Chapter 14 & 15 Flashcards

1
Q

Different types of stock pollutants

A

Stock pollutants: Ökar over time due to the environment’s limited ability to absorb them. Examples include heavy metals and synthetic chemicals. These pollutants persist and cause long-term damage.

Fund pollutants: The environment can absorb them up to a certain level without long-term accumulation, such as organic waste or carbon dioxide. If emissions exceed the absorptive capacity, they behave like stock pollutants.

Local pollutants: Cause damage near the source of
emissions while regional pollutants cause damage
at greater distances.

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1
Q

What is Marginal Damage?

A

Marginal damage in the context of pollution refers to the additional harm or negative impact caused by emitting one more unit of pollution. It represents the increase in damage to the environment, human health, or the economy that occurs as pollution levels rise.

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2
Q

What is Marginal Control Costs?

A

These are the additional costs associated with reducing one more unit of pollution. As more pollution is reduced, the marginal control cost typically increases because finding and implementing ways to cut down further emissions becomes more expensive.

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3
Q

How is the Marginal Damage and Marginal Control Costs interconnected?

A
  • The relationship between marginal damage and marginal control costs is crucial for determining the optimal level of pollution control.
  • The goal is to find the point where marginal control costs equal marginal damage. At this level, the cost of reducing one more unit of pollution (MCC) is exactly balanced by the benefit of avoiding additional harm (MD). This balance minimizes the total social costs of pollution by avoiding excessive pollution and unnecessary control costs.
  • When the harm caused by an extra unit of pollution is greater than the cost to reduce it, more pollution reduction is beneficial. It means society would gain more from avoiding the damage than it would cost to control the pollution.

*When the cost to reduce an extra unit of pollution is higher than the harm it would prevent, it is not efficient to reduce further. In this case, the resources used for additional control could be better spent elsewhere.

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4
Q

Efficient Allocation (Q)

A

Efficiency is achieved when the marginal damage of pollution equals the marginal cost of controlling it. Reducing pollution beyond this point raises costs without enough benefit, while less control increases damage costs.

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5
Q

What is the Horizontal dimension?

A

Describes whether pollutants affect local (near the emission source), regional, or global areas.

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6
Q

What is the Vertical dimension?

A

Indicates whether pollutants cause damage at ground level (e.g., particulates) or in the upper atmosphere (e.g., greenhouse gases).

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7
Q

What is a market failure?

A
  • Occurs when the market, left on its own, fails to allocate resources efficiently, leading to overproduction or underproduction of goods and services.
  • In the case of pollution, the failure lies in the fact that the full costs of production are not reflected in the market price of goods or services. This happens because some costs, such as the harm caused by pollution, are externalized to society rather than being borne by the producer.
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8
Q

How could government intervention ease these issues?

A

Implement policies like pollution limits or emission taxes can internalize the costs.

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9
Q

Problems with government interventions

A
  • Challenges of Information Burden: Authorities lack precise information on the marginal costs of pollution control and damage for each emitter. This makes it difficult to allocate responsibility effectively.
  • Cost-Effective Allocation: The goal is to meet predetermined pollution levels at minimum cost. For uniformly mixed pollutants, the focus is on controlling total emissions while minimizing control costs. Cost-effectiveness is achieved when the marginal costs of control are equalized across all emitters.
  • Example of Cost-Effective Allocation: Using an example with two pollution sources, a 15-unit emission reduction is necessary. The most cost-effective allocation would have one source reduce 10 units and the other reduce 5 units. Any other distribution would increase total costs.
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10
Q

Different Policy instruments

The “command-and-control” approach

A

Also referred to as emission standard. It’s a legal limit on the amount of the pollutant an individual source is allowed to emit.

Technology requirements: Requiring firms to use specific pollution control technologies or practices, such as installing scrubbers on smokestacks.

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11
Q

What is the key idea of emission charges?

A
  • The key idea is that firms will try to reduce pollution in the cheapest way possible. If a firm can reduce pollution at a lower cost than the fee, it will choose to reduce its emissions instead of paying the charge.
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12
Q

How can emission charges work in reality?

A

By using incentive-based policies like emissions charges or trading, authorities can achieve pollution reduction in a cost-effective manner without needing detailed information on each firm’s control costs.
These methods rely on firms’ self-interest to reduce emissions efficiently.

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13
Q

What is emission charges?

A
  • It’s not a governmental intervention in the same way as command-and-control.
  • Also referred to as pollution taxes.
  • Market regulated.
  • Instead of setting a fixed limit on emissions, the government charges a fee for each unit of pollution emitted by a firm.
  • This creates a financial incentive for firms to reduce emissions on their own. Firms that can reduce emissions at a lower cost than the charge will do so, while firms with higher costs will choose to pay the fee.
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14
Q

Comparison between command-and-control & emission charges/trading?

A

Command-and-control: Less flexible, as all firms must meet the same standards regardless of their individual circumstances.

Emission charges: More flexible, as firms can decide how much to reduce emissions based on their own costs.

Command-and-control: May not achieve the most cost-effective pollution reduction, since it doesn’t consider the different costs faced by firms.

Emission charges: Tend to be more cost-effective because firms with lower abatement costs will reduce more, while firms with higher costs may reduce less and pay the fee.

Command-and-control: Provides limited incentives for firms to find new ways to reduce pollution beyond the required standards.

Emission charges: Encourage firms to innovate and find cheaper ways to reduce emissions in order to avoid paying the charge.

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15
Q

What is the cap-and-trade system?

A

**Emission ChargesEmission trading
*
* * Emissions Cap: Authorities set an overall limit on the total amount of pollution that can be emitted by all firms combined. This is known as the cap.

  • Allowances: The cap is divided into allowances, with each allowance permitting a firm to emit a specific amount of pollution (e.g., one ton of CO2). Authorities distribute or sell these allowances to firms.
  • Trading: Firms can buy or sell allowances. If a firm can reduce its emissions at a lower cost, it might have extra allowances to sell. If reducing emissions is expensive for a firm, it may choose to buy additional allowances from other firms.
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16
Q

How does the cap-and-trade system work?

A
  • Firms with lower control costs will sell allowances, while firms with higher costs will buy them. This trading continues until a cost-effective allocation is reached, where marginal control costs are equalized across firms.
  • Cap-and-trade achieves a cost-effective allocation without the need for authorities to know individual control costs. The market mechanism ensures emissions reductions at the lowest possible cost.
  • Whether allowances are gifted or auctioned, the final result is the same: a cost-effective distribution of pollution reduction responsibility.
  • Cap-and-trade avoids the trial-and-error issue of emissions charges and is highly flexible, making it a prominent method in pollution regulation reforms. However, its applicability in developing countries remains a topic of debate.
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17
Q

What is the trial-and-error issue of emission charges?

A

Refers to the challenge of setting the correct level for the pollution charge or fee in order to achieve the desired level of emissions reduction.

18
Q

What are the arguments for developing countries to use marked-based instruments for pollution control?

Pro arguments

A
  • Proponents argue that developing countries should adopt market-based approaches due to their potential for cost-effectiveness in controlling pollution, especially given the high poverty levels and need for revenue in these nations.
  • Some developing countries already implement such systems, suggesting a precedent for further adoption.
19
Q

What are the arguments for developing countries to use marked-based instruments for pollution control?

Arguments against

A

*Critics caution against directly applying lessons from industrialized nations, emphasizing that developing countries often lack the necessary infrastructure for effective monitoring and enforcement of these systems.

  • The absence of strong systems may diminish the advantages of market-based instruments.
  • A middle ground acknowledges that while market-based instruments may not be universally applicable in developing countries, they are not entirely unsuitable.

*Capacity building and infrastructural improvements are seen as essential steps before implementing these systems effectively.

20
Q

Pro arguments for emission charges

A
  • The fees collected generate revenue for the government, which can be substantial depending on the level of emissions and the set charge.
  • Use of Revenue: This revenue can be used to replace distortionary taxes (like income or sales taxes), which can discourage economic activity. For instance: The government can lower other taxes, making it cheaper for people and businesses to earn and spend money.
  • Revenue can also fund public programs, especially those that help low-income households, such as subsidies for clean energy or public transportation.
21
Q

Benefits of cap-and-trade systems

A
  • If allowances are auctioned, the government can generate revenue from the sale of these permits. This revenue can similarly be used to reduce other taxes or fund public services.
22
Q

Disadvantages of cap-and-trade systems

A
  • If allowances are given away for free instead of sold, the government does not collect revenue. This can lead to some unintended consequences:
    Free allowances can result in windfall profits for companies that receive them without having to pay for them. This may not be equitable or beneficial for society as a whole.
  • Free allowances can disproportionately benefit larger firms or wealthy entities, as they may not face the same costs as smaller firms or lower-income communities.
  • If low-income households live in areas with higher pollution levels (like near industrial zones), they might suffer more from pollution-related health issues, while not benefiting from the profits made by firms that receive free allowances. This can lead to a regressive impact, where the poorer communities bear more of the burden without adequate support or compensation.
23
Q

Efficient Ambient Charge

A
  • An ambient charge is a fee that polluters pay based on the impact of their emissions on the environment. In this case, it’s related to the concentration of pollutants at a certain location (called the receptor).
  • This is a measure of how much pollution from a specific source increases the pollution level at the receptor. For example, if a factory emits pollutants into the air, the transfer coefficient indicates how much of that pollution actually reaches the nearby community.
24
Q

Ambient allowance

A
  • An ambient allowance is a permit that lets the holder contribute a certain amount to the pollution concentration at the receptor. It essentially allows the polluter to raise the concentration of pollutants in that specific area by a specified amount.
  • By holding an ambient allowance, a firm is permitted to emit a certain amount of pollution that will cause the ambient pollution concentration to increase by a particular level at the receptor. The total number of allowances distributed or sold would be limited to ensure that the pollution concentration does not exceed a safe or acceptable level.
25
Q

What is “The Revenue Effect”?

A

The Revenue Effect
* Environmental taxes and auctioned allowances
raise revenue.
* Free allocation of allowances does not.

26
Q

How can emission charges result in political resistency?

A
  • Emission charges make it more expensive for businesses to emit pollutants, increasing their operating costs, higher prices for goods and services,
  • Companies may argue that emission charges put them at a competitive disadvantage, especially if their competitors in other regions or countries do not face similar charges
  • f businesses pass on the additional costs from emission charges to customers, it can result in higher prices for everyday goods and services. This can be particularly burdensome for lower-income households, making the policy unpopular with the public.
27
Q

The clean air act

A
  • Originally in 1963, the Clean Air Act was the first legislation aimed at reducing air pollution in the U.S.
  • The law became comprehensive and effective with the Clean Air Act Amendments of 1970, which significantly strengthened air quality regulation.
  • The amendments set the stage for the federal government to take a more active role in air pollution control, setting national standards for the first time.
  • The Environmental Protection Agency (EPA) was established in 1970, around the same time as the Clean Air Act Amendments. he EPA was created to oversee and enforce federal environmental regulations, including the new air quality standards set by the amendments.
  • The 1970 Amendments marked a major shift by introducing National Ambient Air Quality Standards (NAAQS), which set limits on the concentration of specific pollutants in the air to protect public health and the environment.
28
Q

Threshold Concept

A

This idea suggests that there is a specific level of pollutant concentration (threshold) below which no harm occurs to human health or the environment.

29
Q

Issues with the Threshold concept

A

Critics argue that even low levels of some pollutants can still have harmful effects, meaning that setting a threshold might not fully protect public health. Conversely, setting a very strict threshold could lead to excessively high costs without corresponding health benefits.

30
Q

Uniform standars issue

A
  • The National Ambient Air Quality Standards (NAAQS) set by the EPA are applied uniformly across the U.S., regardless of regional differences in pollution sources, population density, or geography.
  • A one-size-fits-all approach may not be cost-effective because the benefits and costs of reducing pollution can vary significantly between regions. For example, it may be more costly to meet the standards in urban areas with higher pollution levels compared to rural areas with cleaner air.
31
Q

The timing of emission flows

A
  • The timing of emission flows is crucial when dealing with pollutants because the concentration levels of these pollutants in the air can vary significantly based on when emissions occur.
  • When emissions occur can influence how much of the pollutant accumulates in the air and the resulting concentrations. For example, if emissions are higher during certain times of the day (such as rush hour), pollutant levels can spike, leading to short-term peaks in air pollution
  • Seasonal Variations: Emissions might have different impacts during different seasons. For instance, ozone levels tend to be higher in the summer due to increased sunlight, which accelerates the chemical reactions that form ozone from other pollutants.
  • Short-Term Exposure Risks: High concentrations of criteria pollutants, even over short periods, can cause immediate health problems, such as respiratory issues and cardiovascular stress.

*

32
Q

Criteria pollutants & concentration

A
  • Criteria pollutants are a group of air pollutants regulated by the EPA due to their harmful effects on human health and the environment. These include ozone, particulate matter, carbon monoxide, sulfur dioxide, nitrogen dioxide, and lead.
  • The concentration of these pollutants in the atmosphere (i.e., the amount present in a given volume of air) is what determines their impact on health and the environment.
33
Q

Command-and-control and its issues

A

Shown be less cost-effective, one-fits-it-all approach! without considering the variability in control costs across firms.

Additionally, regulations often lack flexibility in timing, raising compliance costs.

34
Q

Phased compliance

A

Tillåter företag att gradvis uppfylla regleringskrav över tid, istället för att omedelbart behöva följa strikta standarder.

35
Q

Banking of emission allowances

A

I detta system kan företag spara oanvända utsläppsrätter för framtida bruk, istället för att behöva använda dem inom den aktuella efterlevnadsperioden.

36
Q

Phased compliance and its benefits

A

Flexibilitet: Företag kan planera och investera i teknik för att minska föroreningar i en takt som passar deras verksamhet, vilket hjälper till att undvika plötsliga ekonomiska påfrestningar.

Kostnadseffektivitet: Genom att sprida ut efterlevnaden över tid kan företag välja när de ska investera i teknik baserat på sina operativa behov och ekonomiska förhållanden.

37
Q

Ambient standards

A

Ambient standards refer to the legal limits set for the concentration of pollutants in the outdoor air (the ambient environment) to protect public health and the environment. These standards specify the maximum allowable levels of certain pollutants, such as ozone, particulate matter, sulfur dioxide, nitrogen dioxide, carbon monoxide, and lead, over a specific period.

38
Q

The issue in implementing this in developing countries

A
  • This trend is typical among industrialized nations, which have generally improved both emissions levels and ambient air quality.
  • Conversely, air quality in many developing nations continues to deteriorate. These countries struggle with balancing environmental policies and economic development needs, as they often cannot afford costly, inefficient pollution control strategies.
39
Q

Pollution charge system in Japan

A
  • The pollution charge system is designed so that companies pay fees based on the costs of compensating for past pollution-related damages. This means that the fees reflect the expenses associated with compensating people for health issues or environmental damage caused by pollution in previous years.
  • The high charges create a significant financial incentive for companies to further reduce their emissions. Since companies are required to pay fees that are tied to past compensation costs, they can lower their overall costs by minimizing pollution, thus avoiding or reducing these charges.
40
Q

“Dilution is the solution”

A

Was a common approach to managing air pollution, which involved using tall smokestacks to disperse pollutants into the atmosphere. The idea was that by releasing emissions higher up, pollutants would be diluted over a larger area, reducing their concentration at ground level and minimizing local pollution problems.

By dispersing pollutants over a wider area, immediate local air quality could be improved, as the concentration of harmful substances near the ground would be lower.

Building taller stacks was a relatively simple and inexpensive solution for industries looking to reduce the impact of their emissions without significantly changing their operations.

Failed to Address Regional Pollution: While the “dilution” approach could reduce local concentrations, it did not eliminate the pollutants themselves. Instead, it merely spread the pollutants over a larger area, which often resulted in regional environmental issues.

41
Q

Emission Trading/Cap-and-trade

A
  • The shift toward emissions trading in managing pollution, especially for sulfur dioxide (SO₂), came about because of economic insights into the rising costs of achieving significant reductions in emissions.

*

42
Q

Results of CAT

A
  • The ability to “bank” allowances (save for future use) allowed for a more efficient allocation of abatement costs over time, smoothing out fluctuations in compliance costs.
  • In 2011, the Cross-State Air Pollution Rule (CSAPR) limited trading to within states, leading to a collapse in the SO2 allowance market and a sharp decline in prices.
43
Q

The most important components to have a successful cap and trade system…

A
  • Successful cap-and-trade programs require careful design and adjustments, including provisions for banking and mechanisms like price collars (auction price floors and ceilings) to manage price volatility.
  • Economic Context Matters: The broader economic environment, including energy market changes, can significantly influence program outcomes.

*