Rethinking Regulatory Reform: Toxics, Politics, and Ethics

Jay Michaelson
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引用次数: 14

Abstract

This note discusses harm allocation in environmental regulation, focusing on the regulation of toxic substances and observes cost/benefit analysis shifts such regulation from a proxy liability rule, with the entitlement given to the bearer of the protected body, to a proxy property rule, with the entitlement held by toxics producers. In regulating toxics, the Environmental Protection Agency (EPA) and others must set "acceptable" levels of risk posed by toxic substances, i.e., determine how much cancer is worth the benefits of a given toxic substance. Most discussions of toxics regulation, however, focus on the "science" of risk assessment and the politics of risk management, thus missing the heart of EPA's harm allocation effort: the initial decision of how much harm is to be allowed -- how many people are to die. Part I proposes a new framework for understanding toxic risk allocation with a focus on "risk determination," the process of quantifying "significant" risk. Historically, EPA has usually determined that only de minimis levels of risk (generally defined as one death per million exposed individuals) are acceptable for most toxic substances. This determination, though not one of zero risk, still legitimizes the subterfuge of "good science" -- the myth that EPA is only measuring safety -- and suggests that, when the state controls harm allocation, no nonnegligible amount of death is acceptable. Safety supposedly determines the level of harm allocation. Cost-benefit based reforms of the regulatory process fundamentally alter this ethical and political orientation, as discussed in Part II. By requiring that regulations "justify their cost," they shift risk allocation from a process of determining a de minimis risk level and measuring how much of a toxin yields that amount, to one of defining acceptable risk itself as the amount that is profitable for industry to produce. Obviously, this shift creates enormous practical problems; most immediately, EPA would have to decide how to quantify the "benefit" of freedom from cancer. Yet with the analytical framework provided by this Note, it is clear that the problems with such reforms are ethical as well. Cost-benefit analysis used in this way affects risk determination as well as risk assessment and management, thus redirecting the entire risk allocation process. In effect, cost benefit risk determination shifts toxic regulation from a proxy liability rule, with the entitlement given to the bearer of the protected body, to a proxy property rule, with the entitlement held by toxics producers. This note concludes by suggesting that, as regulatory reform continues to be debated in Washington, such ethical agons may be avoided through less hasty reform of environmental regulation and a clearer understanding of the subtle structural and ethical distinctions within the regulatory process.
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重新思考监管改革:有毒物质、政治和伦理
本文讨论了环境监管中的危害分配,重点是有毒物质的监管,并观察了成本/效益分析,将这种监管从代理责任规则(将权利赋予受保护主体的持有人)转变为代理财产规则(将权利赋予有毒物质生产者)。在管制有毒物质时,环境保护署(EPA)和其他机构必须设定有毒物质造成的“可接受的”风险水平,即确定某种有毒物质带来的好处值得多少癌症。然而,大多数关于有毒物质监管的讨论都集中在风险评估的“科学”和风险管理的“政治”上,从而忽略了EPA危害分配工作的核心:允许多少危害的初步决定——有多少人会死亡。第一部分提出了一个理解毒性风险分配的新框架,重点是“风险确定”,即量化“重大”风险的过程。从历史上看,环境保护局通常确定,对于大多数有毒物质,只有最低的风险水平(一般定义为每百万接触者中有一人死亡)是可以接受的。这一结论虽然不是零风险,但仍然使“良好科学”的借口合法化——即环保署只衡量安全的神话——并表明,当国家控制危害分配时,任何不可忽略的死亡数量都是可以接受的。据称,安全决定了危害分配的程度。正如第二部分所讨论的那样,基于成本效益的监管过程改革从根本上改变了这种道德和政治取向。通过要求法规“证明其成本是合理的”,他们将风险分配从确定最低风险水平和测量毒素产生多少的过程,转变为将可接受的风险本身定义为工业生产有利可图的数量。显然,这种转变带来了巨大的实际问题;最紧迫的是,环保署必须决定如何量化远离癌症的“好处”。然而,从本说明提供的分析框架来看,这些改革的问题显然也是伦理问题。以这种方式使用的成本效益分析影响风险确定以及风险评估和管理,从而重新定向整个风险分配过程。实际上,成本效益风险确定将有毒物质监管从代理责任规则(权利授予受保护实体的持有者)转变为代理财产规则(权利由有毒物质生产商持有)。本文最后建议,随着监管改革继续在华盛顿进行辩论,可以通过不那么仓促的环境监管改革和对监管过程中微妙的结构和道德区别的更清晰理解来避免这种伦理上的痛苦。
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