Ibid . )
In summary, the Guidelines and foregoing cases set forth two main principles relevant to this appeal. First, an existing conditions baseline is ordinarily used in analyzing a project's environmental impacts. Second, a lead agency has the discretion to choose to evaluate the impacts on future conditions, so long as it provides an adequate justification for omitting an existing conditions analysis. These principles serve CEQA's informational purpose by insisting the "CEQA analysis employ a realistic baseline that will give the public and decision makers the most accurate picture practically possible of the project's likely impacts." ( Neighbors for Smart Rail , supra , 57 Cal.4th at p. 449, 160 Cal.Rptr.3d 1 , 304 P.3d 499 .)
3. Application of Principles
The project in this case includes the original LCFS regulations. Thus, the normal baseline would be the physical conditions existing at the time the environmental analysis of the original LCFS regulations commenced. (Guidelines, § 15125, subd. (a); Neighbors for Smart Rail , supra , 57 Cal.4th at p. 455, 160 Cal.Rptr.3d 1 , 304 P.3d 499 ["Guidelines establish the default of an existing conditions baseline"].) Exactly when ARB's environmental analysis commenced is not clear from the record. It probably occurred after January 2007, when Governor Schwarzenegger directed ARB to determine if a LCFS could be adopted as a discrete early action under the California Global Warming Solutions Act of 2006. ( Poet I , supra , 218 Cal.App.4th at p. 700, 160 Cal.Rptr.3d 69 .) It might have commenced in "August 2007[ when] ARB began consulting with the public about a LCFS." ( Id . at p. 701, 160 Cal.Rptr.3d 69 .) Thus, the normal, existing conditions baseline for NOx emissions might have described conditions existing in August 2007 or, if a full calendar year was used to define the baseline conditions, the NOx emissions from calendar year 2006.
ARB used a 2014 baseline and thought such a baseline described existing conditions because ARB misconstrued and misapplied the term "project." The
Part of the background for the wording of paragraph 3 is provided in the section of our opinion addressing the CEQA violation relating to NOx emissions. In that section, we stated: "On remand, ARB may not simply assume that the LCFS regulations will not have a significant adverse impact on the environment. ARB must make a finding of fact, supported by substantial evidence, on the question whether the project will have a significant adverse effect on the environment as a result of the potential increase in NOx emissions." ( Poet I , supra , 218 Cal.App.4th at p. 740, 160 Cal.Rptr.3d 69 .) We used the phrase "will have" instead of the phrase "may cause" appearing in the definition of "project" (§ 21065) for two reasons. The first was an attempt to reduce the chances that ARB would continue its avoidance of the issue (as it did with its assumption) by making alternative findings that the project might or might not cause increased NOx emissions. The second was that the phrases "may cause" or "may have" are more appropriate for the inquiry conducted at the initial-study stage of review when a lead agency applies the fair argument standard to determine whether the project may cause or may have a significant environmental impact and, thus, requires the preparation of an EIR to complete a full environmental review of that impact. (See § 21080, subd. (d) [if "project may have a significant effect on the environment, an
If one assumes (as contended by ARB) that paragraph 3 was concerned only with future impacts, the relevant impacts are those occurring after the 2015 LCFS regulations went into effect on January 1, 2016. ARB has chosen to discuss impacts on a year-by-year basis, a convention that we will use in this discussion. Thus, in 2015, ARB should have addressed NOx impacts in each year from 2016 through at least 2021. That analysis, described in broad terms, includes the following three steps.
First, ARB should have predicted the amount of NOx emissions for each year and subtracted the baseline NOx emissions from that amount. Subtracting the baseline figure would have yielded the total increase in NOx emissions for each year. Second, ARB should have made findings of fact about causation and allocated the increase among the factors causing the increase, which might have included the 2015 LCFS regulations. Third, ARB should have determined whether the amount of any increase caused by the LCFS regulations was "significant" as that term is used in CEQA. (See fn. 8, ante .)
ARB's use of the wrong baseline skewed the calculation performed in the first step. The resulting error was so large that ARB did not reach the second and third steps of the analysis. More specifically, NOx emissions from the combination of biodiesel and renewable diesel increased between 2009 and 2014. Use of 2014 as the baseline of NOx emissions included this increase and, thus, overstated the baseline figure. The inflated baseline had the effect of understating the increase in NOx emissions for 2016 and subsequent years. Consequently, ARB's use of an inappropriate baseline as the point of comparison for the project's NOx emissions requires reversal even if paragraph 3 were interpreted as (1) directing ARB to address only future (i.e., 2016 through 2021) NOx emissions and their
17 The term "potentially" is used because the entire increase may not be caused solely by the project. The factual questions relating to causation are discussed in part I.F.3, ante .
II. REMEDY
The last element plaintiffs must establish to obtain a reversal is prejudice. Accordingly, we consider whether ARB's failure to comply with the writ and CEQA was prejudicial. A starting point for this inquiry is the proposition that employing an incorrect baseline is not necessarily prejudicial. For example, in Neighbors for Smart Rail , supra , 57 Cal.4th 439 , 160 Cal.Rptr.3d 1 , 304 P.3d 499 , the Supreme Court determined the use of a wrong baseline for analyzing traffic was "an insubstantial, technical error that cannot be considered prejudicial." ( Id . at p. 463, 160 Cal.Rptr.3d 1 , 304 P.3d 499 .)
In this case, we conclude that ARB's failure to comply with paragraph 3 resulted in its environmental disclosure documents omitting information (1) required by CEQA and (2) necessary to an informed discussion. ( Citizens Opposing a Dangerous Environment v. County of Kern (2014) 228 Cal.App.4th 360 , 382, 174 Cal.Rptr.3d 683 [test for prejudice].) At least two gaps in information occurred. First, ARB's disclosure did not analyze the increase in NOx emissions for the period from 2009 through the readoption of the regulations. Information about NOx emissions from this period was necessary to inform the public and decision makers. Second, the discussion of the NOx emissions forecast to occur after the adoption of the 2015 LCFS regulations was inaccurate because the wrong baseline was used and, as a result, the discussion misleadingly understated the increase in NOx emissions for 2016 and the years following. This understatement allowed ARB to conclude NOx emissions would decrease and to avoid (1) making findings of fact allocating the increased emissions among the various causes and (2) determining whether the amount of the increased emissions caused by the project was significant. These gaps in information are at the heart of the analysis used to determine whether a project is likely to have a significant adverse environmental impact and, thus, cannot be regarded as insubstantial, technical errors. Consequently, we conclude plaintiffs have shown the failure to comply with paragraph 3 was prejudicial to CEQA's informational goals.
ARB's prejudicial failure to comply with paragraph 3 is more than a failure by a public agency to fulfill the terms of a writ of mandate. The February 2014 writ was issued to remedy violations of CEQA. Thus, ARB's failure to comply with paragraph 3 also constitutes a violation of CEQA. In other words, since 2009, ARB has been in violation of CEQA because its environmental disclosure documents have not provided the public and decision makers with statutorily required information about the project's NOx emissions. As a result, ARB's corrective action taken in reliance on those environmental disclosure documents did not comply with CEQA.
2. Determining What Further Orders are Appropriate
The principle that a court may issue " 'further appropriate orders to compel obedience to the writ' " ( Sanders , supra , 3 Cal.3d at p. 262, 90 Cal.Rptr. 169 , 475 P.2d 201 ) gives rise to the question of how a court determines what is appropriate in a particular case. We have located, and the parties have cited, no case law explicitly addressing this question in a CEQA case. We conclude that, where a CEQA violation was addressed by the underlying writ of mandate, the determination of what further orders are appropriate to compel obedience with the writ is controlled and guided by CEQA's requirements, principles and policies. Consequently, a further order generally will be deemed appropriate if (1) the required action is among the types of relief permitted by CEQA and (2) it promotes the goal of compliance with CEQA, which is why the writ was issued in the first place. Restated in the negative, a further order is not appropriate in a CEQA proceeding if (1) the order contradicts express limitations on relief set forth in section 21168.9 or (2) the order is inconsistent with the purposes of CEQA.
Therefore, we conclude our authority to grant appellate relief in this case is derived from (1) the general provisions in Code of Civil Procedure section 906 and (2) CEQA's provisions governing remedies.
B. ARB's Claims of Unavailable Appellate Relief
ARB has not identified the statutory basis for this court's power to grant appellate relief, yet ARB contends our jurisdiction in this appeal is limited. Specifically, ARB claims the appellate relief available in this case cannot attempt to remedy errors in the way ARB adopted the 2015 LCFS regulations because "the court with jurisdiction over those questions is the superior court handling [plaintiffs'] direct challenge to the new regulation."
ARB also addresses the possibility that this court might enter relief affecting the 2015 LCFS regulations under the theory that the relief is preliminary in nature. ARB contends plaintiffs have not shown the requisite elements for preliminary relief-namely, the likelihood of success on the merits and irreparable injury absent relief.
We reject ARB's argument that we lack the jurisdiction or authority to suspend the 2015 LCFS regulations. First, ARB has cited no statutory authority for such a jurisdictional limitation on the general authority granted by Code of Civil Procedure section 906. Second, ARB has cited no case law recognizing such a limitation on the authority of an appellate court. Third, this court has not limited or surrendered the authority to remedy failures to comply with the February 2014 writ or enforce our disposition in Poet I . For instance, Poet I contains no provision surrendering or otherwise limiting our authority in subsequent appeals. Therefore, we conclude the analysis set forth in part II.A, ante defines our authority to enter relief in this appeal, which is limited to ARB's failure to comply with the writ and
To the extent ARB's argument implies plaintiffs' current request for suspension of the 2015 LCFS regulations is an improper collateral attack on the regulations, we disagree. The challenges raised by plaintiffs in this appeal are limited to issues previously raised in Poet I and dealt with by the February 2014 writ. Thus, the challenges considered in this appeal are not collateral in nature. The directness of the challenges is illustrated by, among other things, their satisfaction of the issue exhaustion requirement set forth in section 21177, subdivision (b) throughout this litigation.
C. Reversal with a Generic Order to Comply with the Writ
Here, the parties impliedly accept the conclusion that the order discharging the writ should be reversed if the order was granted in error. Such a reversal would require further proceedings on remand so ARB could comply with the writ and obtain an order discharging the writ. Consequently, we consider whether our disposition should simply (1) reverse the order discharging the writ and (2) instruct the trial court to issue a generic order directing ARB to comply with the writ.
This theoretically possible disposition would have the effect of reinstating all provisions of the writ. Reinstatement, however, would give rise to disputes between the parties over how the writ's provisions should be applied to the further proceedings. The potential disputes described below demonstrate (1) a simple reversal with directions for ARB to comply with the writ is not appropriate and (2) further orders are needed to clarify matters.
1. Paragraph 6 and the Status Quo
Reinstating the February 2014 writ would reinstate paragraph 6, which stated ARB shall continue "to adhere to the LCFS regulations standards in effect for 2013 until the corrective action is completed." ( Poet I , supra , 218 Cal.App.4th at p. 767, 160 Cal.Rptr.3d 69 .) Paragraph 6's purpose was to preserve the status quo until ARB had complied with the writ and remedied its CEQA violations. ( Ibid . ) The parties' appellate briefing shows they do not agree on paragraph 6's continuing role, if any, after remand.
The parties have adopted different interpretations of paragraph 6's phrase "until the corrective action is completed." ARB has interpreted "is completed" to refer to the point where it finished the administrative steps in its
D. Who Determines the Content of the Further Appropriate Orders
The need for "further appropriate orders" raises the question of which court should determine the content of those orders-this court or the trial court? There are three possible answers. First, we could remand to the trial court with generic directions for that court "to order defendants to comply with the writ and to make any further appropriate orders to compel obedience thereto." ( Sanders , supra , 3 Cal.3d at p. 256, 90 Cal.Rptr. 169 , 475 P.2d 201 .) Second, we could draft the further appropriate orders ourselves and direct the trial court to issue those orders on remand. Third, we could divide the drafting responsibility, addressing some of the
Therefore, we conclude the 2013 standards should not be reinstated. The further orders contained in our disposition will modify the terms of the February 2014 writ to implement this conclusion about the 2013 standards.
F. Voiding and Suspending?
If the 2013 standards are not reinstated, should we adopt plaintiffs' position and suspend operation of the regulations or, alternatively, should we adopt ARB's position and allow the 2015 LCFS regulations and ADF regulations to remain in effect? As the 2015 LCFS regulations and ADF regulations currently are in effect, the question is whether to invalidate (i.e., suspend) those regulations in whole or in part.
2. Principles Governing Severance
The statute directs courts to consider whether "the portion or specific project activity or activities are severable" (§ 21168.9, subd. (b)), but does not set forth a test for severability. Consequently, we turn to the analysis of severability adopted by our Supreme Court.
The first step of that analysis is to look for any severability clauses in the enactment. ( California Redevelopment Assn. v. Matosantos (2011) 53 Cal.4th 231 , 270, 135 Cal.Rptr.3d 683 , 267 P.3d 580 ( Matosantos ).) ARB included severability clauses in the ADF regulations and the 2015 LCFS regulations. (Cal. Code of Regs., tit. 13, § 2293.9 [ADF regulations]; Id ., tit. 17, § 95497 [2015 LCFS regulations].) These clauses establish a presumption in favor of severance, but are not conclusive. ( Matosantos , supra , at p. 270, 135 Cal.Rptr.3d 683 , 267 P.3d 580 ; Verner, Hilby and Dunn v. City of Monte Sereno (1966) 245 Cal.App.2d 29 , 35, 53 Cal.Rptr. 592 [invalid licensing requirements in ordinance materially affected remainder of regulatory scheme; entire ordinance held void despite severability clause].)
Determining whether the presumption holds or is negated involves an evaluation of the three judicially prescribed "criteria for severability: the invalid provision must be grammatically, functionally, and volitionally separable." ( Calfarm Ins. Co. v. Deukmejian (1989) 48 Cal.3d 805 , 821, 258 Cal.Rptr. 161 , 771 P.2d 1247 .) Grammatical (i.e., mechanical) separability exist when the invalid parts can be removed as a whole without affecting the wording or coherence of the remaining parts. ( Matosantos , supra , 53 Cal.4th at p. 271, 135 Cal.Rptr.3d 683 , 267 P.3d 580 .) Functional separability addresses how the enactment would operate without the invalid provision and is present when severance does not destroy the regulatory scheme or the utility of the remainder. ( Calfarm , supra , at p. 822, 258 Cal.Rptr. 161 , 771 P.2d 1247 ; Blumenthal v. Board of Medical Examiners (1962) 57 Cal.2d 228 , 238, 18 Cal.Rptr. 501 , 368 P.2d 101 .) In other words, functional separability depends on whether the remainder of the enactment is complete in itself and can be implemented without the continuation of the invalid provision. ( Matosantos , supra , at p. 271, 135 Cal.Rptr.3d 683 , 267 P.3d 580 .) Volitional separability exists when the legislative body would have
4. Severability of Portions of the LCFS Regulations
Next, we consider whether severing and suspending only a part of the 2015 LCFS regulations is permissible under section 21168.9, subdivision (b). There are many ways to divide the provisions of the 2015 LCFS regulations. For instance, as the CEQA violation concerns only NOx emissions from biodiesel, severance and suspension might be limited to (1) the provisions relating to biodiesel; (2) the provisions addressing all substitutes for conventional diesel, which substitutes include biodiesel and renewable diesel; or (3) the provisions addressing all types of diesel fuel, conventional or otherwise.
As to the first possibility, plaintiffs and ARB both suggest in their supplemental letter briefs that the biodiesel provisions in the LCFS regulations could be severed from the remainder of the LCFS regulations. They contend that severing and suspending the biodiesel provisions would increase the price of credits, which would have the beneficial impact of stimulating the production of fuels with lower carbon intensity values.
Despite the agreement of the parties, we reject a severance of the biodiesel provisions from the remainder of the LCFS regulations. Such a severance would place a disproportionate share of the financial burden of the increase in credit costs on the reporting entities that relied most heavily on biodiesel to bring down the average carbon intensity of the fuels they handled. This shift in the way the costs of the LCFS regulation are borne leads us to conclude the provisions relating to biodiesel are not functionally separable from the remainder of the regulation. The shift in costs would materially affect the operation of the regulatory scheme as to diesel such that the diesel portion of the scheme could no longer be regarded as functioning like the original scheme. ( Matosantos , supra , 53 Cal.4th at p. 271, 135 Cal.Rptr.3d 683 , 267 P.3d 580 .) In other words, the scheme as to diesel fuel and its substitutes would no longer be complete in itself.
The provisions involving biodiesel are intertwined with the provisions regulating the entire category of diesel fuels. For instance, the compliance
Severing the provisions of the LCFS regulations relating to all diesel fuels also meets the two other criteria in section 21168.9, subdivision (b). The provisions of the LCFS regulations addressing gasoline are in compliance with CEQA because the CEQA violation involving the analysis of NOx emissions from biodiesel did not affect the provisions addressing gasoline. (§ 21168.9, subd. (b).) Also, the record and arguments presented do not show that severing the provisions of the LCFS regulations relating to gasoline and allowing those provisions to remain in effect would prejudice ARB's complete and full compliance with CEQA in connection with NOx emissions from biodiesel. ( Ibid .)
Therefore, we conclude that the portion of the LCFS regulations that address fuels other than diesel fuel and its substitutes involve project activities that do not need
Our first inquiry addresses whether allowing the portion of the LCFS regulations addressing diesel fuel and its substitutes to remain in effect would "prejudice the consideration or implementation of particular mitigation measures or alternatives to the project." (§ 21168.9, subd. (a)(2).) In Poet I , we concluded that leaving the written standards in the original LCFS regulations in place instead of suspending them would not affect ARB's consideration of mitigations measures and alternatives. ( Poet I , supra , 218 Cal.App.4th at p. 762, 160 Cal.Rptr.3d 69 .) Plaintiffs argue we should not reach the same conclusion here because they have "demonstrated that, so long as the LCFS regulation remains in place, [ARB] will cut analytical corners, and refuse to consider alternatives and mitigation-all to the detriment of communities affected by criteria pollutants such as NOx-simply to defend the continuing existence of the LCFS program." Plaintiffs refer to ARB's analysis of alternatives after the issuance of the February 2014 writ, noting that ARB considered only a "no project" alternative and various iterations of the LCFS regulation and declined to consider feasible alternatives presented by the public.
Plaintiffs' arguments about bureaucratic momentum are realistic and have some merit. However, those arguments must be placed in the context of this case, which involves CEQA violations on a narrow topic (i.e., NOx emissions from biodiesel) and not CEQA violations that taint the entire project. Furthermore, any lack of discussion about alternatives geared to biodiesel makes sense because alternatives are considered only after a significant environmental effect has been identified. (See Guidelines, § 15126.6 [consideration of alternatives].) Here, ARB's flawed analysis
Our second inquiry under subdivision (a)(2) of section 21168.9 relates to whether suspension of the portion of the LCFS regulations addressing diesel fuel and its substitutes is warranted because that portion of the project activity "could result in an adverse change or alteration to the physical environment." (Italics added.) This inquiry includes distinct questions of fact. First, could the provisions in the LCFS regulations addressing diesel fuel cause an increase in biodiesel usage in California? Second, could any increase in biodiesel use attributable to the LCFS standards cause an increase in NOx emissions? Third, if increased NOx emissions have or will be caused, is the adverse change to the physical environment attributable to that increase outweighed by the reduction in other pollutants caused by leaving the portion of the LCFS regulations addressing diesel fuel and its substitutes in place? (See Poet I , supra , 218 Cal.App.4th at p. 762, 160 Cal.Rptr.3d 69 ; see fn. 6, ante [baby-with-the-bathwater problem].)
The levels of certainty required to resolve these factual questions is addressed by the statutory phrase "could result." (§ 21168.9, subd. (a)(2).) In this context, "could" refers to future events. Consequently, "could" was not used as the past tense of "can," which refers to past ability. ( Quinones v. Pin (2009) 298 S.W.3d 806 , 816.) In reference to future events, "could" is used to indicate possibility, meaning essentially the same thing as "might." ( Ibid . ; Dorrin v. Union Electric Co. (1979) 581 S.W.2d 852 , 859 ["could" denotes mere capability and often is used as meaning "might"].) In this context, the most likely interpretation of the ambiguous phrase "could result" is that it denotes the level of certainty contained in the fair argument standard. Thus, suspension of a project activity pending compliance with CEQA may be an appropriate remedy when there is a fair argument that the project activity might result in an adverse environmental impact. Conversely, suspension of a project activity is not appropriate when the possibility of an adverse environmental impact resulting from that activity falls below the fair argument standard.
If the provisions of the LCFS regulations that address diesel fuels and its substitutes increase biodiesel usage, could that increased usage cause an increase in NOx emissions? We conclude that it could because using biodiesel results in more NOx emissions than using replacement fuels. Specifically, conventional diesel and renewable diesel result in lower NOx emissions. Therefore, if the diesel provisions in the LCFS regulations "could result in" an increase in biodiesel use, they also "could result in" an increase in NOx emissions. (§ 21168.9, subd. (a)(2).)
Our inquiry into whether suspension of the diesel provisions in the LCFS regulations "could result in an adverse change or alteration to the physical environment" (§ 21168.9, subd. (a)(2)) leads us to conclude that the provisions "could result in an adverse change" due to increased NOx emissions. This conclusion lends support to suspending the diesel provisions of the LCFS regulations pending ARB's compliance with CEQA. However, such an exercise of our discretionary authority involves further considerations-particularly, the overall environmental impact of suspension and plaintiffs' argument that ARB did not act in good faith.
Considerations of the overall environmental impact prevented this court from suspending the entire LCFS regulations to remedy the CEQA violations found in Poet I . ( Poet I , supra , 218 Cal.App.4th at pp. 762-763, 160 Cal.Rptr.3d 69 .) We stated that the LCFS regulations "impact on a wide range of air pollutants is not easily quantified" and that "the emissions of greenhouse gases will be less if the LCFS regulations are allowed to remain in effect." ( Id . at p. 762, 160 Cal.Rptr.3d 69 .) The situation is the same in this appeal. The impact of the diesel provisions in the LCFS regulations is difficult to quantify, but suspending all of those provisions might reduce the NOx emissions from biodiesel while increasing the emissions of greenhouse gases. In other words, leaving the category of diesel fuel and its substitutes unregulated by the LCFS regulations would mean
19 Referring to the creation of incentives does not equate to finding those incentives actually changed the behavior of reporting entities.
At oral argument, ARB's counsel argued ARB acted in good faith, maintaining that under
Based on our consideration of all the factors relevant to suspending project activity-including the limited scope of ARB's lack of good faith in taking corrective action-we conclude that the provisions in the LCFS regulations addressing diesel fuel and its substitutes, though severable, should not be suspended while ARB makes another attempt at analyzing NOx emissions from biodiesel in a manner that complies with CEQA and the writ.
7. Maintaining the Status Quo
The final question about the relief granted in this appeal relates to whether we should include a provision preserving the status quo pending ARB's compliance with the writ and CEQA. Freezing the standards contained throughout the 2015 LCFS regulations is not appropriate because the ongoing CEQA violation involves only NOx emissions from biodiesel. Therefore, the status quo provisions in paragraph 6 of the February 2014 writ will be modified.
Any preservation of the status quo should be limited to the provisions (1)
20 Also, our disposition in Poet I directed ARB to proceed in good faith without delay in taking its corrective action and stated a failure to proceed in good faith would result in vacating the provisions in paragraph 6 of the writ that preserved the status quo and suspending the operation of the original LCFS regulations. ( Poet I , supra , 218 Cal.App.4th at p. 767, 160 Cal.Rptr.3d 69 ; see pt. II.C.2, ante .) Thus, we considered ARB's good faith as a factor affecting the remedy imposed in Poet I and we continue to adhere to that general principle in this appeal.
G. Guidance as to the Baseline on Remand
ARB has requested, in effect, that we endorse its use of a 2010 baseline on remand. ARB's theory for use of a 2010 baseline is grounded on the fact that 2010 was a reporting year[21] only and the carbon intensity requirements in the original LCFS regulations did not take effect until January 1, 2011. Thus, ARB reasons that the project could not have caused any changes in biodiesel use during 2010.
Approving the use a 2010 baseline is inappropriate for a number of reasons, three of which we discuss here. First, Guidelines section 15125, subdivision (a) normally requires the use of an existing conditions baseline, which means the conditions "as they exist ... at the time environmental analysis is commenced." The ISOR published on March 5, 2009, contained an environmental disclosure document, which demonstrates that the environmental analysis conducted by ARB commenced before that date. It follows that a 2010 baseline would not be an existing conditions baseline for purposes of Guidelines section 15125, subdivision (a). Consequently, if ARB wishes to use a 2010 baseline on remand, it must justify that departure from the norm and support that justification with substantial evidence. ( Neighbors for Smart Rail , supra , 57 Cal.4th at p. 448, 160 Cal.Rptr.3d 1 , 304 P.3d 499 [departure justified "when necessary to prevent misinforming or misleading the public and decision makers"].)
Second, ARB's argument is oblivious to the possibility that reporting entities began adapting to the new regulation (i.e., modifying their behavior) prior to the effective date of the carbon intensity requirements contained in the original LCFS regulations. ARB previously recognized this possibility in its final Environmental Analysis, which stated that biodiesel "has been incentivized under the existing LCFS Regulation beginning in 2009 ." (Underlining omitted, italics added.) At a minimum, this statement suggests that reporting entities began modifying their behavior by increasing production and imports of biodiesel in 2009, effectively gearing up for the carbon
21 Under the original LCFS regulations, only the reporting, recordkeeping and auditing provisions applied during 2010, while the carbon intensity and other requirements started applying January 1, 2011. (Cal. Code of Regs., tit. 17, former § 95480.1, subd. (a).)
22 ARB's failure to recognize the factual issues underlying the choice of a NOx baseline means it has cited no evidence tending to prove biodiesel producers only reacted to the original LCFS regulations and began producing more biodiesel after the carbon intensity requirements kicked in at the start of 2011. ARB's failure to recognize the underlying factual issues also indicates a misunderstanding of, or an unwillingness to apply, the limits CEQA and the Guidelines place on its selection of a baseline.
The superior court shall issue further orders to compel the Air Resources Board's obedience to the writ and CEQA, including modifying the writ to compel the Air Resources Board to take the following action:
(1) Set aside its 2015 approval of the parts of the final Environmental Analysis addressing NOx emissions from biodiesel.
(2) Address whether the project as a whole "is likely to have"[23] caused an increase in NOx emissions in the past and is likely to cause an increase in NOx emissions in the future. The baseline used for analyzing each period's NOx emissions shall reflect the conditions existing at the time the environmental analysis of the original LCFS regulations was commenced, unless Air Resources Board provides sufficient justification, supported by substantial evidence, for use of a later baseline. In no event shall the baseline conditions describe a year later than 2010. The discussion in the environmental disclosure document shall comply with CEQA, including without limitation an analysis
23 The phrase "is likely to have" appears in section 21061.
The statements that follow are intended to aid in the interpretation and application of the foregoing modifications. First, the modifications to the writ shall not affect the validity and continuing operation of the ADF regulations. Second, there shall be no striking of text from the LCFS regulations; rather, the freeze of the standards for conventional diesel and its substitutes shall operate in the manner of an injunction rather than voiding or invalidating provisions that would have come into effect in 2018 and later. Third, Air Resources Board need not suspend its consideration or approval of additional fuel pathways for diesel fuel and its substitutes.[25]
The superior court shall continue to retain jurisdiction over the proceedings by way of a return to the writ. The superior court may, in an exercise of its discretion, require the Air Resources Board to file an initial return after issuing the order modifying the February 2014 writ. The superior court's jurisdiction shall include the authority to hear a motion for clarification of the terms of the modified writ if the parties dispute its proper interpretation or application. The superior court may hear such a motion on an expedited basis and its decision may be subject to writ review by this court. Interpretation of this disposition and the writ shall be in accordance with CEQA's requirements, principles and polices.
The superior court shall require the Air Resources Board to proceed diligently, reasonably and in subjective good faith while implementing corrective action pursuant to the modified writ and filing a final return. If the Air Resources Board fails to proceed in this manner, the superior court immediately shall vacate the portion of the writ that preserves the status quo with respect to the standards applicable to diesel fuel and its substitutes and shall direct the Air Resources Board to set aside the
25 This statement is inherent in previous statements, but we include a redundancy because the parties raised the fate of new pathways during oral argument.
WE CONCUR:
KANE, Acting P.J.
SMITH, J.
26 For instance, Air Resources Board might chose to exercise its discretion and provide an additional analysis of "reasonably foreseeable indirect physical changes to the environment" (Guidelines, § 15378, subd. (a)) that may have been caused by the project, such as the impacts of fuel shuffling alleged by plaintiffs. The reasonably foreseeable changes resulting from alterations in the behavior of third parties subject to a new law was discussed in detail by this court in County Sanitation Dist. No. 2 v. County of Kern (2005) 127 Cal.App.4th 1544 , at pages 1582 through 1598, 27 Cal.Rptr.3d 28 . That case discussed the reasonably foreseeable indirect physical changes, both inside and outside the county, resulting from the reaction of third parties to the requirements of a new ordinance addressing sewage sludge disposal.
The second major issue in this appeal is how to remedy ARB's failure to comply with CEQA and the writ. Pursuant to our discretionary authority to fashion appellate relief, we reverse the order discharging the writ and remand for further proceedings under a modified writ. The modifications direct ARB to address NOx emissions from biodiesel in a manner that complies with CEQA, including the use of a proper baseline. As to the fate of the current version of the LCFS regulations, only the provisions addressing diesel fuel and its substitutes[3] were affected by the flawed analysis of NOx emissions. Thus, the remainder of the LCFS regulations will be allowed to remain in effect. The provisions addressing diesel fuel and its substitutes appear, on balance, to provide environmental benefits that outweigh the potential adverse impacts and, therefore, we will not invalidate those provisions. Instead, the standards for diesel fuel and its substitutes in effect for 2017 shall remain the operative standards until the modified writ is discharged.
We therefore reverse the order discharging the writ and remand for further proceedings.
FACTS AND PROCEEDINGS
Overview of LCFS Regulations
The goal of the LCFS regulations is to progressively reduce the greenhouse gas emissions from transportation fuels used in California. (Cal. Code Regs., tit. 17, § 95480.) The LCFS regulations use carbon intensity values to approximate the greenhouse gas emissions generated from all stages of
3 The two main substitutes for conventional diesel are biodiesel and renewable diesel. Biodiesel and renewable diesel have different chemical structures and are made by different chemical processes. When used, renewable diesel emits less particulate matter and NOx than conventional diesel. ( Poet I , supra , 218 Cal.App.4th at p. 732, fn. 37, 160 Cal.Rptr.3d 69 .) In contrast, biodiesel emits more NOx than renewable diesel or conventional diesel.
First Appeal
The history of the original LCFS regulations,[4] from the enactment of the authorizing legislation in 2006 through April 2010, is described in the "FACTS" section of Poet I , supra , 218 Cal.App.4th at pages 699 through 707, 160 Cal.Rptr.3d 69
4 For purposes of this opinion, the term "original LCFS regulations" refers to the regulations adopted by ARB in 2009, which the Office of Administrative Law stated became effective on January 12, 2010, and the minor amendments adopted by ARB in 2010, which the Office of Administrative Law stated became effective on April 15, 2010. ( Poet I , supra , 218 Cal.App.4th at pp. 706-707, 160 Cal.Rptr.3d 69 .) In contrast, we use the term "2015 LCFS regulations" to mean the LCFS regulations adopted by ARB in 2015, which went into effect on January 1, 2016. ARB refers to the 2015 LCFS regulations as the "new LCFS regulations," while plaintiffs describe them as the "Readopted LCFS Regulation."
In December 2013, plaintiffs submitted a proposed peremptory writ to the trial court. On January 6, 2014, the trial court signed and filed the proposal. On February 10, 2014, the trial court responded to ARB's objections by filing a modified version of the peremptory writ of mandate (February 2014 writ),[5] which is the operative writ for purposes of this appeal.
As directed by the disposition in Poet I , the February 2014 writ compelled ARB to take action to correct its violations of CEQA. The writ provision at
5 The modifications affected only paragraph 5 of the writ and are not relevant to this appeal.
DISCUSSION
A
. Standard of Review
1. Parties' Contentions
Plaintiffs contend that, under the applicable standard of review, the issue presented is whether ARB prejudicially abused its discretion in its attempt to demonstrate compliance with the February 2014 writ. Plaintiffs refer to the abuse of discretion standard set forth in section 21168.5, which requires the agency to support its findings with substantial evidence and to proceed in the manner required by law.
ARB contends the only issue on appeal is whether the superior court erred in discharging the writ. ( Los Angeles Internat. Charter High School v. Los Angeles Unified School Dist. (2012) 209 Cal.App.4th 1348 , 1355, 147 Cal.Rptr.3d 757 ["issue is whether the trial court erred in ruling that the respondent ... complied with the writ"].) To resolve this issue, ARB urges us to focus on its response to the writ and the superior court's assessment of that response. ARB contends the discharge order can be reversed only if ARB's action pursuant to the writ was so palpably unreasonable and arbitrary as to indicate an abuse of discretion as a matter of law. ( Id . at pp. 1355-1356, 147 Cal.Rptr.3d 757 .)
The parties' slightly different descriptions of the standard of review does not present an authentic controversy because, at bottom, both regard the fundamental issue as whether ARB's action complied with the writ and contend that action is reviewed for an abuse of discretion. We agree that the abuse of discretion standard applies to ARB's actions because ARB's attempt to comply with the writ is, for all practical purposes, an attempt to comply with CEQA. (§ 21168.5.)
2. General Principles Regarding Abuse of Discretion Standard
Our conclusion that the abuse of discretion standard of review applies does not complete the description of the principles applied to evaluate ARB's actions. "The abuse of discretion standard is not a unified standard; the deference it calls for varies according to the aspect of [the agency's action] under review." (
B. The CEQA Violation Relating to NOx Emissions
The California Global Warming Solutions Act of 2006 charged ARB with regulating the sources of emissions of greenhouse gases. To reduce greenhouse gas emissions from the fuel used for transportation, ARB adopted a number of regulations, including the LCFS regulations. Diesel fuel was one of the transportation fuels addressed by the original LCFS regulations. ARB thought it could reduce the greenhouse gas emissions of diesel fuel by promoting the use of biodiesel, either as a substitute for, or blended with, petroleum-based diesel fuel. ( Poet I , supra , 218 Cal.App.4th at p. 731, 160 Cal.Rptr.3d 69 .) Consequently, the original LCFS regulations attempted to encourage the production and use of biodiesel.
The environmental disclosure document[7] generated by ARB in connection with proposing and adopting the original LCFS regulations violated CEQA by
7 Most of the environmental disclosures and discussion were included in the draft Environmental Analysis attached to the Initial Statement of Reasons (ISOR) published on March 5, 2009. The ISOR and draft Environmental Analysis are comparable to a draft environmental impact report (EIR). (See Poet I , supra , 218 Cal.App.4th at pp. 701, 710, 160 Cal.Rptr.3d 69 .) Similarly, the December 2009 Final Statement of Reasons and the final Environmental Analysis are comparable to a final EIR. ( Id . at p. 733, 160 Cal.Rptr.3d 69 .)
The public response to ARB's release of the draft environmental disclosure document included comments challenging the assumption that promoting the use of biodiesel would not increase NOx emissions. ( Poet I , supra , 218 Cal.App.4th at p. 705, 160 Cal.Rptr.3d 69 .) "In response to these comments, ARB reiterated its position that it would 'ensure that biodiesel fuel use does not increase NOx emissions significantly by promulgating a new motor vehicle fuel specification for biodiesel.' " ( Ibid . )
ARB's assurance was an empty promise. The LCFS regulations were put into effect without any specifications for biodiesel sold in California. In April 2009, the Board[9] attempted to have the specifications ready in time by passing
9 For purposes of this opinion, "Board" refers to the group of individuals acting in that group's capacity as the governing entity of ARB. Under this narrow definition, Board is not synonymous with ARB, a public agency. (See Poet I , supra , 218 Cal.App.4th at p. 705, fn. 12, 160 Cal.Rptr.3d 69 .)
adverse environmental effect of increased NOx emissions, and adopt mitigation measures in the event the environmental effects are found to be significant." ( Id . at p. 767, 160 Cal.Rptr.3d 69 .)
This language was tracked in paragraph 3 of the trial court's February 2014 writ (paragraph 3), which stated:
"ARB shall address whether the project will have a significant adverse effect on the environment as a result of increased NOx emissions, make findings (supported by substantial evidence)
The 2015 LCFS regulations took effect on January 1, 2016. They are set forth in sections 95480 through 95497 of title 17 of the California Code of Regulations.
2. Final Environmental Analysis
ARB's final Environmental Analysis stated that "adoption of the proposed LCFS and ADF regulations would be anticipated to result in changes from the 2014 baseline emissions level for several criteria air pollutants (e.g., emissions from the additional use of biodiesel and renewable diesel fuels)."[12]
The final Environmental Analysis also stated:
"Biodiesel and renewable diesel fuels have been found to reduce [particulate matter] emissions relative to conventional diesel. Renewable diesel has been found to decrease NOx relative to conventional diesel; however, biodiesel has been found to increase NOx emissions in some cases, depending on feedstock and type of engine [ ] used."
The final Environmental Analysis described the 2014 baseline conditions by stating approximately 65 million gallons of biodiesel and 114 million gallons of renewable diesel were consumed in California in 2014.[13] Next, it compared emissions from the combination of these diesel fuels with emissions from conventional diesel fuel to produce an estimate of what the emissions would have been if only conventional diesel fuel had been used. This comparison led ARB to conclude the use of the foregoing volumes of
12 Federal regulations define a "[c]riteria pollutant" as "a pollutant for which the Administrator [of the Environmental Protection Agency] has promulgated a national ambient air quality standard pursuant to 42 U.S.C. 7409 (i.e., ozone, lead, sulfur dioxide, particulate matter, carbon monoxide, nitrogen dioxide)." ( 40 C.F.R. § 52.31 (b)(4).) Nitrogen dioxide is one form of NOx.
13 "In 2008, approximately 4.2 billion gallons of diesel fuel were consumed in California, while the state's total commercial biodiesel production capacity was approximately 35 million gallons per year." ( Poet I , supra , 218 Cal.App.4th at pp. 731-732, 160 Cal.Rptr.3d 69 .) The final Environmental Analysis updated the information about production capacity by stating: "In 2013, nine biodiesel producers had an annual capacity of 61 million gallons." Thus, in a span of five years, biodiesel production capacity increased about 75 percent.
The final Environmental Analysis stated that if the proposed ADF and LCFS regulations were adopted in 2015, ARB's staff predicted future decreases in total NOx emissions from biodiesel and renewable diesel. Table 4-1 in the final Environmental Analysis set forth the projected changes in statewide NOx emissions for each year from 2014 through 2022. These projected changes were attributed to the total use of biodiesel and renewable diesel, not the incremental increase in use of these fuels caused by the ADF and LCFS regulations . Using 2014 as a baseline, the projected changes in net NOx emissions ranged from a reduction of 0.1 tons per day in 2015 to a reduction of 1.3 tons per day in 2022. Based on the progressively declining emissions of NOx and the projected reductions in other criteria pollutants, the final Environmental Analysis concluded the long-term impacts on air quality would be beneficial-that is, the regulations would not have an adverse environmental impact. We note that the final Environmental Analysis did not attempt to allocate the increased usage of biodiesel and renewable diesel between (1) the ADF and LCFS regulations and (2) other causes. Such an
14 The reference to "biodiesel-related NOx emissions" probably was meant to cover the NOx emissions from both biodiesel and renewable diesel, not just biodiesel.
5. Trial Court's Order Discharging the Writ
On January 5, 2016, the trial court filed an order without holding a hearing. The order (1) stated the court had read and considered plaintiffs' objections and ARB's response and (2) found ARB had demonstrated satisfactory compliance with the February 2014 writ. Based on this finding, the court ordered the writ discharged.
E. The Scope of Paragraph 3 and the Meaning of "Project"
1. Parties' Interpretations of "Project"
Plaintiffs contend the term "project" used in paragraph 3 includes the whole of an action and, as applied in this case, the whole of the action encompasses both the original LCFS regulations and the 2015 LCFS regulations. In contrast, ARB contends "project" is a reference to the proposed LCFS regulations mentioned in other paragraphs of our disposition and the February 2014 writ, which ARB interprets to mean any new LCFS regulations that ARB might have considered on remand.
2. Project Means the Whole of an Action
We used the word "project" in our disposition because of its breadth and its role in defining the scope of CEQA. We used "project" in the same sense it is used in CEQA, the Guidelines and our many published CEQA decisions.
3. Projects Involving Legislative Action
Guidelines section 15378, subdivision (a)(1) provides examples of "activity directly undertaken by any public agency." The examples include building physical structures, such as "public works construction and ... improvements to existing public structures." ( Ibid .) Direct agency "activity" also includes "enactment and amendment of zoning ordinances, and the adoption and amendment of local General Plans." ( Ibid .) These latter examples support the conclusion that the term "activity" includes a state agency's enactment of regulations. (See CURE , supra , 178 Cal.App.4th at p. 1240, 101 Cal.Rptr.3d 81 [the adoption of a rule or regulation can be a project subject to CEQA];
In Tuolumne CCRG , the city had conditioned the opening of the home improvement center on the completion of the road realignment. ( Tuolumne CCRG , supra , 155 Cal.App.4th at p. 1227, 66 Cal.Rptr.3d 645 .) Thus, the realignment was a necessary step to the achievement of Lowe's objective of opening a new store. Based on "the various connections between the road realignment and the proposed home improvement center," we concluded they were "related acts that constitute a single CEQA project." ( Ibid. )
5. Application of the Test to This Case
Application of the " 'related to each other' " test adopted in Tuolumne CCRG to the original LCFS regulations, the 2015 LCFS regulations, and the ADF regulations is not difficult. They clearly are related to one another and that relationship is extremely close. They share the same overall objective of reducing greenhouse gases. They were adopted by the same entity, ARB, for the purpose of achieving that objective. The regulations cover activity in the same geographical area-California. They address the same subject matter-the chemical composition of transportation fuels and the chemical makeup of the emissions created by burning those fuels. The temporal connection also is close, as is demonstrated by the fact the 2015 LCFS regulations replaced the original LCFS regulations, making them sequential.
Therefore, we conclude that for purposes of CEQA the activities associated with the original LCFS regulations, the 2015 LCFS regulations, and the ADF regulations constitute a single project under the circumstances of this case. Stated another way, they constitute an "activity directly undertaken by [a] public agency" (§ 21065, subd. (a)) and are "part of a single, coordinated endeavor." ( ACE , supra , 116 Cal.App.4th at p. 639, 10 Cal.Rptr.3d 560 .) It follows that those same activities are the "project" referred to in paragraph 3 of the writ.
6. Fulfilling the Writ's Purpose
As we stated under the heading labeled " Corrective Action ," "[s]ubdivision (a)(3) of section 21168.9 authorizes this court to 'mandate that the public agency take specific action as may be necessary to bring the determination,
15 Another way to phrase the question of whether a particular act is a step taken towards the achievement of the proponent's objective is to ask "whether the act is part of a coordinated endeavor." ( Tuolumne CCRG , supra , 155 Cal.App.4th at p. 1228, 66 Cal.Rptr.3d 645 , citing Association for a Cleaner Environment v. Yosemite Community College Dist. (2004) 116 Cal.App.4th 629 , 639, 10 Cal.Rptr.3d 560 [series of acts all part of single, coordinated endeavor] ( ACE ).)
CEQAs' purpose in requiring an environmental disclosure document is "to inform decision makers and the public of any significant adverse effects a project is likely to have on the physical environment." ( Neighbors for Smart Rail v. Exposition Metro Line Construction Authority (2013) 57 Cal.4th 439 , 447, 160 Cal.Rptr.3d 1 , 304 P.3d 499 ( Neighbors for Smart Rail ).) The benefits of informed decision makers are obvious and need not be described here. The benefits of an informed public was explained over 40 years ago by this court:
"Only by requiring the [public agency] to fully comply with the letter of the law can a subversion of the important public purposes of CEQA be avoided, and only by this process will the public be able to determine the environmental and economic values of their elected and appointed officials, thus allowing for appropriate action come election day should a majority of the voters disagree." ( People v. County of Kern (1974) 39 Cal.App.3d 830 , 842, 115 Cal.Rptr. 67 ; Guidelines, § 15003, subd. (e).)
Here, voters will not be informed of the environmental values of ARB and the Board if they are not informed about all of the project's impacts, including the impacts of the original LCFS regulations. In particular, the public is entitled to know that ARB and the Board were willing to accept the risk of higher levels of NOx emissions, with the attendant increase in smog and human health impacts, in exchange for lower overall emissions of greenhouse gases to combat global warming. This information, which provides insights into ARB's environmental values, was omitted from ARB's earlier environmental disclosure document and this deficiency must be corrected if the purpose of CEQA and the February 2014 writ is to be fulfilled.
The dispute over the appropriate baseline cannot be resolved without the proper application of the term "project" to the facts of this case. When the whole of a project is properly identified, then the conditions defining the project's baseline can be determined. Here, ARB's interpretation of "project" was too narrow and, consequently, it chose the wrong year as the conditions establishing the baseline for NOx emissions.
Neighbors for Smart Rail , supra , 57 Cal.4th 439 , 160 Cal.Rptr.3d 1 , 304 P.3d 499 , is more pertinent to the baseline issues raised in this appeal. In that case, the Supreme Court
ARB attempted to justify the use of a 2014 baseline in the paragraph of the final Environmental Analysis that began: "In the interest of public disclosure, ARB staff examined the current and expected future emissions of NOx from biodiesel relative to the NOx emissions from biodiesel that were occurring prior to the adoption of the original LCFS (2009)." The final Environmental Analysis proceeded to make three main points. First, it stated that "[i]n 2009, ... the NOx emissions from biodiesel were minimal." Second, it stated that "since 2009, NOx emissions from biodiesel have increased with the increased use of biodiesel" and attributed the increased biodiesel use to "multiple incentives." This statement identifies the difficulty of determining causation-that is, apportioning the increased use of biodiesel among the factors causing the increase. Third, the final Environmental Analysis stated "it is unclear and impossible to determine what portion of the increase in use is attributable to the original LCFS." The final Environmental Analysis then discussed the federal regulations promoting biodiesel use.
ARB's defense of the 2014 baseline also included its response to a comment asserting the 2014 baseline was inappropriate. ARB stated it did not agree that an earlier "baseline would yield meaningful information for environmental analysis."
As described below, we conclude ARB has not demonstrated its "CEQA analysis employ[ed] a realistic baseline that [gave] the public and decision makers the most accurate picture practically possible of the project's likely impacts." ( Neighbors for Smart Rail , supra , 57 Cal.4th at p. 449, 160 Cal.Rptr.3d 1 , 304 P.3d 499 .) First, the assertion that NOx emissions from biodiesel in 2009 were minimal suggests a 2009 baseline would have been small, a fact that does not make its use
As to the final Environmental Analysis's statement that it would be "impossible" to apportion increases among the original LCFS regulations and other factors, counsel for ARB stated during oral argument that ARB was willing and able to decide the issues relating to causation. Thus, ARB has conceded such findings are not "impossible." Similarly, ARB's conclusory statement that use of a baseline earlier than 2014 would not yield meaningful information is unpersuasive, because it based on ARB's supposed inability to make findings of fact about the causes of increased biodiesel use.
Therefore, we conclude ARB failed to justify its use of a 2014 baseline for the project's NOx emissions and, as a result, ARB failed to comply with CEQA and paragraph 3. When this court decided to allow the original LCFS regulations to remain operative pending ARB's compliance with CEQA, we did not intend to deprive the public or decision makers of information about increased NOx emissions caused by the original LCFS regulations during that compliance period. A proper baseline would identify the conditions that existed before any impacts of the original LCFS regulations began to accrue and, thus, would provide a solid foundation for identifying those impacts. (See pt. II.G, post [baseline on remand].)
G. Meaning of the Phrase "Will Have"
The last question about the proper interpretation of paragraph 3 involves the command that ARB "[a]ddress whether the project will have a significant adverse effect on the environment as a result of increased NOx emissions...." (Italics added.) ARB points to the phrase "project will have" in paragraph 3 and argues it refers to effects of the 2015 LCFS regulations "that might occur from those new regulations in the future ." (Underlining changed to italics.)
As to the meaning of the phrase "will have," we note the verb "will" has many definitions and there are differences within those definitions as to timing. For instance, "will" can be "used to express simple futurity" or "used to express simple action or intention without conscious reference to future time." (Webster's 3d New Internat. Dict. (1993) p. 2616, col. 3.) Also, "will" can be "used to express capability." ( Ibid .) Here, the disposition in Poet I used "will have" to refer to the project's capability of causing adverse environmental effects due to increased NOx emissions. We intended ARB to address this capability for the project as a whole (i.e., original and modified regulations) and "make findings (supported by substantial evidence) regarding the potential adverse environmental effect of increased NOx emissions, and adopt mitigation measures in the event the environmental effects are found to be significant." ( Poet I, supra, 218 Cal.App.4th at p. 767, 160 Cal.Rptr.3d 69 .)
In any event, the ambiguity in the phrase "will have" need not be discussed at length because ARB did not comply with paragraph 3, regardless of whether "will have" is interpreted as referring (1) to the future only or (2) to
1. Basic Principles
No statute specifically defines the appellate relief available when a trial court erroneously discharges a writ of mandate. Code of Civil Procedure section 906 sets forth the general authority of appellate courts to provide relief. Consequently, that section provides the statutory foundation for the appellate relief available in cases of erroneously discharged writs. Code of Civil Procedure section 906 states that an appellate court reviewing an appealable order "may affirm, reverse or modify" the order. The appellate court also "may direct the proper ... order to be entered, and may, if necessary or proper, direct ... further proceedings to be had." (Code Civ. Proc., § 906.) The express statutory authority to direct further proceedings that are necessary and proper fits with an appellate court's "inherent power to decide any issue deemed necessary for a proper disposition of the case." ( Canal-Randolph Anaheim, Inc. v. Wilkoski (1978) 78 Cal.App.3d 477 , 495, 144 Cal.Rptr. 474 .)
Reported decisions provide few examples of relief granted after an appellate court determines an order discharging a writ of mandate was granted in error. The first and obvious type of relief is the reversal of the trial court's order discharging the writ. (See Sanders v. City of Los Angeles (1970) 3 Cal.3d 252 , 261-262, 90 Cal.Rptr. 169 , 475 P.2d 201 [Court of Appeal's reversal of order discharging the writ affirmed] ( Sanders ); Lewis v. Steifel (1950) 98 Cal.App.2d 648 , 652, 220 P.2d 769 ["order discharging and vacating writ is reversed"].) In addition, the appellate court may expand upon the reversal by directing the trial court to order defendants to comply with the writ. ( Sanders , supra , at p. 256, 90 Cal.Rptr. 169 , 475 P.2d 201 ; see Sanders v. City of Los Angeles (1967) 252 Cal.App.2d 488 , 495, 60 Cal.Rptr. 539 ["the court is directed to order all defendants to comply with the writ of mandate"].) The appellate court also may direct the trial court to issue " 'any further appropriate orders to compel obedience to the writ.' " ( Sanders , supra , at p. 262, 90 Cal.Rptr. 169 , 475 P.2d 201 .)
To summarize, when an appellate court determines a public official or agency has failed to comply with a writ of mandate, the basic components of appellate relief are (1) reversal of the order discharging the writ and (2)
The role of CEQA in guiding the determination of what further orders are appropriate in this appeal returns us to Poet I 's discussion of the provisions that may be included in a peremptory writ of mandate issued to remedy CEQA violations. ( Poet I , supra , 218 Cal.App.4th at pp. 756-766, 160 Cal.Rptr.3d 69 .) We stated section 21168.9 provides that the writ may direct the agency "(1) to void, in whole or in part, a determination, finding or decision, (2) to 'suspend any or all specific project activity or activities' if certain conditions exist, or (3) to take specific action necessary to bring the determination, finding or decision tainted by the CEQA violation into compliance with CEQA." ( Poet I , supra , at p. 757, 160 Cal.Rptr.3d 69 fn. omitted; see § 21168.9, subd. (a)(1)-(3).) We concluded these categories of relief remain relevant to deciding what further orders may be appropriate in this appeal.
Also, section 21168.9 supplements its affirmative statement of available relief with provisions explicitly limiting the remedial action that courts may include in the writ of mandate. ( Poet I , supra , 218 Cal.App.4th at p. 758, 160 Cal.Rptr.3d 69 ; see § 21168.9, subds. (b)-(c).) Those express statutory limitations are not set forth here because our discussion of those limitations already is published in Poet I , supra , at page 758, 160 Cal.Rptr.3d 69 and severance is discussed in part II.F, post . As to specific implied limitations, none exist because subdivision (c) of section
As to ARB's specific argument about our lack of authority to suspend the 2015 LCFS regulations, we note that ARB adopted the 2015 LCFS regulations as part of its attempt to comply with paragraph 3 of the February 2014 writ. That attempt did not comply and, as a result, the initial violation of CEQA remains uncorrected and taints the 2015 enactment. To remedy the
18 In other words, we are not asserting any authority (i.e., jurisdiction) to remedy CEQA violations alleged in another lawsuit, only the authority to remedy a CEQA violation that has been a part of this lawsuit since the complaint was filed in December 2009.
Under our view of when ARB's corrective action would have been completed, a reversal of the discharge order would mean that ARB's corrective action would not be regarded as "completed" for purposes of paragraph 6. Thus, paragraph 6 would continue to require ARB "to adhere to the LCFS regulations standards in effect for 2013." ( Poet I , supra , 218 Cal.App.4th at p. 767, 160 Cal.Rptr.3d 69 .) In contrast, under ARB's interpretation, its corrective action was completed no matter what happened subsequently in court and, thus, reinstating the writ would not revive paragraph 6 or the 2013 standards. Under ARB's view, the applicable fuel standards on remand would be determined by the 2015 LCFS regulations because that version of the regulations is currently in effect.
These differing interpretations have had no effect on how this case has proceeded so far. However, these conflicting interpretations could generate uncertainty in subsequent proceedings if further orders do not clarify paragraph 6's role on remand.
2. Paragraphs 6 and 11: Suspending the 2013 Standards
Assuming the parties agreed with our interpretation of the phrase "is completed" and agreed paragraph 6 of the February 2014 writ would be reinstated on remand, a dispute would arise involving the last clause of paragraph 6. That clause states that "the LCFS regulations shall remain in operation and shall be enforceable unless its operationis suspended as provided below ." ( Poet I , supra , 218 Cal.App.4th at p. 767, 160 Cal.Rptr.3d 69 , italics added.) The phrase "as provided below" refers to a provision in Poet I 's disposition that became paragraph 11 of the February 2014 writ. Paragraph 11 states in full:
"ARB shall proceed in good faith without delay. In the event ARB fails to proceed in good faith with diligence, this [trial] Court immediately shall vacate Paragraph 6 of this writ, which preserves the status quo and shall direct ARB to set aside the LCFS regulations (i.e., suspend the operation and enforcement of the regulations)."
Plaintiffs contend ARB did not act in good faith and, therefore, whatever version of the LCFS regulations ARB believes would be in effect on remand should be suspended until ARB actually has complied with paragraph 3. In response, ARB argues it acted in good faith and, moreover, interprets paragraphs 6 and 11 in a manner that gives them no ongoing effect, thus rendering them irrelevant to any proceedings on remand. These arguments
The choice among these three possibilities lies within the discretionary authority of the appellate court. Code of Civil Procedure section 906 provides that an appellate court " may direct the proper ... order to be entered, and may , if necessary or proper, direct ... further proceedings to be had." We interpret the statute's use of "may" as signaling the grant of discretionary authority. ( Wells Fargo Bank, N.A. v. 6354 Figarden General Partnership (2015) 238 Cal.App.4th 370 , 384, 190 Cal.Rptr.3d 13 [generally, a statute using "may" grants discretion].)
In this case, we choose to exercise our discretionary authority by preparing the terms of the order to be issued on remand. Our choice is based on the fact that this court (1) identified the original CEQA violations, (2) drafted the terms of the February 2014 writ designed to remedy those violations, (3) identified ARB's failure to comply with paragraph 3, and (4) is familiar with the purpose of paragraph 3 and the CEQA policies it sought to promote. Also, the present case is a CEQA proceeding and, consequently, this court occupies nearly the same position as the trial court-that is, each court sits as a court of review considering the agency's action. ( Vineyard , supra , 40 Cal.4th at p. 427, 53 Cal.Rptr.3d 821 , 150 P.3d 709 .) This similarity of position, coupled with the trial court's workload, supports our decision to prepare the terms of the order issued on remand.
E. Reinstate the 2013 Standards?
The further orders we direct to be issued on remand should clarify whether the 2013 standards contained in the original LCFS regulations are reinstated and will be the operative standards pending discharge of the writ. (See pt. II.C, ante .) We conclude 2013 standards should not be reinstated and the February 2014 writ should be modified to prevent such a reinstatement.
Section 21168.9 states that a writ of mandate addressing a failure to comply with CEQA may direct "the determination, finding, or decision be voided by the public agency, in whole or in part" and, when certain conditions exist, may direct the public agency and real parties in interest to "suspend any or all specific project activity or activities." (§ 21168.9, subd. (a)(1)-(2).) The phrases "in whole or in part" and "any or all" raise the possibility of severing some part of the approvals and the project from other parts and then invalidating or suspending only the severed parts. Indeed, CEQA makes the consideration of severance mandatory by stating: "Any order pursuant to subdivision (a) shall include only those mandates which are necessary to achieve compliance with [CEQA] and only those specific project activities in noncompliance with [CEQA]." (§ 21168.9, subd. (b); see § 15 [shall is mandatory].) However, a suspension limited to noncompliant project activities is allowed "only if a court finds that (1) the portion or specific project activity or activities are severable, (2) severance will not prejudice
3. The ADF Regulations Will Remain in Effect
The parties agree that the ADF regulations and the 2015 LCFS regulations can be severed from one another. Our own analysis leads us to conclude that
As to the second possibility, broadening the severance and suspension to include the provisions relating to all substitutes for conventional diesel would not solve the foregoing problem. Under a scenario where neither biodiesel nor renewable diesel could be reported to reduce the average carbon content of the conventional diesel fuel handled by a reporting entity, the entity would have even more difficulty in meeting the compliance schedule. Therefore, we conclude neither the provisions relating solely to biodiesel nor the provisions relating to all substitutes for conventional diesel should be severed from the remainder of the 2015 LCFS regulations.
The third possibility involves severing the provisions relating to conventional diesel fuel and all its substitutes from the remainder of the 2015 LCFS regulations. This possibility, unlike the two possibilities previously discussed, was explicitly discussed by ARB as one of three possible alternatives to the project addressed in the final Environmental Analysis. That alternative project "would remove the diesel standard from the proposed LCFS regulation" and would address only gasoline and gasoline substitutes. ARB's consideration of this alternative demonstrates that it is feasible to sever the diesel provisions from the remaining provisions of the LCFS regulations. (Guidelines, §§ 15126.6, subd. (a), 15364 [definition of feasible].) This gasoline-only alternative was not rejected on the ground it would destroy the regulatory scheme or its utility. Instead, it was rejected because ARB determined greenhouse gas emissions could be more effectively reduced by including diesel in the regulation. The test for functional separability does not consider if the entire regulation is more effective, it considers whether the remainder is complete in itself and retains its utility. Here, the LCFS regulations would retain some utility if the diesel provisions were excluded because the gasoline
5. Suspending the Diesel Portions of the LCFS Regulations
In Poet I , the CEQA violations relating to the decision maker tainted the approval of the entire project and, thus, we did not consider suspending only a portion of the regulations. Instead, we considered whether to suspend the LCFS regulations in their entirety, which was a remedy within the discretionary authority granted by section 21168.9. ( Poet I , supra , 218 Cal.App.4th at p. 761, 160 Cal.Rptr.3d 69 .) We stated that the potential suspension of the LCFS regulations was "the most controversial issue regarding judicial relief presented in this appeal." ( Ibid . ) We identified two CEQA provisions addressing whether suspension is appropriate:
"First, suspension requires a finding 'that a specific project activity or activities will prejudice the consideration or implementation of particular mitigation measures or alternatives to the project....' (§ 21168.9, subd. (a)(2).) Second, the suspension appears to be limited to project activity 'that could result in an adverse change or alteration to the physical environment....' (§ 21168.9, subd. (a)(2).)" ( Poet I , supra , 218 Cal.App.4th at p. 761, 160 Cal.Rptr.3d 69 .)
We applied these two provisions to the record and arguments presented in Poet I and reached the unusual conclusion of allowing the LCFS regulations
Next, we consider the question of prejudice from the point of view of what would happen if the LCFS regulations addressing diesel fuel and its substitutes were suspended. Specifically, would "suspending the operation of [that portion] of the LCFS regulations ... open for consideration mitigation
The last factor we consider in exercising our discretionary authority to fashion a remedy in this appeal is plaintiffs' claim that ARB failed to act in good faith in addressing NOx emissions from biodiesel. Paragraph 11 of the February 2014 writ stated "ARB shall proceed in good faith and without delay" and a failure to proceed would cause the trial court to immediately suspend the operation of the LCFS regulations and vacate the part of the writ that preserved the status quo. Plaintiffs contend the language in paragraph 11 should influence the remedy adopted in this appeal.
Initially, we define what the term "good faith" meant. "In ordinary usage, the phrase 'good faith' is commonly understood as referring to a subjective state of mind." ( Ceja v. Rudolph & Sletten, Inc. (2013) 56 Cal.4th 1113 , 1120, 158 Cal.Rptr.3d 21 , 302 P.3d 211 .) A subjective good faith standard is satisfied by a state of mind denoting honesty of purpose and freedom from intention to mislead or defraud. ( Ibid . ; Madera Oversight Coalition, Inc. v. County of Madera, supra, 199 Cal.App.4th at p. 103, fn. 32, 131 Cal.Rptr.3d 626 ; see People v. Accredited Surety Casualty Company (2014) 230 Cal.App.4th 548 , 560, fn. 9, 178 Cal.Rptr.3d 809 [defining subjective good faith].) This court used the term "good faith" in the disposition of Poet I with the expectation that the parties and trial court would adopt the common understanding and treat the term as imposing a subjective standard.
Next, we apply the subjective good faith standard to the facts presented and consider whether ARB's remedial action was taken without honesty of purpose or sincerity of intentions. ARB's remedial action was multifaceted and some of that action complied with February 2014 writ and cured the corresponding CEQA and APA violations. Only ARB's evaluation of NOx emissions from biodiesel failed to comply. Therefore, plaintiffs' claim that ARB did not act in good faith is limited to ARB's evaluation of NOx emissions from biodiesel.
When ARB addressed NOx emissions from biodiesel pursuant to paragraph 3, ARB misconstrued the term "project" and wrongly determined the original LCFS regulations were not part of the "project." ARB's erroneous view of the "project" also provided its justification for choosing the wrong baseline.
Having decided ARB did not act in good faith, we address the role ARB's lack of good faith should have in determining the appropriate relief in this appeal. The agency's good faith is not a factor identified in section 21168.9, but we consider it relevant to the exercise of our discretionary
Accordingly, we will not decide whether a 2010 baseline is appropriate for use on remand. Furthermore, we limit our informal guidance on the choice of baseline to the following observations. First, ARB should determine when it commenced its environmental analysis of the original LCFS regulations. Second, if ARB chooses to adopt a baseline other than the normal, existing conditions baseline, it must provide an adequate justification for that choice and support that justification with substantial evidence. For instance, a conclusory statement that an existing conditions baseline would be misleading is not an adequate justification. Third, the choice of an existing conditions baseline would avoid challenges to that choice based on the argument that baseline chosen includes increases in biodiesel use because reporting entities already had begun modifying their behavior in anticipation of the adoption or implementation of the original LCFS regulations.
DISPOSITION
The order discharging the peremptory writ of mandate is reversed. The superior court is directed to vacate that order and enter a new order (1)
(3) Preserve the status quo relating to conventional diesel fuel and its substitutes by continuing to adhere to the 2017 standard for those fuels, which standard is contained in Table 2 of subdivision (c) of section 95484 of title 17 of the California Code of Regulations, until the corrective action is complete and approved by the trial court in an order discharging the writ.[24]
24 This provision replaces paragraph 6 of the February 2014 writ.
Cases cited
- Poet v. State Air Resources Board 218 Cal.App.4th 681 p. 57
- Haraguchi v. Superior Court 43 Cal.4th 706 p. 63
- Vineyard Area Citizens for Responsible Growth, Inc. v. City of Rancho Cordova 40 Cal.4th 412 p. 63
- California Unions for Reliable Energy v. Mojave Desert Air Quality Management District 178 Cal.App.4th 1225 p. 73
- North Coast Rivers Alliance v. Westlands Water District 227 Cal.App.4th 832 p. 73
- San Joaquin Raptor/Wildlife Rescue Center v. County of Stanislaus 27 Cal.App.4th 713 p. 73
- Tuolumne County Citizens for Responsible Growth, Inc. v. City of Sonora 155 Cal.App.4th 1214 p. 73
- Friends of Sierra Railroad v. Tuolumne Park & Recreation District 147 Cal.App.4th 643 p. 73
- Plastic Pipe & Fitting Ass'n v. California Building Standards Commission 124 Cal.App.4th 1390 p. 74
- Plan for Arcadia, Inc. v. City Council of Arcadia 42 Cal.App.3d 712 p. 74
- Communities for a Better Environment v. South Coast Air Quality Management District 48 Cal.4th 310 p. 78
- Madera Oversight Coalition, Inc. v. County of Madera 199 Cal.App.4th 48 at 102 p. 81
- Neighbors for Smart Rail v. Exposition Metro Line Construction Authority 57 Cal.4th 439 p. 84, p. 701, p. 703
- Citizens Opposing a Dangerous Environment v. County of Kern 228 Cal.App.4th 360 p. 84
- California Redevelopment Ass'n v. Matosantos 53 Cal.4th 231 p. 92
- Verner, Hilby & Dunn v. City of Monte Sereno 245 Cal.App.2d 29 p. 92
- Calfarm Insurance v. Deukmejian 48 Cal.3d 805 p. 92
- Blumenthal v. Board of Medical Examiners 57 Cal.2d 228 p. 92
- Los Angeles International Charter High School v. Los Angeles Unified School District 209 Cal.App.4th 1348 p. 690
- Protect Our Water v. County of Merced 130 Cal.App.4th 488 p. 691
- People v. County of Kern 39 Cal.App.3d 830 p. 701
- Canal-Randolph Anaheim, Inc. v. Wilkoski 78 Cal.App.3d 477 p. 708
- Sanders v. City of Los Angeles 3 Cal.3d 252 p. 708
- Lewis v. Steifel 98 Cal.App.2d 648 p. 708
- Sanders v. City of Los Angeles 252 Cal.App.2d 488 p. 708
- Wells Fargo Bank, N.A. v. 6354 Figarden General Partnership 238 Cal.App.4th 370 p. 712
- Ceja v. Rudolph & Sletten, Inc. 56 Cal.4th 1113 p. 719
- People v. Accredited Surety Casualty Co. 230 Cal.App.4th 548 at 560 p. 719
- Friends of the College of San Mateo Gardens v. San Mateo County Community College District 1 Cal.5th 937 p. 720
- Stonehouse Homes LLC v. City of Sierra Madre 167 Cal.App.4th 531 p. 722