FOUNDATIONS OF THE REGULATORY STATE

Prof. Jeffrey Gordon

Spring Semester, 1999

  

Final Examination -- Spring 1999 
Time Allowed -- Four Hours  

This examination consists of 5 pages, including this one. Please check now to make sure you have all the pages.

 

 

Instructions:

This is an open-book examination. The examination consists of three questions. The weight assigned each question corresponds to the time suggested for each. The suggested times are purely advisory, however. You can allocate your time any way you choose. Please start each question in a separate booklet, following the color scheme as indicated. Write on one side of the page only. Please mark the front of each booklet to indicate which question is answered therein.

 

Organization and conciseness count, so plan your answer before you write.

If for any question you think additional facts would be relevant to the issues discussed in your answer, state what facts you need and how they would affect your analysis.

 

 

Question I

[One and one-quarter hour]

 

The Patients’ Bill of Rights Act of 1999, recently introduced in the U.S. Senate, contains a provision, in full text below, that purports to prohibit certain discrimination on the basis of "predictive genetic information." Pick a role as a lawyer for either (i) the US Chamber of Commerce; (ii) NYPIRG (New York Public Interest Research Group); or (iii) a Senator. Your client wants you to analyze the legislation, including whether it is effective for its purpose, its impact on health insurance markets, its possible implications for the provision of health care, and whether it is desirable public policy taking into account your client’s interests as you understand them. Your analysis could include suggestions as to how the legislation should be modified in light of your analysis.

 

SEC. 714. (a) PROHIBITING PREMIUM DISCRIMINATION AGAINST GROUPS ON THE BASIS OF PREDICTIVE GENETIC INFORMATION. A group health plan, or a health insurance issuer offering group health insurance coverage in connection with a group health plan, shall not adjust premium or contribution amounts for a group on the basis of predictive genetic information concerning an individual in the group or a family member of the individual (including information about a request for or receipt of genetic services).

(b) LIMITATION ON COLLECTION OF PREDICTIVE GENETIC INFORMATION_ Section 702 of the Employee Retirement Income Security Act of 1974 (29 U.S.C. 1182) is amended by adding at the end the following:

`(c) COLLECTION OF PREDICTIVE GENETIC INFORMATION_

`(1) LIMITATION ON REQUESTING OR REQUIRING PREDICTIVE GENETIC INFORMATION_

Except as provided in paragraph (2), a group health plan, or a health insurance issuer offering health insurance coverage in connection with a group health plan, shall not request or require predictive genetic information concerning an individual or a family member of the individual (including information about a request for or receipt of genetic services).

`(2) INFORMATION NEEDED FOR DIAGNOSIS, TREATMENT, OR PAYMENT_

`(A) IN GENERAL_ Notwithstanding paragraph (1), a group health plan or health insurance issuer that provides health care items and services to an individual or dependent may request (but may not require) that such individual or dependent disclose, or authorize the collection or disclosure of, predictive genetic information for purposes of diagnosis, treatment, or payment relating to the provision of health care items and services to such individual or dependent.

(b) AMENDMENT RELATING TO THE INDIVIDUAL MARKET_ The Public Health Service Act (42 U.S.C. 300gg_11 et seq.) (relating to other requirements), as amended ... is amended ... by adding at the end the following:

`SEC. 2753. PROHIBITION OF HEALTH DISCRIMINATION ON THE BASIS OF

PREDICTIVE GENETIC INFORMATION.

`(a) PROHIBITION ON PREDICTIVE GENETIC INFORMATION AS A CONDITION OF ELIGIBILITY_ A health insurance issuer offering health insurance coverage in the individual market may not use predictive genetic information as a condition of eligibility of an individual to enroll in individual health insurance coverage (including information about a request for or receipt of genetic services).

`(b) PROHIBITION ON PREDICTIVE GENETIC INFORMATION IN SETTING PREMIUM RATES_ A health insurance issuer offering health insurance coverage in the individual market shall not adjust premium rates for individuals on the basis of predictive genetic information concerning such an enrollee or a family member of the enrollee (including

information about a request for or receipt of genetic services).

`(c) COLLECTION OF PREDICTIVE GENETIC INFORMATION_

[The proposed language tracks the proposed amendment of section 702 of ERISA described above.]

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Question II

[One and one quarter hour]

Section 313 of the Emergency Planning and Community Right-to-Know Act of 1986 ("EPRCRA") requires large manufacturing facilities to file annual reports on routine releases and transfers of several hundred toxic chemicals found in wastes from ordinary business operations. This has led, for each firm, to the production of company-specific "Toxics Release Inventory" ("TRI"). The reports are collected by the states and the EPA and disseminated through a variety of means. The EPA must make this information public in a computerized database.

Section 313 provides in relevant part:

 

(g) Form

(1) Information required

... the Administrator shall publish a uniform toxic chemical release form for facilities covered by this section.... Such form shall__

(A) provide for the name and location of, and principal business activities at, the facility;

(B) include an appropriate certification, signed by a senior official with management responsibility for the person or persons completing the report, regarding the accuracy and completeness of the report; and

(C) provide for submission of each of the following items of information for each listed toxic chemical known to be present at the facility:

(i) Whether the toxic chemical at the facility is manufactured, processed, or otherwise used, and the general category or categories of use of the chemical.

(ii) An estimate of the maximum amounts (in ranges) of the toxic chemical present at the facility at any time during the preceding calendar year.

(iii) For each wastestream, the waste treatment or disposal methods employed, and an estimate of the treatment efficiency typically achieved by such methods for that wastestream.

(iv) The annual quantity of the toxic chemical entering each environmental medium.

(2) Use of available data

In order to provide the information required under this section, the owner or operator of a facility may use readily available data (including monitoring data) collected pursuant to other provisions of law, or, where such data are not readily available, reasonable estimates of the amounts involved. Nothing in this section requires the monitoring or measurement of the quantities, concentration, or frequency of any toxic chemical released into the environment beyond that monitoring and measurement required under other provisions of law or regulation. In order to assure consistency, the Administrator shall require that data be expressed in common units.

 

(h) Use of release form

The release forms required under this section are intended to provide information to the Federal, State, and local governments and the public, including citizens of communities surrounding covered facilities. The release form shall be available ... to inform persons about releases of toxic chemicals to the environment; to assist governmental agencies, researchers, and other persons in the conduct of research and data gathering; to aid in the development of appropriate regulations, guidelines, and standards; and for other similar purposes.

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A recent commentator writes: "Making the TRI data publicly available to any citizen has been described by an EPA Administrator as ‘among the most important weapons in efforts to combat pollution.’ The present Clinton EPA administration regards the TRI as ‘among our most potent environmental weapons.’" This is buttressed by evidence that over the 1988-94 period, members of the Chemical Manufacturers Association voluntarily reduced their emission of toxics by 52% while sales volume was up 10 percent.

Why should a [voluntary] disclosure program like TRI have been so effective in reducing the release of toxics? Analyze the possible mechanisms of its success. Should disclosure lead to mandatory emission controls? What are the implications of the evidence about TRI for OSHA’s Hazard Communications Standard?

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Question III

[One and one-quarter hour]

Although the matter is not free from doubt, most scientists believe that the earth’s average daily temperature of has increased over the past 100 years and will continue to increase because of the "global warming" effects of the emission of "greenhouse gases" such as CO2 through the burning of fossil fuels. This could lead to significant climate changes that could radically change the distribution of farmable land and raise the level of the ocean.

At a conference held December 1997 in Kyoto, Japan, the US and other developed countries agreed to a set of binding emissions reduction targets of approximately 7% below 1990 levels, beginning in 2008.

Among the other features of the Kyoto Protocol are these:

(1) The parties agreed to the outlines of a plan of emissions permits trading among nations with emissions targets.

(2) Countries with emissions targets may also get credit towards their targets via the Clean Development Mechanism" ("CDM") under which developed countries can enter into cooperative projects to reduce emissions in developing countries such as the construction of environmentally sound power plants or manufacturing facilities.

(3) Countries with emissions targets may also get credit by creating greenhouse gas "sinks"; e.g., reforestration that will absorb greenhouse gases.

(4) Certified emission reductions achieved starting in 2000 will count toward compliance with the first budget period.

(5) To enter into force, the Protocal must be ratified by at least 55 countries, accounting for at least 55% of the total 1990 carbon dioxide emissions of developed countries.

 

You are a senior staffer to Sen. Prolix, a member of the Foreign Relations Committee that will shortly hold hearings on whether the US should ratify the Kyoto Protocol. She wants you to prepare a memo that will analyze each of these features of the Kyoto Protocol, that will provide her with a set of questions to ask about implementation plans (and an explanation as to what turns on the answers), and your view about the impact of the Protocol on relations between the developed and developing world

 

 

SAMPLE ANSWERS

Question I

Exam #701

Role: U.S. Senator

The gist of the plan is quite simple - it prevents insurers from using genetic information to raise premiums or deny eligibility in both the group and individual insurance market. While I will analyze the two markets separately, there are some problems common to both which I will discuss here.

1) Enforcement - there is an important loophole in both plans which allows the provider to request genetic information for the purposes of diagnoses etc. Given the extreme lack of protection for this kind of information (patient confidentiality has become something of a farce in the modern era) this could make for quite an enforcement problem. If insurers did use such information illegally, it would be very difficult for the patient to find out and, even if they did, to afford the necessary legal enforcement.

2) Regulation under uncertainty - nobody is quite sure at this point what exactly genetic science will eventually allow us to do entering with legislation at this point may well cause problems in that we may prevent the use of information which may well become absolutely essential to the practice of medicine. Of course the legislation can always be changed, but given the workload of Congress and the difficulties of garnering its attention the whole plan my be somewhat premature.

The Group Plan

The use of genetic information should definitely be banned in the area and the proposed legislation is probably an excellent idea. The information in question here is extremely relevant to an insurer’s potential adverse selection problem - the problem of taking on a disproportionate amount of bad risks because of information asymmetries. There are two ways around this problem - mandatory pooling and screening. Those already in the group health insurance market are engaged in mandatory pooling, thus although genetic information promises to be an unparalleled screening mechanism here, in this market it could only be abused - used for the purposes of excluding bad risks and creating artificially beneficial risk pools. In summary, given the fact that group based health plans are already subject to mandatory pooling, thus mitigating the adverse selection problem, there is little justification of allowing insurers to screen as well.

An additional problem that would occur in the absence of such regulation in the group markets is that employers would have a tremendous incentive to screen their employees -- to eliminate bad risks before they joined the group plan and raised premiums for everyone -- this legislation prevents that, which is good. Thus, the effects of this legislation on the group market are essentially to protect the status quo -- to allow the mandatory pooling already functioning in these markets to continue functioning as the insurers primary weapon against adverse selection -- by preventing the use of genetic information the legislation protects potential employees from screening by potential employers as well.

Individual Market

The benefits here are far from clear. By definition, in the individual market the insurer is subject to severe adverse selection problems -- there is no mandatory pooling thus leaving the insurer with screening as the only possible option to defend themselves against adverse selection. Genetic screening, at this point, promises to be the most accurate and effective form of screening ever available, and making its use illegal would be a tremendous loss to the insurer. In the absence of effective screening, insurance rates in the individual market will continue to be prohibitively high -- especially given that the types of people who NEED individual insurance are often those who cannot get it through work -- the poor.

The attraction of the legislation is that an individual with an expensive genetic predisposition would have a fighting chance of getting insurance, but this benefit may be dubious and illusory — and using this type of legislation to attain it even more so.

By preventing screening, the legislation effectively forces insurers to charge very high rates to everyone in an inordinately large and impressive risk pool. Allowing genetic screening would create the possibility of tailoring risk pools more accurately, thus reducing the cost of individual health insurance for most and thereby increasing the number of insured. IF the government really wanted to protect those with genetic predispositions, it may be better to do so directly -- through some sort of risk adjustment or subsidy to insurers willing to take on such patients. This would increase the availability of insurance for both those with genetic predispositions and the general market.

The harsh reality is that genetic screening promises to be the most effective means by which insurance companies can set up well tailored risk pools in the individual market. One of the unfortunate side effects of this will be prohibitively high rates for those with costly genetic predispositions. But the solution to this problem is a direct subsidy for that particular pool, not general legislation which makes individual insurance an unaffordable dream for the general population (not eligible for insurance through the workplace). Whether as a senator I would want to support the plan depends on my various constituencies - do a have a disproportionately large % of employed in my state in a group health plans (definite support - at least for the group part of the legislation), or rather, a large % of unemployed/uninsured. Do I have a great deal of insurance industry/money within my State etc. These considerations aside - assuming I have an average state (whatever that means) I think the group plan is definitely worth supporting, while the individual plan less so - especially if we can somehow convince the legislature to take a more direct approach to protecting the poor with bad genetic predispositions.

Exam #715

MEMORANDUM

TO: New York Public Interest Research Group (NYPIRG)

From: Association Counsel

RE: PROHIBITION OF DISCRIMINATION ON THE BASIS OF "PREDICTIVE GENETIC INFORMATION"

The primary goal of Sec. 714 (for the group market) and Sec 2753 (for the individual market) of the newly proposed Patients’ Bill of Rights is to expand the coverage of private health insurance by allowing individuals with certain genetic dispositions that reflect a high possibility of contracting certain diseases to enroll and not be discriminated in private health insurance eligibility and premium. While the objective of the bill is praiseworthy, there exists several problematic concerns that arise from the start. However, the first question is, is the bill effective in seeking to accomplish its purpose.

The question seems to be a YES. For both group plans (say employer health insurance) and individual plans, the bill makes sure that predictive genetic information will not work to deny coverage to a possibly high-risk individual (say carrying a genetic disposition that is 10x more likely to get a certain disease, or even HIV+?) Or raise her premium. What makes the bill truly effective is its inclusion of the phrase "including information about a request for or receipt of genetic services." Normally, an insurer does not specifically have to look at every genetic testing result to discern who might be a high-risk person. Rather, they can INFER from the fact some people purposefully failed to take a certain requested test, or they took a special genetic diagnostic test, etc. This bill, however, forbids the insurers to even make this indirect distinction. Thus it completely assures that a person with "bad" genetic disposition will have a chance to sign for an insurance without being discriminated.

However, is this necessarily good for the health insurance market? There seems to be several problematic aspects. First, from the perspective of the insurers, the bill severely undermines their ability to perform UNDERWRITING, and properly discern the high-risk from the low-risk people. The bill (sec. 714(c)(1)) basically forbids any insurer to ask for predictive genetic information that might reveal the true risk factor of an individual unless the request is limited for aiding in actual treatment, diagnosis, etc. Two significant impacts this will have on health insurance market are adverse selection and cross-subsidy. Adverse selection will kick in as more "high -risk" people with certain predictive genetic information are accepted/not thrown out, resulting in higher use of medical services by these people, thus need for higher premium, and low-risk people dropping out as they feel the premium is too high. The process continues, and ultimately, the high-risk people end up paying premium equal to their risk ( actually, more than their actual risk due to LOADING FEE). In order to prevent adverse selection, one can either conduct SCREENING to find risk, or enforce mandatory insurance on everyone. What the bill denies is the first option of preventing adverse selection. Furthermore, the problem of cross-subsidy will be enlarged, as the low-risk, healthy people must now subsidize for more high-risk, as the insurer is disallowed to deny access to some of these people by law. This is in a way, a strong example of forced redistribution, (Epstein argument) that may be even morally questionable (like forced redistribution for food, housing, etc.) However, there is a distinction between normal case of a forced redistribution and the case of predictive genetic information. In the former, whether it be cross-subsidizing for poverty, illness, disability, etc., one might assume that the harm ensued because of individual’s laziness, stupidity, carelessness, lack of education, etc. In short, they attribute the responsibility of harm to the individual, at least to significant degree. (Thus for Epstein, this becomes problematic). However, in the case of genetic predisposition, there is NO individual action or will involved. Rather, it is strictly determined by genes, and by nature. Thus, in terms of moral force, the bill stands in a much more favorable light than some other forced cross-subsidy. But, there may be another side to this issue. Normally, high-risk people are also very poor (lack of proper diet, unsafe car, etc.) Thus, it makes some sense to cross-subsidize the poor. However, in this case, a "bad" predictive genetic information has no correlation with wealth. A high-risk person under this standard may as well be a millionaire, who can and SHOULD pay for his high-risk. Thus, the argument can go both ways.

One typical problem of insuring high-risked people, that of moral hazard, does not seem to be relevant here however. Because this deals with predictive genetic information, and since people usually do not have control over their genetic makeup, the bill should not cause people to be less careful, etc.

How will this affect the provision of health care? In many ways, this bill is not too drastic as it might seem. There have been other bills, for example, Kassebaum-Kennedy Act, (HIPPA), that allowed those with pre-existing conditions to enroll in health coverage. This bill is not as drastic, since predictive genetic information does not necessarily mean having a certain disease as of now. Thus, the effect on the low-risk people is less. For group plan that is operated by HMO under managed care, the plan may negatively affect the actual health care services by doctors, if capitation fee are used. Under the employer group insurance, the employees would supposedly go to a same set of providers, whom will be forced to deal with more high-risk people. Assuming high-risk people require more services and treatment, that may put pressure on their capitated fee, resulting in doctors giving less than adequate treatment to other less risky people in order to make up for the cost and perhaps still earn some of those HMO provided "bonuses." However, this effect is not as problematic as adverse selection or cross-subsidy.

Overall, the desirability of the plan depends on how many previously denied people in New York will gain access to the plan. If the number is small, inclusion of them might be a good thing ( considering the moral argument that these people have no control over their genes). However, if the number is too large, from the perspective of NY insurance community, this will cause too many negative side effects. One modification of the bill to improve its effect might be to separate the group and the individual plan, and prohibit discrimination on the basis of genetic information only under the group plan. The reason for this is as follows. Because the government subsidizes the employer insurance plan through tax deductions, employees have less incentive to drop out. (For some it’s even mandatory). Thus, the effect of possible adverse selection will be dampened under the group plan. For the individual market, one might find a person dropping out rather quickly if the premium rises even a little bit. Considering they are already paying significantly higher premium for personal insurance without the benefit of tax subsidy, it might be better to not penalize this group. 

 

Exam # 735

For the purposes of this essay I will represent the New York Public Interest Research Group (NYPIRG). Their interests, as I understand them, are to advocate health care policies that improve the extent and scope of health insurance for the average American.

A long-time concern of health care advocacy groups has been the freezing-out of the market of individuals with pre-existing illnesses or predispositions to certain illnesses. Authors such as Stone have argued, in the context of HIV positive individuals, that failure to insure such people essentially posses the burden on to public institutions and, in turn, taxpayers. Those who are ill thus receive care, but it is care provided for them on behalf of the government. (i.e. taxpayers)

Screening for genetic risks differs, of course, from the situation regarding HIV positive individuals in that the illness has not manifested itself (and may be latent for quite some time) and, in normative terms, because behavior is not a factor in terms of genetic predisposition as it is in terms of AIDS or Hepatitis (acknowledging of course that behavior is only one factor among many). The concern with genetic testing then is that insurance companies will use it as a means to segment risk pools; that is they will use the tests to select low-risk individuals rather than high-risk and, in so doing, increase premium prices for the high risk group, potentially pricing them out of the insurance market (just as redlining affects high-risk groups in the lending market).

I will now evaluate the program along two axes: (1) how well does it protect individuals from genetic screening; (2) how does it affect access to coverage in terms of the general population; that is, what are its full equilibrium effects.

Examining the legislative proposal two questions occur in regard to its effectiveness in assisting those with genetic pre-dispositions to disease.

(1) The plan applies to group health plans, and issuers offering coverage in connection with such plans. While providers to individuals are also covered, it is unclear if there are any gaps in applicability. While this will seemingly apply to most plans, it is by no means clear that it will apply to all. Universality is important not only because we want to protect the most individuals possible, but also because we do not want to place certain firms or plans at a competitive disadvantage. If a certain segment of the industry can still screen individuals than this will lower their costs while increasing costs to other insurers – if individuals can transfer plans without screening, increasing even more the costs to those remaining in a far from virtuous cycle.

Thus, without definition of the terms I would want to examine if any insurers are excluded. If they are an important amendment would be to universalize the coverage.

(2) With our focus on the concerns of patients another important aspect of the plan is the exception to (c)(1) contained in (c)(2)(A).

First, the scope of the exception "for purposes of diagnosis treatment or payment" is very broad; so broad as to threaten to swallow the rule. Concern as to the breadth of the exception is heightened by the following problem: although an insurer may request, but not require, information for the reasons cited above there is a strong possibility that the insurer will treat refusal to comply with a request as though it were equal to a negative test result. This could then lead to the very problem we are trying to avoid.

I would therefore clarify this language to ensure that refusal to comply with a request cannot lead to increased premiums, and I would tighten up the definition of the exceptions. For instance, "payment" seems incredibly broad and potentially all inclusive.

We want to ensure that the legislation allows people at-risk to get tested without fear of being priced out of the market, otherwise we would discourage testing and all the possibilities of early detection and treatment that come with it.

(2) The next broad area to address is how the legislative changes made here will affect coverage in the wider population. Any such question must begin with an emphasis on the central insurance tension in this area.

Broad pooling will cover more people but will also drive out those low-risk insurees: e.i. those who see the costs of the group rate being greater than the risks they face as individuals (especially give the "floor" provided by public institutions).

Narrow pooling, by more exactly correlating risk and premium eliminates low-risk flight but threatens to price high-risk groups out of the market.

Here, in the group market, the risk is that the prevention of genetic screening will cause entry of certain high-risk individuals that would otherwise be screened out of the group: this, in turn, will raise the "rate" for the group and lead to drop-outs amongst those at lowest risk.

While the plan clearly prevents direct rate-raising there exists the possibility that insurers will recoup their increased risk through higher "loading costs," which it is unclear that his plan covers or prevents.*

[* But note discussion about individuals; does the legislation prevent

I) Insurer from raising group A’s rates or does it also preclude

II) Insurer from raising all group rates to reflect the increased risk.

If (I) but not (II) then overall rates will rise to reflect increased risk to insurers and low-risk consumers of insurance will be priced out. If (I) and (II) then the discussion illustrates that increased costs to insurers will still be reflected through the system].

 

Second, if insurers cannot pass on costs through direct premium increases they may will seek to cut costs in other areas, as through increased use of managed care organizations. This increased emphasis on efficiency gains in this area could lead to problems of under-treatment or increased reliance on utilization reviews, which will drive up loading costs. In essence then the decision to make insurers accept greater unknown risk will result in increased costs which will then be reflected back through the system.

On the face of the legislation the private individual market is treated differently. Here an insurer may not use predictive genetic testing as a criteria for eligibility or for setting premium rates.

But the problem with this is that while insurers cannot say: "I am raising your premium X because you tested..." they can easily say: "I am raising the average cost of insurance to individuals to reflect my increased risk." This will create a perverse incentive of sorts, for those who have no genetic predisposition the increased average cost will potentially drive them out of the market, while for those with a genetic predisposition the average rate rise will still provide for insurance at below their expected risk. So in a way this is a perfect illustration of adverse selection as those most at risk will be given insurance at a rate below their proper pool (i.e. below what it would be if premiums were correlated to risk precisely).

Thus, the problem, as with any program that increases benefits and/or eligibility is that you will have concurrent cost increases throughout the system that may cause the rate of uninsured to increase.

Pooling may be enforced by either making it mandatory or by providing incentives to make it appealing enough for low-risk to join (i.e. employer-based health plans not taxed on income used for health benefits).

If implemented then the ripple effect of increased coverage for a high-risk group will have to be watched closely, and if there is an increase in the uninsured then incentives may have to be provided to maintain pooling.

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Exam #824

The purpose of the two provisions is the same: to stop layering of insurance pools by insurance companies. Senate does not want groups or individuals to be discriminated against due to their genetic makeup, so they designed two similar statutes see 714 and see 2753 to deal with discrimination. However, it seems that the Senate has failed to realize that the market effect will be different. I will try to explain to the Senators the market effect of both group and individual discrimination prohibitions.

The group prohibition of request or receipt of genetic services is a great idea. Some coverage is bought by groups you can assume to get uncorrelated risks, making insurance much more feasible. Also since it’s doubtful that the genetic makeup of one group is much different from genetic makeup of other group, you will get very little adverse relation among groups. Of course this only case if there is forced pooling within the group, so that low-risk won’t drop out. You can achieve this coercively by law or by providing tax break to make it stupid not to join pool even for low risk. Of course tax break may be regressively set up due to progressive tax % and fact that wealthier people buy more insurance since tolerate less risk. But let’s assume legislature sets up incentive in a way that is distributionally fair.

Since pools accumulate in way that has little difference in cost for each group, this avoids cherry-picking by insurance companies. More importantly, an employer won’t feel the need to screen employees for genetic makeup prior to hiring. In addition, this avoids the problem of lock-in from adverse genetic makeup, since otherwise no new company will hire somone once it knows of the threat . Low-risk individuals might feel unfair to have to cross-subsidize high risk individuals, but as long as we provide them with enough tax incentive they won’t be too mad.

The same problem of pooling due to work conditions which is not uncorrelated within groups still exists, but these 2 statutes not meant to deal with that problem. However, if for some reason genetic pools within worker pools are very correlated, it is a big problem. Let’s say more workers have not only high risk of injury due to work conditions but also mine worker because genetically inferior and more susceptible to disease and sickness, as compared to lawyer. This makes cross-subsidizing bigger and more likely discrimination will occur indirectly. HMO’s can look to other factors such as work or nationality to get around prohibition of discrimination on the basis oi predictive genetic info.

Forgot to mention: you have to prohibit both request and receipt of genetic information. This is case because HMO’s can assume that those who don’t publicize information have inferior genes than those who do.

The treatment, diagnosis and payment provision for groups has problems that Senators may not be aware of. By giving individual choice of disclosure for treatment goal is to provide health care provider with information that will keep costs down and provide optimal level of care. Additionally, patient can keep privacy and pay for treatment instead of disclosing private information. The problem is that the statute is very vague. Why does insurer get to see information; can’t we just limit it to the doctor? Since doctor usually making decision about treatment, in most cases we can. But what if have utilization review? Now insurer gets information, since need it as part of decision-making process. Is this ethically right? Most people have problem changing someone’s care due to genetic makeup and likelihood of successful treatment. Remember this is identified life not statistical. Senator should maybe add provision that no utilization review can take into consideration genetic info. Don’t want someone denied health care just because half as likely as another individual with different genetic makeup to be cured. Very bad public relations in egalitarian society. Problem though we live in a society with scarce resources, have to distribute them somehow, to get best overall welfare. But very bad practical move to distribute them based on genes.

Still making information to doctor very helpful. Now doctor canavoid giving patient certain drugs and procedures that may be harmful. Save life and costs. Nobody will have problem with this. Yet, patient may still not want to fearing later discrimination. What if loose job. Now need insurance and fear word get around, even though doctor patient confidentiality. Fear lock-in, even though other statute take care of this patient still may be worried. Therefore, add that once a person is insured, he or she may to keep the insurance indefinitely (but now you may need to charge the person a fee if unemployed because of the loss of the tax subsidy). Also, patient may fear giving information to insurer. What if company refuses to treat, knowing the patient will die or will just not benefit sufficiently. Individual need guarantees against it.

Benefits for sec. 2753 far less. You have no possibility of employment discrimination here which was big thing feared in sec. 714. Also, no forced pooling here so tremendous problem of adverse selection. Not feasible to try forced pooling through taxes, since individual may be unemployed or poor and very little tax advantage to join pools. Back to problem of adverse selection which is great here. Adverse selection problem of asymmetrical information. Now individual knows about genetic makeup and insurance companies prohibited from knowing about this potentially very important piece of information. Insurance companies will correctly assume that there is something wrong with people who buy insurance. Now people can better predict expected health costs (through genetic testing perhaps) and only those with higher than average risk will buy insurance. Insurance rates go up, further pricing out low risk individuals. This spiral will continue till pool shrinks and get what we call unraveling.

Nothing you can do about it. You can get rid of 2753 (b). This now allows layering by insurance companies. Groups pooled together based on risk. Apply different premiums to each, much more likely to prevent unraveling. However now high risk individuals have to carry own weight, no cross-subsidization. Big problem, as many might not be able to afford it. What may happen is a large percentage of those by not buying insurance decide society will insure them since have little wealth to protect or just not possible to protect wealth and pay insurance fee. Many people also scared of not having insurance may decide to quit job and be eligible for Medicaid. Not good for the economy.

Best alternative for individual coverage is allow layering but subsidize those with high risk. Now low risk insured get benefit of not having to deal with risk adversion on own since in insurance pool, and high risk also insured and not great burden to society. Win election!!!

But we must remember very important thing about partial equilibrium: change one piece of puzzle, other pieces do not stay the same. Behavior of insurance companies and HMO’s change to reflect prohibition of genetic info. This increases adverse selection problem as previously stated since information asymmetry increased: HMO’s and insurance companies will increase studies looking to links between genetic info and behavior or traits they can discriminate against. Although efforts only limited success, may want to pass legislature dealing with those issues.

Finally, main reason prohibit genetic discrimination is not just efficiency. Reason is that society don’t like to hold people responsible for things they are not in control of or traits not responsible for. "Sink or swim together." Great campaign slogan. Win election!

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Question II

Exam # 717

Introduction

Disclosure programs such as TRI provide multiple mechanisms that all work in the same direction as a more hard-line command and control approach to a problem, and also allow regulators to make more informed baseline judgments about the possible need for future command and control or other regulation. While many of the apparent benefits of the TRI plan were probably real, some may be the products of imaginative, self-interest-based number-crunching and "magic tricks" on the part of the regulated industry. This essay will examine the reasons why TRI was apparently so effective in reducing the release of toxins, and will then go on to explore whether the program’s results should lead to mandatory emissions controls, and what its implications are for OSHA’s Hazard Communication Standard.

 

Reasons for TRI’s effectiveness in reducing toxic chemicals release

Legitimate reasons for effectiveness

One of the primary, most obvious, and also most effective reasons for the success of reporting programs such as TRI is the fact that it promotes organization and accountability, both within the firm and in its relationships with the industry, the public, and the government. Before TRI, many of the affected firms may have been exceedingly sloppy in their treatment of toxic chemicals, and eve sloppier in their internal monitoring of that treatment. A pre- TRI company-stated goal of reducing emissions would have been ineffective if lower-level employees did not act out the noble aspirations of the board of directors. TRI, then immediately encourages internal organization and accountability in this realm. Instead of simply proclaiming a goal of reducing or closely monitoring emissions, firm management is forced to develop a concrete plan that will communicate chemical treatment up the rungs of the company ladder. This increased internal accountability, if effective, is likely to have a positive mutating effect on other aspects of the firms operations, thereby increasing internal communication, accountability, and productivity such that other areas of the firm’s operations also benefit. Reporting, though seemingly a burden, may actually increase the firm’s efficiency by forcing it to identify and reconcile internal trouble spots, whether they be in the emissions area or elsewhere. This development may explain, in part, the ability of the members of the Chemical Manufacturers Association increase sales volume while reducing their emissions dramatically.

As well as increasing internal accountability, disclosure programs positively affect accountability to the public and to the political arena. Whether or not it was explicitly designed as such, TRI necessarily must have served as a mechanism to increase public and political awareness of the implications of emissions. This phenomenon increases overall access to infromation - to firms, the industry, the public, and politicians - such that the risk of market failure due to lack of information is reduced. It also reduces the presence of cognitive errors throughout all of these parties. For example, a concrete knowledge of real emissions information will provide consumers of that information with a "typicality" or availability" not previously present. This availability will increase their inferences of negative consequences, and generate public and political action to cut down on emissions. The very threat of this public and political action, even before it occurs, will encourage any firm with reasonable foresight to reduce the visibility of emissions problems so that they are not "jawboned" by regulators into changing their behavior as a result of the new activism.

TRI also increased accountability to insurers. Before TRI, a significant element of moral hazard may have been present in that firms may have emitted hazardous chemicals without regard to negative consequences. Their attitude was likely to be, "If we get sued, the insurance company can pick up the lawyer’s bills and damages awards, and we’ll just take them out for a nice dinner at Le Cirque when it’s all done with." With mandated reporting, however, insurers are able to identify high-risk firms, and pool them such that they pay increased premiums directly based upon the volume and danger of their emissions. In order to keep their premiums down in the face of increased information flow to insurers that allows the insurers to identify real risks, then, TRI provides a powerful financial incentive to reduce emissions. If they do so, they will be able to avoid the possibly higher premiums associated with a negative experience rating, and reap the benefits of the lower premiums associated with a positive one.

In order to reduce emissions to ward off the threat of potential command and control regulation, firms also receive an incentive from TRI to make innovations that will reduce emissions. Such incentives would not have existed to the same extent before TRI. In addition, TRI prevents a "race to the bottom" scenario from occurring, by which firms would spend a minimum amount of resources to address emissions problems in order to maintain the highest possible level of competitiveness within their industry. Indeed, programs like TRI might encourage increased cooperation among firms, since the entire industry would be negatively affected if the voluntary reporting plans indicated to the government that extensive command and control regulation was necessary.

 

Reasons for apparent effectiveness that may be more illusion than reality

Unfortunately, some of the TRI’s apparent effectiveness, lauded by the EPA as a "potent environmental weapon," may represent efforts by firms to present their emissions as lower than they actually are because of self-interest, or may mask certain emissions that are hidden for one reason or another, intentionally or otherwise.

First, the statutory language of Section 313 of EPRCRA allows firms to use either "readily available data" or "reasonable estimates of the amounts [of emissions] involved." It explicitly avoids mandating any additional monitoring techniques beyond those already "required under other provisions or law or regulation." This language would appear to afford firms quite a bit of leeway in establishing internal monitoring and reporting techniques. If the methods already required under other laws are weak or ineffective, the Section 313 does nothing to address this issue, and instead only exacerbates it.

Related to this issue is the problem of enforcement by the EPA. EPA is unlikely to have a large enough enforcement staff to conduct effective checks on the reports of affected firms. Firms would realize this point, and might be encouraged to be dishonest in their reporting procedures, due to competitive pressures and the desire to avoid regulation. Firms, and even an entire industry acting in conclusion, might deliberately minimize the emissions problem in order to convince the government that its regulatory dollars would be better spent elsewhere, since the brunt of the chemical emissions problem had already received apparently effective attention, and any further dollars spent on it by the government might receive diminishing or zero returns. "Please, take those dollars elsewhere, Uncle Sam, to a problem that really needs attention," the chemical firms might say.

In addition, situations may be present where firms are simply unaware that they are polluting, as in the case of New Castle v. Hartford Accident (Economic module p. 54), where New Castle was discharging contaminants without realizing it. The scienter issue in that case created a potential moral hazard situation, since New Castle would have had no incentive to improve their landfill operations if they were not legally responsible for emissions that they did not know were harmful. This is a problem that does not appear to be addressed by TRI.

 

Should disclosure lead to mandatory emissions controls?

The next logical step to take for the EPA is a determination of the action called for by the results of TRI. If it appears that the emissions problem is under control, the perhaps EPA’s budget could be more effectively spent enforcing other, more pressing problems. However, for some of the reasons mentioned above, the apparent magnitude of the emissions issue may be much greater than is facially apparent. At the minimum, EPA would be able to set a baseline of minimum standards for emissions, probably based upon the volume of manufacturing activity of a given firm. However, they might also see fit to institute a tradeable emissions permit system, under which firms could buy and sell permits amongst themselves, provided that the total global emissions were not greater than the chosen baseline level. Regardless of the approach taken, the information culled from TRI (discounting for now the potential problems already discussed) would provide the EPA with the ability to avoid, to some extent, the hazards of regulating under uncertainty.

 

Implications for OSHA’s Hazard Communication Standard

The historically problematic OSHA could apply some of the results and implications of TRI to increase the effectiveness of their Hazard Communication Standards (HCS). A period of health and safety reporting would provide OSHA with a better idea of the extent of the problems that they face. This would, at least in part, address the difficulty of standard setting, for it would provide OSHA with more information on which hazards in the workplace are most in need of abatement. It would not, however, address the more fundamental stumbling block faced by OSHA, which is the nearly impossible task of prescribing how every hazard in every one of the nation’s workplaces is to be reduced or eliminated, and creating standards that will work well in an almost infinitely-wide variety of employment settings.

Broadened reporting as applied to HCS could also have the very positive effect of increasing overall awareness of hazards, and in turn increasing employee demand for safety. Perhaps labor unions would even be encouraged to negotiate over safety issues, something that they have historically resisted. The increased awareness would serve to increase public and political pressure on HCS issues, since it would address the information imbalance that currently exists largely at the expense of the labor market. It would also tend to minimize some of the cognitive dissonance and heuristic biases that might cause the labor force to assume that workplaces are safer than they are in reality. In any event, once again discounting the aforementioned dangers and limitations of voluntary reporting programs, they would at the minimum make employees more knowledgeable consumers, and create a more equitable relationship between employer and employee. They would also have the crucial effect, discussed above in the TRI framework, of increasing overall accountabilty.

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Exam # 735

Part I To examine why a disclosure program like TRI has been so effective in reducing the output of toxins a hypothetical comparison of two firms may help:

Firm B (for bad) merrily pollutes the environment and releases a TRI reflective of its disdain for the trees and fishes around its facility. Now such a firm will face a number of potential costs:

1) Due to the public release of information, transparency is increased and along with it the threat of public pressure. Information disclosure is empowering to concerned groups in that it allows for increased lobbying and even litigation efforts. Thus environmental groups could use TRIs to pressure firms as could community activists. This could take the form of community protests, consumer boycotts or divisive annual meetings (and what director wants to get questions regarding such issues?) Also information disclosure programs may enjoy wide political support as release of information cures an alleged inefficiency of the market while also satisfying advocacy groups by putting information into hands of the public.

2) While the firm need not collect data outside of that already mandated, the provision of such data to government regulatory bodies raises the possibility of further regulatory action by outside agencies which can be very expensive.

Firm A (for altruistic) see that its TRI could prove quite costly, given recent pollution problems at its plant. But Firm A also recognizes that almost its emission problems are probably so-called ‘low-hanging’ fruit; that is problems addressed on a low-cost basis. [Moreover, Firm A will also gain a competitive advantage with B by being able to trumpet its environmental concern to its consumers.] The transparency of self-disclosure and the potential costs associated with it if the results are bad encourage firms to take/find low-cost alternatives rather than face regulatory pressures that could result in high-cost centrally mandated solutions to publicly perceived problems. Providing information on risks may also reduce the psosibility of future litigation and regulatory costs. Think of doctors: studies show that one key determinant in who gets sued is the level of patient/provider trust. Here firms who disclose increase trust and customer loyalty whih maywell increase sales of its products, thus obviating any of the costs of information release.

Part II The mechanisms of success can be analyzed in comparison to normal problems of information gathering.

Ashford & Coldart noted that information on risk is attained in three stages.

(1) Must exist or be created – Here the firms face no cost burden in generating the information needed for the TRIs. This is because the information is a) readily known to or available to the firm, or b) the firm may use data collected pursuant to other provisions of law. This means there is no extra cost to the firm, especially since where no such data is available the section 313 only requires that the firm use "reasonable estimates." Reasonable must be widely denied as section 313(2) goes on to say that nothing requires monitoring or measuring beyond that already required by law.

(2) Must be obtained by the affected parties – Here the EPA and presumably state and local government ensure the distribution of the relevant data. Government involvement in the collection and dissemination of data ensures that no private groups or individuals must bear the costs of collection and dissemination (for which there might not be a market as Breyer notes).

(3)Those parties must be able to interpret the data – Again here the government requires uniformity so comparisons may be made, and thus presents the data in a manageable form understandable to the public.

Thus, the normal informational hurdles are overcome in the case of the TRIs.

 

Now several caveats. The hypothetical concerning Firm A and B illustrates the incentives that operate on a firm to produce TRIs indicating good behavior. This pressure, combined with the emphasis on self-reporting, could produce pressure to skew reports, i.e. by using unreasonable "reasonable" estimates. It is unclear whether the 52% drop in emitted toxins is from an independent study or from the firms’ own reports. If the latter a significant possibility of over-reporting exists.

This caveat also illustrates one reason why mandatory regulation in light of TRIs is unlikely to be beneficial. Such mandatory regulation will increase the incentives on firms to either doctor the numbers or restrict the reports to information garnered from measurements required by other programs.

If firms begin releasing only information already required, the regulatory benefits will be few. Thus, implementation of mandatory emission controls on the basis of the TRIs would raise the costs to firms significantly while reducing the benefits. Also, mandatory regulation would lead to problems of enforcement similar to those suffered under HCS. For instance, how could you enforce a standard as vague as "reasonable estimate?"

The system works well now because it places an emphasis on self-regulation; that is allowing firms to use their own knowledge to implement those changes that are most economical and efficient to them. In this sense transparency and external pressures must be high enough to cause firms to make low-cost changes but not so high as to make the risk of disclosure too high in relation to the benefit. We can also hope, of course, that transparency leads to internalization of outside norms regarding polluting behavior.

HCS was implemented by OSHA in response to the market failures existent in the workplace risk information market. The market failure in information was that:

1) such information did not exist at least not in an easily accessible form.

2) could not be obtained by workers, due to firm reluctance to publish such information (i.e. could reveal trade secrets, could be used against it in trade negotiations).

3)information that was obtained not easily understood by workers as their unions due to the typical questions of workplace disease (how much exposure, how long a latency period) and heuristic biases.

Because information is crucial to any market based approach to workplace safety its absence severely handicapped both workers and theorists (i.e. Viscusi).

But HCS requires mandatory disclosure in accordance with a two-tiered set of guidelines. OSHA created a list of approximately 2400 chemicals that were deemed hazardous and then said firms were to determine if other workplace chemicals were harmful on the basis of "available scientific evidence."

But despite fairly vigorous enforcement attempts it is widely conceded that the HCS mandatory disclosure system has not worked very well.

Success of TRIs allows us to draw several distinctions:

(1)Information collection costs under TRI are very low as noted earlier. Firms very much allowed to collect their own data. By contrast the HCS system has, in an attempt at flexibility, created hard to understand standards (i.e. "Available scientific evidence") that are reliant on value judgments and other fairly subjective criteria. In a mandatory disclosure scheme the presence of standards lead to problems of interpretations and litigation. This vagueness makes enforcement and compliance very difficult.

(2)Class to whom information is given differs widely. HCS mandates disclosure to workers themselves, which is quite distinct form release to the general public.

Firms can see some benefit from release of information to workers, but mainly see the problems that initially prevented them from releasing information. Firms and labor are locked in an adversarial bargaining posture that dilutes possible benefits. This divergence in costs/benefits meant TRIs are far more aligned in accordance with firm interests then the disclosure requirements under HCS are. This lack of incentive leads to mandating disclosure.

By contrast release to the public carries risks but also advantages in increased sales (indeed sales increased 10%) and decreased litigation costs.

(3) One benefit of TRIs that could be applied to HCS is the requirement of "common units" in 313(2). One of the chief problems with HCS is absence of standardized reporting, i.e. forms and education programs may take a shape determined by the company. This leads to difficulty in comparison, and the pressure of visible comparison would be a highly effective means to compel performance. Under TRIs advocacy groups can clearly compare Firm A and Firm B and deploy pressure accordingly.

Thus, TRIs require lower costs on the part of firms and carry greater benefits; HCS imposes more costs on firms for benefits primarily directed at the workers. By the same token it is unlikely firms would release HCS information if there were no mandatory requirements. So the different environments within which disclosure is being generated affect the processes by which that information may be generated.

 

Exam # 747

 The effectiveness of the TRI program may be due to intricacies of the market. Famed economist Adam Smith posited that the invisible hand led to the most efficient outcomes. For example those who produced undesirable products are soon kicked out of the market. The laws of supply and demand allocate resources efficiently. In this instance the laws of supply and demand are at work here as well.

The EPA administration has shown that members of the Chemical Manufacturers Association has reduced their emission of toxins by 52% while sales volume went up 10%.

Increase public awareness of the levels of toxic chemicals could influence the choices consumers make. Those companies that are more environmentally friendly receive a greater demand of their products by consumers. Thus those companies seeking to either capture a larger market share or retain their current percentage would induce programs that would reduce their toxic emissions as the lowest possible costs.

Thus competition may have ensued between companies to be more environmentally friendly. The invisible hand will lead those who can reduce emissions to do so until MC=MB while those who cannot compete in this market will either leave or develop ways in which they can. Thus TRI may lead to new innovations in the industry as well.

The ability of the market to work in this case assumes that there were no market distortions or other instigating factors. For example, this hypothesis assumes that there were substitutes for those environmentally unfriendly products. Thus in a market where there are no substitutes consumer tastes will make no difference. In addition the EPA’s statement does not reveal if their was a 52% on all toxic emissions or among a select group of toxins. This information would suggest that for those toxins while the market does not impact regulation for those substances may be necessary.

The 52% reduction may be due to other causes not necessarily related to increased reporting. For example, current technology used in the industry may have been reducing emissions during this period independent of the reporting. Also one needs to consider if regulations already in place such as the HCS may not have also had an impact in the reduction of emissions. The current regulation does not require any compliance with a standard save those already in place. Thus those limitations imposed elsewhere such as the NAAQ’s may be behind the 52% reduction in toxic admissions.

Without further study it is difficult to know what is actually the cause of the reduction in emissions of toxic substances. It may be that companies are subject to greater accountability that has led facilities to decrease their emissions level. 1(B) requires certification by a senior official. Companies may have seen an increased risk of tort liability through the TRI system in that the public is acutely aware of the dangers posed by their operations. Thus those living near a facility may now have the necessary information that will demonstrate causal links, without requiring expensive fact finding. Part of the large prohibitive costs of legislation are incurred through discovery. Here the government has required the facilities to provide that information to every possible future claimant. Voluntary reduction of emissions may have been a result of a cost benefit analysis. It is cheaper for the companies to pay to reduce emissions now than expensive litigation later.

It is difficult to know whether or not the TRI information should lead to mandatory emissions controls. It must first be determined what are the causes for this reduction. If it is indeed market forces that have led to reduction in emission then it should follow that those substances that don’t respond to market forces should be subject to some form of regulation.

However the types of regulation should be predicated on the costs and benefit produced by the regulation, as well as some risk-risk analysis to determine if the risks posed by the specific toxin actually support large investment capital needed to regulate it. The Clean Air Act of 1970 demonstrates how expensive command and control legislation can be.

In addition one should be wary of consumer preferences in that they are subject to change. Thus consumer choice for environmental friendly companies today may be supplanted by other needs or preferences tomorrow. Thus one should be wary of relying solely on the market to allocate resources where the market is concerned. The Coase theorem of efficient allocation assumes that transaction costs are zero. As transaction costs increase, the economically efficient outcome may not be the most environmentally sound.

Emissions controls may still be necessary in the case where increased accountability has led to reductions. This may be so because the mere fact that a decrease has occurred does not mean that the decrease has occurred at the safe level. It may still be necessary to reduce levels to increase safety. In addition studies have shown that public perception of risks differ from that of experts. Thus although companies are reducing emissions today due to a misperception of public knowledge about the attendant risks associated with their products, tomorrow they may realize that the public has no knowledge of the danger of the substances that they are being exposed to. A similar organization led unions to establish right to know laws. They lacked the necessary expertise to effectively bargain with employers.

The public may not be able to fully use the given information, significantly hampering their abilities to pressure companies to be more environmentally friendly through their purchases or through threats of regulation. In sum mandatory minimum standards may be needed to ensure a minimums level of safety in the TRI’s do not currently effect emissions levels or if these effects will not be long term.

The implications of TRI for OSHA’s HCS are unclear. On the one hand they may signal that HCS are having a significant impact. (If in effect reduction is a result of compliance with the earlier governmental regulation) Or it may illustrate that the type of regulation achieved through HCS may be obtained much more efficiently and cheaply through voluntary means rather that through expensive command and control regulation. Without isolating the cause of the reduction, which may be possible through regression analysis of the type used by Viscusi, it is difficult to know what impact if any TRI has on current or future EPA programs in regulating Health and Safety.

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 In addressing the effectiveness of the TRI data on reducing emissions, I would like to look at the impact of each user group on the firms desire to reduce emissions. I will then address the question of using TRI to set emission standards and the impact on OSHA’s HCS.

Community: The real impact of highly technical data to the community is likely to be small; interpretation problems are likely to create difficulties for communities in understanding data. Also, due to collective-action problems, communities may not be able to garner enough support to hire a consultant or whomever to analyze the data for them. However, the difficulty in understanding the time meaning of the data may lead to some over-reaction by communities, especially given the widespread fear of chemicals in community today. As such, the firms will be pressured into either reducing emissions or educating neighbors that the emissions are not "bad" (in this case, they would be addressing a ‘lemon problem’, e.g. dispelling false fears by release of educating data). Note as well that release of data to the public may affect share price as capital markets react to beliefs (unfounded or well justified) that firm may be subject to future litigation.

Thus, the TRI measures create a pool of data for communities previously unavailable (due to collective action problem which stopped initial collection of data by the community; the non-rivalrous nature of information creates this problem). And, given difficulties in interpretations people are likely to assume the worst and pressure plants to reduce emission. Apparently, the plants have found that reduction of emission is the better way to go (as opposed to dealing with community protests, etc.).

 

Environmental Groups (EG): Again, the release of the TRI data will reduce collective action problems among environmental groups as well as the community. Here, however, the TRI data may be put to use more effectively, as EG’s likely have greater access to interpretive devices/experts. As such, they are likely to have more accurate analysis/perception of risk created by toxic chemicals. Firms, who are aware of this, may view the reduction in emissions as preferable to release of data to EG’s who are likely to put the data through every conceivable test and may be tempted to even "massage" the data to produce the results they desire. Note as well that although the community speaks politically through its representatives, the environmental groups have better, more direct access to political process via individual politicians and agencies.

Agencies: The release of data by firms to agencies is perhaps the biggest reason for the reduction in the emissions. Previously, agency research-arms such as OSHA’s have been forced to do original research into chemical release amounts and effects. They have also been forced, frequently, to defend their findings in court. The TRI is likely to have reduced both of these problems. First, firms will have difficulty disputing their own data. Second, it signals agencies quite strongly as to where they should direct their research (before, agencies may have had to wait until adverse effects sprung up before they began snooping around firms).

Apparently, firms have decided that reducing emissions is better than either a) lying to the agencies or b) trying to defend themselves form the agencies. Also, the reductions allow them to set their own pace of reduction, as efficiently as possible. Firms that find innovative methods of emission reduction are rewarded by avoiding regulatory scrutiny while those that don’t are investigated and research is done into the effects of the emissions or the neighboring environment. Here, again, the PR issue comes up: listeners to Bloomberg Radio are usually not too excited about a stock when they hear that it is under EPA investigation (CEO stock options as an environmental tool!! ). Overall, the TRI functions as a quasi-negotiated regulation tool wherein firms self-regulate to avoid scrutiny.

Given all the hoopla about the effects of public disclosure on pressuring firms to reduce emissions, we may be led to believe that we should take the disclosure data and create a command-and-control type regulation to "beef up" the improvements realized under TRI. Why (I ask)? The measures to date have been effective; they spawn efficiency and productivity (-52% emission w/ +10% output) while promoting continued technological growth in emission reduction mechanisms. Using the emission data to set limits would restrain the need for technological innovation by allowing firms that are in compliance to stop searching for new emission reduction mechanisms. Furthermore, if the new emission caps are adopted instead of the TRI’s, we create new monitoring and enforcement costs for the agencies. Also, the command and control system would fail to signal the agencies as to how changes in market structure are leading to changes in the valuation of pollution "risk" (e.g., an increase in profit for a given good may make it worthwhile for firms to produce X even if it creates a lot of pollution. The TRI system allows firms to make this balancing test; they may choose to pollute if it is worthwhile profit-wise despite the likely public backlash; They should be allowed to make this decision, especially given the weight that firms have been giving to the public opinion/knowledge in making emission decisions).

Overall, then, we see that creating command-and-control measures based on TRI data might reduce the effectiveness of the program and reduce significant incentives to firms.

What are the implications of the effectiveness of the TRI on the OSHA’s HCS? Quite encouraging, I would assume. Workers, like average people, have problems with interpretation of data. But, as we’ve seen, this interpretative problem has not stopped the public from pressuring firms into self-monitoring. Also, workers may be more organized, thus akin to environmental groups, in that they force company union membership (sometimes) and eliminate free-rider collective action problems in the interpretation of data. Also, unions frequently have access to legislature and other political ends, as the environmental groups might. So, we see that a lot of the structures that made the TRI’s effective are in place in the workplace as well.

However, a problem may arise in that the OSHA standards may impose costs on workers in the form of reduced wage that TRI doesn’t impose on people (esp. if elasticity of demand for the product is low for price) or agencies. If we believe that wages are reduced for increased safety measures, we may have "paternalism" questions; can OSHA really make the safety decision/trade-off for workers (I say yes, but it is a question). Also, if we have a work force that is heterogeneous as to productivity, the OSHA HCS may push some workers out of work – (if costs go from X to (X+4), all the once-profitable workers at productivity (X+2) will be laid off if they can be identified).

So, although there are numerous parallels to HCS and TRI, there is always the problem of imposing costs onto the workers who are supposed to benefit from the regulation. (This HCS stuff also may not take into account the inability of workers to exit their jobs if chemical risks are too high; as Anderson says, workers may be locked-in due to firm-specific skills or deferred compensation. To what extent does "lock-in" occur within communities; e.g. is it hard for people to move if the TRI of the local firm indicates high pollution?) But, overall the TRI success probably bodes well for HCS. Also, the moral condemnation of pollution itself may, to some, be an immeasurable benefit of both schemes. Perhaps HCS and TRI both will lead to changes in the normative assessment of risk by pollution, thus reducing the need for later regulation.

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Question III

 

Exam #731

1. Is the risk of very bad global warming consequences really worth the effort of reducing gasses, which will be very expensive?

I think that the answer need not be a certain one, only that the risk is substantial enough given the consequences that that warming will bring. I’m personally convinced that it is, but the question needs to be asked. If either the risk is lower than generally thought, or the consequences not so bad as generally thought, we may reconsider. Glieck’s Chaos theory climate needs to be looked at-– but we must consider not only the risks of global warming, but the risk of being wrong about the risk.

 

2. Assuming the risk is bad, is the target sufficient to avert global warming? Or is it overkill?

It doesn’t make sense to take half-measures that are very expensive. If we cannot get the political consensus to get the required reduction, it may be that something under that doesn’t stem the damage at all, or stems it very little. If that is the case, we might consider no limits since global warming will happen anyways given the political removal of the pareto condition of a lower emissions level. The second-best outcome may be maximum production benefits and take the hit of global warming (since the alternative might be curbs in product plus global warming). Conversely, if the goal is set too low, we may be cutting production more than is necessary to stop the problem. One caveat is that overcompensation may be better than undercompensation–erring on the side of caution, particularly if determining the exact amount necessary is impossible or prohibitively expensive.

 

2a. How expensive will it really be?

It may be that the costs of even an exactly sufficient reduction will be so high that the world will suffer a great depression that will be worse than global warming. If this is a real possibility, we should not ignore it, and if we are convinced it is so, we may want to vote against the treaty. But I don’t think it will be (see last part of question for more on this). It may also be that the prices of global warming are not that high. We might want to ask how much all that lost farm land is worth? It is practical to raise levies to protect our seaboards from flooding? The answers I think are unlikely to sway you against the plan, but you should ask them, and way them against the costs of the plan.

 

3. Will the CDM create an incentive to overproduce power?

That is, perhaps allowing developed countries to gain permits by helping developing countries build cleaner plants will actually increase pollution if it results in building plants that would not have been built at all without the Kyoto agreement. Certainly clean plants are preferable to dirty plants, but no plants (at least in terms of CO2 emissions) are preferable to clean plants. Of course, even if this is a perverse effect, it may be worth it if it causes more developing countries to sign on in the hopes of getting new plants and technologies, if the new plants are offset by these gains.

 

4. Do the incentives for sink creation reflect the fact that some reforestation might take place regardless of the treaty?

If a certain amount of reforestation will take place to increase property values, or for other reasons having nothing to do with Kyoto, giving full credit might devalue the permits and not allow for the most optimal reduction of pollution. We must make sure the credits created for the sinks are not overvalued.

 

5. How much of the greenhouse effect is cumulative from year to year, and how much is the result of peak years?

Although I believe that it is cumulative (which would argue for the banking provision allowing reductions starting in 2000 to count), to the degree that it is not, we may consider adjusting the program. If, for example, a high peak year could cause an immediate problem, we may want to discount them ( a negative interest rate on them when banked), or cap the amount that can be used in one year, realizing that to do so may lower their value and reduce immediate reduction.

 

6. Is there a large level of differences in production enough to sustain a market in permits? Is the market deep enough?

If there is not enough variation between countries in production costs and pollution control methodology, the market mechanism will not work enough to reach our goal ( in which case other measures may need to be taken, perhaps command and control). I doubt this will be a problem as the countries of the world do vary greatly in processes and development levels.

 

7. What will prevent countries from exporting the most CO2 heavy processes to countries outside those that are participants in the treaty?

This is potentially the biggest hole in the scheme. If there is no incentive to join the treaty, we could well imagine some countries opting to cash in on the treaty by not signing on and selling, for example, heavy CO2 (and cheap) power production to countries in the treaty. This could blow up much of the whole scheme. Of course, it would be limited insofar as transportation costs would be added to the production costs of extra-treaty goods–for example, if Slovakia opted out of the treaty to build huge dirty plants to sell electricty at a premium, neighbors would pay extra only to an amount that equaled the marginal cost of domestic power production, including the cost of emission permits; Slovakia’s profits would be reduced by transmissions costs as well as its own production costs. But the better solution to this would be limiting the ability of treaty adherents to buy production from outside-treaty countries, which would directly address the problem by limiting the trade and indirectly address the problem by creating an incentive to join the treaty: to be in the trade block. Alternately, we might offer carrots to prospective joiners to dissuade them from opting out. This may be subject to the hold out-problem however– a few countries outside the treaty would get higher returns if there were fewer of them ( since there would be less competition from other extra-treaty producers) and the costs of "bribing"them into compliance would be higher. For this reason I think the sanction/exclusion approach would be better.

8. How will the enforcement/Inspection mechanism work?

Another large problems will be inspecting all production sources. Monitoring and enforcement procedures are needed to build confidence in the tradable permits market. In the US, SO2 emitters are relatively few so the CAA plan is workable. On a world-wide scale, every potential CO2 polluter is enormous, and the inspection problems are also enormous. Monitoring a fixed source polluter (a power plant, e.g.) is one thing; monitoring mobile sources of CO2 (automobiles) is much harder. Perhaps hard enough to sink the program. If enough pollution gets away unmonitored (and thus without permits), the goal simply won’t be met. The value of permits may plunge as the demand goes down (since cheaters don’t need them). And enforcement is expensive, so the poorest countries will need help. We need to make sure the sanctions for cheating are very high to deter this behavior. Also, we need to ensure that governments have the incentive to catch cheaters–perhaps partially by offering a bounty for catching cheaters. Of course we must be careful not to create an incentive to trump up cheaters.

9. How will the permits be distributed?

Are we going to just give them away, or sell them? Giving them away requires a baseline, perhaps historical. If we make it to close to now, countries will be able to manipulate their results to get more allowances. If we pick an older historical baseline, we can avoid this, but it will probably raise an outcry from developing countries since older, richer countries will be given a disproportionate share of allowances. If we give the allowance on a per capita basis, we may create a re-distributional windfall for certain countries (e.g. China and India!) while people in small, production intensive countries (like the US and many European countries) have to buy allowances like crazy. Selling off allowances to the highest bidders will also discriminate against the poorer countries, though this might be mitigated by giving some of the money gained to them. Also, some of the money could be used to subsidize enforcement.

Nearly any method of distributing the permits is going to have distributional and political problems. We must balance the needs of many countries to make it politically workable (probably more than the 55% minimum). From your standpoint as a US Senator, you must be mindful that the overall costs of the distribution system (or the plan at all) are not greater than the benefits received by the US or your state, even considering the consequences of global warming. Of course, you may feel that your duty to mankind supercedes yours to the US or to your state, but that is your concern.

10. Will creating a market in CO2 commodify pollution and thus reduce pollution control now done altruistically?

We might want to study the effects that creating CO2 markets will cause for people who would have reduced production to "save the world" who will now think, hell, I’m paying for it so pollution is ok. The norm of pollution control may have an instrumental value that may be lost with the trading scheme. If this is strong enough (which I greatly doubt), the overall benefits of the market incentive to reduce pollution may be outweighed or greatly offset by this loss. Given the fact that a lot of CO2 production takes places where bread issues are more important that green issues, I doubt much moral value will be lost that will not be more than replaced by market incentive.

11. Would C&C be cheaper or more effective?

It may be that even if Kyoto is workable, and will solve the problem, command and control will do the job cheaper and/or better. We must at least consider it as a baseline (along with doing nothing). Although C&C loses some advantages (market incentives, technology drive, etc), its administrative and monitoring costs may be so much lower that it is a better package overall than Kyoto. Of course, it may be politically impossible to pass a C&C treaty that everyone would agree to, since it is inherently more invasive and coercive than tradable permits. This would be a factor in the analysis. Of course, if C&C were cheaper and politically feasible, we should go for it over Kyoto.

12. The effect on relations between the developed and developing worlds.

This could go either way. If the plan fosters investment in developing countries and relocation of industries there to earn permits at home, it could do well in redistributing some global wealth from rich to poor countries. I would think this would improve relations since both sides would be getting something out of the bargain, and insofar as working together for common goals helps relations. This is I think the most likely outcome. Yet we must be concerned that workers in richer countries will resent the exportation of jobs and wealth that the treaty may encourage–this would definitely hurt relations. Also we must avoid the possibility that the availability of tax enforcement in poor countries may lead to a wholesale export of industry to the poorest regions, which may bring other pollutants there as well (social dumping).

Another way the plan could go wrong for the relations is if it so depresses global production that there is less wealth to go around. Let’s say it causes a ten year recession in the industrialized world. In this case foreign aid and investment in the developing world might be drastically curtailed–a sneeze in Wall Street causing pneumonia in South America for example. The developing world, with reduced global demand and reduced for aid/investment, might suffer a huge collapse–I doubt this would be at all good for rich/poor country relations.

However, I think on the balance the positive effects of encouraging investment will outweigh the negative. I am skeptical that the Kyoto reductions will cause a huge reduction in economic output. My guess is that there are a lot of cuts to be made simply by optimizing current technological processes (i.e., extending the best control techs to everywhere) and that also the scheme will create a stronger incentive to create new control technologies (since such advances would as lucrative as CO2 reduction becomes a saleable good.). I think also that the overall effects on developing/developed relations will likewise be good. Much of the heavy industry production is becoming less important in the developing world anyway as we shift to information and away from manufacturing. The political strife in the rich countries at the loss of industry now will not be as great as it was say in the eighties.

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Exam #735

Senator Prolix:

I would like to begin with several general notes. First, although evidence on climate change is not conclusive we must distinguish between reversible and irreversible threats. Climate change, because it may well be irreversible, requires us to act while, at the same time, we continue to assemble the best possible evidence and data. Second, as a sponsor of the 1990 CAA and a supporter of Senator Moynihan’s Clean Gasoline Act of 1999, you are well aware of the extent to which varying contexts may affect the viability of an emissions permit trading system.

I will now discuss each of the five elements of the Kyoto Agreement.

(1) The creation of an emissions trading plan, inspired by CAA 1990 will run into some unique problems in regard to global warming. Under this section note as well that it is important to ask who is covered and if industry can escape the strictures of the Kyoto plan by relocating to developing countries not covered. This "leakage" is a critical problem with plans confronting global problems that do not include all global participants. For it will do little if a Cleveland industrial plant can simply relocate to Mexico. Remind the Senator as well that economic dislocation means unhappy voters.

(a) CAA only had to deal with a small number of stationary sources. Need to ask how many sources we are talking about here and if monitoring of them is possible, and if it is possible how much will it cost.

(b) How will permits be distributed? Under Coasion conditions it will not matter if they are given away or if they are sold but here transaction costs are unclear (after all who exactly would administer the program, would a central UN-type agency sell permits or would each country?) And we must be concerned with wealth effects. I would lean towards free give away as it will reduce distributional issues.

(c) Must ask if pollution-abatement costs vary across the developed world. If they do not, permits may not be the way to go as there will be no incentive to trade.

(d) Transaction costs must be low for the market in permits to function well; here, I have my doubts given the governments involved. Must make sure that no government approval is required for trades as this has hurt several domestic programs. Contrast with So2 where no approval required and markets have functioned well.

(e) On a more general level we have to worry about distributional issues as permit trading, while reducing overall levels of the targeted good, may create local "hot-spots." In domestic terms this may be viable but in the international system this may be a hard sell. Could try and implement a regional trading system, i.e. Europe, North America, etc. to lessen the chances of such hot-spots and to ensure benefits are even distributed.

(2) This is a complex issue that relates to the relationship between emissions in developed and developing countries. Clearly if emissions decline by 10% in developed nations but increase by 25% in developing nations we may not be solving the problem. This is termed the problem of "emissions leakage."

By supplying credit to developed country firms for helping firms in developing countries we try to create an incentive to reduce pollution in developing countries. But it is unclear how well this will work:

(a) first, the credit given must exceed the costs of cleaning up an old plant or building a new one. I would guess that such costs are higher than the costs a firm would face in lowering its own emissions (and then selling its extra permits). Thus, the alternative offered here may be a "highest cost" one that firms are unlikely to undertake.

(b) In many ways this allows developing countries to "opt-in" to the plan. This essentially allows for the regulated plant or firm to gain emissions allowances for its claims on reducing emissions in developing countries. This creates the problem of "paper trades" as the regulated plant exchanges its performance against a set baseline for the performance of a developing country plant against an unclear baseline. Note as well the complex enforcement and verification problems this creates. How do we know what a plant in India would have emitted if LILCO had not built a new plant in India.

(3) Here again we would have the problem of fixing the ration of credits to the acreage of reforestation. But more problematic is the following question: if plant X releases 20%, will reforestation absorb that same 20% or does the process of atmospheric release mean that reforestation only absorbs a fraction of what is released. This is critical to determining how many credits to give, and whether to give them at all. For instance, if one ton is emitted only 1/3 of a ton may be capable of reabsorption.

Also, reforestation may be time-limited. What if the forest takes fifty-years to reach maturity. Do we give credits now or later?

Also, reforestation may be so low cost that we will have many forests planted but few emissions reduced. While this may be the forest equivalent of coal-scrubbing (i.e. low-cost solution) we must be certain we can provide this low-cost solution and still reduce emissions by the targeted amount, especially considering the aforementioned questions of time and whether there is a linear relationship between release and absorption.

(4) Here we can refer to part of the reason for the success of the CAA 1990: the sudden and unexpectedly steep drop in emissions was caused in part by husbanding permits now in anticipation of more difficult cuts later.

I am unclear what exactly the term first budget period refers to, but I assume it means post-2000 cuts will count toward the target goal.

Now if these early efforts at compliance result in a lowering of the cost of permits (i.e. become as with So2 we misjudged the marginal cost curve) then the low cost of permits will indicate that greater emission cuts could have been made.

Banking might also allow firms to receive a discount on future abatement (that is if their gamble on future compliance costs is correct).

Given the complex system that would need to be implemented to enact the Kyoto Plan firms might also bank emission reductions for fear of systemic breakdown in the future.

A further problem with banking is the following: banking will be fine if current reductions are as valuable as future ones. If future ones are valued less then banking could be harmful. With So2 the benefits are the same as damage, and reversible, but if global warming is irreversible, then banking may accelerate damage that future reductions cannot undo. Thus in the case here of global warming banking may not be beneficial.

(5) This creates a dilemma as should we require unanimity and risk hold-outs or should we allow majority approval and risk substantial defections.

(a) Several questions would need to be asked. If we require ratification of 55, what is the possible number of signatures? If it is only 65 then we may have set the standard too high.

(b) Also, the 55% threshold raises a number of questions. How much CO2 do any two countries produce? If the US alone or in concert with one or two other countries could block it then we have created the hold out problem.

 

(c) Absent significant pressure this plan will suffer from substantial free-rider problems as a country could not sign on, enjoy the benefits of the effects of the 55 signatories and continue to emit. This country could then demand entry later at its own individually negotiated "price."

(d) Does 55% of 1990 emissions substantially parallel current emissions? If production has shifted, current defectors at 2000 levels could account for more than 55% of current emissions Thus we must make sure the 55/55% thresholds would allow for substantial emissions reductions.

Finally, how will this affect relations between the developed and developing worlds. The Kyoto plan in a sense respects the demands of the developing world that those who have developed not impose strict standards on developing notions that would hinder their development. But of course this compromise only postpones the debate, for as they develop their emissions will increase, possibly offsetting the gains achieved by the developed states. In this sense the plan respects the wishes of developing nations while postponing a final debate.

But the plan raises another issue, namely whether developed country industries can shift operations to developing countries and escape regulation that way. Not only will this affect global emissions levels, but it will also locate dirty industries in developing nations.

The trade-off then for developing countries is a worsening local pollution

problem at the same time the global problem is improving. Developed countries may thus come to resent their sacrifices appearing unmatched by developing countries, while developing countries may resent being the "dumping ground" for dirty industries, noting of course that land developmental needs may trump local environmental concerns (per the Economist).

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Exam #739

The first feature that may present a problem is the limitation of the program to developed countries. While they clearly have the better means to engage in reduction, it does present a free-rider problem, when the developing countries are able to be benefit from the overall reduction yet do not have to contribute to the reduction themselves. Will this encourage them to even increase the amount that they pollute, knowing that the other countries’ reduction will counteract their pollution? Perhaps, although this problem may be addressed by the CDM provision, thereby developing countries will get help to reduce pollution, despite their non-participation in the trading program.

Secondly, the choice to use 1990 as the baseline was wise, since in 1990, seven years before the summit, it was unlikely that any countries were reducing their emissions in order to manipulate the numbers in anticipation of the summit.

The system of tradable permits has many benefits. Rather than forcing a particular technology on countries, it enables them to reduce pollution by any mechanism. Therefore, they have incentive to try new methods and innovative techniques of reduction. (In the acid rain dilemma, the technology resulting from the tradable permits has resulted in new techniques like sulphur-eating bacteria and microwave radiation.) As opposed to a set level of pollution allowed, tradable permits encourages the country to reduce emissions as low as they can, and sell their excess permits. That results in a valuable consequence of pollution abatement falling on the lowest-cost abater, which is something that straight regulations are unable to do.

Permits also have the advantage of easier enforcement. Instead of detailed legislation which requires resources to enforce, permits have low administrative costs. The permit system also allows the participating countries to set the total amount of permitted pollution and trading prices provide a market signal showing true costs of emission control. The price of the permits will vary with changing economic circumstances, and the value or price will not have to be agreed upon by the participating countries, which would be a time-consuming process.

(2) The CDM provision may be useful for counteracting the free-rider problem, as discussed. By giving developed countries incentive to aid developing countries in pollution abatement, we may avoid the problem of increased pollution from the developing countries. There is a danger that the CDM program may be seen as paternalistic. If developing countries are not as concerned about pollution, either because their tastes are different or because their economic concerns are such that they override environmental concerns, perhaps it is inappropriate for wealthier countries to impose our preferences on them. Yet, this argument is questionable because pollution from one country affects people in other countries – and it is not fair for one country to reap the benefits of overall reduction yet still pollute continuously. In addition, preferences may be largely the result of social conditions (Kelman). Just because a certain community would favor small increases in economic welfare over larger increases in environmental welfare does not mean that, if exposed to environmental benefits like cleaner air, they may not come to appreciate it more.

(3) The greenhouse sinks seem like useful idea, enabling even countries that may have a hard time lowering pollution to contribute by reforestation. By providing alternative methods to reduce the effects of the greenhouse gases, without eliminating direct emissions, the sinks and the CDM provision allow for flexibility that will help the effectiveness of the program. While some may criticize that these 2 provisions allow countries to continue polluting through alternate mechanisms, they nevertheless still result in the same effect of reducing the harm of greenhouse gases.

This brings us to a possible problem with the program – by offering "pollution permission", it may show a moral indifference towards motives of polluters. It allows people to pollute according to how much they can pay, and that may present ethical concerns. In particular, the sink and CDM provisions allow countries to continue polluting and still obtain permits. Yet, as mentioned above, they would still be contributing beneficial effects. Overall, the ethical concerns seem to be outweighed by the overall benefit. As Rose notes, in principle everyone should do all he/she can not to pollute is they can pay, but especially in an international setting, a tradable permits system is probably the most useful way to counteract the problem of greenhouse gases, thereby outweighing concerns of commodification of environmental quality.

(4) The effect of provision 4, allowing the banking of allowances, will likely have a positive effect. We must examine whether the marginal harm of CO2 emitted will be higher today – when the emissions are reduced, and permits are banked – or in the future when the banked permits are used. Marginal harm should be lower after 2008, because overall emission levels will be lower (despite the banking) due to the system that will begin in 2008. If we apply a positive discount rate to future harms, marginal harms in the future should count for less today, than the equal amount of harm incurred today.

Also, the early reduction of emissions is a "bonus" reduction – it possibly will not lead to higher future emissions because the countries that voluntarily reduce emissions early, may have to reduce emissions from prior levels in order accrue excess permits.

(5) The 55% provision could possibly result in a hold-out problem, though that is questionable, because it is unclear what the participating countries would offer the "last joiner" to encourage them to join. This is a question Sen. Prolix will have to ask. It seems that countries will join for overall global benefit & benefit to their citizens, and it is not the type of system where countries will hold out in order to be given incentives to join. The 55% provision may present a problem, though, because it will probably not take 55 countries to get 55% of the 1990 emissions. Presumably, the larger developed countries emit more pollution, and participation by fewer countries, if they account for 55% of the pollution, may be sufficient. However, fewer countries may not provide a deep enough trading market to allow for a true competitive market in permits.

Lastly, the 55% provision may ignore the fact that pollution from some countries is more damaging than pollution from others, due to location, winds, or the present location of ozone deterioration. (This is another question Sen. Prolix would have to ask of experts).

 

(1) Are we selling permits initially or giving them away? Selling would present higher administration costs.

(2) What will be do in the case of lower-than expected permit prices? If the actual cost of abatement is lower than we contemplated, will we reduce the number of permits available?

(3) Danger of harms being concentrated in particular areas? Should we allow locations where emissions may pose the least damage to do most of polluting? Won’t that negate the purpose of the program? (may not be a problem for greenhouse effect – would have to ask a scientist)

As for relations with the developing countries, the CDM proposal may be a good thing while (as discussed) it may be seen as paternalistic, it is less so because it requires cooperative efforts. In addition, it allows the developing countries to sustain economic development and growth of industry while still preventing pollution.

One danger is the "moral suasion" argument. Rather than telling developing countries that pollution is harmful and should be avoided, are we telling them it is OK to pollute, as long as you can pay for it? The program may ignore the norm-setting implications; it does not result in pro-environment values. Yet, as mentioned earlier, those issues seem to be outweighed by the possible effectiveness of the program it in its crucial ability to shift abatement to the least-cost abater. I would therefore advise Sen. Prolix that the U.S. should ratify the Kyoto Protocol.

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Exam #747

Memo to Senator Prolix:

Senator, I will begin this memo with the assumption that a seven % reduction is not only a feasible target but that its MB’s [marginal benefits] outweigh its MC’s [marginal costs]. I will also assume that such a reduction will have a significant impact on global warming. I will address each part of the proposal in term as well as questions of implementation they might raise. I will begin by saying that in my view the U.S. should ratify this protocol once the proper Amendments are made. Our position as a superpower places a responsibility upon our nation to lead the way in saving the planet. If we can lead nations into war we surely can leave them into reclaiming the globe. In addition, our participation will provide legitimacy.

(1) Tradable emissions

Our nation’s experience with tradable pollution rights demonstrates that the market is an effective mechanism in reducing pollution. The Clean Air Act of 1990 established a system of tradable rights for SO2 emissions. By the end of phase I of the program, reduction in the level of pollution has exceeded expectations. One of the benefits of tradable pollution system is that once a market is established it is easy to determine the costs of pollution abatement, i.e., would it be more economical to reduce pollution or buy a permit. Tradable permits were an excellent method of combating acid rain;, however, the system was not perfect.

The problem in the acid rain context is that the reduction in some areas are not beneficial, thus the Lilco controversy. However, in CO2 reduction this is not a problem. One unit of reduction anywhere on the globe produces the same amount of benefit relative to any other location. Thus it could not be necessary to create zones of trading or worry about if the system is deep enough trading market. However, the question remains how will permits be allocated? In the U.S. the permits were distributed rather than auctioned. Auctioning would allow those who were wealthier to hoard permits thus reduce the benefits of a trading system, since a monopoly may be formed distorting the market. I would suggest that the permits be allocated.

A second question that needs to be asked is how will emissions be monitored and enforced. If there are no costs for non-compliance then the system will not work. It is important that the protocol identify its sources of pollution/emissions that it will measure and how it will enforce these regulations. If the costs are too high any benefit that may accrue will be lost. For example, although cars are a source of CO2 emissions it is far too costly to attempt to monitor and regulate emissions from those vehicles. (However, should technology change, cars are a good source for regulation). I would then suggest that compliance be relegated to industry, where devices may be installed rather inexpensively to measure what is coming out of the smoke stacks (such devices probably already exist).

(2) This provision will provide incentives for the developed countries to foster development in the LDC’s while protecting the environment. LDC’s typically do not use "clean" industries because of the extreme costs involved. By developing clean industries in these nations one will help solve the ethical dilemma proposed by the Lawrence Summer’s memo. In essence the memo proposed exporting pollution to LDC’s because it would be more economically efficient. In this instance growth in the LDC’s will not be sacrificed in order to promote environmental objectives. It has been stated that clean growth means slow growth. However, this will not be the case here since clean growth will be subsidized by wealthier countries.

A question to consider here would be when would the credits be received under the CDM. I would suggest upon completion, otherwise many countries would propose such partnerships without actually implementing the programs. Thus CO2 emissions may increase rather then be reduced if credits are given out indiscriminately.

Another question to consider relates to the Summer memo: would decreases in participating countries’ CO2 emissions be achieved by exporting "dirty" industries, thus resulting in no net changes in CO2 emissions while deteriorating the environments of the LDC’s? Restrictions need to be imposed as to how reductions can be achieved. Otherwise a decrease in France would be mitigated by an increase in emissions in Tahiti.

(3) Receiving credits for greenhouse sinks doesn’t seem problematic on its face. In practice it may have a discriminatory impact. Questions that arise: where will reforestation take place, in the host country (which would be acceptable) or in other nations? If it is the later, nations would be given credits at the expense of the livelihood of individuals in LDC’s. For example, reforestation in parts of South America may reduce CO2 emissions, but it will also reduce the amount of arable land for that nation. Again we encounter the problem that "clean" growth imposes substantial costs on developing economies.

In addition to the social costs, practical questions must also be considered. Namely, when will credits be given? When benefits from reforestation are demonstrated or at commencement of the project? In order to maintain significant reduction, these policies must be tightly regulated or net benefits may equal zero.

(4) This part of the proposal seems fine; however without knowing the penalties and subsequent target it is difficult to evaluate this proposal. However I will assume that the proposal is similar to the 1990 CAA which allowed for accumulation of permits to be used in the future when standards became stricter.

Thus if one begins counting emissions begun in 2000, there is an incentive to reduce emissions starting now rather than to wait 8 years until the program starts. Especially since a dollar saved today is worth more tomorrow. At the same time this may cause permit prices to be more expensive in the future. However the market should be able to allocate the permits efficiently nonetheless, barring any market distortions.

A question to be determined is how 2000 reductions will be certified; again a reliable accounting system needs to be in place to encourage compliance. Otherwise, all the benefits of the program will not be accrued if participants know that they do not have to indeed reduce their emissions due to a lack of consequences.

(5)The ratification of the proposal illustrates the large numbers problem of collective action. (Indeed this problem overshadows the entire scheme, in that any benefits accrued by participants can be nullified by non-participants). The free-rider problem will be difficult to overcome. This is especially salient in the fact that 1 unit of reduction anywhere on the globe will benefit all. Thus there is no incentive to undertake costly regulatory procedures when the reduction by one’s neighbor will produce identical amount of benefit. Hardin noted this problem of collective action in the tragedy of the commons. Each individual will act in his self-interest, although by the same token it reduces the welfare for all. The solution in the case of the grazing land was to privatize property. However that solution is not available to us here. The atmosphere is a common that cannot be partitioned out and bought and sold.

The tradable permit system is also subject to prisoner’s dilemma: it is beneficial to defect and reap the benefits of some one else’s pollution abatement. To combat this problem it is necessary to produce incentives for nations to cooperate. This is why in my view it is so important for the United States to take part. It will illustrate that we are willing to put our money where our mouth is. Game theory shows that in situations where more than one game is played it is possible to get more cooperation.

Thus it is important that the superpowers participate demonstrating their own willingness to cooperate, thus inducing others to do the same. Member nations may also want to decide to impose strict penalties for defection thereby promoting cooperation. These penalties may take the form of economic sanctions. As with all provisions or policies it should be determined if benefits outweigh the costs. In my opinion a properly devised scheme with the right incentives would be ideal. Public opinion may be a strong factor in influencing incentives. Thus making defection not a viable alternative for member nations.

In my view the protocol can have significant impact on the relation between the developed world and LDC’s. It could replace the resentment that exists in current environmental regulation, namely the "you’ve done it, why can’t we". This has a common sentiment in the regulation of CFC’s which are a major part of the LDC’s economy.

Partnerships that develop as a result of the CDM’s could foster amicable relationships by improving the health of these nations without impairing growth. However, if those CDM’s are undertaken they should be in the form of technology grants, or no strings should be attached. LDC’s are loath to welcome any more invasion in their natural affairs. Nor would they react kindly to a system which would foster existing patterns of domination in the world economy. For many of these nations the wounds of colonialism are still far too fresh to allow developed nations to start running their affairs.

It is important that technological expertise be exported with the new facilities as well, or else this program would be useless.

The Protocol would enable the globe to reduce pollution and enable development.

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Exam #777

 

To: Sen. Prolix

From: Staffer

Re: Kyoto

As per your instructions, I have analyzed the five prongs of the Kyoto protocol, whenever possible I have highlighted questions and suggested the consequences of their answers. In each case, I have noted the implications for relations between the developed (1W) and developing (3W) nations.

(1) This proposal, the chief one of the protocol, would allocate tradable permits to emit greenhouse gasses (GHG) up to a limit set below 1990 levels. This proposal, similar to the generally successful Clean Air Act Amendments of 1990 has a number of virtues. It likely accomplishes any given reduction more cheaply than a C & C mandate would, it allows maximum flexibility in meeting goals, it can shift costs to the lowest cost abater if costs are differential (which they most likely are), and it allows high value uses to continue and shifts abatement onto low value uses even if costs are uniform. A related issue to the final point is that Cap & Trade systems respect some degree of preference as well.

The proposal raises some large questions at once. The biggest question is enforcement. Any international agreement raises the problem of who will have the right and the power to enforce the limits, but C & Trade schemes do require a fairly high level of enforcement. If enforcement powers are weak, you risk creating a prisoner’s dilemma problem, where any nation who defected would be much better off (capture the gain through greater economic growth) and those who followed would lose most (as everyone else polluted to their heart’s content and sucked up all the capital & resources). If enforcement powers seemed too strong, you would raise sovereignty issues and breed political resentment, causing the whole scheme to unravel. In either case, 3W nations both most need development and have good reason to fear 1W dominance, so they are highly likely to defect.

Another key question is how the permits will be allocated. For administrative reasons, permits seem much more feasible than tax-free schemes (see, political problems, supra). But are they to be auctioned or allocated free. The reductions imagined by the plan are indifferent to the distributional effects, but the nations involved certainly aren’t. An auction would raise money which would then have to be distributed somehow. This would increase administrative costs and raise political questions. Free allocation would be redistributive as between nations and not as between nations and an international organization, and thus may be politically more feasible.

One can’t help but suspect that the affect of trading may be to redistribute wealth from the 1W to the 3W. Due to wealth effects 1W nations would likely be more able to pay high costs for permits than poor 3W nations. The result might be to slow development but compensate that by infusions of foreign cash. This redistribution may be offset by wealthier nations valuing clean air and environmental responsibility more than 3W nations. As a side note, it seems absolutely necessary to use 1990 measures as a baseline to reduce rent-seeking. Finally, it seems that however the payments flow, a free allocation system more readily allows abating nations a chance to capture their improvements in the form of revenue through permits sales. This capture would be a good incentive to keep the trading program running smoothly.

Another question is whether the permits will be allocated or sold to governments only, or to corporations and private actors as well. If multinationals can buy them, they may well use their superior capital reserves to buy a high percentage, but employ them in manufacturing and development in 3W nations. This would have the effect of encouraging 3W developments, but may raise political concerns about 1W firms buying the right to pollute 3W nations, although that would undoubtedly please Larry Summers.

(2) The CDM proposal

This proposal would allow credit not just for reduction but affirmative development of "clean" industry in nations least likely to develop it on their own. The proposal clearly seeks to allow continued economic development in 3W countries, while trying to maintain their "under polluted" state. To the extent that any plant requires large capital investment, it also avoids "lock-in", where "dirty" plants are too expensive to either shut down or abate. One might wonder how much credit a 1W nation could get this way. Even "clean" development produces some emission, so balanced against the non-abatement of existing emission, this scheme is not an immediate net improvement. This plan would be better if limited in scope.

It also seems clearly redistributive, in that is an incentive for 1W nations to invest in 3W ones, this redistribution may or may not raise political objections, but the politics may be offset by 3W worries about sovereignty.

Sinks

Another worthy suggestion that raises issues of scope. At least sinks would produce a net drop in GHG. This provision raises equitable distributive questions: will already heavily forested nations get credit for presenting? If only new planting counts, it could perversely give an incentive to expand logging, and increase cut/replant cycles. Arid nations who can’t pursue this option may object. Since most arid nations are in the 3W, and most 1W nations are temperate, this will raise political questions. Finally, one positive effect would be to increase the economic value of land left in (or replaced into) forested state, taking some pressure off deforestation.

(4) Advanced Credit

This proposal seems sound, in that it allows very low-cost marginal abatement to begin almost immediately. To the extent that harm is cumulative and compounded, this will have some benefits. An important question, however, is whether accrued credits can be stockpiled. In general stockpiling seems like a good thing, as gives nations a chance to capture benefits of early abatement and build a hedge against future limits. If too many nations hoarded permits it could retard the development of a market, which could be a problem. Given the development problems 3W nations face, they seem less likely to be able to abate early and stockpile permits, so there may be some distributive glitches early on.

 

 

I don't have adequate statistical information to really assess this proposal. For example, what % of the world’s nations is 55? How many nations are voting on the protocol? And what % do various large, developed nations represent? In general, however, the plan is doomed if too few nations participate – that would essentially lead to a "commons problem", as non-compliant nations experienced greater growth than compliant ones, but externalized the costs. This would place the signers in a modified prisoner’s dilemma, as they would each have an incentive to defect. The plan would quickly unravel. Another way to look at it is as a free rider problem, as non-signing nations will still capture the environmental benefits. Lower GHG’s are a non-excludable, non-rivalrous public good. (This paragraph points out the greatest threat to the scheme, since the usual solution to free-rider/public goods/commons problems in the intervention of state authority, with its coercive powers. But in an international frame, there is no authority to which one can appeal. Perhaps such a plan could be successfully linked to trade agreements, thereby adding an excludable benefit? Maybe also the redistribution would be an incentive to join).

On the other hand, if the bar for ratification is too high, you could wind up with a small numbers/hold out problem, as the last few to ratify attempted to extract from the others to sign. The % pollution prong gives heavy-emitting nations almost automatic veto over the terms, as it’s difficult to imagine reaching 55% without, say, the U.S. involved.

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