assessing costs and benefits of environmental policies & regulations how do we quantify costs?...
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Assessing Costs and Benefits of Environmental Policies & Regulations
How do we quantify costs?
How do we quantify benefits?
Whose costs and benefits?
Recall cookbook: want to account for all significant costs and benefits.
Also recall Tuolumne study – many environmental costs excluded, costs of dam still outweigh benefits (lesson: if you don’t have to rely on non-use values, then don’t)
Important to include costs & benefits over time – use NPV formulation (or E[NPV] if uncertainty).
Costs
Direct costsEg, equipment purchases
Indirect costsEg, consumers forced to buy lower quality low
emission vehicles (LEV’s)
Q, LEV’s
Price
. ...Subsidy
Loss from mandate
Costs (cont)
Lower productivity associated with requiring water based instead of oil based paints
Administrative and compliance costs
Benefits: Types of values
Market values: Commodities traded in
markets or values directly reflected in markets
Usually from direct-use Often “derived demand” Recall, markets ignore
externalities; may misrepresent public good
Non-market values Commodities that
have value to humans, but whose value cannot be measured within a market.
Includes Use and Non-Use Values
Use vs. non-use values
Use values Value from
consumption of a good Current use, expected
future use, possible use
Direct health impacts Non-health impacts
(e.g. smell) Damage to
ecosystems: pollution degrades performance
Non-use values Measurement is
controversial Existence value,
altruistic value, bequest value
Examples
Market values 1 mbf Douglas Fir 1 ton SOx in
RECLAIM 1 ton halibut in Alaska Red cockaded
woodpecker in south Pharmaceutical
potential of natural compounds
Non-market values Sea otters on south
coast Air/water quality Strong swell off Coal
Oil Point Oil spill off Spain Yosemite Nat’l park Golden trout in Sierras
Measuring demand
Revealed preference Observe a real choice
in market; infer value E.g. Value of living
near urban open space: Compare housing prices w/ and w/o urban open space.
Hedonics, Travel Cost, Household production
Stated preference Ask people (survey)
how much they value environmental goods
E.g. Would you accept a $0.05 increase in gas price to require double-hull oil tankers?
Contingent valuation
Some examples of measuring demand Demand for park recreation
Channel Islands MPA Demand for health risk reductions
Seeps off Coal-Oil PointMorbitityMortality
Using Benefits Transfer Methods
Example: Nat’l park fees
Yosemite National Park charges $20 entrance fee, 3 million visits.
Want to use bus to eliminate cars in the Valley to improve recreational experience.
Want to increased fee to pay for bus ($10 million per year).
Will increase to $30 pay for bus? Wrong calculation: $10*3 million = $30 mil
Change in nat’l park entrance fee
Demand for Park Visits
$
QQ20
20 D E
F
Revenue before fee increase: ODEF
O
EntranceFee
Change in nat’l park entrance fee
Demand for Park Visits
$
QQ20Q30
30
20 D
A B
E
C F
Revenue after fee increase: OABC
O
EntranceFee
Change in nat’l park entrance fee
Demand for Park Visits
$
QQ20Q30
30
20 D
A B
E
C F
Will a fee increasefrom $20 to $30 payfor the bus system?ABCO-DEFO > $10 mil?
O
EntranceFee
Human health values
How estimate monetary value of changes in health from environmental change?
2 steps: (1) environmental change to health impact,(2) change in health to $$ [where possible].
Distinguish between mortality (death), morbidity (illness)
Often disaggregate according to: age, sex, physical condition, etc…
Mortality
Crude mortality rate = # deaths per time/relevant population…interpreted as probability of dying.
How will change affect probability of dying? In expectation, how many more people will
die (or how many fewer will die) Total value = $/life * lives. Lead in water: $2.5 million per death
avoided, 2.5*622 = $1.6 billion.
Morbidity (sickness)
Chronic or acute, degree of impairment, type of symptom
“restricted activity days”, “bed disability days”, “work loss days”, “symptom days”
Clean Air Act: protect individuals from adverse health effects.
Lead: $1 million/non-fatal heart attack, $628/case reduced chance of hypertension
Benefits transfer approach
See Rosenberger & Loomis, 2000. The application of existing information &
knowledge to new contexts Useful when collecting primary data and
analysis is impractical (cost or time) 3 important features
1. Policy context must be well-defined2. Data must meet certain criteria3. Study site and new site should correspond
Example: Orange County Oil Spill
Oil tanker spills at Huntington Beach, 2001 Beaches in southern Orange County closed for
month+ Big loss: lost beach recreation days Benefits transfer: value of lost beach
recreation days at other beaches
Sample of other studies:
Policy context
Identify extent and type of impacts from proposed action
Identify affected population Identify data needs of assessment
Type of measure, kind of value, degree of uncertainty, etc.
Study site data requirements
Make sure study site data & analysis technique are sound
Study site analysis contains details (for comparison) of physical & socioeconomic characteristics, & reports statistics
Correspondence between sites
Similar expected change in resource quality and quantity.
Markets in two sites are similar; demographics are similar.
Condition and quality of environmental good is similar.
Limitations of benefit transfer Quality of original study The more primary studies, the better. Primary data vs. summary statistics
(may limit ability to conduct new analysis).
Characteristics of sites may differ, Assumptions made in original study
that do not apply.
Approaches to benefit transfer
Value transfer Point estimate(s) from
study site Identify change,
translate into physical impact (e.g. use), identify applicable study sites, select (range of) benefit measures, calculate $ value.
Function transfer Demand or benefits
function from study site. Identify change,
translate into physical impact, identify applicable study sties, determine if demand function available, adapt demand (benefit) function to fit new site.
Next 2 lectures
Revealed Preference Hedonics Travel Cost Household Production
Stated Preference/ Constructed Markets Contingent
Valuation