Transcript Slide 1

Chapter 14
Defining Water Quality: The U.S.
Clean Water Act
© 2004 Thomson Learning/South-Western
Understanding Water Resources for
Policy Development
 Identifying Water Resources and Their
Interdependence
Surface water – bodies of water open to the earth’s
atmosphere as well as springs, wells, or other
collectors directly influenced by surface water
Ground water – fresh water beneath the earth’s
surface, generally in aquifers
Hydrologic cycle – the natural movement of water
from the atmosphere to the surface, beneath the
ground and back into the atmosphere
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Understanding Water Resources for
Policy Development
 Targeting Water Quality Policy
Point Source – any single identifiable source of
pollution from which pollutants are released, such
as a factory smokestack, a pipe, or a ship
Nonpoint Source – a source of pollution that cannot
be identified accurately and degrades the
environment in a diffuse, indirect way over a
relatively broad area
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Understanding Water Resources for
Policy Development
 Setting the Policy Agenda
Water quality is important not only to protect human
health but also to protect the ecology and to ensure
that all uses of water are maintained
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Water Quality Legislation in the United
States: Overview
 Early U.S. Water Quality Laws
Rivers and Harbor Act of 1899
Water Pollution Control Act of 1948
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Water Quality Legislation in the United
States: Overview
 Evolving Toward Today’s Policy Position
Marine Protection, Research, and Sanctuaries Act
(MPRSA)
Federal Water Pollution Control Act (FWPCA)
Clean Water Act (CWA) of 1977
Water Quality Act of 1987
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Policy Objectives Under the Clean Water
Act (CWA)
 Zero Discharge Goal – a U.S. objective
calling for the elimination of all polluting
effluents into navigable waters
 Fishable-Swimmable Goal – an interim U.S.
objective requiring that surface waters be
capable of supporting recreational activities
and the propagation of fish and wildlife
 No Toxics in Toxic Amounts – a U.S. goal
prohibiting the release of toxic substances in
toxic amounts into all water resources
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Policy Objectives Under the Clean Water
Act (CWA)
 Identifying Pollutants Under the Clean Water
Act
Toxic pollutant – a contaminant which upon
exposure, will cause death, disease abnormalities,
or physiological malfunctions
Conventional pollutant – an identified pollutant that
is well understood by scientists
Nonconventional pollutant – a default category for
pollutants not identified as toxic or conventional
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Defining Water Quality: Standard-Setting
Under the Clean Water Act
 Receiving water quality standards –
state-established standards defined by use
designation and water quality criteria
 Use Designation - a component of receiving
water quality standards that identifies the
intended purposes of a water body
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Defining Water Quality: Standard-Setting
Under the Clean Water Act
 Use-Support Status – a classification of a
water body based on a state’s assessment of
its present condition relative to what is
needed to maintain its designated uses
 Water Quality Criteria – a component of
receiving water quality standards that gives
the biological and chemical attributes
necessary to sustain or achieve designated
uses
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Analysis of Receiving Water Quality
Standards
 Absence of Benefit-Cost Analysis in Setting
the Standards
Even in states’ reports to the EPA on use-support
status, benefit-cost assessment is not being done,
even though the law calls for such an analysis
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Analysis of Receiving Water Quality
Standards
 Lack of Consistency with the TechnologyBased Effluent Limitations
The link between the water quality standards and
the effluent limitations is blurred because each is
motivated differently
Standards are motivated by water usage
The effluent limits are motivated by technology
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
 Benefit-Cost Analysis of the FWPCA of 1972
Estimating the Benefits of the FWPCA of 1972
Estimating the Costs of the FWPCA of 1972
Benefit-Cost Comparison
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
Figure 14.2(a) Benefit-Cost Analysis of the U.S. FWPCA of 1972,
as of 1985
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
Figure 14.2(b) Benefit-Cost Analysis of the U.S. FWPCA of 1972,
as of 1985
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
 Advances in Benefit-Cost Analysis of U.S.
Water Quality Policy
Updated Benefit Estimate of U.S. Water Quality
Controls
Contingent valuation method (CVM) can capture
existence value as well as user value of
environmental resources
Comparable Costs of U.S. Water Quality Controls
Updated Benefit-Cost Comparison for U.S. Water
Control Policies
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
Figure 14.3 Benefit-Cost Analysis of U.S. Post-1972 Water Quality
Policy: Total Social Benefits and Total Social Costs
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Benefit-Cost Analysis of U.S. Water
Quality Control Policy
Figure 14.4 Benefit-Cost Analysis of U.S. Water Control Policy for
1985-1990: Marginal Social Cost and Marginal Social Benefit
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