Lecture 4 - Environmental Values and Environmental Valuation Flashcards

(46 cards)

1
Q

Definitions of Value

A

There are different definitions:
1. Intrinsic (more egocentric; value of nature itself not provided to humans; all nature treated equally)
2. Instrumental (what can nature give us?; value thorugh economic methods)
3. Inherent (more of an anthropocentric approach and about spiritual)
4. Ecological (nature is important for keeping up ecological system)

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2
Q

Value of Nature in Environmnetal Law

A

No international law instruments are founded purely on ecological undertanding of value of nature
- International law usually reflects anthropocentric values of nature
- Although gradual shift acknowledging biodiversity

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3
Q

The Value of Nature in Environmental Policy

A
  • Markets and societies usually undervalue nature
  • Learn about trade-offs: if one part of nature is overusd, what other parts should be less used in order to maintain critical functions?
    —> Environmental values and valuation are important from many perspectives of pivotal interest for correcting market failures, improving markets, and better policies
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4
Q

Externality

A

The impact of one person’s action on the well-being of a by-stander outside the price mechanism
- E.g. power station generations emissions of SO2 causing damage to building materials and human health.

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5
Q

Negative v. Positive Externalities

A

-Negative externality has the PC (production cost) lower than the SC (social cost) so paying less than you should be socially while positive is the opposite.

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6
Q

The Coase Theorem

A
  • Practical view on making choices
  • If a victim has property rights (and can enforce them) then will go after efficient solution whether that be paying the victim if abatement costs > damage costs, or abating polluting if damage costs > abatement costs.
    Negotiations among affected parties will result in effiicnet outcome under standard assumption of competitive markets IF property rights are well-defined
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7
Q

Applying the Coase Theorem

A
  • Provides polluters a right to pollute if they compensate the victims for damages (and if the victims have property rights).
  • The ‘optimal’ level of pollution is when the marginal benefits to the company balance the marginal costs to the community from pollution.
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8
Q

The Result of Coase Theorem and Complications that Mean NOT free market environmentalism

A
  • Requires robust legal order to assign and enforce property rights
  • Costs to negotiate (transaction costs) and procedural aspects like free riding, holdout effect, asymmetry of wealth and power, etc.
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9
Q

Stern Review (2006 and 2013)

A

Came up with ‘worst case scenario’ in ground-breaking 2006 study but then new study in 2013 said it’s actually even worse
- 2006: CC could cost b/w 5-20% of global GDP until 2100/2200 but could abate to 1-2%
- 2013: underestimated speed; emissions are rising faster than expected and some effects coming more quickly too

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10
Q

Critical Factors for Calculating the Costs of CC, its Abatement and Adaptation to it

A

-Magnitude & regional patterns of impacts
- Market impacts on humans & ecosystems including catastrophe probaility
- Abatement costs of alternative pathways
- Valuing future options (social discount rate)
- Valuation methods
- Ethical considerations: How much is a life worth?
- Non-market impacts

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11
Q

Landmark Paper Callahn and Mankin (2022)

A
  • Looked at the damages to each country form US emissions from 1990 - 2014
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12
Q

Cost-Benefit Analysis (CBA)

A
  • Balances positive and negative consequences of proposed actions TO help make a decision BUT need to be aware of dynamic changes (e.g. path dependency) and estimate value of changes to environment
  • Ekins doesn’t think should use CBA, instead use Risk-Opportunity Analysis (ROA)
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13
Q

Risk-Opportunity Analysis (ROA)

A
  • New alternative to CBA
  • Identify risks & opportunities of different courses of action
  • For estimating climate damage costs (w high risk and high uncertainty), ROA has already replaced the CBA –> ‘well below’ 2C target is a risk-based assessment from IPCC analysis and the move from 60% to 80% to ‘net zero’ in Climate Change Act
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14
Q

Natural Capital and Ecosystem Services –> UNEP Millenium Ecosystem Assessment, 2005 (what does the ecosystem do for us)

A
  1. Supporting (Soil formation, primary production, etc.) leads to
  2. Provisioning (food, freshwater, etc.)
  3. Regulating (climate, flood, etc.)
  4. Cultural (aesthetic, spiritual, etc.)
    Need to keep these balanced!
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15
Q

Direct Environmental Values

A

Values that appear directly in the utility function

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16
Q

Indirect Environmental Values

A

Influence variables that appear in the utility function (e.g. clean air is in utility function, air pollution affects it, need to know dose-response function to calculate cost of different levels of air pollution)

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17
Q

Direct methods of environmental valuation

A
  • Stated preference (SP) (e.g. CVM/contingent valuation)
  • Revealed preference (RP) (e.g. TCM, hedonic pricing)
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18
Q

Indirect methods of environmnetal valuation

A

-Production function approaches (environment as input to production of a market good)
- Damage costs, adaptation costs, repair costs, mitigation costs, etc. (e.g. WTP for medicine to cure environmental disease)

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19
Q

Types of environmnetal use values to measure:

A
  1. Direct use value (e.g. value of cropland and prices for crop)
  2. Indirect use value (e..g vlaue of forested land filtering water for surrounding communities)
  3. Non-use value (i.e. biological diversity)
    3a. Existence value (e.g. endangered species)
    3b. Option value (having the option of using at some point(
    3c. Bequest value (value of leaving undamaged environment for future generations)
20
Q

Total Economic Value Equation

A

=Use + Non Use Values
= (Direct + Indirect) + (Existence+Option+Bequest)

21
Q

WTP/WTA (Contingent Valuation Methods)

A

-WTP depends on preferences and income (has to be within budget constraint)
-WTA only depends on preferences
-Should be the same but are not because of loss aversion, property rights, intrinsic values, etc.
-In CV surveys, can’t say infinte’ WTAs (i.e. I won’t accept anyything); treated as irrational

22
Q

Theory of Welfare Economics (Kaldor-Hicks)

A

Social welfare decreases if environment deteriorates

23
Q

Natural Capital Approach

A

The environment serves important functions for economies

24
Q

Stated Preference Valuations

A

-How policy makers find a rationale for environmental policy based on surveys and voters’ preferences
a) Contingent Valuation (CV) - basically a survey estimating WTP/WTA
b) Choice Experiments (CE)
c) Benefits Transfer

25
Contingent Valuation (CV)
- A SP method - Basically a survey estimating WTP/WTA by obtaining bids for a hypothetical
26
Problems with CV
-Hypothetical martket bias (overestimating WTP) -Choice of response mode --> Ye/no, payment ladders - Information provision (issue known to public? Valuation workshops) - Voluntary/Non-Voluntary payments (free riding? Minimum required commitment)
27
Choice Experiemnts (CE)
- A SP method - Captures different attributes and how people look at them - Also called 'choice modelling' - Steps: Identify relevant attributes, derive choice sets from bundles, design questionnaires and analyse data and calcualte a WTP (implicit price) - i.e. what option would you prefer the government went ahead with? A B or C? and here are prices for each, etc.
28
Pros of CE
Pros: - Force respondents to consider trade-offs - Makes frame of reference explicit to respondents - Enables implicit prices to be estimated - Reduces incentive for respondents to behave strategically
29
Cons of CE
Cons: - What attributes should you include and how should you describe them? - How to pick a price? - How are the attributes combined in the choices? - How many choice options should be included? Accomodating Variation --> Use regression models Issues with experiment design --> Open questions, sample selection Hypothetical market bisa --> status quo bias/anchor Adding up values is sensitive so consider doing a CV is whole is more important than parts
30
Benefits Transfer
-SP Method - Practice of extrapolating existing information on one site to non-market values in another to predict compensation/equivalent variation - Often uses CV or CE tools for support; can come along with transfers of mean WTP values - Not valid unless valuation contexts are very similar
31
Revealed Preference Methods:
a) TCM b) Hedonic Pricing
32
TCM
-'RP Method TCM used to estimate benefits or costs from changes in access costs for recreational site, elimination of recreational site, etc. - How far is avg. perosn travelling to reach environmental service - Why is person making this trip?
33
Problems w TCM
- Value of time (OC of travel; separate time and costs) - Valuing place - how often and living close to high-value site may undervalue results - Choice set: Different attributes! Different statistical approaches - Measuring site characteristics: Subjective v. objective characteristis; preference heterogeneity
34
Hedonic Pricing
-RP Method Valuation of enviornmental services as they relate to value of marketed goods (e.g. housing prices: airport <-> forest). Used to estimate economic benefits or costs associated with: - Enviornmental quality (air pollution, water pollution, noise) - Environmental amenities (e.g. aesthetic views or proximity to recreation sites)
35
Problems w Hedonic Pricing
-Omitted variable bias -Multi-collinearity (check explanatory variables and simplify) -Choice of functional form (econometrics) -Market segmentation -Subjective/objective
36
Engineering Cost Method
- Method to value environment by evaluating the cost to mainain, duplicate, or replicate environmental services or natural resources (e.g. fish)
37
Production Function
In order to get particular quantity of output, we can reduce costs from MC0 to MC1 curve and this shows agricultural output improvement?
38
Application of Valuation methods to Policy
-Setting targets: socially derived to reflect safe limits and preferences; benefits may deteroriate but within a safe limit
39
QALY
-Way to value human health and life -Quality-adjusted life year (QALY) is generic measure of disease burden, including quality and quantity of life lived - Used in economic evaluation to assess value of money of medical interventions 1 QALY = one year in perfect health; if individuals health is below maximum, QALYs are accured at rate of <1/yr. - Can have negative QALYS if 'worse than dead' QALY valuations can be used to value health improvements from environmental improvement
40
VoSL (Value of Statistical Life)
-Often used by economists to consider the value of a statistical life when looking at risk/reward trafe-offs people make re: their health - VoSL is value individual places on marginal change in likelihood of death - VoSL is different from value of life --> it is value placed on changes in likelihood of death, not price to avoid certain death. - Could look at RP studies to see risks people take and how much paid to take them --> Often uses a wage hedonic approach (how wages change w job w diff risk of death) - Could also use CV by just asking people WTP for reduction in lieklihood of dying BUT irrational human valuations of risk Estimates include: $50k/yr of quality life to $9M
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Intrinsic value
Intrinsic value represents the importance of nature by itself regardless of human uses and experiences
42
Instrumental value
Instrumental value refers to the importance of nature to satisfy human needs, interests and preferences through the provision of benefits (such as food, energy and materials)
43
Relational value
Relational value refers to the importance of the meaningful relationships between people and nature and among people within nature
44
Inherent value
Nature has value for humans, but in non-economic, deeper cultural or spiritual ways.
45
Ecological value
Ecological value refers to the importance of ecosystems, species, habitats, and ecological processes in maintaining the structure, function, and resilience of the natural environment. As recognized by the Millennium Ecosystem Assessment and the Convention on Biological Diversity, ecological value encompasses the essential roles that natural systems play in sustaining biodiversity, regulating climate, purifying water, supporting nutrient cycles, and ensuring the overall stability and adaptability of ecosystems. This concept is foundational in environmental law, conservation planning, and sustainable development, as it guides the identification and protection of ecologically significant areas and informs decisions that affect the health of the planet.
46
Characteristics theory of value
The value of something is best explained in terms of the characteristics or attributes of that thing, and any thing (e.g. a forest) is actually a bundle of attributes and what people value is this bundle