At last, empirical elicitations of the magnitudes of those risks (and costs!) too small to matter and those too large to abide

IF 3 3区 环境科学与生态学 Q2 ENVIRONMENTAL SCIENCES Human and Ecological Risk Assessment Pub Date : 2023-11-08 DOI:10.1080/10807039.2023.2251585
Adam M. Finkel, Branden B. Johnson
{"title":"At last, empirical elicitations of the magnitudes of those risks (and costs!) too small to matter and those too large to abide","authors":"Adam M. Finkel, Branden B. Johnson","doi":"10.1080/10807039.2023.2251585","DOIUrl":null,"url":null,"abstract":"AbstractScholars, decision-makers, and pundits have long tossed around words and numbers meant to demarcate those health/safety risks that are too small to matter at all (called, variously, “trivial” or “de minimis” or “insignificant”), or risks that are so large as to be abhorrent (“unacceptable,” “intolerable,” and the like). But there has been nothing approaching a consensus about how large or small these important probabilities are, and worse, there have been no serious attempts to explore these concepts via any carefully-elicited preferences from laypeople themselves. Perhaps even more concerning, the dominant paradigm—cost-benefit analysis (CBA)—requires balancing of (monetized) risks against the costs of controlling them, but the parallel concepts of de minimis costs and intolerable costs have never been formally considered. As a result of these lapses, all attempts to consider equity or justice in the distribution of how risks and costs are borne are an absurdity, despite claims to the contrary.This article reports on a pair of elicitations involving 1350 laypeople. In one elicitation, a careful set of background and contextual explanations and a structured series of questions probed where each subject perceived lifetime excess mortality risk (from involuntary exposure) to become “so small you would not spend a moment thinking about it,” and where it becomes so large that “you would strongly object, as an ethical matter, to ever having to face it.” With a separate sample, we asked the parallel questions with regard to regulatory costs imposed by the government in the name of risk reduction.Although there was significant interindividual variation in responses, the central tendency of each of these four science-policy-values “goalposts” was as follows: (1) de minimis risk—a lifetime excess chance of premature death of 1 in 770,000; (2) intolerable risk—1 chance in 570; (3) de minimis cost—$25 per year; and (4) intolerable cost—$775 per year. These results offer, for the first time, a principled and evidence-based starting point for further refinement of which risks or costs to individuals can/should be disregarded in setting policy, and which must dominate policies regardless of how total “monetized lives saved” and total dollar costs compare to each other when viewed simplistically.We offer several prescriptions for how CBA might change, and how environmental/health/safety policy might improve, to take account of these fundamental thresholds in how risks and costs actually impose burdens on citizens. Both those interventions that impose intolerable costs while only reducing diffuse and trivially small risks, and those failures to intervene (sufficiently) that perpetuate intolerable risks for the sake of avoiding trivial and eminently manageable costs, are inefficient, unjust, and are thus unethical.Keywords: Risk assessmentstated preferencecost-benefit analysisde minimis riskenvironmental equity AcknowledgementsWe gratefully acknowledge the financial support provided by the U.S. National Science Foundation (Decision, Risk, and Management Sciences Program), under Grant # 1629287. We thank Marcus Mayorga for computer programming of the surveys, and a small group of colleagues and students at the University of Michigan School of Public Health who served as a focus group to help refine and shorten the risk experiment. We especially thank two anonymous reviewers for their helpful comments.Both psychometric surveys were approved as exempt by the Institutional Review Board (IRB00011706) of Decision Science Research Institute, Inc. The cost experiment was approved on Dec. 2, 2019, and the probability experiment on Feb. 26, 2020. The IRB concluded that the survey questions posed minimal risk to subjects, and that all information was obtained so that the identity of the human subjects cannot readily be ascertained, directly or through identifiers linked to the subjects.Author contributionsBoth authors jointly developed, tested, and refined the psychometric instruments, and analyzed the data collected. AMF wrote the first draft of this ms. and BBJ commented on it.Disclosure statementThe authors report there are no competing interests to declare.Data availability statementData and instruments for all our NSF project studies, including the one reported here, are archived at Johnson, Branden, and Finkel, Adam. Estimating the Net Benefits of Environmental, Public Health and Safety Regulations. Ann Arbor, MI: Interuniversity Consortium for Political and Social Research [distributor], 2022-07-30. https://doi.org/10.3886/E1756 61V1.Notes1 “De minimis” is Latin for “about trifles,” as in the hallmark aphorism that “the law is not concerned with trifles” (de minimis non curat lex). Therefore, we expect that the judicial system will refuse (in a principled way) to take up matters where the harm is so trivial as to be indistinguishable from no harm at all, or, at worst, from the kinds of harms humans silently bear incessantly.2 Eliciting citizen views directly is not the only way to learn about them. “Revealed preference” studies can sometimes infer these views by observing behavior, as when economists assert that the value of life can be inferred by estimating the extra wages paid to workers who “demand” them to compensate for specific excess risks of death. We encourage others to see if there exist any analogous ways to infer what risks citizens deem de minimis or intolerable by observing which risks they apparently pay zero attention to or seek to avoid at all costs. But this “stated-preference” experiment is how we’ve chosen to begin the effort.3 In effect, “intolerable cost” is often currently defined as “whenever a special interest successfully argues that he/she/they shouldn’t have to pay that much,” which is of course (worse than) no definition at all.4 In the specific but rare case of perfectly equal distribution, the “body count” and the individual risk are just scalar multiples of each other, akin to measuring weight in milligrams versus kilograms.5 This quote is attributed to pioneering asbestos researcher Dr. Irving Selikoff.6 In this article, we are concerned only about de minimis risks when the consequences are maximally severe (premature death). There is a separate literature about trivial consequences (e.g., what amount of cognitive decrement from lead exposure is too small to concern even those affected?).7 We note particularly three excellent books published between 1976 and 1987—Lowrance Citation1976, Fischhoff et al. Citation1981, and Whipple Citation1987—devoted in part to discussions of de minimis risk. However, none of the chapters in any of these books attempt to estimate RD using elicitations from laypeople, as we do here.8 Besides these single studies we cite, there are several excellent reviews of multiple studies here, notably Mumpower Citation1986, Wilson Citation1988, Hrudey and Krewski Citation1995, Hunter and Fewtrell Citation2001, Rae Citation2007, and Roy and Kshirsagar Citation2021.9 FDA has described certain very small risks as de minimis, which of course is consistent with using a higher threshold (1/million) as an upper limit for this concept. Blumenthal (Citation1990) notes that the estimated cancer risk for D&C Orange #17 was one in 19 billion, which FDA described as de minimis.10 Using January 2022 data from Oxford’s Global Change Data Lab (https://ourworldindata.org/grapher/united-states-rates-of-covid-19-deaths-by-vaccination-status), the risk of death for a boosted individual was about 0.3 per 100,000 per week. Using a 95% reduction to approximate the effectiveness of a well-fitted N95 respirator, this equals roughly a 7.5 × 10-6 per year fatality risk. It’s hard to extrapolate this mid-pandemic annual risk to a lifetime risk, but it is clearly far higher than 1/million/lifetime, so Allen is favoring a quite permissive definition of “not much else in life as low as that.”11 To be more precise, the language from the “Benzene” case referring to 10-9 used the example of “taking a drink of chlorinated water.” So it is possible that upon converting this one-time tiny probability to a lifetime one (say, by multiplying by 8 drinks/day and 25,500 days per 70 years), this de minimis pronouncement actually represented a lifetime risk of 2 × 10-4—although this would be suspiciously close to the other risk value (10-3) that Court used in the same sentence as unacceptably high. It’s probably more likely that the Court meant a 10-9 lifetime risk, in apposition to a 10-3 lifetime risk, and just explained the former example poorly.12 This background rate is roughly 2 × 10-4/yr in the U.S. and E.U., so 5% of that annual risk, converted to a 70-year lifetime, would imply a rather high estimate of RD, at 7 × 10-4.13 As Richard Wilson wrote in Citation1988 (supporting a value of 7 × 10-5 as de minimis because it is about 1/10th of the variability in the natural background exposure to ionizing radiation), “I know of no one in the world who alters, or even chooses, his place of residence or his lifestyle to keep his natural radiation dose level low.”14 A related approach was discussed by Hunter and Fewtrell (Citation2001), who suggested that society could look at all cases of a particular disease (they used gastroenteritis as an example), deeming as de minimis any exposure that contributed to less than some percentage (say, 5%) of all cases.15 Lundgren and Stefansson make two other unusual arguments that we disagree with. First, they say that because “one person’s sure death cannot be de minimis,” the entire concept is flawed. We respond that RD is a probability for all, not a certainty for any one. Second, they say that if the world population was 1020, a risk of 10-12 might not seem so negligible. We agree, but point out that the actual world population is 8 × 109, with obvious implications for RD.16 The claim that the probability of a given harm could even have its own “disutility function” is controversial. Some observers (Pratt and Zeckhauser Citation1987) claim that this is nonsensical—that only the outcome (in this article, death) can have disutility, but the probability of the outcome cannot. By this view, a 1-in-X chance of harm has exactly 1/Xth the disutility of the harm itself, for all X; different people can have different views about (different willingnesses to pay for) the harm, but not about the probability (see EPA Citation2011, p. 6: “it seems unreasonable… that an individual would value a second risk reduction of Δp much less than an initial reduction of Δp”). This view, of course, would not allow even for the very notion of de minimis risk (a very small probability of a given harm is just a very small fraction of whatever the disutility of the bad outcome is), or of intolerable risk (Shrader-Frechette Citation1985). It also reflects an expected-utility view of human perception, a view that has been waning for nearly a century (Allais Citation1953) and that continues to be supplanted by richer depictions such as regret theory (Bell Citation1982) and prospect theory (Thaler Citation1980; Tversky and Kahneman Citation1992; Booij and van de Kuilen Citation2009).17 One similar invocation of citizen preferences is much older than Byrd and Lave’s article. According to Hey et al. (Citation2010), the Comte de Buffon argued in 1777, as an attempt to use RD to “resolve” the “St Petersburg Paradox,” that a rational person would offer no more than $13 to play this infinite-expected-value game. Buffon argued that since a 56-year-old man “ignores the possibility of dying in the next 24 hours,” which had a probability of 1/10,189 according to mortality tables of the time, events with less than 1/10,000 probability could be ignored.18 The upper end of the Supreme Court’s pronouncement in the “Benzene” case is 10-3 per lifetime; although there is very little case law suggesting that OSHA has an absolute duty to regulate risks above 1/1000, by leaving it to OSHA to determine where below 1/1000 the boundary between “significant” and “insignificant” risk must fall, the Court may have implied that its upper benchmark for risk is prima facie “intolerable.”19 For example, the OSHA PEL for trichloroethylene (TCE) is 100 ppm. EPA’s inhalation unit risk factor for TCE is 2.3 × 10-5 per (part per billion).20 Since 1996, U.S. federal regulatory agencies must separately analyze the economic effects of their rules on small businesses, and three major agencies (EPA, OSHA, and the Consumer Financial Protection Bureau) must invite a panel of 15 small business representatives to jointly develop a report recommending special accommodations for this constituency. This requirement gives “intolerable cost” to one subgroup a favored (early) place in the regulatory development process, and there is no parallel consideration extended to those who bear intolerable risk (perhaps caused by the harm-promoting exemptions given to small business!); see Finkel Citation2011, also Bromberg and Finkel Citation2023, for a proposal in this regard.21 A reviewer helpfully pointed out that some subjects may not see a lawnmower as at all useful in their life, while others might regard a power mower as necessary and a push mower as an unacceptable though safer alternative. See Section 4.7 (“Limitations”).22 Another important implication of the way we designed this scenario is that all of the data herein should be interpreted as pertaining to a single narrow matter like the costs and benefits of one particular product, hazard, or exposure. We are not seeking estimates of “de minimis cumulative risk from all air pollutants considered together,” or “what aggregate risk from all EPA-regulated substances is intolerable?”, or “how much should a citizen never be expected to pay for all public policies combined?” Future research could certainly define the “four corners” in more expansive ways.23 We asked each subject to provide an alias last name for themselves, just to personalize the script (while keeping their real last name hidden). So if someone said their last name was “Johnson,” and indicated they were female, a photo of a doctor talking to a woman would appear on-screen, and the script would start with “I’m so very sorry, Mrs. Johnson, to have to tell you this awful news, but…”24 Specifically, we told subjects that “if you name a very large probability (that is, 1 in ‘extremely small number’), you are in effect saying that to gain the moderate benefits of this consumer product you are willing to consider almost any probability of harm as tolerable. If you name a very small probability (1 in ‘extremely large number’), you are in effect saying that almost any probability of harm is too intolerable to justify the benefits of this consumer product, and you are willing to give it up for yourself and others (e.g., a ban).”25 Similarly, a few subjects used “something positive that’s never happened to them or anyone they know,” like getting the grand prize in a lottery, to estimate D by analogy.26 We conducted the survey very early in the U.S. experience of Covid-19, and a few subjects cited the Covid death rate of 2.3% (although this was at the time the case fatality rate, not a risk) as helpful to their answer.27 Not every respondent imagined mortality in the numerator; one subject chose 1/35 as intolerable because of the probability of “being called on in class when you don’t know the answer.”28 As this article was in final preparation post-review, an interesting controversy began to influence the future of regulatory cost-benefit analysis. The White House Office of Information and Regulatory Affairs proposed sweeping revisions to Circular A-4, the guidance governing CBA review in the federal system, and OIRA’s new-found enthusiasm for agencies to apply “distributional weights” to costs affecting poor citizens versus rich ones dominated the comments received (Xie et al. Citation2023). Some commenters (Sullivan Citation2023) argued that these weights are inappropriate and policy-laden, despite OIRA’s clear (and we believe, correct) argument in the revisions that agencies have always been applying weights, merely implicit and equal ones. But others (see, e.g., Adler Citation2023; Finkel Citation2023) explicitly argued that such weights are the only ways to correct the long-standing error in CBA that fails to transform units of dollar cost into units of welfare decrement, as the welfare toll of a given dollar cost is clearly larger for a poor person than a rich one.29 Situs inversus is a benign genetic condition in which all the internal organs in the chest and abdomen develop in a mirror-image (left to right) position to the “normal” arrangement.Additional informationFundingU.S. National Science Foundation (Decision, Risk, and Management Sciences Program), under Grant # 1629287.","PeriodicalId":13118,"journal":{"name":"Human and Ecological Risk Assessment","volume":null,"pages":null},"PeriodicalIF":3.0000,"publicationDate":"2023-11-08","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Human and Ecological Risk Assessment","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.1080/10807039.2023.2251585","RegionNum":3,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q2","JCRName":"ENVIRONMENTAL SCIENCES","Score":null,"Total":0}
引用次数: 0

Abstract

AbstractScholars, decision-makers, and pundits have long tossed around words and numbers meant to demarcate those health/safety risks that are too small to matter at all (called, variously, “trivial” or “de minimis” or “insignificant”), or risks that are so large as to be abhorrent (“unacceptable,” “intolerable,” and the like). But there has been nothing approaching a consensus about how large or small these important probabilities are, and worse, there have been no serious attempts to explore these concepts via any carefully-elicited preferences from laypeople themselves. Perhaps even more concerning, the dominant paradigm—cost-benefit analysis (CBA)—requires balancing of (monetized) risks against the costs of controlling them, but the parallel concepts of de minimis costs and intolerable costs have never been formally considered. As a result of these lapses, all attempts to consider equity or justice in the distribution of how risks and costs are borne are an absurdity, despite claims to the contrary.This article reports on a pair of elicitations involving 1350 laypeople. In one elicitation, a careful set of background and contextual explanations and a structured series of questions probed where each subject perceived lifetime excess mortality risk (from involuntary exposure) to become “so small you would not spend a moment thinking about it,” and where it becomes so large that “you would strongly object, as an ethical matter, to ever having to face it.” With a separate sample, we asked the parallel questions with regard to regulatory costs imposed by the government in the name of risk reduction.Although there was significant interindividual variation in responses, the central tendency of each of these four science-policy-values “goalposts” was as follows: (1) de minimis risk—a lifetime excess chance of premature death of 1 in 770,000; (2) intolerable risk—1 chance in 570; (3) de minimis cost—$25 per year; and (4) intolerable cost—$775 per year. These results offer, for the first time, a principled and evidence-based starting point for further refinement of which risks or costs to individuals can/should be disregarded in setting policy, and which must dominate policies regardless of how total “monetized lives saved” and total dollar costs compare to each other when viewed simplistically.We offer several prescriptions for how CBA might change, and how environmental/health/safety policy might improve, to take account of these fundamental thresholds in how risks and costs actually impose burdens on citizens. Both those interventions that impose intolerable costs while only reducing diffuse and trivially small risks, and those failures to intervene (sufficiently) that perpetuate intolerable risks for the sake of avoiding trivial and eminently manageable costs, are inefficient, unjust, and are thus unethical.Keywords: Risk assessmentstated preferencecost-benefit analysisde minimis riskenvironmental equity AcknowledgementsWe gratefully acknowledge the financial support provided by the U.S. National Science Foundation (Decision, Risk, and Management Sciences Program), under Grant # 1629287. We thank Marcus Mayorga for computer programming of the surveys, and a small group of colleagues and students at the University of Michigan School of Public Health who served as a focus group to help refine and shorten the risk experiment. We especially thank two anonymous reviewers for their helpful comments.Both psychometric surveys were approved as exempt by the Institutional Review Board (IRB00011706) of Decision Science Research Institute, Inc. The cost experiment was approved on Dec. 2, 2019, and the probability experiment on Feb. 26, 2020. The IRB concluded that the survey questions posed minimal risk to subjects, and that all information was obtained so that the identity of the human subjects cannot readily be ascertained, directly or through identifiers linked to the subjects.Author contributionsBoth authors jointly developed, tested, and refined the psychometric instruments, and analyzed the data collected. AMF wrote the first draft of this ms. and BBJ commented on it.Disclosure statementThe authors report there are no competing interests to declare.Data availability statementData and instruments for all our NSF project studies, including the one reported here, are archived at Johnson, Branden, and Finkel, Adam. Estimating the Net Benefits of Environmental, Public Health and Safety Regulations. Ann Arbor, MI: Interuniversity Consortium for Political and Social Research [distributor], 2022-07-30. https://doi.org/10.3886/E1756 61V1.Notes1 “De minimis” is Latin for “about trifles,” as in the hallmark aphorism that “the law is not concerned with trifles” (de minimis non curat lex). Therefore, we expect that the judicial system will refuse (in a principled way) to take up matters where the harm is so trivial as to be indistinguishable from no harm at all, or, at worst, from the kinds of harms humans silently bear incessantly.2 Eliciting citizen views directly is not the only way to learn about them. “Revealed preference” studies can sometimes infer these views by observing behavior, as when economists assert that the value of life can be inferred by estimating the extra wages paid to workers who “demand” them to compensate for specific excess risks of death. We encourage others to see if there exist any analogous ways to infer what risks citizens deem de minimis or intolerable by observing which risks they apparently pay zero attention to or seek to avoid at all costs. But this “stated-preference” experiment is how we’ve chosen to begin the effort.3 In effect, “intolerable cost” is often currently defined as “whenever a special interest successfully argues that he/she/they shouldn’t have to pay that much,” which is of course (worse than) no definition at all.4 In the specific but rare case of perfectly equal distribution, the “body count” and the individual risk are just scalar multiples of each other, akin to measuring weight in milligrams versus kilograms.5 This quote is attributed to pioneering asbestos researcher Dr. Irving Selikoff.6 In this article, we are concerned only about de minimis risks when the consequences are maximally severe (premature death). There is a separate literature about trivial consequences (e.g., what amount of cognitive decrement from lead exposure is too small to concern even those affected?).7 We note particularly three excellent books published between 1976 and 1987—Lowrance Citation1976, Fischhoff et al. Citation1981, and Whipple Citation1987—devoted in part to discussions of de minimis risk. However, none of the chapters in any of these books attempt to estimate RD using elicitations from laypeople, as we do here.8 Besides these single studies we cite, there are several excellent reviews of multiple studies here, notably Mumpower Citation1986, Wilson Citation1988, Hrudey and Krewski Citation1995, Hunter and Fewtrell Citation2001, Rae Citation2007, and Roy and Kshirsagar Citation2021.9 FDA has described certain very small risks as de minimis, which of course is consistent with using a higher threshold (1/million) as an upper limit for this concept. Blumenthal (Citation1990) notes that the estimated cancer risk for D&C Orange #17 was one in 19 billion, which FDA described as de minimis.10 Using January 2022 data from Oxford’s Global Change Data Lab (https://ourworldindata.org/grapher/united-states-rates-of-covid-19-deaths-by-vaccination-status), the risk of death for a boosted individual was about 0.3 per 100,000 per week. Using a 95% reduction to approximate the effectiveness of a well-fitted N95 respirator, this equals roughly a 7.5 × 10-6 per year fatality risk. It’s hard to extrapolate this mid-pandemic annual risk to a lifetime risk, but it is clearly far higher than 1/million/lifetime, so Allen is favoring a quite permissive definition of “not much else in life as low as that.”11 To be more precise, the language from the “Benzene” case referring to 10-9 used the example of “taking a drink of chlorinated water.” So it is possible that upon converting this one-time tiny probability to a lifetime one (say, by multiplying by 8 drinks/day and 25,500 days per 70 years), this de minimis pronouncement actually represented a lifetime risk of 2 × 10-4—although this would be suspiciously close to the other risk value (10-3) that Court used in the same sentence as unacceptably high. It’s probably more likely that the Court meant a 10-9 lifetime risk, in apposition to a 10-3 lifetime risk, and just explained the former example poorly.12 This background rate is roughly 2 × 10-4/yr in the U.S. and E.U., so 5% of that annual risk, converted to a 70-year lifetime, would imply a rather high estimate of RD, at 7 × 10-4.13 As Richard Wilson wrote in Citation1988 (supporting a value of 7 × 10-5 as de minimis because it is about 1/10th of the variability in the natural background exposure to ionizing radiation), “I know of no one in the world who alters, or even chooses, his place of residence or his lifestyle to keep his natural radiation dose level low.”14 A related approach was discussed by Hunter and Fewtrell (Citation2001), who suggested that society could look at all cases of a particular disease (they used gastroenteritis as an example), deeming as de minimis any exposure that contributed to less than some percentage (say, 5%) of all cases.15 Lundgren and Stefansson make two other unusual arguments that we disagree with. First, they say that because “one person’s sure death cannot be de minimis,” the entire concept is flawed. We respond that RD is a probability for all, not a certainty for any one. Second, they say that if the world population was 1020, a risk of 10-12 might not seem so negligible. We agree, but point out that the actual world population is 8 × 109, with obvious implications for RD.16 The claim that the probability of a given harm could even have its own “disutility function” is controversial. Some observers (Pratt and Zeckhauser Citation1987) claim that this is nonsensical—that only the outcome (in this article, death) can have disutility, but the probability of the outcome cannot. By this view, a 1-in-X chance of harm has exactly 1/Xth the disutility of the harm itself, for all X; different people can have different views about (different willingnesses to pay for) the harm, but not about the probability (see EPA Citation2011, p. 6: “it seems unreasonable… that an individual would value a second risk reduction of Δp much less than an initial reduction of Δp”). This view, of course, would not allow even for the very notion of de minimis risk (a very small probability of a given harm is just a very small fraction of whatever the disutility of the bad outcome is), or of intolerable risk (Shrader-Frechette Citation1985). It also reflects an expected-utility view of human perception, a view that has been waning for nearly a century (Allais Citation1953) and that continues to be supplanted by richer depictions such as regret theory (Bell Citation1982) and prospect theory (Thaler Citation1980; Tversky and Kahneman Citation1992; Booij and van de Kuilen Citation2009).17 One similar invocation of citizen preferences is much older than Byrd and Lave’s article. According to Hey et al. (Citation2010), the Comte de Buffon argued in 1777, as an attempt to use RD to “resolve” the “St Petersburg Paradox,” that a rational person would offer no more than $13 to play this infinite-expected-value game. Buffon argued that since a 56-year-old man “ignores the possibility of dying in the next 24 hours,” which had a probability of 1/10,189 according to mortality tables of the time, events with less than 1/10,000 probability could be ignored.18 The upper end of the Supreme Court’s pronouncement in the “Benzene” case is 10-3 per lifetime; although there is very little case law suggesting that OSHA has an absolute duty to regulate risks above 1/1000, by leaving it to OSHA to determine where below 1/1000 the boundary between “significant” and “insignificant” risk must fall, the Court may have implied that its upper benchmark for risk is prima facie “intolerable.”19 For example, the OSHA PEL for trichloroethylene (TCE) is 100 ppm. EPA’s inhalation unit risk factor for TCE is 2.3 × 10-5 per (part per billion).20 Since 1996, U.S. federal regulatory agencies must separately analyze the economic effects of their rules on small businesses, and three major agencies (EPA, OSHA, and the Consumer Financial Protection Bureau) must invite a panel of 15 small business representatives to jointly develop a report recommending special accommodations for this constituency. This requirement gives “intolerable cost” to one subgroup a favored (early) place in the regulatory development process, and there is no parallel consideration extended to those who bear intolerable risk (perhaps caused by the harm-promoting exemptions given to small business!); see Finkel Citation2011, also Bromberg and Finkel Citation2023, for a proposal in this regard.21 A reviewer helpfully pointed out that some subjects may not see a lawnmower as at all useful in their life, while others might regard a power mower as necessary and a push mower as an unacceptable though safer alternative. See Section 4.7 (“Limitations”).22 Another important implication of the way we designed this scenario is that all of the data herein should be interpreted as pertaining to a single narrow matter like the costs and benefits of one particular product, hazard, or exposure. We are not seeking estimates of “de minimis cumulative risk from all air pollutants considered together,” or “what aggregate risk from all EPA-regulated substances is intolerable?”, or “how much should a citizen never be expected to pay for all public policies combined?” Future research could certainly define the “four corners” in more expansive ways.23 We asked each subject to provide an alias last name for themselves, just to personalize the script (while keeping their real last name hidden). So if someone said their last name was “Johnson,” and indicated they were female, a photo of a doctor talking to a woman would appear on-screen, and the script would start with “I’m so very sorry, Mrs. Johnson, to have to tell you this awful news, but…”24 Specifically, we told subjects that “if you name a very large probability (that is, 1 in ‘extremely small number’), you are in effect saying that to gain the moderate benefits of this consumer product you are willing to consider almost any probability of harm as tolerable. If you name a very small probability (1 in ‘extremely large number’), you are in effect saying that almost any probability of harm is too intolerable to justify the benefits of this consumer product, and you are willing to give it up for yourself and others (e.g., a ban).”25 Similarly, a few subjects used “something positive that’s never happened to them or anyone they know,” like getting the grand prize in a lottery, to estimate D by analogy.26 We conducted the survey very early in the U.S. experience of Covid-19, and a few subjects cited the Covid death rate of 2.3% (although this was at the time the case fatality rate, not a risk) as helpful to their answer.27 Not every respondent imagined mortality in the numerator; one subject chose 1/35 as intolerable because of the probability of “being called on in class when you don’t know the answer.”28 As this article was in final preparation post-review, an interesting controversy began to influence the future of regulatory cost-benefit analysis. The White House Office of Information and Regulatory Affairs proposed sweeping revisions to Circular A-4, the guidance governing CBA review in the federal system, and OIRA’s new-found enthusiasm for agencies to apply “distributional weights” to costs affecting poor citizens versus rich ones dominated the comments received (Xie et al. Citation2023). Some commenters (Sullivan Citation2023) argued that these weights are inappropriate and policy-laden, despite OIRA’s clear (and we believe, correct) argument in the revisions that agencies have always been applying weights, merely implicit and equal ones. But others (see, e.g., Adler Citation2023; Finkel Citation2023) explicitly argued that such weights are the only ways to correct the long-standing error in CBA that fails to transform units of dollar cost into units of welfare decrement, as the welfare toll of a given dollar cost is clearly larger for a poor person than a rich one.29 Situs inversus is a benign genetic condition in which all the internal organs in the chest and abdomen develop in a mirror-image (left to right) position to the “normal” arrangement.Additional informationFundingU.S. National Science Foundation (Decision, Risk, and Management Sciences Program), under Grant # 1629287.
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最后,经验得出的结论是,这些风险(和成本!)的规模太小,无关紧要,而那些太大,让人难以忍受
长期以来,学者、决策者和专家们一直在用词语和数字来区分那些太小而无关紧要的健康/安全风险(各种各样的说法,“微不足道”、“极小”或“微不足道”),或大到令人厌恶的风险(“不可接受”、“无法忍受”等)。但是,对于这些重要的概率有多大或有多小,还没有达成任何共识,更糟糕的是,没有人认真尝试通过外行人自己精心引出的偏好来探索这些概念。也许更令人担忧的是,占主导地位的范例——成本效益分析(CBA)——要求在(货币化的)风险与控制风险的成本之间取得平衡,但最小成本和不可承受成本的平行概念从未被正式考虑过。由于这些失误,所有考虑在如何承担风险和成本的分配中公平或公正的企图都是荒谬的,尽管声称相反。这篇文章报道了一对涉及1350个外行的启发。在一次启发中,一组仔细的背景和背景解释,以及一系列有条理的问题,探讨了每个受试者在哪些方面认为(来自非自愿接触的)终身超额死亡风险会变得“小到你不会花一点时间去想它”,在哪些方面会变得如此之大,以至于“作为一个道德问题,你会强烈反对不得不面对它”。通过一个单独的样本,我们就政府以降低风险的名义施加的监管成本提出了类似的问题。尽管在回应中存在显著的个体差异,但这四个科学政策价值“门柱”的中心趋势如下:(1)最小风险-一生中过早死亡的额外机会为77万分之一;(2) 570的不可容忍风险- 1机会;(3)最低费用-每年25美元;(4)难以忍受的成本——每年775美元。这些结果首次提供了一个原则性和基于证据的起点,可以进一步细化在制定政策时可以/应该忽略个人的哪些风险或成本,以及哪些必须主导政策,而不管从简单的角度来看,“货币化的生命拯救”和总美元成本如何相互比较。考虑到风险和成本如何给公民带来负担的这些基本门槛,我们为CBA如何改变以及环境/健康/安全政策如何改进提供了一些建议。无论是那些只减少分散的、微不足道的小风险而造成无法忍受的成本的干预,还是那些为了避免微不足道的、明显可管理的成本而使无法忍受的风险持续存在的(充分的)干预,都是低效的、不公正的,因此是不道德的。关键字:风险评估偏好成本效益分析最小风险环境公平感谢美国国家科学基金会(决策、风险和管理科学项目)提供的资金支持,授权号1629287。我们感谢Marcus Mayorga为调查编写的计算机程序,以及密歇根大学公共卫生学院的一小群同事和学生,他们作为焦点小组帮助完善和缩短了风险实验。我们特别感谢两位匿名评论者的有益评论。两项心理测量调查均获得决策科学研究所机构审查委员会(IRB00011706)的豁免批准。成本实验于2019年12月2日获批,概率实验于2020年2月26日获批。IRB的结论是,调查问题对受试者构成的风险最小,并且所有信息都已获得,因此无法轻易确定人类受试者的身份,直接或通过与受试者相关的标识符确定。两位作者共同开发、测试和改进了心理测量工具,并分析了收集到的数据。AMF写了这篇文章的初稿,BBJ对此进行了评论。作者报告无利益竞争需要申报。数据可用性声明我们所有NSF项目研究的数据和仪器,包括这里报告的,都存档在Johnson, Branden和Finkel, Adam。估计环境、公共卫生和安全条例的净效益。密歇根大学校际政治与社会研究联盟[j], 2018-07-30。61年https://doi.org/10.3886/E1756 v1。注1“De minimis”在拉丁语中是“关于琐事”的意思,如著名的格言“法律与琐事无关”(De minimis non curat lex)。 其次,他们说,如果世界人口是1020,10-12的风险可能看起来不是那么微不足道。我们同意,但指出实际世界人口是8 × 109,这对RD.16有明显的影响。声称给定伤害的概率甚至可能有其自己的“负效用函数”是有争议的。一些观察者(Pratt和Zeckhauser Citation1987)声称这是荒谬的——只有结果(在这篇文章中是死亡)会有负效用,但结果的概率不会。根据这个观点,1/X的伤害概率是伤害本身负效用的1/X,对于所有X;不同的人可能对危害有不同的看法(不同的支付意愿),但对可能性却没有不同的看法(见EPA citation ation2011,第6页:“似乎不合理……一个人对第二次风险降低Δp的重视远远低于对第一次风险降低Δp的重视”)。当然,这种观点甚至不允许最小风险的概念(给定伤害的非常小的概率只是坏结果的负效用的非常小的一部分),或者不可容忍的风险(Shrader-Frechette Citation1985)。它还反映了人类感知的预期效用观,这种观点已经衰落了近一个世纪(Allais Citation1953),并继续被更丰富的描述所取代,如后悔理论(Bell Citation1982)和前景理论(Thaler Citation1980;Tversky and Kahneman citation; 1992;[j] and van de Kuilen citation . 2009).17一个类似的公民偏好调用比伯德和莱夫的文章早得多。根据Hey等人(Citation2010)的说法,布冯伯爵在1777年提出,为了尝试使用RD来“解决”“圣彼得堡悖论”,一个理性的人不会提供超过13美元来玩这个无限预期价值的游戏。布冯认为,由于56岁的人“忽略了未来24小时内死亡的可能性”,根据当时的死亡率表,未来24小时死亡的概率为1/10,189,因此,概率小于1/10,000的事件可以被忽略在“苯”案中,最高法院判决的上限是10-3人一生;虽然很少有判例法表明OSHA有绝对责任监管1/1000以上的风险,但通过让OSHA决定1/1000以下“重大”和“微不足道”风险之间的界限必须落在哪里,法院可能暗示其风险的上限基准是初步的“不可容忍的”。“19例如,三氯乙烯(TCE)的OSHA PEL为100 ppm。EPA对TCE的吸入单位风险系数为2.3 × 10-5 /(十亿分之一)自1996年以来,美国联邦监管机构必须分别分析其规定对小企业的经济影响,三个主要机构(EPA、OSHA和消费者金融保护局)必须邀请一个由15名小企业代表组成的小组,共同编写一份报告,建议为这一群体提供特别的便利。这一要求将“不可忍受的成本”给予了一个次级群体,使其在监管发展过程中处于有利的(早期)位置,而对那些承担不可忍受风险的人(可能是由于给予小企业的促进伤害的豁免造成的!)参见Finkel Citation2011,以及Bromberg和Finkel Citation2023,关于这方面的建议一位评论者很有帮助地指出,一些受试者可能认为割草机在他们的生活中根本没有用,而另一些人可能认为电动割草机是必要的,而推式割草机是一种不可接受的替代品,尽管更安全。参见章节4.7(“限制”)我们设计这个场景的方式的另一个重要含义是,这里的所有数据都应该被解释为与一个特定产品、危害或暴露的成本和收益有关。我们不是在寻求“综合考虑所有空气污染物的最小累积风险”的估计,或者“所有epa管制物质的总风险是什么?”或者“一个公民永远不应该为所有公共政策支付多少钱?”未来的研究当然可以以更广泛的方式定义“四个角”我们要求每个受试者为自己提供一个别名姓氏,只是为了使脚本个性化(同时隐藏他们的真实姓氏)。所以如果有人说他们姓"约翰逊"并表示他们女,一个医生与一个女人的照片会出现在屏幕上,和脚本将开始“约翰逊太太,非常抱歉要告诉你这个可怕的消息,但是……”24日具体地说,我们告诉对象,“如果你的名字一个非常大的概率(即1在极小的数量),你实际上是在说,这个消费产品的温和的好处你愿意考虑任何伤害的概率可以忍受的。
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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来源期刊
Human and Ecological Risk Assessment
Human and Ecological Risk Assessment 环境科学-环境科学
CiteScore
9.60
自引率
2.30%
发文量
68
审稿时长
2 months
期刊介绍: Human and Ecological Risk Assessment provides a resource for professionals researching and assessing environmental hazards to both humans and ecological systems. The editors expect papers published to be original, of sound science, purposeful for risk analysis (assessment, communication, management) and related areas, well written (in English), and a contribution to the scientific literature. The journal''s emphasis is on publication of papers that contribute to improvements in human and ecological health. The journal is an international, fully peer-reviewed publication that publishes eight issues annually. The journal''s scope includes scientific and technical information and critical analysis in the following areas: -Quantitative Risk Assessment- Comparative Risk Assessment- Integrated Human & Ecological Risk Assessment- Risk Assessment Applications to Human & Ecosystems Health- Exposure Assessment- Environmental Fate Assessment- Multi-Media Assessment- Hazard Assessment- Environmental Epidemiology- Statistical Models and Methods- Methods Development/Improvement- Toxicokinetics Modeling- Animal to Human Extrapolation- Risk Perception/Communication- Risk Management- Regulatory Issues
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