Efficient Voter Rule

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In the study of voter behavior, the efficient voter rule speaks to the desirability of voter-driven outcomes. It applies to situations involving negative externalities such as pollution and crime, and positive externalities such as education. Related efforts to achieve socially optimal quantities of externalities have long been a focus of microeconomic research, most famously by Ronald Coase [1] and Arthur Pigou. [2] Externality problems persist despite past remedies, which makes newer approaches such as the efficient voter rule important.

Contents

In the context of negative externalities, the efficient voter rule states that when individuals who receive the same harm from a problem vote on whether to eliminate that problem at a uniform cost per individual, the outcome will be efficient, regardless of each individual’s contribution to the problem. [3] The Rule applies similarly to positive externalities, as exemplified by the solar panel example below.

The efficient voter rule indicates that voting on a collective action or policy change should lead to an efficient outcome. [4] Possible applications include policy decisions about clean energy, noise pollution, over-fishing, mandatory immunizations, smoking bans, zoning, septic systems, and fuel economy standards.

In the context of crime, recent applications include votes on the strict enforcement of traffic laws. The vote in Tucson, Arizona, on whether to use cameras to catch drivers who run red lights provides one example. The community voted against this strict level of enforcement. According to the efficient voter rule, this outcome indicates that community members collectively received a greater benefit from occasionally skirting the law than from protection from malfeasance.

The literature [5] [6] explains why the efficient voter rule applies even if individuals cause differing levels of damage and if a given amount of damage from each individual is completely external.

Example

Consider a policy proposal to require each of the 100 households in an economy to rent a solar panel that costs $400 per year, net of the value of the energy provided to the user. Suppose each panel would prevent $600 worth of harm from pollution in the economy each year. The pollution is uniformly distributed, so each of the 100 households incurs 1/100 × $600 = $6 worth of the harm that could be avoided by each panel yearly.

Although society's $600 annual benefit from each panel exceeds the $400 annual cost, each household only internalizes $6 worth of the environmental benefit—far less than the rental cost of a panel. So the privately optimal decision is to not rent a panel.

To reach the socially optimal decision, residents could vote on the policy proposal. If enacted, the policy would cost each household $400 per year. The total damage each household would avoid each year if the policy were enacted—the household's annual benefit from policy enactment—would be 100 x $6 = $600. So the voting mechanism causes each household to internalize the entire $600 yearly benefit to society of purchasing a panel, and the incentive is for households to vote in favor of the socially optimal policy.

Suppose instead that each panel would prevent only $300 worth of harm from pollution in the economy each year, again spread uniformly among 100 homes. In that case, it would not be socially optimal for residents to purchase panels, because the $400 annual cost would exceed the $300 annual benefit. Again, a vote would yield the socially optimal solution: If the policy were implemented, each resident would avoid its 1/100 x $300 = $3 share of the harm from each of 100 panels yearly, but this $300 benefit would fall below the $400 annual cost of a panel, so each resident would vote against the requirement and collectively the community would achieve the socially optimal outcome.

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<span class="mw-page-title-main">Ronald Coase</span> British economist and Nobel laureate (1910–2013)

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In economics, an externality or external cost is an indirect cost or benefit to an uninvolved third party that arises as an effect of another party's activity. Externalities can be considered as unpriced goods involved in either consumer or producer market transactions. Air pollution from motor vehicles is one example. The cost of air pollution to society is not paid by either the producers or users of motorized transport to the rest of society. Water pollution from mills and factories is another example. All consumers are made worse off by pollution but are not compensated by the market for this damage. A positive externality is when an individual's consumption in a market increases the well-being of others, but the individual does not charge the third party for the benefit. The third party is essentially getting a free product. An example of this might be the apartment above a bakery receiving the benefit of enjoyment from smelling fresh pastries every morning. The people who live in the apartment do not compensate the bakery for this benefit.

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References

  1. Coase, Ronald (1960). "The Problem of Social Cost". Journal of Law and Economics. 3: 1–44. doi:10.1086/466560. S2CID   222331226.
  2. Pigou, Arthur (2016). The Economics of Welfare. London: Wentworth. ISBN   978-1361970485.
  3. Anderson, David A. (2019). Environmental economics and natural resource management (Fifth ed.). Abingdon, Oxon. ISBN   9781351121477. OCLC   1055566815.{{cite book}}: CS1 maint: location missing publisher (link)
  4. Anderson, David A. (2020). "Environmental Exigencies and the Efficient Voter Rule". Economies. 8 (4): 7. doi: 10.3390/economies8040100 . hdl: 10419/257149 .
  5. Anderson, David A. (2011). "A Voting Approach to Externality Problems" (PDF). Journal of Economic and Social Policy. 14: 10. S2CID   55775170. Archived from the original (PDF) on 2019-02-24.
  6. Anderson, David A. (2020). "Environmental Exigencies and the Efficient Voter Rule". Economies. 8 (4): 7. doi: 10.3390/economies8040100 . hdl: 10419/257149 .

Further reading