Comments on “Increasing Consistency and Transparency in Considering Benefits and Costs in the Clean Air Act Rulemaking Process”

M. Luttrell
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Women, in particular, have been negatively impacted by the lack of normal childcare supports during this time, and COVID-19 infections have disproportionately affected people of color. Many organizations have requested an extension of time to respond to this rulemaking;unfortunately, EPA provided only a week’s extension, leaving a comment period of less than 60 days. Under the circumstances, this refusal to allow adequate time for the public to review and critique the proposed econometric and scientific methodologies—which are to be applied to a diversecollection of very complicated provisions—was unreasonable, arbitrary and capricious.And the stakes here are incredibly high. Consider PM 2.5 pollution, which causes tens of thousands of excess deaths every year. Virtually any CAA regulation that reduces any type of air pollution will—intentionally or not—reduce the number of fatalities that result from exposure to PM 2.5. The issue of how we value this human impact of pollution regulation and deregulation is far too important to be given such rushed treatment. Rather than carefully consider the best way to conduct an econometric analysis—if one is even appropriate—or the best way to use risk assessment data, the Trump EPA seems instead to be intent on codifying a set of biased methodologies while it still has control of the agency. If successful, the outcome will be dramatic—a thumb on the scale in favor of weaker standards, with millions of undercounted and systematically undervalued human lives hanging in the balance.This rulemaking is an effort to use a general authorization to issue CAA regulations to enable the EPA to override the more specific provisions of the CAA that limit or prohibit certain considerations. This is not a legitimate use of section 301(a)(1) of the Clean Air Act. Many of the regulatory analyses being “standardized” with this rulemaking did not begin to gain traction in the environmental context until after the CAA had been enacted. It is thus unsurprising that they often do not square well with the objectives, substance, and procedure actually laid out in the CAA. To overlay the methodologies advanced in this NPRM over the entire mass of diverse CAA provisions would re-write those provisions to favor factors that are currently in vogue among regulated industry (and, often, the think tanks and the holders of academic institutes that they help fund), but which were not intended to be enacted in 1970 when Congress established the CAA.In addition, the attempt to solicit the legal authority for the rule from the public is contrary to the requirements of the APA, which requires that notice must include “the legal authority under which the rule is proposed.” Moreover, by requiring justification for any departure from OMB Circular A-4, this NPRM essentially codifies A4’s CBA methodological requirements. Unfortunately, A-4 sets out methodologies that generate “garbage out” results. In an attached publication submitted herewith, I trace the origin of these cost-benefit rules, demonstrating that Circular A-4 was developed through a fundamentally flawed process, one that intentionally excluded majority viewpoints in several relevant academic disciplines. Circular A-4 also contains serious methodological mistakes. If these mi takes were to be applied to, for example, CAA regulations addressing domestic greenhouse gas emissions (that is, if EPA follows the rules as set out in this NPRM), this injection of both outright irrationality and arguably unethical subjective biases into domestic regulatory policy would threaten to derail substantive U.S. action on climate change.In the instant NPRM, EPA claims that “OMB Circular A-4 . . . was issued after peer review and public comment and has been widely accepted for more than a decade as embodying the best practices for conducting regulatory cost-benefit analysis.” This is simply not true;A4 was not subjected to meaningful peer review. Similarly, EPA’s claim in the instant NPRM that A-4 was subjected to public “notice and comment” is misleading, since the phrase evokes notice-and-comment procedures under the APA, which were not followed in the establishment of A-4.CBA is a microeconomic tool that was originally developed to evaluate comparatively small projects, such as TVA dam projects. It was never meant to—and it cannot—serve as a meaningful tool in evaluating policies that will influence the entire economy, such as determinations of whether to reduce greenhouse gas emissions meaningfully. These concerns are inherently macro, and these decisions involve complicated feedback mechanisms and othercomplexities that make them unsuited for the tools agencies currently use in RIAs prepared under the direction of OIRA and Circular A-4.Executive Order 12,866 is impossible to comply with in a literal manner, because it creates a series of “max/min” problems with no common solution. This creates a conundrum that, over and over again, would be resolved under these cost-benefit rules in favor of maximizing quantifiable, monetized “net benefits,” at the expense of promoting a set of competing yet also important rights- and duty- based factors that the text of the parent executive order ostensibly puts on equal footing. These deontological concerns deserve attention from EPA, and should not be summarily dismissed in favor of an anti-regulatory, entirely welfarist analytical rubric.","PeriodicalId":233762,"journal":{"name":"U.S. Administrative Law eJournal","volume":"50 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2020-08-03","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"2","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"U.S. Administrative Law eJournal","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.2139/ssrn.3923773","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 2

Abstract

Were this anti-regulatory NPRM—or any logical outgrowth of it—to be finalized, it would result in repeated violations of the Clean Air Act and the Administrative Procedures Act. The problematic methodologies being codified in this NPRM would often generate nonsensical, arbitrary results, and would promote multiple biases that undermine the goals of the Act.It is unfortunate that the Trump administration is rushing out a slew of standards during a national pandemic. The stakeholders that normally would organize and engage to protest these actions through participation in notice-and-comment rulemaking and strategic litigation are spread thin, and many do not have sufficient time to participate meaningfully. Women, in particular, have been negatively impacted by the lack of normal childcare supports during this time, and COVID-19 infections have disproportionately affected people of color. Many organizations have requested an extension of time to respond to this rulemaking;unfortunately, EPA provided only a week’s extension, leaving a comment period of less than 60 days. Under the circumstances, this refusal to allow adequate time for the public to review and critique the proposed econometric and scientific methodologies—which are to be applied to a diversecollection of very complicated provisions—was unreasonable, arbitrary and capricious.And the stakes here are incredibly high. Consider PM 2.5 pollution, which causes tens of thousands of excess deaths every year. Virtually any CAA regulation that reduces any type of air pollution will—intentionally or not—reduce the number of fatalities that result from exposure to PM 2.5. The issue of how we value this human impact of pollution regulation and deregulation is far too important to be given such rushed treatment. Rather than carefully consider the best way to conduct an econometric analysis—if one is even appropriate—or the best way to use risk assessment data, the Trump EPA seems instead to be intent on codifying a set of biased methodologies while it still has control of the agency. If successful, the outcome will be dramatic—a thumb on the scale in favor of weaker standards, with millions of undercounted and systematically undervalued human lives hanging in the balance.This rulemaking is an effort to use a general authorization to issue CAA regulations to enable the EPA to override the more specific provisions of the CAA that limit or prohibit certain considerations. This is not a legitimate use of section 301(a)(1) of the Clean Air Act. Many of the regulatory analyses being “standardized” with this rulemaking did not begin to gain traction in the environmental context until after the CAA had been enacted. It is thus unsurprising that they often do not square well with the objectives, substance, and procedure actually laid out in the CAA. To overlay the methodologies advanced in this NPRM over the entire mass of diverse CAA provisions would re-write those provisions to favor factors that are currently in vogue among regulated industry (and, often, the think tanks and the holders of academic institutes that they help fund), but which were not intended to be enacted in 1970 when Congress established the CAA.In addition, the attempt to solicit the legal authority for the rule from the public is contrary to the requirements of the APA, which requires that notice must include “the legal authority under which the rule is proposed.” Moreover, by requiring justification for any departure from OMB Circular A-4, this NPRM essentially codifies A4’s CBA methodological requirements. Unfortunately, A-4 sets out methodologies that generate “garbage out” results. In an attached publication submitted herewith, I trace the origin of these cost-benefit rules, demonstrating that Circular A-4 was developed through a fundamentally flawed process, one that intentionally excluded majority viewpoints in several relevant academic disciplines. Circular A-4 also contains serious methodological mistakes. If these mi takes were to be applied to, for example, CAA regulations addressing domestic greenhouse gas emissions (that is, if EPA follows the rules as set out in this NPRM), this injection of both outright irrationality and arguably unethical subjective biases into domestic regulatory policy would threaten to derail substantive U.S. action on climate change.In the instant NPRM, EPA claims that “OMB Circular A-4 . . . was issued after peer review and public comment and has been widely accepted for more than a decade as embodying the best practices for conducting regulatory cost-benefit analysis.” This is simply not true;A4 was not subjected to meaningful peer review. Similarly, EPA’s claim in the instant NPRM that A-4 was subjected to public “notice and comment” is misleading, since the phrase evokes notice-and-comment procedures under the APA, which were not followed in the establishment of A-4.CBA is a microeconomic tool that was originally developed to evaluate comparatively small projects, such as TVA dam projects. It was never meant to—and it cannot—serve as a meaningful tool in evaluating policies that will influence the entire economy, such as determinations of whether to reduce greenhouse gas emissions meaningfully. These concerns are inherently macro, and these decisions involve complicated feedback mechanisms and othercomplexities that make them unsuited for the tools agencies currently use in RIAs prepared under the direction of OIRA and Circular A-4.Executive Order 12,866 is impossible to comply with in a literal manner, because it creates a series of “max/min” problems with no common solution. This creates a conundrum that, over and over again, would be resolved under these cost-benefit rules in favor of maximizing quantifiable, monetized “net benefits,” at the expense of promoting a set of competing yet also important rights- and duty- based factors that the text of the parent executive order ostensibly puts on equal footing. These deontological concerns deserve attention from EPA, and should not be summarily dismissed in favor of an anti-regulatory, entirely welfarist analytical rubric.
关于“在清洁空气法规则制定过程中考虑收益和成本时提高一致性和透明度”的评论
如果这个反监管的nprm——或者它的任何逻辑结果——最终确定下来,它将导致对《清洁空气法》和《行政程序法》的一再违反。NPRM中编纂的有问题的方法往往会产生荒谬的、武断的结果,并会促进多种偏见,从而破坏该法案的目标。不幸的是,特朗普政府在全国大流行的情况下匆忙出台了一系列标准。通常会通过参与通知-评论规则制定和战略诉讼来组织和参与抗议这些行动的利益相关者分散了,许多人没有足够的时间进行有意义的参与。在此期间,由于缺乏正常的儿童保育支持,妇女尤其受到负面影响,而COVID-19感染对有色人种的影响尤为严重。许多组织要求延长时间来回应这一规则制定;不幸的是,EPA只提供了一周的延长,留下不到60天的评论期。在这种情况下,拒绝给公众足够的时间来审查和批评拟议的计量经济学和科学方法——这些方法将被应用于各种非常复杂的条款——是不合理的、武断的和反复无常的。这里的风险非常高。以每年造成数万人额外死亡的pm2.5污染为例。实际上,任何减少任何类型空气污染的CAA法规都会有意或无意地减少因暴露于PM 2.5而导致的死亡人数。我们如何评估污染监管和放松管制对人类的影响,这个问题太重要了,不能如此仓促地处理。特朗普环保局没有仔细考虑进行计量经济分析的最佳方法(如果合适的话),也没有考虑使用风险评估数据的最佳方法,反而似乎有意在其仍然控制该机构的情况下编纂一套有偏见的方法。如果成功,结果将是戏剧性的——这是支持较低标准的一个拇指,数百万被低估和被系统低估的人的生命悬在天平上。本规则制定是利用一般授权发布CAA法规的一种努力,使EPA能够超越CAA中限制或禁止某些考虑因素的更具体的规定。这不是对《清洁空气法》301(a)(1)条款的合法使用。直到CAA颁布之后,许多监管分析才开始在环境背景下被“标准化”。因此,它们经常与CAA中实际列出的目标、内容和程序不太一致,这并不奇怪。将NPRM中先进的方法覆盖到所有不同的CAA条款中,将重写这些条款,以支持当前在受监管行业(通常是他们帮助资助的智囊团和学术机构的持有人)中流行的因素,但这些因素在1970年国会建立CAA时并不打算颁布。此外,试图向公众征求该规则的法律权威与《行政程序法》的要求相悖,《行政程序法》要求通知必须包括“提出该规则的法律权威”。此外,通过要求任何偏离OMB通告A-4的理由,该NPRM基本上编纂了A4的CBA方法要求。不幸的是,A-4列出了产生“垃圾输出”结果的方法。在随函附上的一份出版物中,我追溯了这些成本效益规则的起源,证明a -4号通函是通过一个根本有缺陷的过程制定的,这个过程故意排除了几个相关学科的多数观点。通告A-4也有严重的方法错误。例如,如果将这些错误应用于解决国内温室气体排放的CAA法规(也就是说,如果EPA遵循本NPRM中规定的规则),那么将完全非理性和不道德的主观偏见注入国内监管政策将有可能破坏美国在气候变化方面的实质性行动。在即时NPRM中,EPA声称“OMB通告A-4……是在同行评审和公众意见之后发布的,十多年来被广泛接受,作为进行监管成本效益分析的最佳实践。”这根本不是真的;A4没有受到有意义的同行评审。同样,EPA在即时NPRM中声称A-4受到公众“通知和评论”的误导,因为这一短语唤起了APA下的通知和评论程序,而A-4的建立并没有遵循这一程序。 CBA是一种微观经济工具,最初用于评估相对较小的项目,如TVA大坝项目。它从来就不是,也不可能成为评估影响整个经济的政策的有意义的工具,比如决定是否有意地减少温室气体排放。这些问题本质上是宏观的,这些决定涉及复杂的反馈机制和其他复杂性,使它们不适合机构目前在OIRA和通告A-4指导下编制的ria中使用的工具。第12866号行政命令是不可能严格遵守的,因为它造成了一系列没有共同解决方案的“最大/最小”问题。这就产生了一个难题,这个难题将在这些成本效益规则下一次又一次地得到解决,这些规则有利于最大化可量化的、货币化的“净效益”,而代价是促进一系列相互竞争但又重要的基于权利和义务的因素,而这些因素表面上是由上级行政命令的文本置于平等地位的。这些义务论方面的担忧值得环保局关注,不应该被草率地排除在反监管、完全福利主义的分析范畴之外。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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