chapter 3 tragic choices. - despite our seemingly frequent attempts to build a no-risk-society,...
TRANSCRIPT
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CHAPTER 3
TRAGIC CHOICES
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- Despite our seemingly frequent attempts to build a no-risk-society, there is no such thing
- Scientific progress has both:(a) created technical hazards(b) uncovered these hazards
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Conversely, perceptions of risk and culturally dictated response to risk, are ancient parts of the human psych… flood/drought/etc. as “blessing”
or ”punishment” from the Gods… predicting / “controlling” physical or human environments… “survivability” of nuclear war
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- The challenge is to accept that risks and hazards are a part of our daily lives
- The decision making processes related to risks and hazards is often little more than a “balancing act” of goals and responsibilities
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How much is a life worth?
In order to carry out the larger discussion of risk/hazard/etc., basic information on the risk/hazard (so far as it is understood) is necessary… what are benefits/positive attributes as well as risks… what are spatial and temporal attributes of benefits/risks… what are political/economic/social costs
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Information categories necessary for making risk decisions
1. Risk of an option must be articulated2. Benefits of an option must be stated3. Alternative options and associated
risks/benefits must be stated4. The level of certainty and uncertainty
associated with risks/benefits must be stated
5. How will these technical assessments be conveyed to decision makers
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Analytical Tools: Cost-Benefit Analysis
- A long tradition as a chief tool of decision making--- involved comparing estimated short-term and long-term costs and benefits of alternatives
- Used properly, a reasonable guide for estimating future behavior
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Analytical Tools: Cost-Benefit Analysis, cont
Some very controversial aspects:(1) What discount rate(s) should we
assign (2) Cannot be applied democratically(3) Assumes “full-cost information”(4) Pulling a price on environmental
goods is at best debatable(5) Rules out any possibility of
catastrophic events
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Analytical Tools: Cost-Benefit Analysis, cont
A fundamental construct of C-B is that there exists anOptimal level of risk/hazard
Is there such a thing?
Policy makers have sought an alternative methodology
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Risk-BenefitComparing risk with anticipated
benefits--- greater risk accepted in anticipation of greater benefit--- not always quantitatively driven
[“balance sheet” methodology]--- still not perfect – weighs a current
perspective to risk and benefit; issues of equality; etc
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Revealed Preferences
Starr, Science magazine, 1969Based on the idea that study of
historical data on risk-benefit comparison will illustrate “patterns” of acceptability across a range of technologies
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Revealed Preferences, cont
From study of cost-benefits Starr developed acceptability laws:
1. Risks are acceptable from a technology if they are proportional to the 3rd power of the benefit
2. The public will tolerate risks from voluntary activities (order of 1000x) over that of involuntary risks
3. Risk acceptability is inversely related to the population at risk
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Revealed Preferences Limitations
Cutter provides two (I think viewing as three makes more sense):
1. Risk is defined as human fatalities… human health/welfare; environmental degradation; etc, are not addressed
2. Ignores delay between technology introduction and impact
3. Fails to examine equity
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Expressed Preferences
Assessment of public views / attitudes on risk… most commonly through direct
opinion polling… timing of polling and nature of
risk directly affects public sentiment… realistically, very limited use
potential
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Risk Assessment
Uses incidence data and modeling techniques to develop hypothesizes and conclusions about the level of harm from human activity
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Risk Assessment, contFour “stages” to risk assessment:Stage 1. Risk Assessment
identification or determination of an activity/chemical link to health effect- Looking at chemicals, there are a myriad of possible impacting chemicals
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A Legal Question
Exposure to a pesticide in year Y gives rise to 10 additional cases of cancer in a population of 100,000 in the year Y+20…
Who should be allowed to sue for damages, and for how much?
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Risk Assessment, cont
Chemicals, cont- acids- hematoxins- neurotoxins - carcinogens - mutagens- teratogens
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Risk Assessment, contChemicals, cont
- additionally, research indicates that long-term exposure to
certain compounds will effect:(1) endocrine system(2) immune system(3) nervous system- hormonal copycats
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InterestingThe Delaney Amendments to the Food,
Drug and Cosmetics Act, forbidding the sale of any food additive containing a carcinogen in however small a quantity, had to be partially repealed when science advanced to the point of detecting such minute levels of carcinogens that clearly harmless substances were being outlawed
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Risk Assessment, contStage 2. Examination of the
relationship between magnitude of exposure and the probability of occurrence of adverse health effects as identified in Stage 1… this is toxicology… we are seeking to quantify
dose-response
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Risk Assessment, contDose-response, cont- Whether or not a substance is
dangerous is a result of:(1) Size of dose over a period of time(2) frequency of exposure(3) who is exposed(4) how well the body’s detoxification
system is operating
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Risk Assessment, contInteresting:
Legally a poison is a chemical of LD50 – a lethal dose of 50 milligrams or less per kilogram of body weight
[LD50 is the amount of a chemical received in one dose that kills 50% of animals in a test population within a 14 day period]
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Risk Assessment, contStage 3. Calculation of range and extent
of exposure- examined include:
(1) source and amounts of exposure
(2) amounts absorbed, distributed and stored in the body
(3) amount excreted(4) effects on different parts of
the body
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Risk Assessment, cont
Researchers distinguish between: acute exposure chronic exposuresub-chronic exposure
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Risk Assessment, cont
Stage 4. Risk characterization –description of the nature and magnitude of human risk as well as some statement of uncertainty for the estimate
* As a methodology, risk assessment has its own areas of disagreement *
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Risks to Human Health- Usually based on involuntary
exposure - Most common ways of
examining this risk:(1) disease clusters – based on
identification of abnormal patterns of disease
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Most Common Ways of Examining Risk, cont
Clusters, cont- considered least valuable identification methodology- least scientific- rarely conclusive- is observed a true aberration?
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Most Common Ways of Examining Risk, cont
Clusters, cont- valuable as an indicator of the need for more intensive
examination- relatively inexpensive
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Most Common Ways of Examining Risk, cont
(2) Epidemiological data – studies of populations of humans exposed to compounds - general sense a study of toxicity and hazard by answering the question of why some in a population are susceptible to a hazard
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Most Common Ways of Examining Risk, cont
Epidemiological, cont- a field study methodology attempting to show a correlation between environmental contamination and human disease- a statistical study of an exposed
population vs a control population
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Most Common Ways of Examining Risk, cont
Epidemiological, cont- conclusive evidence difficult to attain:
(a) multiple chemical sensitivity (MCS)
(b) delay between exposure and on-set
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Most Common Ways of Examining Risk, cont
(3) Animal bioassay data(laboratory investigations)- usually on test animals- chronicles body parts affected
and process of the harming action - basis for toxicological studies
--- premise that animal studies can be extrapolated to humans
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Most Common Ways of Examining Risk, cont
Animal bioassay data, cont- question of extrapolation- question of validity of extrapolating large dose animal
studies to smaller-dose long term exposure to humans
- most common investigative methodology for acute toxicity
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Most Common Ways of Examining Risk, cont
Animal bioassay data, cont- lab experimentation seeks to
establish dose-response curves
--- controlled experiments--- cohort group
experiments
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Most Common Ways of Examining Risk, cont
Animal bioassay data, cont- “Fairly high” doses are tested
to:(1) reduce lab animals needed(2) shorten time needed to document a response(3) lower cost
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Most Common Ways of Examining Risk, cont
Animal bioassay data, cont- Problems lab experimentation:
(1) extrapolation validity – doselinear dose-response modelthreshold dose-response
model(2) extrapolation validity – species(3) long and expensive process
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Most Common Ways of Examining Risk, cont
(4) Experimental studies of mutagenicor carcinogenic property- comparison of molecular structure to isolate chemical
structures that might identify carcinogens
- based on premise that known carcinogens might share a common chemical structure
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Interesting
Animal bioassayChance rat will No. of sodas/daydevelop tumor human must drink
for same dose1 in 50,000 11 in 5000 101 in 500 1001 in 50 10001 in 5 10000
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Environmental Risks
- Result from a number of sources: technological systems failure; environmental processes; human behavior patterns
- complex because both human risk and environmental impacts are taken into account
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Environmental Risk Techniques
Fall into three broad categories (see Table 2-2):(1) monitoring and surveillance(2) modeling(3) screening and testing for
exposure/response
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Environmental Surveillance
The (1) above- Observation of spatial and temporal
patterns of environmental indicators and their variations
- Source of baseline data for comparative trends and geographic analysis
- Source of data for annual international reporting
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Interesting Applied Example
Sept 1998 Ft. Campbell RAB were told of two methodologies under study for modeling contaminant flow through karst(1) Present-Future(2) Mass-Transport
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CausalityStage 2 above- Delineation of chain of events,
pathways and processes connecting cause (or source) of a problem to its effects--- environmental modeling is often used
… forms: schematic; mathematical; interactive computer
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Simple illustration of this causality
As the average grade of ore declines from 8% or more to 3%, there is a barely perceptible increase in the amount of mine waste generated per ton of final metal. Below 3% wastes per ton increase dramatically. Eventually the cost of dealing with the wastes will exceed the value of the metal produced.
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Exposure Response
Stage 3 above- Seeks to determine the relative characteristics of the impact of exposure (dose) to the type of environmental impact (effect)- As seen before, illustrated by use of graph curves and useful for prediction of effects of very high or very low exposure
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Exposure Response, cont
Text tells us that two main types of dose-response relationships are worth noting (p 43):(1) threshold relationships(2) zero threshold
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Who’s Right: The Experts or the Public?
Expert vs Public Views(1) social changes(2) increasing reliance on technology(3) the public’s increasing distrust of institutions(4) the institutionalization of
scientific conflict
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