Chapter 8: Risk Reduction and Environmental Justice
Poor neighborhoods in our cities suffer must often from toxic
pollution. Cleaning up the toxic wastes will create new jobs in
these neighborhoods for those people and make them safer places
to live, to work, and to do business.
President Bill Clinton
Although pollution affects all people, no matter where they live,
direct exposure to pollutants and other environmental hazards
are disproportionately distributed. Some studies have indicated
that low-income, racial and ethnic minorities are more likely
to live in areas where they face environmental risks.
Actions to reduce environmental risks will depend on analysis
of toxic substances and of how they are created by the flow of
materials in the U.S. economy (see Chapter 9: Environmental Economics).
The variety of materials used to manufacture the goods that have
become an essential part of modern society-machines, housing,
roads, cars, packaging, and other consumer products-has increased
over the years. The impacts of these uses on the environment are
increasing and may disproportionately impact minorities and low-income
communities in proximity to the manufacturing processes.
As material flows increase, the waste products from extraction,
processing, use, and ultimate disposal of materials also increase.
Only a combination of change in industry practice, new technology
development, shift in material use, and change in consumer behavior
will change the growing residuals-producing trend. Otherwise current
environmental problems may worsen since the ability of the environment
to absorb waste products is limited.
Since the earliest days of U.S. industrial development, substantial
volumes of waste have been produced and disposed of in ways that
created problems for current and future generations. Wastes generated
in the home or workplace were swept away, buried, or poured down
drains or directly into streams, rivers, lakes, and oceans. Some
were sold as fill for uneven ground or marsh. Much was burned
in local stoves or community incinerators, and even more was dumped
in backyards, backlots, and rural backroads.
The major development in solid and hazardous waste management
in 1993 was continued groundwork on congressional reauthorization
of the Resource Conservation and Recovery Act (RCRA), as revised
by the Hazardous and Solid Waste Amendments of 1984, and of the
Superfund legislation.
Many areas of the United States face serious problems in safely
and effectively managing the waste that they generate. As the
nation generates more trash than ever before, the limits to traditional
waste management practices become obvious. Many landfills and
combustors have closed, and new waste disposal facilities are
difficult to site. Some communities are paying premium prices
to transport waste long distances to available facilities. Other
communities have found creative solutions through source reduction
and recycling programs, but much still needs to be done.
The generation of municipal solid waste grew steadily between
1960 and 1990 (the latest date for which data are available),
from 88 million to 195 million tons per year. Per capita generation
increased from 2.7 pounds per day in 1960 to 4.3 pounds per day
in 1990.
By the year 2000, total municipal solid waste generation is projected
to be 222 million tons per year with a per capita waste generation
of 4.5 pounds per day. These projections, which represent a slowdown
of waste production rate, hinge on hard-to-predict variables,
such as the following:
. Demographic changes,
. Economic factors,
. Consumer preferences such as lighter packing materials,
. Social trends such as decline in newspaper readership,
. Source reduction such as backyard composting,
. Packaging reduction, and
. Production of more durable goods.
Resource recovery-materials removed from the wastestream for recycling
or composting-has gradually increased from 7 percent of the municipal
solid waste generated in 1960 to 17 percent in 1990. Projected
recovery rates are 20-30 percent in 1995 and 25-35 percent in
the year 2000. To achieve these recovery rates, some products
will have to be recovered at rates of 50 percent or more, and
the nation will have to achieve substantial composting of yard
trimmings.
Incinerators or combustors handled 30 percent of the municipal
solid waste generated in 1960, most of them with no energy recovery
and no air pollution controls. In the 1960s and 1970s, combustion
dropped steadily as old incinerators were closed, reaching a low
of 10 percent of municipal solid waste generated by 1980. More
recently combustion has increased to 16 percent in 1990. All major
new facilities have energy recovery and are designed to meet air
pollution standards. Projected estimates of combusted municipal
solid waste (35 million tons in 1995 and 46 million tons in 2000)
are based on an assumption that the facilities will operate at
80 percent of capacity.
The amount of waste sent to landfills fluctuates with changes
in the use of alternative municipal solid waste management methods.
In 1960 approximately 62 percent of municipal solid waste was
sent to landfills. This increased to 81 percent in 1980, then
decreased to 67 percent in 1990 as the result of changing trends
in combustion and recovery rates.
The EPA waste reduction program implements a national strategy
for businesses, which provides guidance on waste prevention and
recycling and on improving and expanding markets for recycled
products. Municipal landfills, however, remain an integral part
of solid waste management. As federal regulations on landfills
are phased in, landfills will become safer for adjacent communities
and for the environment. In 1993 the EPA maintained partner-ships
with states, tribes, industry, and individual citizens to keep
landfills from becoming sources of pollution.
The Resource Conservation and Recovery Act and its amendments
provide the legislative mandate for a nationwide program to protect
human health and the environment from the risks of hazardous and
solid wastes. The RCRA program, the world's largest, most stringent
regulatory program for managing wastes, has revolutionized the
waste management industry. It has spawned new partnerships in
waste management and new technology in waste prevention and reduction.
In 1993 the RCRA program, administered by the EPA, emphasized
risk- based management standards. To develop hazardous and solid
waste management strategies that ensure equitable and efficient
program implementation, the agency is taking the following actions:
. Focus resources on areas presenting the greatest risk to human
health and the environment;
. Work in partnerships with states to carry out national waste
management objectives;
. Emphasize pollution prevention, source reduction, waste minimization,
and recycling in EPA regulations; and
. Develop new regulations and revise existing ones to incorporate
the latest science and technology for the safe disposal and processing
of hazardous and solid waste.
In 1993 the EPA focused RCRA initiatives on environmental justice
through siting, permitting, public involvement, corrective action,
disproportionate impacts, and Native American tribal issues. For
example the EPA is expanding public involvement and improving
its own ability to include environmental justice in public health
considerations and to assure that priority-setting methods adequately
address environmental justice concerns.
Hazardous Waste Management. The RCRA encourages hazardous
waste generators to minimize waste products through process or
equipment changes and recycling. The result has been a 17-percent
decline in the amount of RCRA hazardous waste generated in the
United States.
Strategy on Combustion and Waste Minimization. In 1993
the EPA developed a strategy that defines the appropriate roles
for hazardous waste incineration and applies economically sound
source reduction practices to achieve an integrated waste management
program. The strategy strengthens technical controls on waste
incineration and increases opportunities for public participation
in the permitting process. The new controls will be based on the
latest, most viable technical advances in risk assessment and
management. Using extensive risk assessments at facilities burning
hazardous waste, the EPA will issue guidance concerning assessments
of direct and indirect exposure at specific sites. Increased EPA
presence at commercial hazardous waste combustion facilities will
support state inspections and enforcement.
Strategy for Corrective Action through Stabilization. The
EPA can require corrective actions to address all releases of
hazardous waste or hazardous constituents from any facility required
to have a RCRA hazardous waste permit. The agency has begun implementing
a strategy to increase the number and pace of cleanups at RCRA
treatment, storage, and disposal facilities that require corrective
action. This strategy of corrective action stabilization emphasizes
controlling the immediate spread of contamination as soon as feasible.
Comprehensive facility cleanup is the long-term goal for the program,
but corrective action stabilization emphasizes the immediate need
to control releases at hazardous waste facilities. It allows the
EPA and the states to address the most serious releases at a larger
number of facilities in a shorter period of time. In 1993 approximately
1,000 hazardous waste facilities were candidates for stabilization
action.
Underground Storage Tanks. Petroleum or hazardous substances
that escape from underground tanks can contaminate drinking water
supplies. Fumes from these tanks can cause fires and explosions
and pose other health hazards. The RCRA amendments require tank
owners and operators to register their tanks and comply with leak
prevention, corrective action, and financial responsibility regulations.
As of August 1993, states and private parties had confirmed 227,000
releases, initiated 174,000 cleanups, and completed 79,000 cleanups
of leaking underground storage tanks. The EPA is working with
states to streamline corrective action processes and encourage
the use of improved technologies to help keep pace with the growing
cleanup workload. When a responsible party for a tank cannot be
found to oversee corrective action, the EPA authorizes states
and territories to use the Leaking Under ground Storage Tank Trust
Fund for cleanups. Approximately 86 percent of these funds were
disbursed to states in 1993 for cleanup activities.
The Comprehensive Environmental Response, Compensation, and Liability
Act (CERCLA) and its amendments established the Superfund program
as a response to the release or threatened release of hazardous
substances, pollutants, and contaminants stemming from accidents
or uncontrolled hazardous waste sites. The act requires parties
responsible for contamination to conduct the cleanup. Where EPA
enforcement is not successful, the federal government can clean
up a site using the CERCLA Trust Fund (Superfund), which is supported
by excise taxes on feedstock chemicals and petroleum and by a
more broadly based corporate environmental tax. If the Superfund
program conducts the cleanup, the government can take court action
against responsible parties to recover up to three times the cleanup
costs.
Now more than 12 years old, the Superfund program has reduced
risks posed to human health and to the health of ecosystems from
releases of hazardous substances. As part of the program, the
EPA will establish, by the end of FY 1995, community advisory
groups to address environmental justice issues in the vicinity
of Superfund sites. A summary of Superfund initiatives follows.
Site Evaluations. As of June 30, 1993, the EPA had identified
37,921 potentially hazardous waste sites across the nation. Of
these sites, 94 percent have undergone a preliminary assessment
to determine the need for further action.
National Priorities List. The EPA maintains the Superfund
National Priorities List (NPL), which identifies the nation's
most seriously contaminated hazardous waste sites eligible for
permanent Superfund cleanup. As of June 30, 1993, a total of 1,320
sites had been listed or proposed for listing; work was underway
at 93 percent of the these sites, and cleanup construction was
in process or complete at 43 percent. In FY 1992 permanent cleanup
construction had been completed at 149 sites since inception of
the program. In FY 1993 this figure rose to 217 out of the 650
sites targeted for completion through the year 2000.
Removal Program. The Superfund removal program responds
to releases or threats of releases of hazardous substances that
present an imminent threat to public health, welfare, or the environment.
Removal actions are generally shortterm, relatively low-cost actions
intended to respond to near-term threats to human health and the
environment. Where additional response actions are appropriate,
removal actions serve to protect the public and the environment
until a long-term solution can be implemented. In other cases,
the removal action sufficiently addresses the problem. Removal
activities to stabilize or eliminate the threat posed by a release
can include excavating or pumping hazardous substances for treatment
or off-site disposal; providing alternative water supplies to
nearby residents; treating hazardous wastes on-site; relocating
residents temporarily; and installing fences to prevent exposure.
Removals can be undertaken at both NPL and non-NPL sites but generally
are limited under CERCLA to one year and $2 million. Since inception
of the Superfund through 1993, the removal program has conducted
3,400 removal actions, including 2,500 at non-NPL sites.
EPA Technology Innovation Office. Established in March
1990 to promote the development and application of new treatment
technologies for remediation of contaminated soils and groundwater,
the EPA Technology Innovation Office (TIO) supports projects such
as the following:
. Development of a database with information on specific vendors
of innovative technology;
. Completion of a joint EPA-Air Force effort summarizing the
status of 48 cleanup technologies;
. Assessment of the commercial marketplace for innovative technologies;
. Initiation by the U.S. EPA, California EPA, and Air Force of
a Public-Private Partnership Program with Fortune 500 companies
to address contamination problems at McClellan Air Force Base
in Sacramento, California; and
. Initiation of similar technology evaluation projects at sites
operated by the Department of Energy, the Army, and the Navy.
Superfund Innovative Technology Evaluation Program. The
SITE program measures the effectiveness of new technologies through
field demonstrations. The program provides grant funding for emerging
technologies such as physical/chemical/biological processes that
can destroy, immobilize, or reduce contaminated hazardous materials.
Since its creation the SITE program has completed 49 full-scale
field demonstrations of new technologies for commercialization
and 23 laboratory and pilot-scale studies.
In 1993 the Clinton Administration evaluated Superfund and how
it has worked over the last dozen years, taking into account criticisms
that the program has generated in the following areas:
. The pace and cost of cleanup;
. The degree to which sites are cleaned;
. The fairness of liability under CERCLA;
. The role of states in the process; and
. The role of local communities, particularly disadvantaged communities,
in the Superfund program.
To explore options for making administrative improvements to Superfund,
the EPA established a task force with members from EPA headquarters
and regional offices and from the DOJ. On June 23, 1993, the task
force issued an Administrative Improvements to Superfund Report
containing four goals and nine initiatives that can be achieved
without changing the statute. Priority was given to actions that
could be implemented before September 30, 1994, the date set for
Superfund reauthorization.
In 1993 the EPA began to implement the task force initiatives,
incorporating several ongoing initiatives as part of administrative
improvements to Superfund.
Goal: Enhance Enforcement Fairness and Reduce Transaction Costs.
Initiative 1: Make Greater Use of Allocation Tools. The
Superfund program has been criticized for the high transaction
costs incurred by Potentially Responsible Parties (PRPs) in reaching
settlements and in litigating, where settlement efforts are unsuccessful.
The EPA is offering alternative dispute resolution (ADR) to facilitate
PRP efforts to allocate cleanup responsibility. ADR uses a neutral
third party to organize negotiations, facilitate settlement deliberations,
and provide an opinion to negotiating parties. The EPA may adopt
Non-binding Allocations of Responsibility (NBARs) as a preliminary
step to allocating response costs among PRPs. The agency also
is testing a binding allocation process. The agency assists allocation
efforts by gathering follow-up information to share with PRPs.
Initiative 2: Foster More Small Volume Waste Contributor Settlements.
Small volume waste contributors often complain that they are not
able to settle with the EPA until late in the remedial process
or when complete information about all PRPs is available.These
settlements can be time consuming and resource intensive for the
EPA. PRPs assert that they incur substantial costs in forming
a steering committee group and distributing information. Parties
responsible for small amounts of waste, referred to as de micromis
parties, find themselves subject to contribution actions by major
waste contributors. To address these issues, the EPA is taking
the following actions:
. Issue a directive to reduce the amount of information necessary
to make de minimus findings under Section 122(g) of CERCLA and
allow greater flexibility and use of judgement in entering into
these settlements; increase the number of sites where the EPA
can enter into such settlements and facilitate them early in the
process.
. Issue guidance on identifying sites where de micromis parties
are subject to contribution actions and on settling with those
parties.
. Institute negotiations at sites where PRPs have brought contribution
actions against de micromis parties and develop a communications
strategy to assist PRPs involved in the de minimus and de micromis
process.
Initiative 3: Assure Greater Fairness for Owners at Superfund
Sites. Concerns have been raised in the past that the EPA
may not have given property owners sufficient notice and opportunity
for comment before perfecting liens on their property. Uncertainty
regarding the meaning of -all appropriate inquiry- for purposes
of the CERCLA innocent-landowner defense may have discouraged
the purchase and use of previously developed land and the provision
of loans for such purchases. The EPA policy on settlements with
prospective purchasers may have been overly narrow in defining
the circumstances under which the agency would be willing to grant
a covenant not to sue to a prospective purchaser. To address these
issues, the EPA is taking the following actions:
. Issue supplemental federal lien procedures providing site owners
an opportunity to submit information or meet with the EPA before
the agency perfects a lien on their property.
. Clarify the requirements of -all appropriate inquiry- under
CERCLA.
. Issue supplemental prospective purchaser guidance as well as
a model prospective purchaser agreement.
Initiative 4: Evaluate Mixed Funding Policy. Mixed funding
refers to cleanups that are jointly funded by the Superfund and
PRPs. Some PRPs have objected to the EPA interpretation of its
mixed funding authority as too conservative. PRPs also believe
that the documentation requirements associated with mixed funding
are overly burdensome. The EPA is taking the following actions:
. Evaluate different mixed funding options, including an analysis
of cost implications to the Superfund Trust Fund, exploring options
for streamlining the mixed funding decisionmaking and documentation
requirements.
. Enter several mixed funding settlements as pilots, evaluating
them to assess changes in the EPA mixed funding policy.
Goal: Enhance Cleanup Effectiveness and Consistency.
Initiative 5: Streamline and Expedite the Cleanup Process.
Critics claim that the Superfund program takes too long to decide
upon remedies at sites and to achieve cleanup. They claim that
the site-specific decisionmaking process is a major source of
delay and inconsistency. To accelerate the pace of cleanups, the
EPA is taking the following actions:
. Promote the use of presumptive or standardized remedies to
clarify the land use policy.
. Set out approaches for dealing with lead contamination at sites.
. Provide a strategy to address the problem of Dense Non Aqueous
Phase Liquids (DNAPLs) in groundwater, including solvents that
are particularly difficult to clean up.
Initiative 6: Develop Soil Screening Levels. Cleanup levels
of soil have historically been set through a risk assessment process
for each site. The EPA is developing soil screening levels for
90 chemicals to identify contaminant levels below which there
is no concern and above which further site-specific evaluation
is warranted. Soil screening levels will accelerate investigation
of soil contamination at sites, streamline the baseline risk assessment,
and increase consistency between the RCRA corrective action program
and Superfund soil cleanups.
Goal: Enhance Public Involvement.
Initiative 7: Implement an Environmental Justice Strategy for
Superfund Sites. The EPA is taking steps to assess potential
areas of inequity at Superfund sites and to identify solutions.
The agency is completing a preliminary analysis of populations
living near 300 listed Superfund sites. The analysis links minority
and site variables and identifies ethnic populations living near
multiple sites. The agency is undertaking the following efforts:
. Environmental Justice Demonstration Sites. In each EPA Region,
the agency is designating a demonstration site where strategies
to address equity and other environmental justice issues will
be developed.
. Superfund Environmental Justice Strategy. Lessons learned from
demonstration sites along with other data and analysis will form
the basis of a new Superfund Environmental Justice Strategy. The
EPA will assign site project managers and community relations
staff with appropriate language skills and cultural sensitivities.
The agency will simplify applications for Technical Assistance
Grants (TAGs) and publish them in English and Spanish.
Initiative 8: Pursue Early and More Effective Community Involvement.
A critical problem in the Superfund program is the lack of support
for the cleanup among communities located around Superfund sites.
Citizen groups and communities often are dissatisfied with both
the pace and the results of cleanups. Community involvement problems
include difficulties in obtaining technical assistance grants
and in interpreting health studies, inaccessibility of information
and of site decisionmakers, and lack of opportunity for interaction
early in the process. To address these problems, the EPA is undertaking
the following efforts:
. Superfund Public Participation Plan. In 1993 the EPA prepared
a Superfund public participation plan based on comments from citizens
at EPA Superfund Public Forums and other meetings. The plan, which
includes community involvement, is scheduled for use at Superfund
sites.
. Site-Specific Advisory Boards. The EPA is monitoring progress
made by other federal agencies establishing Site-Specific Advisory
Boards at federal facility cleanup sites.
Goal: Enhance the State Role.
Initiative 9: Expand State Deferrals. The EPA and the states
agree that the number of hazardous substance sites requiring cleanup
is larger than either level of government can address alone. The
EPA will be unable to address environmental threats at some sites
for years, leaving PRPs in doubt regarding liability and local
communities at risk from unremediated sites and without the productive
use of affected land. Several states have developed increasingly
sophisticated programs to clean up non-NPL sites, relying in part
on EPA technical assistance and funding. The EPA can encourage
more environmental cleanups sooner by expanding state authority
to address sites of NPL-caliber and by enlisting state participation
in a complementary cleanup program. The use of deferrals can encourage
states to address NPL-caliber sites, thus accelerating cleanup,
minimizing the risk of duplicative state-federal efforts, and
assuring PRPs that only one agency will address the site. Deferrals
provide a negotiated division of responsibility for pre-NPL sites
and determine which agency will address a site. The EPA is planning
several state deferral pilot projects in which states will take
the lead for low- or medium-priority NPL-caliber sites that the
EPA would not be able to address for several years. Sites would
have state-identified PRPs. The EPA is developing policy-defining
scope and standards for state deferrals along with the federal
oversight role. Continuing Management Initiatives Over the past
several years, the EPA implemented the following reforms to improve
the effectiveness, efficiency, and equity of the Superfund program:
Accelerated Cleanup. The technical complexity of hazardous
waste sites coupled with complex Superfund site study and cleanup
requirements give rise to concern about the slow pace of Superfund
cleanups. These concerns resulted in development of the Superfund
Accelerated Cleanup Model (SACM). After completing field demonstrations
in 1993, the EPA intends to implement the model, which has the
following major components:
. Integrated site assessment;
. A team approach to selecting sites for cleanup action;
. An increased number of early actions, with immediate threats
to public health and safety to be eliminated first;
. Long-term remediation; and
. Enforcement actions and community relations activities throughout
the process.
Enforcement First. Under this policy, adopted in 1989,
the EPA, rather than spending the Superfund, uses enforcement
authority to compel responsible parties to clean up hazardous
sites. The total value of private party commitments to conduct
site study and cleanup at Superfund sites exceeded $7.4 billion
in 1993. In addition to testing ways to increase fairness, reduce
transaction costs, and accelerate and complete cleanup, the EPA
explores ways to encourage PRPs to conduct investigations and
cleanups earlier in the process through actions such as the following:
. Unilateral Administrative Orders. Creative use of enforcement
tools is essential to complete construction and accelerate cleanup.
Settlements with PRPs are preferable, but when necessary the EPA
uses unilateral administrative orders (UAOs) and judicial actions,
including actions for temporary and preliminary injunctive relief,
to compel PRPs to undertake response actions.
. Monitoring of PRP Compliance. Equally important is effective
monitoring of PRP compliance with existing Consent Decrees, Unilateral
Administrative Orders, and Administrative Orders on Consent. The
EPA takes enforcement action in response to failure or refusal
to comply.
Effective Contracts Management. Scrutiny of Superfund contracts
by parties within and outside the EPA point to the need for good
contract management. In 1993 the EPA implemented recommendations
of the Agency Task Force on Alternative Remedial Contracting Strategy
(ARCS) and implemented the Superfund Long-Term Contracting Strategy
to assure reliable cost-effective contracts. The EPA trains personnel
to oversee procurement and administration of Superfund contracts
and involves senior management as essential for accountability.
Other Improvements. The EPA also is improving the Superfund
program through the following initiatives:
. Accelerating cleanups to allow closing military bases to be
used for other purposes;
. Promoting the use of innovative cleanup technology; and
. Improving the effectiveness of cost recovery.
Because of their proximity to hazardous waste facilities, minorities
and low-income communities are at special risk from chemical emergencies.
The EPA sponsors a cooperative program to prepare local communities
for accidents involving hazardous materials, to reduce the number
of such accidents, and to assist in mitigating effects on public
health and the environment should they occur. Participants include
state, tribal, and local governments, industry, labor groups,
environmental groups, and other stakeholders. A number of laws
and initiatives support state and local right-to-know and emergency
response planning.
Included in the Superfund Amendments and Reauthorization Act of
1986 (SARA) was the Emergency Planning and Community Right-to-Know
Act.
Community Right to-Know. This section of the law provides
local governments and the public with information about chemical
hazards in their communities. The EPA establishes national community
right-to-know reporting requirements for inventories and releases
of hazardous chemicals. Because of these requirements, many facilities
have reduced inventories or substituted less hazardous chemicals
thereby reducing risks.
In May 1993 the EPA issued results of the fifth Toxics Releases
Inventory (TRI), which covered the calendar year 1991. Under the
TRI facilities are required to report on releases of listed chemicals
into the air and water, on the land, and underground at the facility
and transfers of chemicals off-site for the purposes of treatment,
disposal, energy recovery, or recycling. According to the 1991
data, reported releases and transfers of listed toxic substances
have declined for the fourth straight year.
TRI data for 1988 through 1991 are used to allow comparisons across
years to help identify changes and trends. Although 1987 was the
first year for TRI reporting, 1988 has been chosen by the EPA
as the baseline year because of concerns about the quality of
industry's submissions in the first year. In addition only those
chemicals listed for all reporting years 1988 through 1991 are
included in trend analysis; any chemical added or deleted during
that time was not included. For example the seven chlorofluorocarbons
(CFCs) and halons added to the list for the reporting year 1991
were not included. Similarly data on transfers for recycling and
energy recovery, which were reported for the first time in 1991,
were not included in the 1988-1991 trend analysis.
Since 1988 TRI-reported releases have declined nearly 31 percent
and transfers have dropped 33.5 percent. Reported air, land, and
underground releases declined each year after 1988; water releases
first decreased and then increased in each of the last two reporting
years due to runoff at several large facilities. Transfers to
publicly owned treatment works and to other off-site locations
for treatment and disposal also decreased during the 1988-1991
period. The greatest net change occurred between 1989 and 1990
when reported releases decreased nearly 16 percent and reported
transfers decreased nearly 10 percent. Some of these decreases,
however, may be explained by changes in reporting requirements
and options.
Emergency Preparedness, Prevention, and Response. This
section of the Community Right-to-Know Act encourages and supports
emergency planning for chemical accidents. The act recognizes
that the responsibility for understanding and reducing risk and
for responding to a chemical emergency resides at the lowest level
of government. Supportive mechanisms include State Emergency Response
Commissions (SERCs) in each state and 3,400 Local Emergency Planning
Committees (LEPCs) nationwide. Each LEPC uses facility-provided
hazard information to plan for chemical emergencies, thereby reducing
risk.
The Clean Air Act Amendments (CAAA) involve the EPA in chemical
emergency programs, such as the following.
Accidental Release Prevention Program. To prevent accidental
chemical releases and to minimize their consequences, Section
112® of the amendments established requirements for risk
management programs. The EPA has listed hazardous substances and
the threshold quantities for which these requirements apply. Facilities
handling listed substances above the threshold quantity must conduct
hazard assessment, develop accident prevention and emergency response
programs, and prepare risk management plans. In 1993 the EPA approved
eight grants to states, local communities, and one Native American
tribe to assist in implementing Section 112®.
Hydrogen Fluoride Study. The amendments required a study
of the hazards of hydrogen fluoride, which the EPA completed in
1993.
Review of Federal Authorities. The amendments called for the President
to conduct a review of the chemical release prevention, mitigation,
and response authorities of federal agencies. The EPA undertook
this study with the National Response Team.
The United States has been successful in having fundamental democratic
principles accepted as part of the foundation for international
chemical accident programs such as the following:
Organization for Economic and Cooperative Development (OECD).
OECD has developed Guiding Principles for Chemical Accident Prevention,
Preparedness, and Response, in use by both developed and developing
countries.
United Nations Environment Program (UNEP). The UNEP, in
addition to adapting the OECD principles for industrializing nations,
assists these nations in establishing chemical accident programs
under a UNEP program, Awareness and Preparedness for Emergency
at the Local Level (APELL).
Joint Contingency Plans. The United States worked with
Mexico and Canada to develop Joint Contingency Plans (JCPs) and
Joint Response Teams (JRTs) to ensure an effective, efficient,
and coordinated response to a transboundary chemical accident.
United Nations Economic Commission on Europe. The UNECE
has finalized the Convention on the Transboundary Effects of Industrial
Accidents which codifies much of the U.S. principles dealing with
chemical accident prevention, preparedness, and response.
The average annual radiation exposure for a person living in the
United States is 360 millirem. Naturally occurring radiation accounts
for approximately 82 percent of public exposure, most of which
comes from indoor radon (for a discussion of radon, see Chapter
1: Air Quality and Climate), followed by radiation from outer
space, from the earth's crust, and from the naturally occurring
radioactive element potassium in human bodies. Anthropogenic sources
of radiation account for the remaining exposure: 3 percent from
consumer products such as radon in drinking water and 15 percent
from medical procedures such as x rays, mammograms, nuclear medicine,
and gastrointestinal series. Additional annual exposure for people
living near nuclear power plants is less than 1 millirem.
Radioactive Waste. Radioactive waste in the United States
arises from five main sources:
. The commercial nuclear fuel cycle;
. Department of Energy-related activities;
. Institutions such as hospitals, universities, and research
foundations;
. Industrial uses of radioisotopes; and
. Mining and milling of uranium ore.
Radioactive waste is broadly categorized as spent nuclear fuel,
high-level waste (resulting from the reprocessing of nuclear fuel),
transuranic waste (lower-level wastes resulting from fuel reprocessing
and from the fabrication of plutonium weapons and plutonium-bearing
reactor fuels), uranium mill tailings (earthen residues remaining
after the extraction of uranium from ores), and low-level waste
(radioactive waste not classified as one of the above).
Over time radionuclides decay to nonradioactive, stable isotopes.
As an example the short-lived radionuclides found in spent nuclear
fuel rapidly decay during the first few years after the fuel is
removed from the reactor. Other radioactive wastes can remain
radioactive for hundreds to thousands of years.
Although chemical contamination of food by pesticides and additives
has declined over the last two decades, microbial contamination
has increased. In 1993 the EPA, U.S. Department of Agriculture
(USDA), and U.S. Food and Drug Administration (FDA) worked with
the White House Domestic Policy Council to strengthen existing
legislative authorities governing pesticides. The Administration
supports legislation to increase the overall safety of the food
supply that at the same time will make the various components
of the food safety program more consistent and more efficient.
Diet is a major source of exposure to pesticides. To minimize
exposure of the general public to pesticide residues in food,
the federal government regulates pesticide use through such laws
as the Federal Insecticide, Fungicide, and Rodenticide Act (FIFRA)
and the Federal Food, Drug, and Cosmetic Act (FFDCA).
The EPA sets tolerance levels to limit levels of pesticide residues
in foods. Tolerances-the maximum legal limit of a pesticide residue
allowed in or on a raw agricultural commodity and some processed
food-are set for all pesticides used on food crops. Tolerance
concentrations, based primarily on the results of field trials
by pesticide manufacturers, reflect the highest concentrations
likely under normal conditions of agricultural use rather than
health consideration.
The FDA monitors pesticide residues on domestically produced and
imported foods. Two categories of samples are collected for analysis:
. Surveillance Samples. These samples are taken when the FDA
has no prior knowledge or evidence that a food shipment contains
illegal pesticide residues. Most foods contain some pesticide
residues, but few samples violate EPA tolerance limits. For 30
years FDA testing has found 2-4 percent of foods tested for residues
in violation of legal tolerances, and no samples have contained
pesticides prohibited for use on food. In 1993 of the 5,703 domestic
surveillance samples analyzed, 64 percent had no detectable residues,
less than 1 percent had over-tolerance residues, and another 1
percent had residues of pesticides for which no EPA tolerance
had been set for that particular pesticide-commodity combination.
Of 6,463 import surveillance samples, 97 percent showed no violative
residues.
. Compliance Samples. These samples are collected and analyzed
as follow-up to the finding of an illegal residue or when other
evidence indicates that a residue problem may exist. In 1993 a
total of 223 domestic and 362 import compliance samples were collected
and analyzed. The violation rates were expectedly higher than
those for surveillance samples: 17 percent for domestic and 11
percent for import.
Aquaculture Survey. The FDA initiated an aquaculture survey
in 1990 that has been continued in succeeding years. The survey
focuses on persistent halogenated pesticides in aquaculture products.
These chemicals, such as DDT, although no longer registered for
food use, are present as a result of past agricultural uses. Of
the 308 samples tested, 44 percent had no detectable pesticide
residues. DDT was found in 35 percent of the samples at levels
ranging from trace to 1.0 parts per million (ppm), but well below
the 5 ppm FDA action level; chlordane was found in 3 percent at
levels of 0.01 to 0.07, but lower than the 0.3 ppm action level.
Residues of pesticides with no set tolerance levels were also
found in a small number of samples: chlorpyrifos (trace-0.02 ppm),
diazon (trace), and DCPA (an herbicide with the trade name Dacthal
at 0.01-0.09 ppm).
Milk Survey. In addition to routine surveillance monitoring,
the FDA analyzed 308 milk samples from 58 metropolitan areas for
pesticide residues in 1993. Samples from 37 of the metropolitan
areas had pesticide residues. Of the 308 samples, 35 percent had
detectable residues. The most frequently found residues were the
DDT derivative p,p-DDE (69 findings) and dieldrin (49 findings).
The highest residue level found was 0.01 ppm p,p-DDE. Results
indicate low levels of these environmentally persistent chemicals
in foods of animal origin.
Dietary Intakes of Pesticides. A major element of the FDA
pesticide residue monitoring program is the Total Diet Study,
in which foods are purchased from supermarkets or grocery stores
four times a year, once from each of the four geographic regions
of the country. Foods prepared table-ready are analyzed for pesticide
residues as well as radionuclides, industrial chemicals, toxic
elements, and essential minerals. Of the nearly 300 chemicals
that can be determined by analytical methods, 99 pesticide and
pesticide-related chemicals were found in foods analyzed between
September 1991 and July 1993. Table 99, in Part II of this report,
contains a summary of the findings of the Total Diet Study. Residues
of two pesticides appeared most frequently in the samples:
. Malathion. The most frequently found pesticide residue,
Malathion, is used on a variety of crops both pre and postharvest.
. DDT. Residues of DDT have been the next most prevalent
residue, although occurrence is declining, which suggests the
continuing degradation of this persistent environmental residue.
To learn more about infant and child sensitivity to pesticides,
Congress commissioned the National Academy of Sciences (NAS) to
study EPA risk-assessment processes and recommend improvements.
On June 27, 1993, the NAS issued Pesticides In the Diets of Infants
and Children, with the following major findings and recommendations:
. Infants and children eat types and proportions of foods that
differ from those eaten by adults and, per unit of body weight,
tend to eat more than adults. As a result their exposure to pesticides
may differ substantially from adult exposure.
. Additional data should be collected on the food consumption
patterns of infants and children.
. Children may be more or less sensitive than adults to toxic
effects depending on the pesticide to which they are exposed.
. Toxicity testing procedures should be developed that specifically
evaluate the potential vulnerability of infants and children.
. The process for setting tolerances should be modified so that
it is based more on health considerations than on agricultural
practices, using improved residue and toxicology information.
. EPA estimates of total exposure to pesticide residues should
better reflect the unique characteristics of the diets of infants
and children and should account also for the dietary intake of
pesticides.
. Analytical methods and reporting procedures for tests of pesticide
residues in food should be standardized and results should be
collected in a centralized database.
The Delaney Clause. In 1992 the United States Ninth Circuit
Court of Appeals issued a decision striking down the EPA interpretation
of the Delaney Clause in the Federal Food, Drug, and Cosmetic
Act (FFDCA). The clause regulates residues in processed foods
for pesticides that cause cancer in laboratory animals. In 1993
the EPA listed 32 pesticides, involving 80 chemical-crop combinations.
A February 5, 1993, notice in the Federal Register requested comments
on legal and policy issues necessary to implement the court decision.
The EPA revoked and denied a number of emergency exemptions for
pesticide uses and joined the USDA and FDA to issue a joint statement
of policy on EPA review and approval of requests for emergency
exemption under Section 18 of the Federal Insecticide, Fungicide,
and Rodenticide Act (FIFRA). The EPA revoked the food additive
regulations for the four chemicals named in the decision and in
1994 will issue a proposal on the remaining pesticides potentially
affected by the decision-on whether to revoke food additive regulations
and raw food tolerances and possibly to cancel registrations.
In August 1992 the EPA issued the Worker Protection Standard (WPS),
a regulation to protect employees on farms and forests and in
nurseries and greenhouses from occupational exposure to agricultural
pesticides. To implement the rule, the EPA issued notices requiring
registrants of pesticides to make label changes incorporating
the new protective requirements. Label changes began to appear
on pesticide products in 1993 and must be on all pesticides sold
after October 23, 1995. In partnership with states and Native
American tribes, the EPA took the following actions:
. Developed a manual, poster, and other materials to help agricultural
employers comply with the WPS;
. Held a series of workshops to train EPA regional and state
personnel in WPS requirements so that they, in turn, can train
agricultural employers;
. Developed pesticide safety training materials for agricultural
workers and pesticide handlers; and
. Developed a compliance monitoring checklist for state, tribal,
and federal inspectors to enforce the WPS.
Microorganisms are naturally present in soils, water, and air.
Many are beneficial, playing key roles in natural chemical and
biological processes, but others are pathogens to humans. They
gain access to human food sources through various routes:
. The Environment. For example exposure to contaminants
in the terrestrial or aquatic environment may serve as a route;
. The Food Processing and Distribution System. For example
entry routes may include shipping, slaughter, processing, mishandling
of food after processing, temperature abuse, and cross-contamination;
. Food Preparation Stages. At retail food operations and
in individuals households, mishandling food after cooking or not
thoroughly cooking food prior to consumption can be a route.
Foodborne illness is a major cause of morbidity in the United
States. Among outbreaks since the early 1970s in which the etiology
was determined, bacterial pathogens caused the largest number
of outbreaks (66 percent) and cases (87 percent). Chemical agents
caused 25 percent of the outbreaks and 4 percent of the cases;
parasites, 5 percent of the outbreaks and less than 1 percent
of the cases; and viruses, 5 percent of the outbreaks and 9 percent
of the cases.
Salmonella and Campylobater accounted for over half of
the bacterial disease outbreaks and were the most frequently reported
bacterial pathogens for each year since 1973. Fish poisoning because
of ciguatoxin and scombrotoxin accounted for 73 percent of the
outbreaks caused by chemical agents. T. spiralis and Giardia were
the leading causes of parasitic disease outbreaks, and Hepatitis
A caused 71 percent of viral food poisoning outbreaks.
The most commonly reported food-preparation practice that contributed
to foodborne disease was improper storage or holding temperature,
followed by poor personal hygiene of the food handler.
Inadequate cooking and contaminated equipment are also commonly
reported causes. Food obtained from an unsafe source was the least
commonly reported factor.
Pesticide residues in food and outbreaks of food poisoning are
risks that can be unevenly distributed across the population.
Federal agencies conduct programs to alleviate these risks for
all Americans, but special initiatives target the innercity and
rural poor. Food safety reform is a collaborative effort by the
EPA, USDA, and FDA in concert with farmers, environmentalists,
consumer groups, and state agencies.
One of the first reports to document the correlation of risk,
race, and income was the 1971 annual report of the Council on
Environmental Quality. This report suggested that low-income racial
and ethnic minorities are more likely to live in areas where they
are exposed to environmental hazards. This report also recognized
and highlighted the interaction between severe urban environmental
problems and the social and economic conditions of the Nation.
A report by the U.S. General Accounting Office (GAO) found that,
in EPA Region 4 (Alabama, Georgia, Florida, Kentucky, Mississippi,
North Carolina, South Carolina, and Tennessee), three of the four
commercial hazardous waste facilities in the region were in predominately
African-American communities and the fourth was in a low-income
community.
A follow-up study by the United Church of Christ Commission for
Racial Justice, based on 1980 population data, expanded the GAO
study to all EPA regions and found that in communities with two
or more commercial waste facilities, the average minority percentage
of the population was three times that of communities without
such facilities. The report of this 1987 study concluded that
race, not income, was the factor more strongly correlated to residence
near a hazardous waste site. An update of the study, based on
1990 population data, was scheduled for release in 1994.
In addition minority and low-income communities face a number
of other environmental risks. Low-income residents of dilapidated
buildings are more suspectible to lead poisoning in their homes.
Migrant farmworkers face a disproportionate likelihood of pesticide
poisoning, and those who work without adequate protective clothing
are even more likely to be exposed to pesticides and toxic hazards.
Uranium-contaminated Navajo land and water are believed to contribute
to the high incidence of organ cancer-many times the national
average-in Navajo teenagers. The level of exposure for minority
and low-income communities is increased by poor housing conditions,
unsafe water supplies, and inadequate sewage facilities.
Lead is an ubiquitous, persistent environmental pollutant. It
enters the human environment through various pathways:
. Automobile and industrial emissions;
. Paint pigments and solder;
. Old lead water pipes, particularly in older northeastern cities;
. Leaching of lead solder applied to water pipes in homes prior
to 1988; and
. Brass faucets that contain some lead.
Lead emitted into the air ultimately settles as soil dust and
into waterways, where it can be recycled through the environment
and into humans. Opportunities for lead to enter the human food
chain are enhanced by animal grazing, home gardening, and general
agriculture in areas where lead contaminates soils.
In major urban areas, lead poisoning among children is a persistent
public health problem. Lead-based paint is the most common source
of high-dose lead exposure for children. Children are exposed
to lead from soil when they play outdoors in areas contaminated
by deteriorating exterior lead-based paint, emissions from automobiles
using leaded gasoline, and/or lead emissions from smelters. Urban
atmospheric lead levels may be up to 20,000 times higher than
those in rural regions. In addition to environmental sources,
the use of folk medicines and pottery containing lead is prevalent
among some minority groups and has caused severe cases of childhood
lead poisoning. Studies indicate that African American children,
followed by Hispanics, have a higher prevalence of elevated blood-lead
levels than white children, regardless of age, household income,
or degree of urbanization. Screening and abatement activities
for homes with lead paint hazards, intensive education efforts,
and decreased contributions from sources such as leaded gasoline
may account for recently observed decreases in blood-lead levels
and new cases of lead poisoning.
Although children are more at risk for lead exposure, lead-induced
health effects are known to occur in adults across a wide range
of exposures, including among others:
. Workers who process automobile and industrial batteries to
reclaim their lead and plastic content;
. Workers who mix lead chromate-based pigments to formulate color
concentrates for the plastics industry;
. Workers who solder or weld with lead;
. Workers who repair automobile radiators; and
. People who consume illicitly distilled alcohol, such as moonshine
distilled in automobile radiators containing lead-soldered parts.
One outcome of a conference held by the University of Michigan
in January 1990 in Ann Arbor, Michigan, was formation of the Michigan
Coalition, a group of social scientists, civil rights leaders,
and environmentalists interested in environmental justice as a
public policy issue. In October 1991 an Environmental Leadership
Summit was held in Washington, D.C., where 650 participants adopted
Principles of Environmental Justice. These principles include
the rights of a community to clean air, clean water, and a safe,
healthy, and livable environment.
In response to the concerns of the U.S. Congressional Black Caucus
and the Michigan Coalition, the EPA formed the Environmental Equity
Workgroup. A cross-section of senior EPA staff reviewed and evaluated
the evidence that low-income persons and minorities bear a disproportionate
burden of environmental risks. The findings, published in a 2-volume
report entitled Environmental Equity: Reducing Risk in All Communities,
included the following:
. No clear differences were found between racial groups in terms
of disease and death rates; however a general lack of data exists
on environmental health effects by race and income. The notable
exception is lead poisoning. A significantly higher percentage
of African American children, compared to white children, have
unacceptably high levels of lead in their blood.
. Minorities and low-income populations experience higher-than-average
exposures to selected air pollutants, hazardous waste facilities,
contaminated fish, and farm pesticides in the workplace.
. Data are not routinely collected on health risks posed by multiple
industrial facilities, cumulative and synergistic effects, or
multiple pathways of exposure.
In 1992 in response to recommendations of the workgroup, the EPA
created the Office of Environmental Equity to coordinate agency
efforts to address environmental justice issues.
Where environmental remedies are not applied equitably across
racial and socioeconomic groups, minority and low-income communities
face a higher level of environmental risk, including direct exposure
to hazardous materials and wastes during their production, disposal,
and containment. Federal and state agencies set pollution standards
to protect all of the environment and all of its inhabitants,
but recent studies, such as those on lead poisoning in children,
indicate that minority and low-income communities bear a disproportionate
share of the nation's air, water, and waste problems.
In the past neither the extent nor the seriousness of environmental
inequities and injustices were well documented or analyzed, but
despite incomplete health effects data, federal agencies have
begun to gather data on exposure and risle levels to determine
whether there are disproportionally high and adverse human health
environmental effects.
Despite limited empirical data to document the extent of direct
health impacts, support for action on environmental justice issues
is mounting. In 1993 the President directed the EPA and DOJ to
begin an interagency review of federal, state, and local regulations
and enforcement that affect minorities and low-income communities
with the goal of formulating an aggressive investigation of the
inequities in exposure to environmental hazards. As part of this
evaluation, the DOJ and EPA, in conjunction with the departments
of Housing and Urban Development (HUD) and Labor (DOL), will identify
examples of communities in which environmental decisionmaking
may have affected minorities and low-income populations adversely.
Federal agencies have assumed leadership of environmental justice
initiatives to ensure that the nation provides equal protection
under the law. Realizing that environmental inequities can not
be solved or even evaluated overnight, federal agencies are coordinating
data collection, analysis, and remedial actions with states, municipalities,
academia, industry, and the affected communities themselves and
are directing compliance and enforcement at the most severe risks,
which include those that disproportionately affect minorities
and low-income groups.
Working through the Office of Environmental Equity (OEE), the
EPA took the following actions in 1993:
. Expanded environmental justice education and outreach programs;
. Promoted community-based self-help programs such as economic-
environmental development;
. Established a clearinghouse for environmental justice information;
and
. Provided financial and technical assistance to groups involved
in environmental justice initiatives, such as minority academic
institutions, community organizations, and state and local governments.
Databases. The EPA is expanding databases on the demographics
of Superfund and solid waste facilities in low-income communities
disproportionately exposed to environmental hazards.
Equitable Enforcement and Rulemaking. Investigations are
underway to determine if racial or socioeconomic inequities have
influenced implementation and enforcement of environmental regulations
and if such inequities have affected the speed and thoroughness
of cleanups in low-income communities.
The EPA Office of Environmental Equity (OEE), established on November
6, 1992, to deal with environmental impacts affecting minorities
and low-income communities, serves as the public point of contact
for environmental justice outreach, technical assistance, and
information. A separate senior executive committee, the Equity
Cluster, was formed at the same time to develop policy guidance
documents and an agenda for environmental justice. The OEE and
the Cluster worked in concert to frame the issues and develop
broad directives.
EPA regions have developed environmental justice policies, strategic
plans, and action plans. The strategic plans outline regional
commitment to ensure equitable environmental protection for all
communities; the action plan provides managers and staff with
a framework on which to develop environmental justice efforts.
Each region and program office initiated environmental justice
work groups, quality action teams, advisory boards, or steering
committees to oversee environmental justice activities.
Ethnic Study Groups made up of EPA personnel develop discussion
topics and position papers on how environmental justice issues
affect each ethnic group. Volunteers identified equity issues
pertinent to the program in which they worked.
To better communicate with local communities and private-sector
groups, OEE efforts include the following:
. An Environmental Justice Hotline is open on 1-800-962-6215;
. The Environmental Equity Update Memo, a status report published
several times a year, highlights environmental justice activities
and initiatives;
. Equity programs are sponsored on ethnic radio and TV networks,
such as Hispanic Network Radio and the Black College Satellite
Network;
. Public understanding of environmental justice is refined through
interviews on public TV, technical advice to museum exhibits,
sponsorship of booths at national conferences, and service as
advisors to university drama clubs on creation of environmental
justice dramas.
. Meetings were held with senior officials to discuss the concerns
and listen to the suggestions of nongovernment environmental justice
leaders. The EPA is formalizing input by establishing a Federal
Advisory Committee on Environmental Justice.
. The EPA encouraged regions to reach out to community groups,
industries, and state and local organizations to bring them together
to discuss local environmental problems and solutions. The OEE
sponsored pilot symposia as national models and coordinated projects
and shared environmental justice information across media offices
by forming networks in all program and regional offices. Each
EPA region and program office has appointed an environmental justice
coordinator.
. The EPA worked on plans for a 3-tiered environmental justice
infrastructure to work with the OEE. The structure, set for initiation
in January 1994, will establish an Executive Steering Committee,
reconstitute the Equity Cluster as an Environmental Justice Policy
Working Group, and strengthen Environmental Justice Coordinators.
. The Executive Steering Committee, comprised of Deputy Assistant
Administrators and Regional Administrators from at least three
regions, will provide agency direction on strategic planning to
ensure environmental justice is incorporated into EPA operations
and to provide direction to the Policy Group.
. The Policy Working Group will ensure cross-media coordination
of environmental justice projects and technologies.
. Environmental Justice Coordinators will continue to provide
education and outreach for environmental justice information in
their offices and regions.
. The EPA is integrating environmental justice into its offices,
as the agency moves toward a multimedia, holistic approach to
protecting public health and the environment.
. Multimedia Component. As part of the evolving multimedia
enforcement strategy, linking for instance air, water, and soil
violations, the EPA and DOJ are developing an environmental justice
component to focus on socioeconomic and racial fairness in future
enforcement actions. They are targeting areas with a host of multimedia
environmental problems for intensified enforcement.
. Embedded Injustices. In addition to analyzing rulemakings
currently underway to preclude embedded injustices, the EPA is
seeking to increase involvement of affected communities in the
rulemaking process.
Multicultural Participation. Historically minority and
low-income groups have not been involved in environmental issues,
and few programs have been designed to reach out to these populations.
As evidence of change, the following recently developed programs
are designed to enfranchise low-income populations:
. Chesapeake Bay Program. Through better structuring of
informational materials and educational programs, the program
is involving minority and low-income communities in restoration
of the Chesapeake Bay.
. Radon. The EPA is translating radon public information
documents into Spanish and distributing them to Spanish speaking
communities. A number of Indian tribes are using EPA grants to
implement radon programs on their reservations. In a public survey
to measure radon awareness, Native American tribes displayed the
broadest knowledge of the issue.
. Environmental Management by Tribes. Native Americans
have both a special relationship with the federal government and
distinct environmental problems. In this day of multimedia pollution,
tribes often lack the trained personnel and financial resources
needed to protect their lands, health, and safety. Through a combination
of outreach, training, and support, the EPA is working with tribes
to educate their own environmental managers.
. Superfund and Federal Facilities. EPA efforts are involving
minority and low-income communities located near Superfund and
federal facility cleanup sites. In addition to providing educational
materials and holding public meetings, the EPA administers local
grants to hire outside experts to explain community rights under
environmental laws (see Superfund Program section of this chapter).
. Teacher Training. The EPA offers training to teachers
from culturally diverse school districts to assure that young
people receive information on environmental issues to empower
them to make sound environmental choices.
. Intern Programs. In 1993 three EPA-sponsored grants
placed 150 culturally diverse summer interns in positions throughout
the agency.
In 1993 the Civil Rights Division of the Department of Justice
used its computerized database to identify and evaluate low-income
communities, and together the DOJ and EPA identified ongoing litigation
in which environmental justice goals can be implemented. This
information is being used to establish enforcement priorities.
The DOJ-EPA partnership is developing as a model of cooperation
for other federal agencies.
Established as a part of the National Institutes of Health (NIH),
the National Institute of Environmental Health Sciences (NIEHS)
has supported research targeted at decreasing health inequities
among minorities and low-income populations. The institute supported
the research on lead poisoning that established the link between
high blood lead concentration and IQ deficits in many innercity
African-American communities. Research on migrant populations
exposed to pesticides uncovered adverse health effects previously
undiagnosed. Research on the health effects of air pollutants
continues to yield solutions to the pulmonary problems found in
areas of high ambient air pollution.
Equity in Environmental Health Workshop. In August 1992
the NIEHS, the EPA Office of Health Research, and the Agency for
Toxic Substances and Disease Registry (ATSDR) cosponsored a 2-day
workshop entitled -Equity in Environmental Health: Research Issues
and Needs.- Participants examined scientific evidence of environmental
justice and health effects resulting from prolonged environmental
exposure and identified health research needs and opportunities.
Multidisciplinary Developmental Centers. On March 29, 1993,
the NIH Office of Research on Minority Health and the EPA signed
a Memorandum of Understanding that provided $25 million over five
years to address minority environmental health concerns. One result
has been the development of multidisciplinary developmental centers
planned in close proximity to areas of minority communities with
environmental concerns. In 1993 the first such center was established
by Tulane and Xavier universities in New Orleans.
Projects sponsored by the Agency for Toxic Substances and Disease
Registry (ATSDR) to address minority health impact issues include
the following.
First National Conference on Minority Health. A minority
health program initiated in 1986 sponsored the first national
conference on minority health and the impact of toxic substances
on the health of minorities.
Applied Research. An ATSDR-sponsored program of applied
research at Historically Black Colleges and Universities is evaluating
the impact of toxic substances on the health of minority communities,
Mitigating Adverse Health Effects. The Mississippi Delta
Project, conducted by ATSDR in collaboration with EPA, CDC, NIEHS,
OSHA, and state and local agencies, seeks to prevent or mitigate
adverse health efforts on minority populations living in communities
near hazardous waste sites.
Demographical Data. The ATSDR has undertaken a 6-year effort
to gather demographic data and information on environmental hazards
faced by minorities and low-income community residents living
near waste sites.
The United States is predominantly an urban nation. At the time
of the 1990 census, 192.7 million persons or 77.5 percent of the
U.S. population lived in inner cities of metropolitan areas and
in their surrounding suburbs, an area which comprises only about
2.5 percent of the nation's land area. In contrast, nearly 56
million persons lived in nonmetropolitan or rural territories
which comprise over 97.5 percent of the land.
Poverty is as much a fact of life in rural areas as it is in nation's
inner cities. Although the rural poverty rate has exceeded the
total metropolitan poverty rate over the past two decades, the
public perception of poverty as an urban problem may result because
most people live in or near urban areas where they observe urban
poverty firsthand. The rural poor are more dispersed and less
visible.
Innercity poor are much more likely to live in families headed
by a woman than the poor in suburbs and rural areas, although
poverty among woman-headed families is a growing problem in rural
areas.
Recent urban population growth continues to outpace rural growth.
Metropolitan areas have a considerably higher rate of natural
increase-births minus deaths-than do nonmetropolitan or rural
areas; however, differential migration is the main reason for
the more rapid increase in the metropolitan population.
Central Cities vs. Suburbs. In 1900 most of the urban population
lived in central cities. Until 1930 both central city and suburban
populations grew rapidly, increasing their national shares, but
since then central cities as a group have grown more slowly, maintaining
a steady share of the total U.S. population. At the same time,
half of metropolitan growth took place in the suburbs. By the
early 21st century, if not before, metropolitan suburban areas
are likely to account for more than half of the U.S. population.
Farm Residents. Relatively few rural residents now live on farms.
In the peak period of farm residence, from 1910 to 1920, some
32 million persons resided on farms, and as late as 1950, the
nation had 23 million farm residents. The U.S. Bureau of the Census
estimates that the farm population dropped below 10 million in
1970 and is now just under 5 million.
Nonfarm Rural Residents. Offsetting part of the loss of rural
farm population over the past 20 years was an increase in nonfarm
rural residents. During the rural renaissance of the 1970s, nonmetropolitan
population grew by 15 percent, which is above the national average.
The decreasing ability of rural areas to retain and attract residents
resulted, however, in slower population growth during the 1980s,
with a rate similar to the 3-percent increase of the 1960s.
Minorities continue to be disproportionately poor. Although poverty
increased most among rural Hispanics in the 1980s, rural African
Americans continue to have the highest poverty rate, 39.5 percent
in 1990. The number of poor rural whites and their poverty rate
also increased during the 1980s. Poverty is concentrated regionally,
with the South having 55 percent of the nation's rural poor, 30
percent of the central-city poor, and 41 percent of the suburban
poor. Rural poverty is concentrated in counties with high poverty
rates and persistently low incomes, such as Appalachia, and in
areas with high proportions of African Americans, Hispanics, and
Native Americans. Since 1980 the rural West has had the greatest
increase in the poverty rate.
Poverty rates reflect the current growth and distribution of the
U.S. population, as shaped by historical trends in births, deaths,
immigration, and internal migration. The ongoing decline in mortality
is a factor in the aging of the population through an increase
in the proportion that are elderly and in the elderly poor. The
impact of immigration is apparent in the changing racial and ethnic
distribution of the population, with internal migration apparent
in the regional distribution of the population and the increasing
population density of coastal areas. Although population growth
has been moderate and steady during the past several decades,
settlement patterns varied for urban and rural sections and for
coastal and noncoastal areas.
The U.S. resident population as of December 31, 1993, was 258.2
million persons, 3.8 percent above the 1990 census count of 248.7
million. The population growth rate for the 1980-1990 decade was
the second lowest in census history. Only in the Great Depression
decade of the 1930s when the childbearing rate dropped to two
births per woman and net immigration from abroad became negligible
was the growth rate lower. In contrast the growth rate increased
substantially in the 1950s, which included the peak of the post-World
War II baby boom with a childbearing rate of three births per
woman. Since 1990 the growth rate has increased, mostly as a result
of natural increase (births minus deaths) but also because of
a net gain in international migration and from U.S. armed forces
returning from abroad.
Fastest Growing Age Groups. Over a third of the nation's
poor are either children under 18 years or persons over 65, and
these two age groups are among the fastest growing in the population.
Although persons aged 35 to 44--the babyboomers-were the fastest
growing age group in the last decade, the population under five
experienced the second largest gain, reflecting an increase in
the childbearing population. The third most rapidly increasing
age group consisted of persons 75 to 84. Another group that increased
rapidly with implications for poverty contained persons 85 and
older. A higher proportion of elderly than nonelderly are -near
poor,- living just over their respective poverty threshold.
Life Expectancy. For the U.S. population as a whole, life
expectancy at birth continues to rise. This increase has managed
to keep pace with the growth of the population over the past several
decades. Between 1980 and 1990, overall life expectancy at birth
increased from 73.7 years to 75.8 years.
Immigration. Each year since 1980, approximately 29 percent
of the nation's population growth has resulted from net international
migration. Among legal immigrants, including refugees, a major
transition occurred in distribution by country of origin. Since
1969 Latin America has been the major source of legal immigration
to the United States, with Mexico the primary country of birth.
For legal immigrants other than Latin Americans, the country of
birth has shifted from Europe to Asia.
The western region of the United States has experienced the most
rapid population increases throughout the twentieth century, with
growth rates consistently higher than the nation as a whole. This
trend has continued into the 1990s. Since World War II, five states
have dominated the list of most rapidly growing states: Arizona,
Florida, and Nevada led each decade through the 1980s, with Alaska
and California missing as lead states only in the 1970s.
The West. Nevada has been the fastest growing state since
1980, with net immigration the dominant force behind the growth.
Alaska is the second fastest growing state, with population change
tied to trends in the energy industry. Population growth in California,
where half of the population in the West resides, dropped considerably
in the early 1990s.
The South. With 34 percent of the nation's inhabitants,
the South is the most populous and second fastest growing region.
The population in the South reached its lowest level in 1930 and
1960 and has increased each decade since. Half of the recent gains
result from net immigration drawn by a relatively low cost of
living, with inter-regional migration induced by the search for
new employment. Generally the rate of growth in the South has
slowed over the last ten years.
The Midwest. Since 1900 the Midwest's share of the U.S.
population has declined more sharply than other regions. Although
it is the second most populous region in the nation, the Midwest
has lost population through out migration related to economic
slowdowns in industrial and agricultural sectors. Since 1990,
however, natural increase and international net migration has
led to a moderate population increase in the region.
The Northeast. In 1910 and 1920, the northeastern portion
of the nation's population reached its 20th century peak before
declining in each subsequent decade. In the 1980s the Northeast
grew by a modest degree despite net out migration of half a million
persons. Its sluggish growth rate continued into the 1990s, precipitated
by a population decline in New England.
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Mohai, P. and B. Bryant, -Race, Poverty, and the Environment,-
EPA Journal 18(1):6-8, (March/April 1992).
National Academy of Sciences, Pesticides In The Diets Of Infants
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Perfecto, I. and B. Velasqez, -Farm Workers: Among the Least Protected,-
EPA Journal 18(1):13-14, (March/April 1992).
Schwartz, J. and R. Levin,, -Lead: Example of the Job Ahead,-
EPA Journal 18(1):42-44, (March/April 1992).
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and Race in the United States: A National Report on the Racial
and Socio-Economic Characteristics of Communities with Hazardous
Waste Sites, United Church of Christ, 1987.
U.S. Department of Agriculture, Economic Research Service, -Nonmetro
Access to Complete Plumbing Increases,- Rural Conditions and
Trends, 4(3):56-57, (Washington, DC: USDA, ERS, Fall 1993).
Nonmetro Poverty Rate Inches Back Up,- Rural Conditions and
Trends,
4(3):48-49, (Washington, DC: USDA, ERS, Fall 1993).
Poverty a Persistent Problem in Rural America,- Farmline,
14(3):12-15, (Washington, DC: USDA, ERS, 1993).
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P23-175, (Washington, DC: DOC, BOC, May 1992).
U.S. Department of Energy, Oak Ridge National Laboratory, Integrated
Data Base for 1993: U.S. Spent Fuel and Radioactive Waste Inventories,
Projections, and Characteristics, (Oak Ridge, TN: DOE, ORNL, March
1994).
U.S. Department of Health and Human Services, Public Health Service,
Centers for Disease Control and Prevention, -Foodborne Disease
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Blood Lead Levels Among Children in High-Risk Areas - California,
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and Mortality Weekly Report 39(SS-4):1-8, (Atlanta, GA: HHS,
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Elevated Blood Lead Levels Associated with Illicitly Distilled
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Report 41(17):294-295, (Atlanta, GA: HHS, PHS, CDC, May 1992).
Lead Exposures Among Lead Burners - Utah, 1991,- Morbidity
and Mortality Weekly Report 41(17):307-310, (Atlanta, GA:HHS,
PHS, CDC, May 1992).
Lead Chromate Exposures and Elevated Blood Lead Levels in Workers
in the Plastics Pigmenting Industry - Texas, 1990,- Morbidity
and Mortality Weekly Report 41(17):304-306, (Atlanta, GA:
HHS, PHS, CDC, May 1992).
Lead Poisoning Among Battery Reclamation Workers - Alabama, 1991,-
Morbidity and Mortality Weekly Report 41(17):301-304, (Atlanta,
GA: HHS, PHS, CDC, May 1992).
Surveillance of Children-s Blood Lead Levels - United States,
1991,- Morbidity and Mortality Weekly Report 41(34):620-622,
(Atlanta, GA: HHS, PHS, CDC, May 1992).
Surveillance of Elevated Blood Lead Levels Among Adults - United
States, 1992,- Morbidity and Mortality Weekly Report 41(17):285-287,
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U.S. Environmental Protection Agency, Office of Solid Waste and
Emergency Response, Characterization of Municipal Solid Waste
in the United States: 1992 Update, (Washington, DC: EPA, OSWER,
1992).
U.S. Environmental Protection Agency, Environmental Equity:
Reducing Risks For All Communities, (Washington, DC: EPA,
1992).
Wernette, D.R. and L.A. Nieves, -Breathing Polluted Air,- EPA
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