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United States Office of Research and Office of Regional Operations
Environmental Protection Development and State/Local Relations
Agency Washington, DC 20460 Washington, DC 20460
EPA/625/R-94/009
September 1994
Planning for
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A Guide for Local
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EPA/625/R-94/009
September 1994
Environmental Planning for
Small Communities
A Guide for Local
Decision-Makers
United States Environmental Protection Agency
Office of Research and Development
Office of Science, Planning and Regulatory Evaluation
Center for Environmental Research Information
26 West Martin Luther King Drive
Cincinnati, Ohio 45268
Office Of Regional Operations and State/Local Relations
Washington, DC 20460
)Printed on Recycled Paper
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Disclaimer
This document has been reviewed by the U.S. Environmental Protection Agency (EPA)
and approved for publication. Mention of trade names or commercial products does not
constitute endorsement or recommendation of their use.
Acknowledgments
Many people contributed their expertise to the preparation and review of this publica-
tion. Overall technical guidance was provided by Randy Revetta and James Kreissl of
U.S. EPA's Center for Environmental Research Information. The document was
prepared by Eastern Research Group, Inc. The following people provided guidance
and review:
Pauline Afshar
Kelly Beard-Tittone
Kate Becker
Sylvia Bell
Hamilton Brown
Michael Caughman
Ann Cole
Henry Ferland
David Flowers
Richard Gardner
Charles Gomez
Beth Hall
John Harkins
Jack Hardinger
Judy Kane
Keith Jones
KenJones
Lou Kerestesy
EPA Region 8
EPA Region 7
EPA Office of Solid Waste and Emergency Response
EPA Office of Water
National Association of Towns and Townships
South Carolina State Budget and Control Board
EPA Office of Regional Operations and State/Local Relations
EPA Office of Solid Waste and Emergency Response
Cedarburg, WI
Idaho Rural Development Council
EPA Region 8
EPA Office of Water
EPA Region 4
EPA Region 8
EPA Office of Solid Waste and Emergency Response
National Rural Water Association
Northeast Center for Comparative Risk
EPA Office of Regional Operations and State/Local Relations
Contents i
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Acknowledgments (continued)
Alfred Krause
Jan Lambert
Vanessa Leiby
Lawrence Martin
Patricia Miller
Wade Miller
Richard Minard
John Mori
Amy Naylor
Lane Nothman
Ernesto Perez
Jackie Pine
Charles Pycha
A.R. Rubin
Deborah Rutherford
Jane Schautz
Mary Settle
Peter Shanaghan
Ron Slotkin
James E. Smith, Jr.
Kathy Stanley
John Thune
Charles Vanderlyn
Stephanie von Feck
Sam Wade
Dov Weitman
James Werntz
Floyd Winsett
EPA Region 5
EPA Region 7
Association of State Drinking Water Administrators
EPA Office of Research and Development
National Small Flows Clearinghouse
Wade Miller Associates, Inc.
Northeast Center for Comparative Risk
West Virginia University
State Office Representative, Lewiston, ME
Ross & Associates
EPA Region 4
EPA Region 3
EPA Region 5
North Carolina State University
EPA Office of Solid Waste and Emergency Response
The Rensselaerville Institute
EPA Office of Water
EPA Office of Water
EPA Office of Research and Development
EPA Office of Research and Development
Rural Community Assistance Program
South Dakota Municipal League
EPA Office of Water
EPA Office of Water
National Rural Water Association
EPA Office of Water
EPA Region 10
EPA Region 10
Contents
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Contents
Introducing Environmental Planning for Small Communities:
An Open Letter 1
2 Getting the Right People Involved 7
Forming a Planning Team 7
Finding Local Experts 8
Working with Local, County, State, and Federal Personnel 9
Encouraging Public Participation 9
Developing a Community Vision 13
Involving the Community 13
Asking the Right Questions 13
Pulling the Vision Together 15
Defining Your Community's Needs 19
What Are the Boundaries of Your Environmental Planning Area? 19
What Environmental Regulations Affect Your Community? 21
Do Any Environmental Problems Threaten Public Health, Ecosystems, or
the Quality of Life in Your Community? 23
How Effective Are Your Community's Environmental Facilities? 28
Is Your List of Needs Adequate To Meet Your Community's Vision for the Future? . . 34
MI
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Finding Feasible Solutions for Your Community 37
Technology and Management Options for Small Communities: An Overview .... 37
Evaluating Costs for Technology and Management Options 39
Narrowing the Options 40
Finding Solutions: Drinking Water 42
Finding Solutions: Wastewater 48
Finding Solutions: Solid Waste 53
Finding Solutions: Hazardous Waste 57
Finding Solutions: Nonpoint Source Pollution 60
Finding Solutions: Underground Storage Tanks 63
Putting the Plan Together 69
Targeting the Problems 69
Setting Priorities for Action 70
Looking at the Big Picture 72
Implementation: Putting the Plan Into Action and Keeping
It On Track 77
Developing a Schedule for Putting the Plan Into Action 77
Financing the Plan 78
Roles of Government and Other Organizations 79
Roles of Community Members 85
Evaluating and Revising the Plan 87
Appendix A Environmental Community Agreement Between
the Kenai Peninsula Borough and the Alaska Department
of Environmental Conservation 93
iv Contents
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What Environmental Regulations Affect
Your Community? 99
Drinking Water Quality 99
Wastewater Treatment 108
Wetlands Protection 112
Nonpoint Source Pollution 113
Solid Waste Management 114
Hazardous Waste Management 117
Underground Storage Tank Safety 119
Emergency Response to Hazardous Substance Spills 124
Asbestos-Containing Materials in Buildings 126
Radon Gas in Homes and Other Buildings 128
Air Pollution 130
Floodplain Zoning 132
Assessing Risks from Environmental Problems
in Your Community 133
Questions to Help You Assess Risks to Health, Ecosystems, and Quality of Life . . 133
Assessing Human Health Risks in Your Community 134
Assessing Ecological Risks in Your Community 135
Assessing Risks to Quality of Life in Your Community 137
Status of Comparative Risk Projects: States, Cities, and Tribes 138
Where To Turn for Help 143
U.S. Environmental Protection Agency Regional Small Community Contacts ... 143
Other Organizations 144
Technical Support Centers and Hotlines 146
Publications 149
Electronic Bulletin Boards and Databases 152
Tools 153
Contents
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Introducing Environmental
Planning for Small Communities:
An Open Letter
Dear Small Community Decision-Maker:
As a leader in a small community, you face many difficult challenges in managing
environmental issues. You must juggle many issues at once, including how to provide safe
drinking water, how to manage wastewater from homes and businesses, and how to manage
the community's solid waste. The list seems endless, and the resources available are all too
limited and continue to dwindle. Not only that, but you have many other responsibilities
besides environmental protection, such as schools, roads, and public safety. How do you
do it all?
This book offers a tool to help you meet these challenges—a process for developing a
community environmental plan. The goals of creating this plan and putting it into action
are to:
Provide a sensible way for your community to set priorities and decide how
to make the best use of your resources to protect people's health and the
environment.
Help your community save money—by dealing with issues before they
become big problems, by making sure that environmental services are
provided in the most efficient way possible, by planning to use the right
combination of environmental programs and services, by workingwith other
communities where possible, and by making use of local talent and resources.
A plan also will help you take advantage of opportunities to prevent pollu-
tion, the cheapest and most effective solution of all.
Provide a blueprint for compliance with the environmental regulations
that affect your community, to help you avoid the need to react to enforce-
ment actions by state, county, or federal agencies.
Empower your community to take charge of its own destiny by charting
its best course.
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Build community awareness and support for actions (such as possible rate
increases) that you, the decision-maker, must take to protect public health
and the quality of the environment.
Help promote the economic health and well-being of your community
by providing the environment, infrastructure, and quality of life that make
your community a good place to live and to do business.
In the past, people tended to look at the environment in pieces: how to protect the air,
how to protect the water, how to protect the land. Today we know that environmental
protection won't really work unless we treat the environment as an integrated whole. We
also know that local governments can't carry out their environmental protection respon-
sibilities without considering the community as a whole: its resources, its economy, public
opinion, and all its other needs. With a comprehensive environmental plan, you can create
an integrated approach to protecting the environment and meeting your community's
needs. (Keep in mind that this guidebook focuses on the environmental issues and
problems addressed by the U.S. Environmental Protection Agency; your community must
take into account other issues, such as public safety and agriculture, that are important in
your community.)
The environmental plan described in this book is like a road map that shows you where
you are and where you are going, and provides some ideas of how to get there. Without a
plan for your community's environment, you are likely to waste a lot of time and money.
You also might lose valuable natural resources, as well as community support, that can
never be replaced.
Developing a plan and putting it into action, on the other hand, can help put you "in the
driver's seat." Planning ahead to solve environmental problems can especially help small
communities that do not have the resources to meet all of the regulatory requirements at
once. Your environmental plan will help the community prioritize solutions to environ-
mental problems and develop a strategy for regulatory compliance. This approach lets the
community decide how best to use its resources, rather than simply react to regulatory
deadlines set by distant government offices. It gives you the time and opportunity to
develop the best approach for complying with important regulations, well before any
enforcement actions are taken.
Federal and state regulatory agencies are aware of the problems that face small communi-
ties in meeting environmental regulations. It will take time, however, to modify the existing
laws and regulations to allow for the community-based approach discussed throughout
this guidebook. Some state regulators have already been flexible regarding enforcement
(fines) when a community can show that it has a schedule for meeting regulatory
requirements and intends to address the worst environmental problems first. Your com-
munity can use its environmental plan to begin a discussion with regulators. You might
need to negotiate which problems to solve first, but the regulatory agencies will probably
accept a well-planned schedule of environmental actions if you show that you are doing
the best you can with the resources you have.
This guidebook presents some ideas and approaches to creating and implementing a com-
munity environmental plan. Adapt them to your local needs as you see fit:
2 Chapter 1: An Open Letter
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Chapter 2 helps you build a planning team that can lead your community
in creating its environmental plan.
Chapter 3 helps you develop a shared vision for your community's future—
that is, decide what you want your community to be like in 10 or 20 years.
Chapter 4 shows you how to define your community's needs by determining
the greatest problems facing your community's public health, environment,
and quality of life; by determining which environmental regulations apply to
your community; and by evaluating the effectiveness of your environmental
facilities.
Chapter 5 explains how to figure out which technologies and strategies
can work in your community.
Chapter 6 discusses how to weigh your community's needs and possible ways
of meeting those needs to setpriorities for action. Here, you will put all your
work together into your plan.
Chapter 7 helps you implement your plan.
Throughout the planning process, you will discover many people outside your commu-
nity—such as people from government agencies, colleges and universities, and organiza-
tions that specialize in helping small communities—who can give you assistance and advice.
Ultimately, however, the residents of your community are responsible for making decisions
that reflect your community's history, values, resources, and vision for the future. It's up
to you and your community to decide how best to handle your environmental
challenges. No other community faces exactly the same environmental issues, with the
same constraints and the same resources. No one outside your community knows what is
best for you. Local talent and energy are needed to develop the plan that's right for your
community. The tools in this guidebook, adapted for your situation, can help your
community turn its environmental challenges into a positive force for the future.
Major Environmental Responsibilities of Small Communities
Part of creating a comprehensive environmental plan
is identifying the environmental issues facing your com-
munity. If you don't recognize the problems, you can't
figure out the solutions.
Although each small community is unique, nearly all
have responsibilities in the following areas:
Drinking water quality.
• Wastewater management.
• Solid waste management.
• Leaking underground storage tanks.
Household hazardous waste management.
Emergency response to hazardous waste spills.
• Ground-water protection.
Some environmental issues affect some communities
more than other communities, including:
• Wetlands protection.
Air pollution.
• Industrial wastewater management.
• Nonpoint source pollution (pollution carried by storm-
water runoff, etc.).
Floodplain zoning.
Asbestos in public buildings.
Chapter 1: An Open Letter 3
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Comprehensive
Environmental Planning
1. Put together a planning team.
2. Develop a vision for the future.
3. Define your community's needs.
4. Identify feasible solutions.
5. Set priorities for action (with schedule).
6. Implement your plan.
4 Chapter 1: An Open Letter
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Meet Ruraltown, USA
Ruraltown, population 1,500, could be in any region of the United States.
About half of the families in the community own and run farms. Another
100 people work in a coal mine in Quarryville, 15 miles away. Employers in
Ruraltown include a tannery, several small stores, one restaurant, and a movie
theater. The nearby county park provides many summer jobs. The average house-
hold income is about $25,000 a year. The average home is worth $70,000. The
average farm is worth $500,000. The 300 children in Ruraltown go to Ruraltown
Elementary and to Carroll County High School, which is 20 miles away. There
are no buses, taxis, or subways in Ruraltown.
The nearest town, Hoppington, is 10 miles away and has 2,500 residents. The
nearest city, Metro Center, is 45 miles away and has a population of 300,000 people.
Ruraltown, Hoppington, and Metro Center are all part of Carroll County.
Ruraltown has no full-time mayor, no town attorney, and no environmental planner.
Ruraltown does have two full-time paid government employees. One is the town
clerk, who writes all birth and death certificates, keeps track of all state and federal
requirements (and does all the accompanying paperwork), collects all town taxes,
and is part of the volunteer fire department. The town also employs a full-time
public works director to operate the drinking water and wastewater treatment plants
and coordinate the municipal solid waste program.
Decisions in Ruraltown are made at a twice-yearly town meeting. The town meeting
is run by the part-time mayor, who has served as Ruraltown's mayor for more than
30 years. Ruraltown also has a part-time town council. The town council presents
information at the town meeting and gives advice on what the town should do.
The council also meets every month to take care of business that needs attending
to between town meetings.
Ruraltown is facing some serious environmental issues. Its drinking water treatment
plant is barely big enough to supply water to all the people in the community who
currently use town water, hi addition, the drinking water plant has recently had
violations of the limit for coliform bacteria.
Chapter 1: An Open Letter 5
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About 200 residents get their drinking water from private wells instead of the public
water supply. Some private wells have been contaminated by nearby septic tank systems;
others could be contaminated in the future by sources such as underground storage tanks,
improperly disposed of used oil and household hazardous waste, runoff from farms, and
contaminants leached from the landfill. The solid waste landfill poses other problems:
It does not meet all state design requirements, and it's running out of space.
Rural town also has problems in the area of wastewater treatment. Only 20 percent of
the homes and businesses in the town have sewer hookups, and the wastewater treatment
facility is old and sometimes violates permit levels. The rest of the homes and a few
businesses use septic systems. In the areas of town with shallow ground water, septic
systems have been failing during the wet seasons (spring and fall).
To help meet its environmental challenges, Ruraltown leaders have decided they need a
community environmental plan.
Throughout this guidebook, we will check in with Ruraltown and see how it's doing with its
community environmental plan. This will give you a better idea about how the planning process
works and what it might look like in one small community.
6 Chapter 1: An Open Letter
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Getting the
Right People
Involvec
Who are the "right" people to get in-
volved in creating your environmental
plan? Anyone who is concerned
enough about the quality of life in the
community to invest some time and energy. You
will also need people with some expertise on
environmental and health issues. You will probably find that people welcome the
chance to work together to find solutions to challenging issues that will shape the com-
munity's future as well as save tax dollars.
Forming a Planning Team
Someone needs to oversee the community's environmental plan. That "someone" can be
a planning team made up of people who represent the different views and constituencies
in your community. The planning team will guide the community through each step of
the planning process, including developing a community vision, identifying needs and
possible solutions, setting priorities for action, and carrying out the plan.
There are many possible approaches to forming a planning team. For example, many
communities already have land use planning commissions. This commission has demon-
strated an interest and commitment to community environmental issues, and might be
willing to oversee the environmental planning process. This approach will ensure that the
environmental planning process is well integrated with your community's comprehensive
land use plan, and vice versa.
No matter what approach you use, your team should include some of the following types
of people:
Managers or operators of environmental facilities (such as water and wastewater
systems), who are knowledgeable about environmental issues and the condition of
existing facilities.
Elected officials or board members, who already are involved in managing local
communities and are familiar with issues that affect the area's environment.
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Local physicians, engineers, and scientists, who can provide technical information
about environmental and health issues, links between pollution and health, and other
key data.
I County and state health agencies, which can provide local, state, and national health
statistics so that local conditions can be compared with state and national averages.
Emergency response personnel, usually the community's fire department, who often
know about environmental accidents, the location of underground storage tanks, and
potential sites and types of community exposure or risk.
Community residents, who represent specific interests or the "general public."
Business owners and farmers, who represent important views in the community and
can help determine future trends. (Getting a local industry or agriculture enterprise
involved is especially important if the industry or enterprise is a current or potential
source of pollution.)
Make an open invitation to the members of your community to join the planning team
and see who is interested. Try to assemble a planning team of a workable size. A team of
20 people would probably be unwieldy, but only one or two people probably would be
unable to handle all the work involved, and probably could not represent the diverse
interests of the community. If too many people volunteer, divide up into different teams
to handle specific problems or to seek out different types of information. Never turn
anyone away—you can always find some productive way to use someone's time and energy.
If too few people volunteer, keep spreading the word. No matter how large or small the
team, however, the team must include effective leaders who can produce agreement on
solutions and get results for your community.
Finding Local Experts
Right in your community, you probably have some of the expertise you need to develop a
sound environmental plan. For example, managers or operators of systems that can directly
affect the environment and people's health—drinking water, wastewater treatment, and
solid waste management systems—have the most detailed knowledge of the operation of
these systems. Scientists or engineers from local businesses and schools might be able to
answer technical and scientific questions that arise. Long-time residents often are a gold
mine of information about your community, past and present, and they might also have
financial, management, or other experience to contribute. Physicians or environmental
health professionals can provide public health statistics that might identify problems that
need to be solved immediately.
Every knowledgeable person in the community does not need to serve on the planning
team. Some people can give advice to the team when needed, even if they don't have time
to attend regular meetings. Some ways local experts can assist the committee include
answering questions by phone, providing written materials, reviewing technical documents
that deal with relevant information, and speaking at public meetings. Your team should
seek advice from local experts early on. In this way, experts can help shape the plan from
8 Chapter 2: Getting the Right People Involved
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the beginning, knowing their ideas are valued and will be considered throughout the
process.
Working With Local, County, State, and Federal Personnel
As your team develops its environmental plan, you should consult with people in local,
county, state, and federal agencies. Most of these people will do their best to be a valuable
source of information and assistance for the environmental concerns your community
faces. In fact, your state environmental agency is generally the best place to start to obtain
assistance for dealing with environmental issues. (One model for state assistance is shown
in Appendix A, which presents a cooperative environmental community agreement be-
tween state government and a borough in Alaska.) In addition, if regulatory agencies
understand your efforts to address environmental problems in your community, they might
be able to exercise some flexibility in dealing with the community on enforcement of
regulations.
The planning team might want to offer certain government agency personnel an open
invitation to attend the planning team meetings. The main role of government agency
employees, however, will be to provide information that the planning team has determined
to be important to its efforts. Local resource providers, such as Rural Community
Assistance Programs, the National Rural Water Association, and the Cooperative Exten-
sion Service, can also be a valuable source of information and assistance for small
communities. See Appendix D for a list of these useful organizations.
Encouraging Public Participation
The public includes everyone in the community. Members of conservation and environ-
mental groups, long-time residents, and people who are active in the community are good
candidates to become involved in creating the environmental plan. Including the public
in local environmental planning is essential for the following reasons:
The residents of your community are the ones who will end up paying for most new
environmental programs.
Residents will benefit from good environmental planning and management.
The public knows the community and has ideas about the kind of place in which they
want to live.
If concerned, responsible community leaders are involved in the process, they are more
likely to generate broader support for the environmental plan and for the work needed
to carry it out.
With their knowledge and ideas, community residents can help the planning team define
environmental needs and priorities.
Once you have your planning team set up, local experts committed, and key residents
identified, you are ready for the next step: creating a vision of what residents want their
community to be like in the future.
Chapter 2: Getting the Right People Involved 9
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Ways Your Planning Team Can Encourage
Public Participation
Distribute flyers and other information, such as one-
page fact sheets on local environmental issues written
by local experts, minutes of planning team meetings,
or information about important team decisions. You
can give out these materials at public meetings,
through mailings (such as with utility bills), and at local
stores, and publish them as notices or articles in the
local newspaper. The planning team should develop a
mailing list of interested groups and individuals.
Talk to local groups, such as volunteer organizations,
PTAs, service clubs, and business associations. Tell
them about the issues your planning team will address,
how the community will be affected, and why it would
be valuable for them to participate at this stage of the
planning process.
Publicize the meetings of your planning team, or hold
special meetings to get community input, so that
residents, experts, and team members can express
their concerns, exchange views, and explore possible
solutions. These meetings can be large (in the school
auditorium) or small (in someone's living room). If they
are held as part of a town meeting, you may have the
benefit of more people attending, but the agenda will
probably be quite full and the evening a long one. Be
sure to advertise the meetings well in advance—in
local newspapers, on local radio and television sta-
tions, through public notices in the town hall and in
local businesses, and in mailings to interested parties.
Ask for volunteers for tasks such as conducting sur-
veys, taking minutes at team meetings, organizing
public meetings, and reviewing information.
Invite the public to attend planning team meetings. If
elected officials serve on the team, allowing the public
to attend your meetings may be required by local or
state law. In any case, having at least some of your
team meetings open to interested members of the
public is a good idea.
Do a survey. Ask people how they feel about local
environmental issues. The survey can in elude questions
such as: "Which of the following do you think is the
most important environmental issue in our community,
and why?" List areas of particular concern in your
community. Also, use the survey to find out whether
and how much people would be willing to pay for
improvements in the areas about which they are most
concerned. The survey can be done in several ways,
such as mailing the survey to all or a percentage of
town residents (perhaps with a utility bill) or interview-
ing people about their concerns. Make sure that survey
respondents explain their views (such as why drinking
water quality is an important concern to them).
Organize school activities on local environmental
issues. You can hold a workshop, classroom program,
or festival on water conservation, recycling, or other
environmental issues. These events can be for children
only, or can be set up so that the activities are fun for
both adults and children. Children often communicate
ideas from school projects to their parents.
Talk to your friends and neighbors. Don't forget how
much news is spread byword of mouth. Talk with and
listen to your neighbors about the community environ-
mental plan at the barber shop, grocery store, gas
station, and post office. Let them know that the plan-
ning team wants their help.
10 Chapter 2: Getting the Right People Involved
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How Ruraltown Got the Right
People Involved
A Ruraltown town council member, a county health officer (Ruraltown
doesn't have one of its own), and the Ruraltown public works director
got together to form the planning team. First, they made an announcement at
the next council meeting inviting all interested citizens to contact them about
becoming members of the planning team. They also asked the local paper to
carry the same announcement. Then, they made a list of people with particular
expertise in environmental issues, including local, county, and state government
officials, facility managers and operators, local businesses, scientists and engi-
neers, environmental and civic groups, long-time residents, members of the
fire department, farmers, and school staff. They got some of these names by
looking at a local business directory and the phone book, and by asking people
in town for suggestions. They came up with a long list:
Drinking water and wastewater
treatment plant manager.
Town council member.
County health officer.
Landfill manager.
Fire chief.
Soil scientist from County
Community College.
Engineer from Tech, Inc..
Manager of the Quarryville
coal mine.
Manager of the local tannery.
Three farmers.
Town clerk.
Three retired members of the
community.
Member of PROTECT, a county-
wide conservation group.
League of Women Voters member.
Rotary Club member.
Owner of Construction, Inc..
County Extension Service agent.
Staff person from State Department
of the Environment regional office.
Staff person from State Department of
Health regional office.
Restaurant owner.
Chapter 2: Getting the Right People Involved 11
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Along with this list, they had a list of 12 people who responded to the town council and
local paper announcements about the planning team. The town council member, county
health officer, and public works director thought that if all of these people agreed to be
on the planning team, the team might be too large. So they reviewed the list and decided
to ask only one farmer, one high school teacher, and one retired resident. They also
decided to ask the staff from the state environmental and health departments, the engineer
from Tech, Inc., and the school principal to serve as advisors instead of serving on the
planning team.
They then divided up the lists and spent a busy week talking to these people about the
community environmental plan. While some were too busy or declined for other reasons,
10 agreed to serve on the planning team and several others agreed to serve as advisors.
Two planning team members (a retired resident and the PROTECT member) agreed
to find ways to get the public involved in the community's environmental plan. They
decided to:
• Set up a public meeting to introduce the idea of the environmental plan, get input and
direction from the community, and ask for volunteers. The meeting was scheduled for
one month later to allow the planning team time to prepare and to reserve the school
auditorium.
• Write and send public service announcements (PSAs) to local radio and television stations
and a press release to the local newspaper. These were run free of charge. The PSAs
and press release announced that the community would be creating an environmental
plan and invited people to the first public meeting.
• Develop a one-page flyer describing the purpose of the community environmental plan,
announcing the public meeting, and asking for volunteers to work with the team on
specific projects. This flyer was posted in local stores and the town hall, hi addition,
the flyer was mailed out with water and sewer bills and, with the help of the gas and
electric cooperative, with electric bills to all local businesses and residences. The team
also offered to speak about the planning process and what it would mean for the
community at meetings of PROTECT, the League of Women Voters, the Rotary
Club, and other groups.
• Organize an environmental poster contest in the elementary school. The theme would
be "How We Can Make a Difference in Ruraltown." The team would present awards
to the winners, and the best poster would be printed in the local newspaper.
12 Chapter 2: Getting the Right People Involved
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Developing a
Community Vision
LANDUSE
ECONOMIC
GROWTH
hat do you want your community to be like in
10 or 20 years? This is one of the first questions
that planning team members should ask them-
selves and other people in the community. The
picture you come up with is your community vision. This l- - ^^-T^8*^^^^-
vision should address not only environmental issues but all the issues you consider cen-
tral to your community's future, such as economic development, education, govern-
ment services, and quality of life. You will be creating a framework to help you make
choices about environmental goals and solutions as you develop your comprehensive
environmental plan.
To create your community vision, let your imagination go. Forget about what needs to get
done by tomorrow at noon, and instead picture what you would like to see when you look
at your town some time in the future.
Involving the Community
Because the community vision will shape important decisions, itneeds to represent a broad
consensus. Your team needs to make residents aware of what is at stake for the community
and invite them to participate in creating the vision. If you have done this well, you are
much more likely to have support for the work you do later in the planning process.
A community meeting is a good place to develop a vision for the future. (See page 10 for
some ideas about how to interest people in attending such a meeting.) Explain to those
attending what comprehensive environmental planning is all about, and ask them to guide
the planning team by defining what they want for their community.
Asking the Right Questions
You can ask questions to help people focus on what they would like the community to be
like in the future. Questions that can help the process along include:
What makes our community what it is today? Who makes up our population
(average age, income, and other characteristics)? What is unique and important about
our community socially, culturally, and historically? What are the strengths and
weaknesses of the local economy? What are important characteristics of the commu-
nity's natural environment?
13
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What are our community's values with respect to the environment, economic
growth, and lifestyle? For example, different communities have different attitudes
toward growth: some prize stability and traditional ways of life, while others view
economic growth as much more important. Some communities place great value on
preserving their surroundings in a natural state; others are more interested in promoting
population growth or industrial development.
What changes or improvements would we like to see? Changes or improvements
in the following areas might be appropriate:
— Our community's natural environment. Do we see any trends, such as loss of natural
resources or increasing pollution, that should be reversed?
— Land use. Is the current mix of land used for industrial, commercial, residential, and
recreational purposes a good balance? Should some areas be used differently in the
future? What is happening in surrounding areas? Could a major manufacturing
plant be built in the town next door? Should the planning area be enlarged to
include such possibilities? What does the county comprehensive plan call for?
— Infrastructure (roads, environmental facilities, parks, schools, libraries, police and fire
departments, etc.). What level of services do we think the community should provide?
Do we need to correct problems with our current infrastructure? How old are
components of the infrastructure, and how long will they last? If we expect the
population to grow, what new services or facilities will we need? How can these
best be integrated with existing services and facilities within the community and
neighboring communities?
— Demographics (population size, number of school-aged children, retired persons, etc.). Do
we want our population to grow or remain about the same? How much could the
population grow without seriously straining our infrastructure, resources, and the
environment?
— Economic growth. Do we want to attract new businesses to our community? What
kinds? What resources should be developed to attract new businesses? How will
this affect our quality of life?
— Community health. Does our community need to address health problems such as
infant mortality, childhood lead poisoning, nutrition, or access to health care? How
does public health in our community compare with national, state, and rural norms?
— Quality of life. What is our vision for our community in areas such as economic
well-being of residents, safety, recreational activities, aesthetics, and our sense of
community?
— Local government. Would we like to change the size, role, or structure of local
government? Should it take on or drop any areas of responsibility? Will it be
adequate given how we see our community changing in the future?
— Pollution prevention. What can be done to prevent pollution from occurring in the
first place?
14 Chapter 3: Developing a Community Vision
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Pulling the Vision Together
List all the suggestions for elements of a community vision on a flip chart or blackboard
in your meeting room. After you have discussed the questions above (and any others you
decide are important), you are likely to have a fairly long "wish list" for the future—as well
as a list of problems that residents are concerned about. You might want to take a straw
poll to let participants choose the five or six elements of the community vision that are
most important to them. Ask for more discussion of items that seem controversial, and
take another straw poll. (Expect some extreme positions to come up—such as "no growth"
or "growth at any cost"—and encourage open, frank discussion of these views.) Alterna-
tively, use a technique like that described in the box on the following page.
When you've reached some consensus, ask participants to discuss how the different parts
of the vision fit together. Do any of the goals for the future seem to conflict with each
other (such as preserving the natural environment and attracting certain businesses)? If so,
ask the participants to come up with some ideas for solving the conflict. (You might decide
to change your ideas about what types of industry you favor; or you might try to find out
whether a historically "dirty" industry has adopted cleaner manufacturing methods.)
A strong, unbiased chairperson or facilitator for this meeting is crucial to make sure that
everyone has a chance to participate and to keep the discussion on track. But don't worry
about dotting every "i" and crossing every "t" in your vision statement. The important
thing is to get direction from the community as a whole about where the community should
be going. Think of the meeting as a group of artists creating a picture in broad, bold strokes;
you and the rest of the planning team can fill in missing details later.
To tap the creativity and energy that people will bring to the meeting, be flexible and make
the meeting fun. Don't burden people with speeches that are too long or too technical.
Make sure everyone understands that they have something to contribute, even if they have
no training in planning or environmental issues.
After you've created your initial community vision, it's time for the next step: developing
a plan to make that vision a reality. This will be a dynamic process—you will need to revise
your vision as your team gathers new information and your community makes new
decisions.
Chapter 3: Developing a Community Vision 15
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Techniques for Your Community Meeting
Many different techniques are available for helping a
group define problems and agree on solutions. One of
these is the Nominal Group Technique, developed by
Dr. Andre Delbecq of the University of Wisconsin/Madi-
son. It is designed to help a group of people from
different backgrounds and experiences to clarify issues,
achieve insights into complex problems, and come to a
shared judgment. The technique allows the group to reach
conclusions in just a few hours, and it ensures equal
participation by preventing more outspoken participants
from having too much influence in group decisions.
No special training is necessary to lead a group through
the Nominal Group Technique. Materials for the method
include paper, pencils, and 3x5 index cards for the par-
ticipants, and a blackboard or flip chart for each group
leader. The seven steps in the process are described
below.
Step 1: Introduction and Statement of Task
(5 to 10 minutes). On a flip chart, the coordinator writes
the question that the participants are to respond to and
briefly explains what is going to happen. Participants
are then divided into groups of five to seven people with
a leader assigned to each group. The coordinator can
lead a group, or float between groups to ensure they
are keeping on roughly the same schedule.
Step 2: Silent Generation of Ideas (10 to 20 minutes).
Each person works silently and independently using
paper supplied to list his or her own items in response
to the statement of the task. The group leader can also
participate.
Step 3: Round-Robin Listing of Items on Flip Chart (10
to 25 minutes). Each group member concisely states one
item from his or her list. The group leader writes the
item (without rewording) on the flip chart and assigns
it a number. There is no discussion at this time. Do not
be concerned if items appear to duplicate or overlap.
Continue in round-robin fashion until all items have
been covered.
Step 4: Discussion of Items (15 to 30 minutes). Each
group member, in turn, clarifies one of the items he or
she has listed on the sheet. Other members may ask
questions about the item to be sure of its meaning. Do
not combine items. This continues until each item has
been discussed.
Step 5: Silent Listing and Ranking by Priority (5 to 10
minutes). On separate 3x5 cards, each group member
lists, by name and number, 10 of the items that he or
she considers most important from the total list. Group
members then rank the items according to their personal
priorities and write a large number 10 (for 10 points)
on the corner of the card that has the highest priority;
9 (for 9 points) on the next, and so forth for all 10 cards.
The group leader collects the cards and has someone
help record directly on the flip chart the number of votes
each item received. The number of votes received for
each item is tabulated.
Step 6: Discussion of Vote (10 to 15 minutes). The
group discusses the results of the vote. If necessary, the
group members can get additional clarification about
the meaning of individual items.
Step 7: Silent Re-Ranking of Items (5 to 10 minutes).
Using the same procedure as in Step 5, re-rank those
10 items which received the highest total scores. Re-
member, use the number 10 for the highest priority item
and the number 1 for the lowest priority item. The group
leader and his or her assistant collect the cards, record
the number of votes each item received, and tabulate
them. If there is more than one group, each group
leader turns in the completed flip chart and the 3x5
cards to the coordinator.
Many other methods exist for reaching agreement in a
group. (See Effective Meeting Skills: A Guide for More
Productive Meeting, by Marion E. Haynes, Crisp Pub-
lications, Inc., 95 First Street, Los Altos, CA 94022.)
Choose or design a discussion or voting technique that
fits your particular meeting goals and needs.
16 Chapter 3: Developing a Community Vision
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Ruraltown Creates a Vision for the Future
Nearly 50 people attended the public meeting that the planning team
held to kick off the planning process. The mayor of Ruraltown chaired
the meeting.
The planning team leaders devoted part of this meeting to discussing a vision for the future.
The people at the meeting listed some of the values and characteristics that defined the
community. The people of Ruraltown strongly value their self-reliance and independent spirit.
They don't like to be told how to run their town. At the same time, the community is proud
that it is close knit, and that people look out for each other. The residents want to preserve
their rural lifestyle but are concerned about the slow economy and the slight decline in
population throughout Carroll County. Every year, a number of family farms go under, either
because they are in financial crisis or because the young people decide to live and work
elsewhere. Few new businesses have come to Ruraltown in recent years. The community is
also concerned about a growing number of residents living near the poverty line.
With respect to its natural environment, Ruraltown residents feel fortunate to have lakes,
streams, and woods in and near the town that have been popular for fishing and other
recreational activities. They have noticed a decline in fish catches in recent years, however,
and wonder if that problem might be linked to local industries, construction, or farmland
around Running River and lakes in the area. Many community residents expressed a desire to
strengthen the environmental awareness of Ruraltown, both to protect people's health and to
preserve the natural resources of the area.
At the town meeting, residents agreed on a list of goals for the future. In 20 years, Ruraltown
should have:
• A clean environment that supports fishing, hunting, swimming, and other recrea-
tional activities. These activities and surroundings would attract vacationers as
well as people wishing to retire to a rural setting.
A substantial number of new small businesses, although farming would remain the
mainstay of Ruraltown's economy. These businesses would include those catering
to vacationers (stores, restaurants, motels) and a small to medium-size manufactur-
ing firm.
Environmental facilities (drinking water, wastewater, solid waste) to support a
moderate and sustainable economic and population growth.
New residential housing for about 50 families.
• A family physician to practice in Ruraltown.
A new community center to house recreation facilities for children and cultural ac-
tivities, such as a library. This, along with the new jobs created by small busi-
nesses, would help keep young families in Ruraltown.
Chapter 3: Developing a Community Vision 17
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Defining Your
Community's
Needs
Once you have established your planning team
and defined your vision for the future, it is
time to turn to your community's current
environmental needs. The planning team
should clearly identify the environmental needs
within the community and collect information on
these issues. Answering the following questions can help the planning team identify the
community's needs:
What are the boundaries of your environmental planning area?
What environmental regulations affect your community?
I Do any environmental problems threaten public health, the environment, or the quality
of life in your community?
I How effective are your community's environmental facilities?
This chapter helps you answer these questions.
What Are the Boundaries of Your Environmental Planning Area?
Defining the boundaries of your community's environmental planning area will help you
determine your community's environmental needs. Your community's environmental
planning area should include:
I "Problem" areas that might have actual or potential public health and ecological
impacts, such as waste disposal sites and industrial areas.
I Areas and resources that you want to preserve and protect, such as drinking water
supplies and rivers.
I Facilities and resources that are used to protect public health or environmental quality,
such as solid waste and wastewater facilities.
19
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You can define the boundaries of your community's environmental planning area in
different ways. Choose the approach that makes sense for your community.
Advantages of Beginning Small
Begin with a geographic area small enough to ensure that your community has the
resources and authority to carry out the plan it develops. For example, you could define
your environmental planning area as the area within your town or village boundaries,
if your community is incorporated. You might also wish to add nearby areas that are not
within the town or village boundaries but that might influence or be affected by your town's
environmental planning, for example, areas served by your drinking water, wastewater,
solid waste, fire department, or other facilities.
The Regional Advantage
Alternatively, you might wish to use county boundaries (or boundaries of other political
units) to define the environmental planning area. And, if an important natural resource,
such as an underground drinking water source, crosses county lines, consider including
the larger area served by this resource in your environmental planning area. County or
other regional boundaries offer the opportunity for several localities to work cooperatively
on common environmental and infrastructure issues and to share costs. If you are
considering a regional approach, consult with the neighboring communities to see whether
they are interested in collaborating with your community. Check with county agencies,
too; without county support, a lack of authority will limit the value of a regional approach.
Where permitted, special purpose districts may solve this problem.
Physical Characteristics and Natural Conditions
You could also limityour planning area by usingphysical characteristics rather than town
or county boundaries. This approach is appropriate for regions where a mountain ridge,
for example, tends to separate the towns on one side from towns on the other. If this is the
case in your community, consider limiting your community's environmental responsibility
(facilities) to the area on your side of the mountain or other natural feature that separates
the two regions.
To prepare for the planning process, be sure to examine the natural conditions within your
planning area to identify locations that might be more or less vulnerable to environmental
damage. For example, if you overlay a map showing onsite septic system failures onto a
soil map, you might be able to see clearly the areas of good soil where onsite wastewater
treatment systems will work well and the areas where wastewater collection and cluster or
centralized treatment and disposal are needed. An additional overlay of ground-water
quality might further refine this analysis.
Adjusting the Area as Appropriate
In general, you should begin with your community boundaries. These boundaries can be
adjusted if needed, for example, if new data on projected growth becomes available, or if
one or more issues suggest that you should consider a combined (regional) approach. Once
you have defined the boundaries of your environmental planning area, you can identify
the environmental concerns within this area.
20 Chapter 4: Defining Your Community's Needs
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What Environmental Regulations Affect Your Community?
As you develop a community environmental plan, keep in mind that you are not operating
in a vacuum. Federal, state, and county governments have many regulations covering
almost every environmental issue that could concern local governments. These regulations
are meant to protect everyone from the potential hazards associated with pollution.
Unfortunately, this goal cannot be achieved in the same way in all types of communities.
Local governments have justifiable concerns that these regulations cannot be implemented
without outside funding, but remember that pollution does not respect boundaries. If a
town upriver from your town dumps untreated sewage into the river, this sewage could
pollute your water supply. Even if your community is environmentally responsible, you
can't be sure that other communities will be the same. Protecting the environment and
preventing pollution has to be a collective effort.
You should be aware of environmental regulations when you develop your environmental
plan for several reasons:
The regulations might help youidentify some of the environmental issues thatyou face.
Complying with regulations will help you protect people's health and the environment.
Complying with regulations will help you avoid the direct financial costs of pollution.
(Pollution of natural resources costs money and jobs.)
You might incur fines and legal fees if you don't comply with environmental regulations,
even if your reason for noncompliance was being unaware of the regulation's existence.
Understanding what regulations apply to your community will help you avoid these
costs.
Environmental regulations might themselves present major problems for small commu-
nities. These are some common complaints heard from small community decision-makers:
There are too many different regulations. (Actually almost 800 regulations exist, of
which half require the town to do something and the other half require the town to
oversee other people, places, or things.)
Finding out about new regulations that affect my community is difficult.
The regulations are written in complicated, technical language.
The regulation deadlines don't give my community enough time to comply.
The regulations require my community to do something that it can't afford
and don't help pay for it.
The regulations require costly actions to prevent or stop problems that do not
exist in my community.
These are important concerns, addressed in part by Appendix B of this guidebook. The
appendix describes the major federal regulations that affect most small communities and
gives information on the steps your community is expected to take to meet these require-
ments. In addition, the assistance providers listed in Appendix D can help you understand
exactly which regulations apply to you and how.
Chapter 4: Defining Your Community's Needs 21
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Regulatory Compliance Needs
in Ruraltown
Ruraltown planning team members consulted with state regulatory officials
to review the regulations that applied to the town. The team then made
a list of the regulations that the town was not meeting:
Drinking water samples at the community treatment plant recently ex-
ceeded the maximum contaminant level (MCL) for coliform bacteria.
• The drinking water system cannot meet firefighting requirements in
certain parts of town due to low pressure.
The drinking water plant is not meeting all the applicable monitoring
requirements for chemical contaminants.
• Discharges from the wastewater treatment plant exceed permit limits for
suspended solids and organic matter during some periods.
The landfill does not meet state design requirements.
• The elementary school has not been inspected for materials containing
asbestos.
22 Chapter 4: Defining Your Community's Needs
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The information in Appendix B can help you determine which regulations apply to your
community and what the deadlines for compliance are. You will probably need to consult
with staff from your state agency to develop a complete and accurate list of the regulatory
requirements you must meet. This list can be important when you set priorities for action
(Chapter 6).
The descriptions in Appendix B are based on information available in 1994. Some of this
information is likely to change in the future. In addition, state and local requirements might
differ from federal regulations. Be sure to contact someone at your state regulatory agency
to find out if your state's rules are different in any way. Also, find out whether there are
county regulations in addition to your state's requirements.
Do Any Environmental Problems Threaten Public Health, Ecosystems, or
the Quality of Life in Your Community?
A key step in defining your community's needs is determining whether any environmental
problems pose a serious threat to your residents and surrounding ecosystems. Your team
can develop a list of environmental problems by thinking about possible threats to the
health of residents (such as unsafe drinking water), specific pollutants or pollutant sources
in the community (such as pesticides used near drinking water wells or leaking petroleum
storage tanks), and natural resources being affected by pollution (such as a river with
degraded aesthetic qualities and a declining fish population). Also think about threats to
residents' quality of life, such as loss of recreation areas or higher taxes to pay for replacing
a polluted drinking water well.
Your list of environmental problems should include not only concerns that exist today but
also possible future problems. For example, a town's drinking water well might not be
contaminated now, but possible releases of pollutants from particular sources (such as gas
stations or a landfill) near the well might contaminate the well in the future. Suchpotential
risks should be included in your list of environmental concerns. To help determine
potential risks, ask "what if" questions, such as "If pollutants leaked from the landfill,
what effects might this have on people's health or the environment?"
It's a good idea to involve the broader community in this step. People outside your planning
team might have concerns that you haven't considered. If these concerns are never heard
by the team, public support for the comprehensive environmental plan might suffer. If you
held a communitywide meeting to define a community vision, you probably came up with
a list of residents' concerns at that time. If not, consider conducting a special open meeting
of the planning team to involve interested members of the public.
After you've developed a comprehensive list of environmental problems, your team should
determine which are the "high-risk" problems: which pose a serious threat to health, the
environment, or quality of life. This will help you targetyour resources wisely when putting
your environmental plan together. To help you figure out which problems are high-risk,
Appendix C presents a more detailed discussion about risks along with some questions to
help you assess risks. You might also want to consult with experts to help you determine
the high-risk problems in your community. Start with any scientists who have been
Chapter 4: Defining Your Community's Needs 23
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Topic
Potential Sources of Information About Risks in Your Community
Potential Source (see key)
Air quality
Asbestos in public buildings
Business and industry information
Chemical hazards
Chemical releases/spills
Climate
Disease rates in the community
Drinking water quality
Ecosystem/habitat quality
Fish and wildlife
Flood hazard areas
Forest quality
Ground water
Hazardous waste sites
Land use/topography
Lead paint hazards
Nonpoint source pollution
Parks and other recreation areas
Pesticides
Population figures
Regulatory information
Radon
Soils
Solid waste
Surface water
Underground storage tanks
Wastewater system performance
(onsite)
Wellhead/watershed protection
Wetlands
1,8,14
1,8,16
7,8,17, 19
1,6,8,14, 15,19
1, 7, 8, 19
5,14
6,8, 13, 14, 15, 16
1,8,13, 16
1,8,9,10, 14,20
1,8,9,10, 14,20
2,18
1,8,9,10, 14,20
1,2,8,14,21
1,8,19
2,4,8,14, 18
1,8, 13, 15, 16
1,8
9,10,20
1,3,4,6,8, 11, 12,14
8,16, 18,22
1,8, 12, 13, 16, 18
1,8,13, 14,15, 16
2,4,8,12, 14
1,8
1,2,8,13, 14,16,20,21
1,8,19
1,8,12, 16
1,2,8,12, 14,21
1,2,4,8,14
Key
1. U.S. Environmental Protection Agency
(EPA) regional office
2. U.S. Geological Survey (USGS)
3. U.S. Department of Agriculture (USDA)
4. USDA Soil Conservation Service
5. National Weather Service
6. Agency for Toxic Substances and Disease
Registry (ATSDR)
7. Toxic Release Inventory (TRI)
8. State regulatory agency (e.g., department
of health, department of environment, de-
partment of natural resources)
9. State department of fish and wildlife
10. State department of forestry; U.S. Forest
Service
11. State farm bureau
1 2. County agricultural extension service
13. Local or county board of health
14. Local university or college
15. Local physician
16. County health officer
1 7. Local chamber of commerce
18. Local/Regional planning board
1 9. Local emergency response team (usually
the fire department)
20. State, county, or local parks and recreation
department
21. Local water department
22. State data center
24 Chapter 4: Defining Your Community's Needs
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working with or advising your planning team. If they can't provide the help you need, ask
them who might be able to, or get in touch with one or more of the following:
Representatives of the state department of health, natural resources, or environmental
protection, or of the EPA regional field office.
Scientists at a nearby college or university.
The county health officer or local physicians.
The box on page 24 contains a more detailed list of information that might be available
from agencies and organizations. These experts will not have any magic formulas to help
you understand the risks you face. Scientific information about environmental risks often
does not exist, is incomplete, or is hard to interpret. Experts should, however, help you get
a clearer picture of what the most serious risks are, and perhaps help you uncover some
problems you otherwise would not have addressed.
Of course, identifying certain problems as "high-risk" is only one of the tools to help you
put together your environmental plan—it does not mean you can forget about the rest of
the problems. You might need to address lower risk problems for regulatory reasons.
Community residents might consider lower risk problems of great importance. You might
be able to implement some simple, low-cost solutions to lower risk problems, while still
giving adequate attention to the highest risks. Chapter 6 discusses in more detail how you
can take all these factors into account and set priorities for action.
A number of states and cities have carried out complex "comparative risk" projects to
evaluate risks to people and ecosystems and to help them make the best use of their
environmental protection resources. These projects usually involve teams of scientists and
other experts who spend months analyzing data and discussing their relevance. Appendix
C includes a list of the states, cities, and tribes that have comparative risk projects
completed, under way, or in the planning stages. If such a project exists in your state, you
might be able to obtain valuable information or insight from the project to help you identify
high-risk problems in your community.
The box on pages 26 through 28 describes how Ruraltown went about defining the
boundaries of its environmental planning area, listing its environmental problems, and
identifying which problems were potentially serious threats to its residents and the
environment.
Chapter 4: Defining Your Community's Needs 25
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Ruraltown's Environmental
Problems: Defining Boundaries and
Identifying High-Risk Problems
The planning team discussed what locations to include in the community's en-
vironmental planning area. Everyone on the team agreed that at least everything
within the town boundaries should be included, since the town had its own landfill
and drinking water and wastewater plants. Using town boundaries would also include
private wells and septic systems. A staff person from the State Department of Natural
Resources suggested that the team consider including a larger area than the town
boundaries, because some areas near the town's drinking water wells but outside of
the town boundaries (including some farms and onsite septic systems) could affect
drinking water quality in the future. The team discussed this with county officials,
who agreed to help the team implement necessary programs in these areas where
they had the authority to do so.
The planning team held a meeting to develop a list of environmental concerns in
the community. The team opened the meeting up to interested members of the
public, placing a notice in the local newspaper several weeks in advance. At the
meeting, team members listed the following environmental concerns:
The drinking water treatment plant had recent violations of the coliform maxi-
mum contaminant level (MCL).
• The drinking water treatment plant's monitoring program for chemical con-
taminants had been cited as inadequate by the state.
The drinking water system is undersized; pressure is too low to meet firefight-
ing requirements in some parts of town.
There are high fecal coliform counts in private well supplies near septic tank
systems in areas with high ground water.
Pesticides are used near drinking water wells.
• Underground fuel storage tanks at the school and fire station are aging and
might leak.
• Discharges from the wastewater treatment plant occasionally exceed permit
limits for suspended solids and organic matter, especially after severe storms.
26 Chapter 4: Defining Your Community's Needs
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• The landfill is almost full and doesn't meet the new state guidelines.
• Land-applied fertilizers in rainfall runoff are polluting lakes and streams.
• Leaf burning by residents is blamed for some health problems in the town.
• Improper disposal of used oil on the ground and to septic systems by "do-it-your-
self oil changers could cause contamination of drinking water wells.
• Improper disposal of household hazardous waste to the landfill could result in con-
tamination of drinking water wells.
The custodian suspects that there is deteriorating asbestos insulation in Ruraltown
Elementary School, which has not been tested for asbestos.
Several community residents attending the meeting added concerns to the list:
There is deteriorating lead paint in many homes.
• Runoff from construction sites upriver from the town might be causing a reduced
fish catch in Running River; tannery wastes also might be polluting the river.
The planning team then spent time over the next several weeks talking to local and state
experts about each topic. They asked the experts to help them figure out the risks posed
by each problem. These advisors provided much of the information the team needed.
For example, the team had the drinking water from two private wells tested for pesticides
used on nearby farms. The wells chosen for testing were those located closest to and
"downstream" from the farms. The team asked a scientist from the state environmental
agency to explain the potential health effects from consuming water containing the small
quantities of pesticides that were detected. This scientist advised the team that the current
risks were small but could increase in the future if pesticide contamination continued.
She confirmed the town's concern that the aging underground storage tanks and surface
water pollution from fertilizer were serious threats to natural resources. Several other
scientists suggested that the team consider radon in homes a potential concern, since a
number of homes in nearby communities had been found to have elevated levels of radon.
Armed with the information they had obtained, the team met again, discussed Ruraltown's
environmental problems, and hammered out a list of the high-risk problems. They
were:
• Drinking water samples that exceed coliform MCL (high risk to health).
• Drinking water system that is undersized (high risk to quality of life).
High coliform counts in drinking water well supplies near septic systems in areas
with high ground water (high risk to health).
Chapter 4: Defining Your Community's Needs 27
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Aging underground storage tanks (high risk to health and quality of life).
Wastewater treatment plant effluent that exceeds organic matter and suspended sol-
ids limits (high risk to natural resources and quality of life).
Septic systems failing during wet seasons (high risk to health and
quality of life).
Landfill that doesn't meet design requirements and is almost full (high risk to
quality of life).
Surface water pollution by fertilizers (high risk to natural resources and
quality of life).
Lead paint in homes (high risk to health and quality of life).
How Effective Are Your Community's Environmental Facilities?
The most basic step in identifying your community's needs is the evaluation of your
community's environmental facilities, such as solid waste (some combination of landfills,
incinerators, transfer stations, and recycling centers), drinking water (some combination
of a centralized source and treatment plant, distribution system, and private wells), and
wastewater (either a centralized collection and treatment plant, smaller plants serving
several buildings with sewers, or individual home systems). Your environmental facilities
might also include structures involving little or no capital or equipment, such as buffer
strips, wet ponds, and swales for runoff management.
Your planning team should work with the people who manage and operate your environ-
mental facilities to identify problems. A facility might perform ineffectively if it is too
small to serve the number of people in the community or if it is operated improperly or
inefficiently. Some problems might even pose a risk to health, ecosystems, or quality of
life. For example, a landfill could leach chemicals into ground water that constitutes the
town's drinking water, or a wastewater treatment plant could generate odors in the
surrounding area.
Ineffective performance of environmental facilities is also a constant drain on a commu-
nity's finances. Inadequate performance might indicate that operations at the existing
facility could be improved or that a community needs a new or upgraded facility. Often,
minor modifications of an existing facility greatly improve performance and lower costs.
Evaluating facility performance also helps the community identify potential risks to
people's health and the environment and helps determine whether the community is
complying with regulatory requirements.
28 Chapter 4: Defining Your Community's Needs
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To find out whether your community's environmental facilities are performing adequately,
the planning team, along with each facility's manager, should consider several factors,
including the design, administration, operation, and maintenance of each facility, as
discussed below. This step might require assistance from outside experts. Many states can
assist in this process, as can independent resource providers such as the National Rural
Water Association and the Rural Community Assistance Program (see Appendix D).
Does the Facility's Design Meet the Community's Needs?
Each facility, including its equipment and processes, was designed with certain goals in
mind. Determine whether your community has the same goals today. Your community
might or might not have changed since the facility was designed. Asking the following
questions will help the planning team determine whether the facility's design is still
adequate:
I Is the plant design adequate for the community's current requirements (such as the
number of people now receiving public drinking water)? Can it meet needs (such as
new people or businesses moving into the community)?
Does the facility meet the requirements of current regulations? Will it meet the
requirements of regulations that have been issued but are not yet in effect?
Are maintenance problems increasing as the plant ages? For example, do staff often
"jury-rig" solutions to operating problems?
Will the facility meet your future needs? (Refer to your community's vision for the
future.)
Is the Facility Run Effectively?
Administration of a facility involves managing, staffing, training, and funding. You can
assess how well the facility is run by asking the questions below.
Management
Are facility managers clear about what the system is supposed to accomplish and
whether these goals are currently being achieved?
I Have managers evaluated whether services, equipment, and facilities will need expan-
sion to meet future needs?
I Have alternatives (such as another water source, transfer of solid waste to another
facility, alternate wastewater treatment options, or intergovernmental agreement to
share equipment, personnel, or services) been identified if needed in an emergency or
for future increased use?
Staffing
Are there enough employees to handle the job?
Do employees understand their specific responsibilities?
Are staff encouraged to make recommendations for improved performance?
Chapter 4: Defining Your Community's Needs 29
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Are employees capable of handling future needs if services change or increase (for
example, if recycling is added to solid waste facilities)?
I If the state requires certified (licensed) operators to perform certain tasks, does your
staff meet these requirements, or have you made other arrangements with neighboring
certified operators?
Training
Do any employees need specific training to perform tasks properly?
Do employees periodically receive additional training from universities or other sources
to update their knowledge and skills?
Do they receive proper training whenever they are required to perform new tasks or
procedures?
Is the staff encouraged to seek certification training (if a certification program exists)?
Funding
Are the revenues generated adequate to meet operation, maintenance, and all other
costs, including unanticipated emergencies? Do customer rates include all costs of
providing the service?
I Are enough funds available to replace equipment at the end of its nominal or estimated
service life?
Are funds being set aside for improvements and expansions?
I Has the community considered using qualified local people, rather than more expensive
outside personnel, to perform necessary tasks? Has the community considered recruit-
ing qualified volunteers (individuals or service/professional organizations)?
Efficient Operations Are Key to Good Performance
The following operational factors should be evaluated for each of the environmental
facilities in a community:
I Capacity. Are the drinking water and wastewater facilities operating close to the limits
of their design? Is the landfill almost full? If the answer is "yes" to either of these
questions and you expect the population to increase significantly in the near future,
increased capacity will probably be needed in the near future. Consider alternative
approaches to such costly expansion as soon as possible, while they are still viable.
Flexibility. Can the facility cope with potential changes in the quality of raw water supply,
changes in wastewater flow during storms, or changes in the flow of solid waste?
Equipment. Is old equipment breaking down often? Should it be rebuilt or replaced? Is
equipment performing as efficiently as possible? Does it meet design performance
specifications?
Processes. Are mechanisms that control each process operating well? Have adjustments
been made to make the process more efficient or effective?
30 Chapter 4: Defining Your Community's Needs
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Operational Hazards. Have potential hazards been identified, and are they controllable?
Ways to prevent operational hazards include employee training, building a secondary
containment structure to store and contain chemicals, and installing safeguards and
interlocks on equipment.
Procedures. Have operating procedures been developed and incorporated into an up-to-
date operations and maintenance manual? Are employees familiar with correct proce-
dures? Are easily understandable, written operating procedures readily available to
employees at all times, and are they used? Are notices prominently displayed listing
procedures that should not be used (such as mixing incompatible chemicals)?
Emergency Response. Is emergency equipment readily available and regularly checked?
Have emergency procedures been established? Are all employees aware of emergency
procedures? Are telephone numbers and addresses of important officials and emergency
response team members readily available?
Recordkeeping. Are good records kept? (For example, for drinking water systems, this
should include records of the amounts of water treated; chemicals used and amounts;
results of water quality tests; and maps showing the entire distribution system, including
locations of mains, service connections, valves, pipes, pressure vessels, instrumentation,
and shutoffs.)
I Chemical Use. Are chemicals being used efficiently in drinking water and wastewater
treatment plants? Is more of a chemical being used than was anticipated? If so, why?
Can a chemical be used that is less expensive, is less harmful, or requires less operation
and maintenance?
I Corrective Actions. If operating problems were identified in the past, have they been
corrected?
Training. Are programs in place to train new employees and keep current employees
up to date?
Preventive Maintenance. Does the facility staff perform preventive maintenance on a
regular basis to minimize equipment failures? Are noncapital facilities, such as wet
ponds and buffer strips, adequately maintained?
If problems exist at a facility, the planning team has identified another potential environ-
mental need: improving the environmental facility. The community might need to define
the problems further, for example, by undertaking a Composite Correction Program with
the help of a state or local assistance provider (see Appendix D). Once the problems have
been defined, the community needs to determine the possible costs of resolving the
problem (for example, the costs of buying new equipment, using supplemental processes,
or constructing a new facility). Make sure to consider the possibility of partnerships with
other units of government (towns, counties, special districts) to perform maintenance tasks
(see Chapter 7).
The boxes on pages 32 and 33 include additional information specifically for drinking
water, wastewater, and solid waste facilities. The box on page 3 5 describes how Ruraltown
evaluated its environmental facilities.
Chapter 4: Defining Your Community's Needs 31
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How Effective Is Your Drinking Water Facility?
Are water samples taken regularly and
properly as required by the state?
Has drinking water failed to meet regula-
tory limits? How many violation notices
has the facility received?
Have residents complained often about
the odor, appearance, or taste of the
water?
Are operators knowledgeable about the
facility's treatment processes (such as floc-
culation, sedimentation, filtration, and
disinfection)? Are these processes per-
forming effectively, and are corrections
made when they are not functioning at
their best?
Does the facility use water meters to
charge its customers for water use? Me-
ters can provide an incentive to conserve
water, since the less a customer uses, the
less he or she pays. Is the accuracy of
meters checked periodically?
Does the facility manager know how
much "water loss" is occurring? Water
loss is the amount of water being pro-
duced that is not being received by or
billed to customers.
Do charges cover the cost of operation
and maintenance and planned replace-
ment costs?
How Effective Is Your Wastewater Facility?
Are your wastewater treatment plant op-
erators knowledgeable about the treat-
ment facility's processes, such as aeration,
clarification, and sludge (biosolids) han-
dling? Do they regularly monitor and
adjust processes to improve perform-
ance?
Is your sludge management system capa-
ble of properly processing all the sludge
produced?
Does excessive infiltration/inflow of
stormwater occur in the collection sewer
line? Does the flow bypass the treatment
system during peak flow conditions?
Is your system in compliance with all Na-
tional Pollutant Discharge Elimination
System (NPDES) permit limits or condi-
tions?
Has the facility received complaints from
residents regarding odors, appearance,
receiving water quality, overflows, orhigh
user charges?
How Effective Are Your Community's Septic Systems?
Is the water draining slowly from or back-
ing up into sinks or toilets? If so, the pipes
might be clogged (with disposable dia-
pers, sanitary napkins, etc.), a pipe might
be broken (from heavy machinery travel-
ing over the ground above the pipe), or
tree roots might have entered a pipe.
Is smelly or dark liquid present on the
ground surface above the drainfield? If
so, the drainfield or soil may be inade-
quate to soak up the liquid during wet
periods of the year.
How often has the tank been pumped? If
more often than every 3 years, the reason
should be determined. The problem is
usually in the soil, not the tank, and pump-
ing only provides temporary relief.
32 Chapter 4: Defining Your Community's Needs
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How Effectively Does Your Community Manage Solid Waste?
Even if your community's handling of solid
waste is not an immediate concern, it most
likely will be in the very near future. Think
about the following questions:
Landfill Concerns
Is the community's landfill almost full?
Will you need a new place to dispose of
solid waste within the next few years?
Has the community identified an alterna-
tive disposal method or area?
Does the landfill meet state/federal
ground-water monitoring requirements?
(Check with your state agency.)
Waste Reduction
• Does your community have a waste re-
duction program? Is one required by the
state?
Recycling Efforts
Does the community have a recycling pro-
gram (including collecting the materials,
finding markets, and getting and keeping
residents involved)? Many states have
passed regulations requiring increased
recycling of various materials, such as
paper, glass, metals, yard wastes, and
plastics. Check with your state agency to
find out about your current and future
compliance with the regulations and the
markets for these materials in your area.
Costs
• How much does solid waste disposal cost
your community? Is the cost rising signifi-
cantly? If so, think about alternatives to
disposal (recycling, composting, or re-
gional incineration programs).
Do fees charged to community residents
reflect all costs of solid waste manage-
ment (such as costs to collect the trash, run
the disposal facility, and administer the
program)?
• Can the community's landfill meet state
requirements for financial assurance, li-
ability, and postclosure care? Check with
your state agency about these require-
ments.
Management
Has the community conducted an analysis
of its solid waste to determine its content
and amounts produced? Most small com-
munities have not done such an analysis,
but it could help the community decide the
best ways to manage wastes (such as what
percentages could be recycled, com-
posted, incinerated, and disposed of in a
landfill). This information can also help
the community decide what services or
equipment are needed (such as trucks,
bins, landfill/incinerator capacity, types
of markets for recyclables). This analysis
should include anticipated future changes
in disposal and recycling patterns. (Refer
to your community's vision for the future.)
Since local data are not likely to be avail-
able, national average data can be used
for planning purposes.
Regional Approaches
• For many small communities, a regional
approach to solid waste management is
the best solution. If several communities
join together, they can:
— Share the task of looking for markets
for recyclables and offer these markets
larger quantities of materials (a big
plus in the recycling business).
— Combine the wastes that each commu-
nity sends to landfills or incinerators
and pay lower user fees for these
higher volumes.
— Jointly use collection trucks.
Chapter 4: Defining Your Community's Needs 33
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Is Your List of Needs Adequate To Meet Your Community's Vision
for the Future?
After you have done the work suggested in this chapter, you will have defined your
community's environmental needs using three approaches: what problems pose the great-
est threat to your community's residents and natural resources, how well your environ-
mental facilities are serving your community, and what regulations you must meet. You
will probably see a lot of overlap among these three lists. Combine all three into a "master
list" of needs that eliminates duplication and is easier to work with. Then revisit the
community vision to make sure that the goals expressed there are addressed by your list
of current needs. If an important item is missing, you might want to add it to your list of
current needs. For example, if you envision economic or population growth in the coming
years, as Ruraltown does, make sure that you evaluate whether expanded capacity of your
drinking water, wastewater, and solid waste facilities is needed.
34 Chapter 4: Defining Your Community's Needs
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Ruraltown Evaluates Its
Environmental Facilities
Ruraltown's planning team talked with the people who manage and operate
the town's environmental facilities, and summarized the facility needs in
the following list:
• Landfill does not meet state requirements and is almost full; need to
expand or find alternatives.
Need to increase capacity of drinking water treatment system; already un-
able to attain firefighting pressures at certain locations, and some people
with private wells want to be connected to public water supply. Also need
to meet coliform MCL and monitoring requirements for chemical
contaminants in drinking water.
Need to improve performance of wastewater treatment plant with respect
to suspended solids and organic matter removal, because town wants to re-
duce reliance on septic systems, especially in areas with shallow ground
water. Improving the wastewater treatment system will encourage growth
and development in the town center and help prevent further loss of rural
landscape and farms.
Before making any final decisions about the drinking water and wastewater
facilities, the planning team asked for help from state and local assistance
providers. The state performed a comprehensive performance evaluation on the
wastewater treatment plant. This evaluation showed that the plant could be
brought into compliance, except during rainstorms and snow melting periods.
(The town would need to make long-term improvements in the collection
system and the treatment plant, however, to realize its vision for the future.) A
coalition of resource providers analyzed the drinking water plant. This analysis
verified earlier findings that distribution system and disinfection system up-
grades were needed.
Chapter 4: Defining Your Community's Needs 35
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Finding Feasible
Solutions for Your
Community
Cnce you've defined your community's
needs and refined your community vision
for the future, it's time to look for possible
solutions. You've pinpointed a destination
on the road map and convinced many people
in the community to make the journey. Now it's
time to look at the vehicles you can use to get
there. There are many factors to consider: You
probably can't afford a Porsche, but you don't
want an old car that breaks down in the middle of a trip. To get adequate transportation,
you might need to car pool with neighbors. And you have to consider whether your vehicle
will need frequent maintenance.
This chapter helps you begin to figure out which solutions will work for your community.
Although most small communities do not have every problem discussed in this chapter,
and many will have problems that are not discussed, some of the best solutions for the
typical problems faced by small communities are presented. This chapter shows you how
to evaluate available options, taking into account such factors as cost and local environ-
mental constraints. Some of the possible "vehicles" for reaching your destination are
technological (structural), such as new treatment technologies. Others are management
(nonstructural) solutions—setting up a water conservation program or an educational
program about household hazardous waste, for example. A solution to one problem might
affect (positively or negatively) another problem. At this step, you should determine all
solutions that are feasible for your community and estimate what they might cost and what
they might achieve. This information will be critical when you set priorities for action.
Technology and Management Options for Small Communities:
An Overview
The list of solutions that can be applied to environmental problems is nearly endless. This
chapter presents a brief description of some of the solutions to issues that nearly all small
communities face. You will need to find out more about these solutions if you think they
37
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might be suitable for your community. Your goal here is to gain information about the
solutions that might be suitable for your community, including:
What each solution can achieve.
What factors can limit a solution's effectiveness.
What the capital and operating costs are.
I How easy or difficult implementation is.
Pollution Prevention
Preventing pollution—rather than trying to treat it after
it happens—should be a basic principle of your com-
munity's environmental plan. Pollution prevention is the
process of identifying areas, processes, and activities
that create excessive waste byproducts to try to minimize
or eliminate the amount or toxicity of these byproducts.
This approach will help you avoid the costs of cleaning
up pollution. Here are just a few examples:
• Conserve water! A communitywide effort to conserve
water can help your town in several important ways.
Heavy pumping of an aquifer over time can cause
changes in the amountyou can pump and the chemical
quality of the water you pump. High water usage also
means that more wastewater is generated that needs
to be managed. Some simple steps—such as starting
a leak detection program and using water-saving
devices in homes—can help prevent these problems
and help avoid the cost of developing additional
drinking water and wastewater facilities.
• Don't dump used oil! Used oil should be recycled or
disposed of so that it won't pollute the environment.
Even small amounts of used oil poured on the ground,
down the drain, or into the water can contaminate the
drinking water supply of an entire community. Your
used oil should be taken to a collection center or
service station that can handle it properly. The com-
munity is responsible for providing a market or use for
this used oil for ensuring its safe disposal.
• Safely dispose of household hazardous waste! Many
common household products (e.g., most cleaning flu-
ids, disinfectants, pesticides, and paint thinners and
removers) contain hazardous constituents. Dumping
these household hazardous wastes down the drain,
into the garbage can, or on the ground can contami-
nate ground water, surface water, and soil. Many
communities have started household hazardous waste
collection programs (or worked with other communi-
ties to start them) to gather these wastes and dispose
of them safely.
Save energy! This is something every resident can do
to prevent pollution. In most areas of the country,
power plants bum oil, coal, or gas to generate elec-
tricity. Burning these fuels creates air pollution. If less
energy is needed, less air pollution is produced. Sav-
ing energy can also save you money. Your community
should promote energy conservation through public
service announcements and other means.
• Protect the area around your drinking water wells!
Every state in the nation has had incidents of contami-
nated ground water. If you protect your water source
before it gets contaminated, you can avoid some major
costs, such as the costs of sophisticated treatment
equipment, cleanup and remediation, consulting and
legal fees, water rate increases, and even reduced real
estate prices. Ask your state environmental agency,
your state Rural Water Association, or other resource
provider how to start a wellhead protection program
in your community.
Don't be a throw-away community! Landfill space is
becoming limited, and building a new landfill that
protects water, soil, and air from contamination is
expensive. At the same time, people keep generating
more and more trash. Try to reuse materials instead of
throwing them away. Try to recycle glass, plastic,
aluminum, and paper. Don't buy products with extra
packaging that has to be thrown away. A community
can provide leadership in such efforts by developing
purchasing programs that reduce waste and maximiz-
ing the use of recycled materials.
Don't litter! If everyone helps, the cost of littercollection
and management can be reduced.
Your environmental plan should also include teaching
community residents about pollution prevention. Pollu-
tion prevention is a "mind set"—a way of looking at
the world and the way we live. If everyone reduces
pollution in his or her own life, the community, its
environment, and the future will benefit.
38 Chapter 5: Finding Feasible Solutions for Your Community
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How a solution might affect other environmental problems you face or other important
community considerations.
What opportunity costs are associated with various options. (Opportunity costs are the
costs of the next best alternative—what you are giving up by choosing the option you
choose.)
At the end of this chapter, some specific solutions are presented for the following issue
areas:
I Drinking water.
Wastewater.
Solid waste.
Hazardous waste.
I Nonpoint source pollution.
Underground storage tanks.
For more information, you can read the publications listed in Appendix D and talk to one
of your local experts, your state environmental agency, and some of the organizations listed
in Appendix D.
Evaluating Costs for Technology and Management
Options
To evaluate the costs of possible solutions, consider several cost factors:
I Unit costs (such as the cost per thousand gallons treated, cost per cubic yard or ton of
waste disposed).
I Capital costs (the costs of constructing, purchasing, or upgrading equipment or
facilities).
I Annual operating costs (the costs of running equipment and facilities on a day-to-day
basis).
To make meaningful cost comparisons, the facility size must be comparable between
options and must be sufficient to handle the maximum material flows (drinking water,
wastewater, solid waste, recyclables) anticipated over the estimated life of the facility. For
example, a low unit cost for wastewater treatment will not save money if the minimum
plant size required to achieve that cost savings is four times the maximum expected
wastewater flow from your community.
Even before cost comparisons, the best screening method is to identify the conditions for
which the option is best suited. For example, small-diameter gravity systems are likely to
be the first choice where slopes provide gravity drainage to a treatment plant. "Pockets"
of homes that do not drain in this way because of their lower elevation can be fitted with
septic tank effluent pumping (STEP) units and fed into the small-diameter system.
Likewise, dense developments of 50 or more homes might be best served by vacuum
Chapter 5: Finding Feasible Solutions for Your Community 39
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sewers, while pressure sewers may be more suitable for developments of fewer than 50
homes. By knowing the best uses of each technology, a preliminary screening can assist
the planning group in discarding certain options that are unlikely to solve identified
problems.
All cost factors—unit costs, capital costs, and operating costs—should be evaluated
together. There might be a tradeoff between capital costs and operating costs. A well-de-
signed facility with higher initial costs usually provides better performance and has lower
operating and maintenance costs than a lower capital-cost, high-maintenance facility. A
variety of financial factors should be considered when deciding among options, as discussed
in Chapter 7.
Narrowing the Options
Once you have a list of possible generic options for the key environmental issues facing
your community, you need to eliminate the options that are not feasible. First, you can
eliminate any option that will not work because of factors specific to your community.
These factors could include:
I Population density.
Distance from significant population centers.
Type of water bodies and land features.
Water quality, chemistry, and quantity.
Soil type and geology.
Even though the solutions described in this guide are considered appropriate for small
communities, local conditions can preclude their use in certain circumstances. For exam-
ple, there is little point in planning for long-term use of onsite septic tank systems if no
soils in the community can support their proper functioning (because they are all imper-
meable clay soils).
Second, you can eliminate solutions that are clearly more expensive than your community
can afford. Also consider whether the costs (economic, social, ecological, or health-related)
of failing to invest in a solution are acceptable. Be careful, however, not to underestimate
what your community can afford. Your community might be able to get grants and
low-interest loans to pay for some options. Your community can also cooperate with other
communities or form partnerships with private companies to pay for some solutions (see
Chapter 7).
Third, eliminate options that require more advanced technical skills than your community
has access to, or that are too complicated for your community to administer. For example,
waste-to-energy facilities are an option for solid waste management. Solid waste is burned
in these facilities, and the heat produced is used to generate electricity. Waste-to-energy
facilities use very advanced technology, however, and are probably not feasible for most
small communities. Keep in mind, though, that cooperating with other communities and
forming partnerships with private companies might allow you to use technologies that are
too complex for your community to use alone.
40 Chapter 5: Finding Feasible Solutions for Your Community
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Looking at Characteristics of
Soil and Ground Water in Your Community
To determine whether certain technology
options are feasible, it is important to un-
derstand the characteristics of soil and
ground water in your community. For ex-
ample, some soil conditions, such as shal-
low bedrock or water table, might require
the use of special onsite wastewater systems
in unsewered areas. By the same token, a
shallow water table is more easily contami-
nated than a deep water table. The vulner-
ability of ground water affects site selection
for landfills, underground storage tanks,
and a variety of potentially contaminating
industrial/commercial activities.
Information about soil and ground water in
many areas is available from the U.S. Geo-
logical Survey and from soil surveys pro-
duced by the Soil Conservation Service
(SCS) of the U.S. Department of Agriculture.
SCS has published soil surveys for most
counties in the eastern and midwestern
United States and many counties in western
states. SCS soil maps define map units con-
taining similar soil characteristics based on
landscape position, slope, soil wetness,
depth to bedrock, type of bedrock, and
other factors. A published soil survey con-
tains tables providing information for each
map unit, including:
• The number of acres mapped.
Ratings for corrosion risk for uncoated
steel and concrete.
• Limitations forsanitary facilities, including
embankments, ditches and levees, septic
tank soil absorption fields, sewage la-
goons, trench landfills, and area landfills.
Suitability ratings for use as daily cover
for landfill.
• Suitability for dwelling structural support.
• Potential for flooding.
These maps are a very useful planning and
evaluation tool. For example, the soil map
can be placed over a township map marked
with sites where septic systems have been
repaired or replaced. This can show
whether and where a long-term strategy
relying on these systems is feasible. Laying
a map of the wellhead protection area for
the community's water supply over the other
two maps could show additional areas
where the use of septic systems should be
restricted.
Make sure that you understand exactly what each remaining solution can achieve and
whether it will create any new problems. Reviewing this information for each solution still
on your list might cause you to remove some solutions from consideration. For example,
if your community has a corrosive water supply that causes the wastewater treatment plant
to exceed discharge limits for lead and copper, you might consider adding phosphate to
the drinking water to inhibit corrosion. This strategy, however, could cause wastewater
discharges to exceed phosphate limits, and removing phosphate before discharging the
treated wastewater will increase costs.
Finally, keep in mind that you might want to use a combination of solutions for some
problems. Different solutions can complement each other or be used to handle different
aspects of a problem. For example, a community experiencing problems with septic tank
systems might develop a combination of onsite, cluster, and centralized systems for treating
wastewater, along with a communitywide water conservation program to improve the
performance of all of them. A central treatment plant can be built to serve residences and
businesses in more densely settled areas of the community, while cluster systems can serve
outlying homes for which onsite systems are not suitable.
Chapter 5: Finding Feasible Solutions for Your Community 41
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Once you have narrowed the options, you will have a list of the solutions that are feasible
for your community, along with a good idea of what they cost and what they can achieve.
Finding Solutions: Drinking Water
Your community needs an adequate supply of safe drinking water. The solutions to
consider fall into two categories: quality (source protection and treatment) and quantity
(conservation, leak detection, and expansion of supply).
Drinking Water Quality: Protecting the Source
About 95 percent of rural communities use ground water as a drinking water source. The
best way to protect ground-water resources is a wellhead protection program. A
wellhead protection program seeks to manage the land area through which water enters
the ground water that provides your drinking water. For communities that use ground
water as a drinking water source, a wellhead protection program minimizes contamination
of this valuable resource.
Similarly, your community can protect its drinking water source through a watershed
protection program if your drinking water is drawn directly from a lake, river, or other
body of surface water. Your watershed is the area of land from which water drains into
that source of surface water. Through a watershed protection program, your community
can protect its surface water resources by limiting contamination in surrounding areas.
Both wellhead protection and watershed protection are forms of pollution prevention,
which can directly benefit your community. Wellhead and watershed protection programs
involve:
Forming a community planning team.
I Delineating the wellhead or watershed area.
I Identifying and locating potential sources of contamination in the wellhead protection
area or watershed.
Managing the area to prevent contaminants from entering the water supply. This
includes regulatory (such as zoning), nonregulatory (such as public education), and
financing strategies (such as purchase of development rights).
Reviewing the protection program every year and developing a contingency plan for
alternative water supplies.
These programs are the "ounce of prevention" that can help you avoid some very expensive
cures—installing treatment, cleaning up the source, or finding a new water source, all of
which are far more costly than preventive measures. In most cases, your state and county
42 Chapter 5: Finding Feasible Solutions for Your Community
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officials can help you implement simple, inexpensive preventive measures that go a long
way toward protecting your drinking water source.
Drinking Water Quality: Treatment Technologies
Drinking water must be treated to protect the health of the people who drink it. Different
types of treatment processes tend to be used for ground water than for surface water. The
major types of drinking water treatment include disinfection, organics removal, inorganics
removal, and filtration. Although filtration is sometimes used for ground-water sources,
this process is primarily used with surface water. Table 5-1 describes some of the advantages
and disadvantages of some treatment technologies appropriate for small communities.
Proper disinfection kills disease-causing microorganisms (viruses, bacteria, and some
parasites). The process that small communities use most often is chlorination, in which
chlorine gas or hypochlorite solutions are added to the water. Removal of organic
contaminants (such as pesticides and solvents) and inorganic contaminants (such as
nitrate and lead) is important if your drinking water contains any of these substances at a
level that might be harmful to human health (usually equated to a level higher than the
EPA maximum contaminant level [MCL]). For small communities, the most suitable
technologies for removal of organic contaminants might be aeration, which strips certain
organics from the water to the air, or granular activated carbon (GAG) treatment, in which
water passes through specially treated carbon particles that have an extensive surface area
onto which the organics can attach. In the few cases where the additional removal of
inorganic contaminants is required, any one of several processes listed in Table 5-1 can be
used. Filtration removes particles of solid matter from water, usually by passing the water
through sand or other porous materials. Filtration also helps to control biological con-
tamination. Cloudy water (cloudiness is measured as turbidity) can contain harmful
microorganisms and reduces the effectiveness of disinfection.
Drinking Water Quality: Restructuring Options
Small communities may at times feel overwhelmed by the cost and complexity of owning
and operating a water treatment and distribution system. Every community wants to
provide its residents with the best possible service at the lowest possible cost. Many small
communities have found that they can achieve this goal by restructuring their water system.
Restructuring refers to changes in ownership, management, or operations that allow a
system to improve service and/or lower costs.
There are many different restructuring options available to small communities. For
example, a community may wish to join together with some of its neighbors to form a
"mutual aid" network. Through such a network, communities can share expensive equip-
ment and staff. Another restructuring option is contracting out the operation and main-
tenance of the water system. Contract service companies can be hired to handle some or
all aspects of operating and managing the water system. With contract operations, the
policy-making and financial decisions remain with the town council, thus preserving local
control. For some adjacent communities, physical interconnection with a neighboring
Chapter 5: Finding Feasible Solutions for Your Community 43
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system might be possible and might allow communities to share the cost of treatment
facilities. See Chapter 7 for more information about restructuring options.
Table 5-1
Technologies for Drinking Water Treatment
Purpose
Technology
Advantages
Disadvantages
Costs
Corrosion control
Organics removal:
Radon and organic
chemicals, including
volatile organic
chemicals (such as
benzene, PCBs,
carbon tetrachlo-
ride, and gasoline)
Ultraviolet Easy to operate and
radiation maintain.
Produces no known toxic
byproducts.
Safer than chlorine for
operations.
Limestone Easy operation.
contactor Compact.
Best for acid waters.
Aeration Easy operation.
No chemicals.
Also removes other
contaminant gases.
Best for high CC>2 waters.
See aeration systems on
next page.
Chemical addition I Economical first cost.
Very compact.
Capable of best lead and
copper control.
Granular No gaseous emissions.
activated carbon Low to medium O&M, labor,
and power requirements.
Relatively low energy needs.
A secondary disinfectant
(chlorine) must be used to
prevent bacterial regrowth
in the distribution system.
Not for very hard,
high-iron, high-CO2
waters.
Energy costs higher.
i May have high O&M
with hard water.
See aeration systems on
next page.
High operation costs —
chemicals and
equipment/controls
requirements.
Potential waste disposal
problems.
Very expensive.
Capital:
O&M:
Capital:
O&M:
Capital:
O&M:
Capital:
O&M:
Capital:
O&M:
Medium
Medium
Medium
Low
See
aeration
systems
on next
page
Low
Medium
High
High
44 Chapter 5: Finding Feasible Solutions for Your Community
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Table 5-1
Technologies for Drinking Water Treatment (continued)
Purpose
Technoloqv
Advantages
Disadvo
Costs
Organics removal
(continued)
Packed column
aeration
Diffused aeration
High efficiency for removing
volatile contaminants.
Low O&M labor
requirements.
Simple construction.
Low O&M requirements.
Potential air emissions Capital: High
problems. O&M: Medium
Might need pretreatment
to remove solids and to
prevent iron deposits and
biological growth.
Potential air emissions. Capital: Medium
Variable removal O&M: Medium
effectiveness.
Multiple tray
aeration
Simple construction.
Low O&M requirements.
Low energy needs.
Potential air emissions.
Variable removal
effectiveness.
Might need pretreatment
to remove iron and
manganese and to prevent
biological growth.
Might be subject to
Capital:
O&M:
Medium
Low
corrosion
proble
Inorganics removal:
Cadmium,
chromium, arsenic,
silver, and lead
Coagulation and
settling
Reliable process.
Also removes some organics,
bacteria, parasites,
suspended solids, and
turbidity.
High capital and O&M
costs.
Requires high skill level
for operation.
Removes only small
amounts of nitrogen,
nitrites, radium, or barium.
Large amounts of sludge
generated must be
managed.
Capital: High
O&M: High
Inorganics removal:
All inorganics
Reverse osmosis
and similar
membrane systems
Very high removal efficiency.
Simple operation.
Insensitive to dissolved
solids content.
Bacteria and colloidal
particles also removed.
High capital and
operating costs.
High level of pretreatment
required.
Very large volume
reject stream disposal
problems.
Capital: High
O&M: High
Inorganics removal:
Barium, radium,
cadmium, lead,
silver, chromium,
nitrites, nitrates,
selenium, and
radionuclides
Ion exchange
Insensitive to flow variations.
Usually best choice for
removing radionuclides.
Spent regenerant waste
disposal problems.
Might need multiple
treatments to remove all
contaminants.
Pretreatment required to
protect resin.
Capital:
O&M:
High
High
Chapter 5: Finding Feasible Solutions for Your Community 45
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Table 5-1
Technologies for Drinking Water Treatment (continued)
Technology
Advai
Disadvantages
Filtration Slow sand Economical. Significant quantities of Capital:
Easy to operate. land needed. O&M:
No chemicals required. Only particular types of
Minimal power needed. sands are suitable.
High removal of disease- May require more
causing organisms. maintenance if high-solids
or high -turbidity
source is not pretreated.
Dual or mixed I Economical first cost. Operator training Capital:
media filters Only used with pretreatment necessary. O&M:
by coagulation and settling. Pretreatment with
Land requirements less than chemicals required.
for slow sand, but more when May not be suitable for
coagulation/settling included. small communities.
High
Low
Medium
Medium
Drinking Water Quality: System Options
In some cases, when a contaminant reaches potentially harmful levels in only one part of
the service area and/or interferes with only one specialized use, a community might
consider point-of-use or point-of-entry devices. These devices are installed at a home-
owner's tap or at the point of entry to a larger area, such as a street or trailer park. Types
of treatment available with these devices include reverse osmosis, activated carbon,
activated alumina, and ion exchange. The public water supplier must monitor and ensure
the quality of water treated with these devices; therefore, the ability to monitor is the
controlling step in allowing the use of these devices.
Package plants might offer a low-initial-cost alternative to permanent treatment struc-
tures. These are modular units that usually are assembled off site and shipped to the
community. The plants contain a number of treatment technologies in one unit
and are usually used to treat surface water supplies to remove color, turbidity, and
microorganisms. Package plants that remove organic and inorganic substances, however,
are also available. Because the operational requirements for package plants are quite
significant, except in rare instances a small community should consider using them only if
the community can transfer the responsibility to another party (such as the county or a
private contractor) or restructure (e.g., combine the local system with other small systems)
to improve its ability to operate such sophisticated systems.
46 Chapter 5: Finding Feasible Solutions for Your Community
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Drinking Water Quantity: Conservation
People can do many simple things to use less water, for example, use low-flow shower
heads and toilets, place a filled plastic bottle or toilet dam in the toilet tank, or shut off the
tap while brushing teeth. Every gallon saved is one less gallon pumped, treated, and
delivered to the consumer. A water conservation program can consist of updating building
codes, conducting public education, or promoting conservation through financial incen-
tives, such as higher water rates or scaled charging systems. For example, a powerful tool
to keep water demand in check is regressive user charges, which charge customers who
use more water a higher fee per gallon used. These charges penalize usage beyond basic
requirements and encourage people to use less so that they can save money.
Check with your state about water conservation requirements. For example, for more than
10 years, California and other states have required communities planning expansion of
water infrastructure to compare structural approaches to expansion (wells, sewers, treat-
ment plants) with nonstructural approaches (leak repair, rate structure modification, and
toilet and other water fixture retrofits).
Drinking Water Quantity: Leak Detection
Finding and preventing leaks can save a lot of water. A water audit compares the total
quantity of water produced with metered water consumption. If the total metered water
usage is less than 85 percent of the total metered water production, a systemwide leak
detection survey should be conducted. Distribution pipes, treatment facilities, and water
pumps all can be sources of large leaks. Finding a leak can be difficult and expensive. Fixing
the leak, which often involves excavating covered pipes, can also be expensive. If the leak
is severe, however, the expense can be justified.
Drinking Water Quantity: Finding a New Supply
Except for communities with large growth potential or a major new water-consuming user
(such as a large subdivision), water conservation, leak correction, reuse options, and
regressive user charges may be enough to keep a community from having to seek a new
water supply. To justify these programs to members of the community, explain that the
programs avoid major capital expenses that go along with developing new water supplies.
If a major increase in the demand for drinking water is expected, however, a new water
supply might be necessary. This could be an excellent long-term alternative if a relatively
pure supply is close and available. Depleting a natural resource, however, always has a price.
Keep in mind, too, that increasing the supply will increase the cost of drinking water and
will also affect wastewater management costs.
Chapter 5: Finding Feasible Solutions for Your Community 47
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Finding Solutions: Wastewater
Domestic wastewater must be properly managed to avoid public health problems. Three
types of wastewater handling systems can be used in small communities: onsite systems,
cluster systems, and centralized systems. Your community might need a combination of
these systems, such as onsite systems in outlying areas, cluster systems in small residential
subdivisions, and centralized systems in more populated or commercial areas.
Onsite Systems
Septic systems handle the wastewater from one residence on site. These systems are very
common in small communities where homes are not close together. Septic systems consist
of a tank that retains the wastewater solids and a drainage field (leachfield) where the tank
effluent is distributed. In the leachfield, natural processes purify the liquid as it drains
through the soil.
Conventional septic systems work best on large lots with deep, permeable soils. A variety
of alternative onsite system designs are available to accommodate a range of difficult site
and soil conditions. The most appropriate system depends on factors such as how
permeable the soil is, how high the water table is, and how shallow the bedrock is.
Poorly sited, designed, installed, or maintained septic systems can result in surface ponding
in yards. Surface ponding that continues for an extensive period is considered a health
hazard and requires corrective action. Because maintenance is the only factor that can be
controlled once an onsite system is installed, a program of periodic inspection and/or
pumping is advisable. This approach, combined with public education to ensure that
owners are putting only appropriate materials down the drain, is the easiest to implement.
Repairs and replacements should always be done by professionals with the approval of local
or state authorities, since exposure to inadequately treated sewage and hydrogen sulfide
gas presents a health risk.
Although individuals usually own septic systems, a community can take a variety of steps
to maintain effective systems, including:
Periodically inspecting the system and requiring pumping when necessary.
I Requiring an operating permit that must be renewed periodically to ensure mainte-
nance.
Keeping files of all septic system locations and maintenance performed.
I Requiring prior approval by the town or county health officer of all repairs and
replacements.
48 Chapter 5: Finding Feasible Solutions for Your Community
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Setting up a fund to help homeowners with needed repairs or replacements.
In some states, legislation permits setting up onsite wastewater management districts. Of
course, one important way to improve the performance of an onsite system is to conserve
water. This reduces the volume of water the system has to handle. Detecting and repairing
leaky faucets and toilets, using low-flow showerheads, toilet dams, low-flush toilets, and
faucet aerators, and eliminating wasteful water use habits all conserve water.
Cluster Systems
In some neighborhoods individual onsite systems are inappropriate, either because lots are
too small or because other land characteristics make them impractical. In this situation, a
cluster system might be appropriate. A cluster system normally uses low-cost alternative
sewers to collect wastewater from homes in the area and transport it to a reliable, low-cost,
easily operated treatment/disposal facility. This type of system can be suitable for devel-
opments or neighborhoods of up to 100 homes but is often used for smaller groupings.
Several types of alternative sewer systems can be used to collect and transport wastewater
from residences to the treatment facility. (See Table 5-2 for a description of alternative
sewer systems.) The treatment facility is usually a larger version of an individual onsite
system, such as subsurface soil absorption systems or sand filters.
As with any treatment system, a maintenance program is essential to ensure proper
operation of a cluster system. Compared with conventional collection and treatment
systems, cluster systems require minimal maintenance. The maintenance program, how-
ever, should always be in place and clearly spelled out to homeowners who use the cluster
system.
Centralized Systems
In more densely settled areas, where multiple cluster systems are needed and onsite systems
are not practical, a centralized wastewater system might be necessary. Constructing
conventional sewers to collect the wastewater, however, is almost never practical for small
communities because of the high cost. Conventional sewers usually account for over
three-quarters of the total cost of a conventional wastewater collection and treatment
system. The high cost of constructing the sewer system might be acceptable on a
per-household basis, however, if no lift stations are required, but alternative designs are
almost always cheaper under the same circumstances. Alternative sewers—small-diameter
gravity, pressure, and vacuum sewers—can save 25 to 50 percent of the capital cost of
wastewater collection in small communities.
Many types of technologies are available for treating wastewater at a centralized plant.
Natural treatment technologies use natural processes associated with soils, vegetation, or
wetland environments to treat wastewater and include land treatment, lagoons, slow sand
filters, and constructed wetlands (see Table 5-3). These systems generally require larger
land areas than mechanical systems. Wastewater must be treated (usually by sedimentation
or lagoons) before application to land, filters, or wetlands.
Chapter 5: Finding Feasible Solutions for Your Community 49
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Table 5-2
Alternative Sewer Systems
Sewer
Option
Small-
diameter
gravity sewers
Small-
diameter
pressure
sewers
Septic tank
effluent
pump
(STEP).
Grinder
pump (GP).
Vacuum
sewers
Costs Relative
Description
A septic tank at
each house,
usually followed by
a small-diameter
sewer of
lightweight plastic
that can be buried
at shallow depths.
STEP sewers pump
settled septic tank
liquid to a
treatment facility.
GP sewers grind
up solids in
wastewater and
pump liquids and
solids to treatment
facility. Both use
small-diameter
piping buried at
shallow depths.
Wastewater is
collected in sumps
and enters sewer
through valve.
Wastewater is
drawn through
small-diameter
pipes to a central
vacuum station,
where it is then
pumped to
conventional sewer
or treatment facility.
Applications Advantages Disadvantages to Conventional
Suitable for areas
with:
Topography
sloping
downward
toward treatment
site.
Low-density
population.
High ground
water or shallow
bedrock.
Suitable for areas
with:
Flat or upward-
sloping topo-
graphy.
Low-density
population.
High ground
water or shallow
bedrock.
Suitable for areas
with:
Flat terrain.
Higher density
population.
High ground
water or shallow
bedrock.
•
•
Can be easily diverted •
around, above, or
below obstacles.
Installed at shallow
depth; can often follow
contours of land.
Low infiltration of
ground water and
stormwater.
No power required.
No infiltration of
ground water or
stormwater.
Can be built around
buildings and trees.
No septic tank
required for GP.
Installed at shallow
depth.
Some manufacturer
technical assistance
available.
Single central power
connection.
No septic tanks
required.
Least likely to have
odor and corrosion
problems.
Minimal infiltration of
ground water and
stormwater.
Installed at shallow
depth .
Manufacturer provides
technical assistance
Each service Capital:
connection requires O&M:
a septic tank.
Pumping and
disposal of septage
from each tank
required.
Pump stations might
be required in rolling
terrain.
Power required for Capital:
pumping units at O&M:
each house.
Higher operation
and maintenance
costs.
Septic tank
pumping and
septage disposal
required for STEP.
High-strength GP
wastewater.
Skilled operation Capital:
and maintenance O&M:
required.
Minimum number of
connections is about
50 homes per
vacuum station.
Low
Low
Low
Medium
Low
Medium
program.
50 Chapter 5: Finding Feasible Solutions for Your Community
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Table 5-3
Centralized Wastewater Treatment Technology Options
Technology
Description
Advantages/Disadvantages Costs
Land application:
Slow-rate infiltration (SRI).
Rapid infiltration (Rl).
Overland flow (OF).
Subsurface wastewater
infiltration systems (SWIS).
Treated wastewater is sprayed or
flooded onto vegetated soils, sandy
basins, or a grass-covered slope,
or is distributed from pressurized
laterals below the surface in gravel
trenches. Natural processes purify
the wastewater.
All but SWIS require buffer area
for separation and require a
long-term commitment of a
large land area.
Ground water contamination by
nitrates might be a concern with
SWIS and Rl.
Except for overland flow, no
discharge permit required.
SRI and OF unsuitable for
treating wastewater in cold
weather, requiring holding ponds
for storage during winter months.
Capital:
O&M:
Medium
Low
Lagoons:
Facultative.
Aerated.
Controlled discharge.
Wastewater is placed in a large
pond and is treated by the
interaction of sunlight, wind, algae,
and oxygen over time. Deeper
lagoons can be aerated to provide
additional oxygen.
Odors possible.
Large amount of land required.
May not always meet
effluent requirements.
Aerated lagoons require
significant power.
Capital:
O&M:
Low
Low to
medium
Constructed wetlands:
Free water surface (FWS).
Submerged flow (SF).
Settled wastewater is applied to a
SF-constructed wetland. Lagoon-
treated effluent is applied to FWS
wetlands. Natural processes purify
the wastewater.
FWS requires very large land
area.
Present SF design removes
organics and solids.
Low energy requirements.
Capital:
O&M:
Low
Low
Trickling filter
Settled wastewater trickling down
through a bed of rock or plastic
media is purified by the bacteria
living in the medium. The bacteria
slough off and separate as sludge
in a final settling tank.
Process is vulnerable to
freezing temperatures.
Less effective removal of toxics
and metals than activated sludge
(AS) systems.
Capable of meeting secondary
effluent standards.
Large volume of sludge
generated.
High power requirements.
Capital:
O&M:
Medium
Medium
Oxidation ditches
Screened and degritted raw
wastewater is mechanically aerated
in an oval ditch. After treatment,
liquid and sludge are separated in
a final settling tank.
Most stable performance of all
continuous flow mechanical
biological systems.
May be designed and operated
to meet water quality limits
beyond secondary effluent.
Skilled maintenance required.
Large volume of sludge
generated.
Capital:
O&M:
Medium
High
Chapter 5: Finding Feasible Solutions for Your Community 51
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Table 5-3
Centralized Wastewater Treatment Technology Options (continued)
Technology
Description
Advantages/Disadvantages Costs
Sequencing batch
reactor
A tank is filled with screened and
degritted wastewater. Wastewater
is aerated, solids are allowed to
settle, and the effluent is drawn off
and discharged. One tank or
multiple parallel tanks can be used.
Subsequent (disinfection)
processes must be oversized
or require equalization.
Most flexible mechanical
biological treatment systems
capable of phosphorus and/or
nitrogen removal.
Large volume of sludge
generated.
Can be designed and operated
to meet water quality limits
beyond secondary effluent.
Capital:
O&M:
Medium
Medium
Slow sand filters:
Recirculating (RSF).
Intermittent (ISF).
Settled wastewater is applied to the
surface of a sand bed and allowed
to percolate through the bed,
where it receives treatment.
Reliable, high-quality treatment. Capital:
RSF capable of removing (-50%) O&M:
nitrogen.
Required land area intermediate
between natural and mechanical
system.
Medium
Low
Mechanical treatment technologies use engineered facilities that treat large volumes of
wastewater in a relatively small space. They require more skilled attention and energy to
operate and are less sensitive to changes in climate compared with most natural systems.
Mechanical systems appropriate for small communities include trickling filters, oxidation
ditches, and sequencing batch reactors.
All of the above treatment systems are usually capable of meeting state standards for
discharge to surface water. (All systems that discharge to surface water must obtain a
National Pollutant Discharge Elimination System [NPDES] permit, which determines
the amount of treatment and monitoring required.)
All treatment systems produce some amount of sludge, which must also be treated and/or
properly managed. Sludge treatment systems reduce sludge volume by removing water
(dewatering). They can reduce the number of disease-causing organisms in sludge and
reduce its attraction for insects, rodents, and other animals through digestion, composting,
or adding lime. Spreading treated sludge on the land to improve soil or placing it in a
landfill are the most common disposal methods for small communities.
Depending on the wastewater discharge standards that apply to your community, a
centralized wastewater treatment facility might be required to disinfect the effluent before
discharging it to a water body. Your state may also restrict the use of certain natural
wastewater treatment or sludge disposal techniques.
52 Chapter 5: Finding Feasible Solutions for Your Community
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Finding Solutions: Solid Waste
The best approach to solving a community's solid waste problem is integrated solid waste
management—using a combination of techniques and programs to manage the municipal
waste stream. An integrated system is designed to address a specific set of local solid waste
management problems, and its operation is based on local resources, economics, and
environmental impacts.
The idea behind integrated solid waste management is that a combination of approaches
can be used to handle targeted portions of waste stream. Local officials should consider a
series of activities, each of which is designed to complement the others. For example, a
recycling program can have positive impacts on the development of a waste-to-energy
facility. Source reduction, recycling, combustion, and landfilling can all have positive
impacts on the local municipal waste management problem.
To reduce waste management problems at the national level most effectively, states,
municipalities, and the waste management industry should first consider source reduc-
tion—reducing the amount and toxicity of the solid waste generated. Recycling of useful
waste materials is the next most desirable approach. Finally, composting, incineration, and
landfilling complete the solid waste hierarchy. Suitable combinations of these alternatives
are considered an integrated management program.
For small communities, regional cooperation in solid waste management offers several
advantages. Communities that join forces can share the resources needed to promote
reduction at the source and operate recycling and composting programs. For example,
communities often can obtain better contracts for selling recyclable materials with the
higher volume of materials resulting from regional cooperation. With incineration, a
regional facility is probably the only economically feasible approach. With landfilling,
regional cooperation can result in greater efficiency and cost savings in collecting and
transferring trash and in operating the solid waste facility. Larger facilities are more
attractive to private industry, which can relieve individual towns of the responsibilities of
operating these facilities. Host counties and communities can also claim additional cost
savings.
Pollution Prevention: Source Reduction, Recycling, and Composting
Source reduction, recycling, and composting reduce the total volume of waste that must
be disposed of, thereby lowering disposal costs and extending the life of your disposal
facility (landfill).
Chapter 5: Finding Feasible Solutions for Your Community 53
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Source Reduction
Source reduction is an approach that changes the way products are manufactured,
purchased, and used so that less solid waste is generated. You can ask community members
to generate less waste by:
Reusing plastic and paper shopping bags, lunch bags, and containers. For example, local
merchants can cooperate by offering a reward for each bag returned.
I Eliminating unnecessary packaging.
Using long-life and energy-efficient products (such as light bulbs).
Avoiding disposable products if reusable items are available (such as razors and batter-
ies).
Using mulching mowers so that grass does not have to be bagged.
Similarly, your town government should consider leading by example, revising its purchas-
ing practices to follow the same principles listed above. Your community could also
consider using "pay-as-you-throw" rates for garbage collection to reduce the amount of
garbage. Over 1,000 communities, including many small communities, have adopted this
kind of system, which charges residents different disposal rates based on the amount of
garbage they generate. However, charges should reflect community attitudes. At many
locations where these systems were initiated without community support, illegal dumping
of solid waste has increased.
Recycling
Some solid wastes can be collected separately and sold to manufacturers as raw materials
for making products. Town leaders can tap into the desire among community members to
"do the right thing" by designing programs that make it easy to recycle. Recycling
collection programs range from simple, low-technology dropoff centers to complex
separation at material recovery facilities. Table 5-4 shows several recycling options.
Critical to the success of a recycling program is the availability of markets for collected
materials. Without proper markets, storing, transporting, and disposing of the recyclables
that have been collected can result in significant costs. You will need to identify marketable
materials and the potential volume of each, and find potential buyers for the materials. In
general, marketable recycling materials include:
Aluminum cans Other metal cans
I Glass bottles Some plastic bottles
High-grade office paper Newspaper and magazines
Cardboard I Metals
Wet cell batteries (such as car batteries)
For the recycling process to go full circle, the recyclable materials that have been collected
must actually be reused. Small communities can help "close the loop" by purchasing
products with recycled content and encouraging citizens and local industries to do the
same; this helps create markets that ensure collected recyclables are reused.
54 Chapter 5: Finding Feasible Solutions for Your Community
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Table 5-4
Recycling Options for Small Communities
Collection System
Description
Advantages/Disadvantages
Recycling in conjunction with
other public service
Recyclables are collected with other
public services, such as solid waste
collection.
Profits from sales of recyclable materials
are internalized within the solid waste
management program.
Regional facilities
Collected materials are pooled in a
regional recycling center or facility.
Practical in areas with sparse population.
The recycling program has independent
budgeting and money-raising power.
Able to handle more recyclable
materials, which are more marketable
for buyers.
Private recycling
operations
Recycling is done through private entities,
such as industry or waste management
firms.
Reduces capital investment in collection
equipment.
Can be selective in accepting recyclable
materials (low-value materials such as
mixed paper may not be accepted).
Public recycling drives with
volunteers
Recycling programs are run as
fundraising or public service activities.
These programs are often operated in
conjunction with local governments,
which may supply buildings, equipment,
and staff.
Increases public involvement and
awareness.
Recycling alone will not solve a community's solid waste problems, but it can divert a
significant portion of the waste stream from disposal in landfills or combustion facilities.
For a community of 1,000 people, recycling the materials listed on the previous page would
typically reduce the amount of waste disposed of in a landfill by about 5 percent.
Composting
Yard wastes (leaves, grass, weeds, and remains of plants) account for close to 20 percent
(by volume) of the municipal solid waste stream. Yard wastes can be easily decomposed by
bacteria and fungi to form a humuslike product useful as a soil amendment for gardening,
landscaping, and agriculture. A centralized yard waste composting program can be
relatively inexpensive and easy to operate, and can help reduce the amount of solid waste
bound for disposal. You can encourage homeowners to compost yard waste on their
property if a centralized system is not practical. Because home composting might attract
unwanted animal life or breed insects if not done properly, a public education or assistance
program is important. In addition, community programs that encourage the use of
mulching mowers and low-maintenance plantings can be very effective in reducing the
amount of yard waste generated.
Chapter 5: Finding Feasible Solutions for Your Community 55
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Table 5-5
Alternative Collection Systems for Sparsely Populated Areas
Collection System
Description
Advantages
Disadvantages
Direct haul
Wastes are directly hauled by
residents to a transfer or
disposal facility.
Appropriate in sparsely
populated areas, where a
collection system is impractical.
Low costs.
Can be inconvenient for
residents.
Difficult to control waste
separation.
Higher incidence of illegal
dumping.
Green box or roll-off
containers
8- to 12-cubic-yard (or larger)
steel containers are placed
strategically throughout the
community, to which residents
must deliver waste. A larger
collection vehicle collects the
waste from the container.
Reduces the travel distance
for residents, compared with
direct haul.
Less traffic congestion near
disposal facilities.
Reduces incidence of illegal
dumping compared with direct
haul.
Difficult to control waste
separation.
Costs somewhat more than
direct haul.
"Mailbox" collection
Residents leave their waste
near their mailboxes for
scheduled collection.
No community capital costs
for purchasing containers
and constructing pads.
Minimizes illegal dumping.
Assumes a collection vehicle
can travel same routes as
mail delivery vehicle.
More expensive due to labor
and need for collection vehicle.
Green bag/blue bag
collection
Residents separate their wastes
forcurbside pickup.
Allows collection of com-
postable and noncompostable
waste.
Usually feasible only for a
large (e.g., countywide)
program.
Solid Waste Collection and Transfer
Because it is labor intensive, collection is often the most costly part of a community's solid
waste management program. Efficiency in the collection system can therefore save a
community a significant amount of money. Municipal workers or private collection
services can operate the collection system. Table 5-5 describes the advantages and disad-
vantages of alternative collection systems.
Collected solid wastes are delivered either to a transfer station or directly to disposal
facilities. Transfer stations are centralized facilities where waste is unloaded from several
small collection vehicles and loaded into a large vehicle; the large vehicle then transports
waste to the disposal facility. In this way, only one vehicle has to travel the last segment of
the journey to the disposal facility. In addition, operation of a transfer station can be
integrated with other waste management options such as recycling programs. Because of
its high capital and operating costs, however, you will need to perform a careful cost-benefit
analysis when evaluating the use of a transfer station. By sharing a regional transfer station,
communities that use the same disposal facility can substantially reduce their individual
costs.
56 Chapter 5: Finding Feasible Solutions for Your Community
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For most rural and sparsely populated communities, green box or mailbox collection
programs are the most practical approach, but in some very rural settings, direct haul
might be the only option.
Solid Waste Disposal
The most common methods for solid waste disposal are landfilling and incineration.
Landfillinginvolves placing wastes in a large, specially designed cavity, then covering them
with soil (or approved alternative materials) each day. The daily cover prevents attraction
of animals and insects. Federal law mandates many specific requirements for landfills,
including that the bottom of the landfill be lined with more than one layer of impermeable
materials (synthetic plastic and natural clay) to prevent the contamination of ground water
by liquid leaching from the landfill.
Incineration involves burning combustible solid wastes (such as paper and plastic mate-
rials) in a large, specially designed furnace. The waste is reduced to an ash, which must
then be disposed of, usually in a landfill. Incinerators can generate valuable energy as a
byproduct.
Regional landfills and incineration facilities can provide practical and cost-effective re-
gional solutions for several small communities. Capital and operating costs for these
facilities are shared by a larger number of users, reducing the cost to individuals in any one
community.
Finding Solutions: Hazardous Waste
Improper disposal of household hazardous waste (HHW), including used oil, can have
major environmental consequences for small communities, especially for drinking water
supplies. A number of small communities have begun HHW collection programs and used
oil recycling programs to prevent pollution from these substances.
Household Hazardous Waste Collection Programs
Many common household products contain hazardous constituents (see Table 5-6). These
products become HHW once the consumer no longer has any use for them. The average
U.S. household is estimated to generate more than 20 pounds of HHW per year. As much
as 100 pounds can accumulate in the home, often remaining there until the family moves
or does an extensive cleanout. HHW can pose risks to people and the environment if it is
not used and stored carefully and disposed of properly.
HHW programs benefit communities by reducing the risks to health and the environment
resulting from improper storage and disposal of HHW. While programs vary across the
Chapter 5: Finding Feasible Solutions for Your Community 57
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Product
Table 5-6
Some Potentially Harmful Components of Common Household Products
Typical Toxic or Hazardous Components
Antifreeze (gasoline or coolants systems)
Automatic transmission fluid
Automobile battery acid (electrolyte)
Degreasers for driveways and garages
Degreasers for engines and metal
Engine and radiator flushes
Hydraulic fluid (brake fluid)
Motor oils, waste oils, grease and lubes,
gasoline, diesel fuel, kerosene,
#2 heating oil
Rustproofers
Carwash detergents
Car waxes and polishes; bug/tar
removers
Asphalt and roofing tar
Paints, varnishes, stains, dyes
Paint and lacquer thinner
Paint and varnish removers, deglossers,
strippers
Paintbrush cleaners
Metal polishes
Laundry soil and stain removers
Other solvents
Refrigerants
Household cleansers, oven cleaners
Drain cleaners
Toilet cleaners
Disinfectants
Ointments
Pesticides (all types)
Photochemicals
Printing ink
Wood preservatives (creosote)
Swimming pool chlorine
Lye or caustic soda
Jewelry cleaners
Cosmetics
Methanol, ethylene glycol
Petroleum distillates, xylene
Sulfuric acid
Petroleum solvents, alcohols, glycol ether
Chlorinated hydrocarbons, toluene, phenols, dichloroperchloroethylene
Petroleum solvents, ketones, butanol, glycol ether
Hydrocarbons, fluorocarbons
Hydrocarbons
Phenols, heavy metals
Alkyl benzene sulfonates
Petroleum distillates, hydrocarbons, xylene
Hydrocarbons
Heavy metals, toluene
Acetone, benzene, toluene, butyl acetate, methyl ketones
Methylene chloride, toluene, acetone, methanol, xylene
Hydrocarbons, toluene, acetone, methanol, glycol ethers, methyl ethyl ketones
Petroleum distillates, isopropanol, petroleum naphtha
Hydrocarbons, benzene, trichloroethylene, 1,1,1-trichloromethane
Acetone, benzene
1,1,2-trichloro-l ,2,2-trifluoroethane
Xylenols, glycol ethers, isopropanol
1,1,1-trichloromethane
Xylene, sulfonates, chlorinated phenols
Cresol, xylenols, heavy metals
Heavy metals
Naphthalene, phosphorus, xylene, chloroform, heavy metals, chlorinated
hydrocarbons
Phenols, sodium sulfite, cyanide, silver halide, potassium bromide
Heavy metals, phenol-formaldehyde
Pentachlorophenols
Sodium hypochlorite
Sodium hydroxide
Sodium cyanide
Heavy metals
Source: Adapted from University of Rhode Island. 1988. Natural resources facts: Household hazardous wastes. Fact sheet no. 88-3
(August).
58 Chapter 5: Finding Feasible Solutions for Your Community
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Table 5-7
Selected Household Hazardous Waste Collection Systems
System
Description
Advantages
Disadvantages
One day dropoff
collection
A licensed hazardous waste
contractor signs a contract with
the community (or several
communities) to collect HHW
on site. Residents drop off the
wastes at specified locations
on a specified day.
Most HHW is accepted.
Costs may be reduced if
more communities are involved.
Most widely used collection
method.
Possible congestion or delays
at collection point.
Public participation is limited
to volunteers.
Some cost to community.
Mobile facility
dropoff
A moveable facility allows
periodic collections on a
regular schedule at different
sites within a county or several
communities.
Increases public participation
over dropoff method as
number of sites increases.
Initial investment is very high
(contract rental may reduce
the costs).
Curbside collection
Scheduled collection
conducted by contract collector
(usually 1-4 times/year).
Efficient if well managed.
Maximizes public
participation.
Most convenient for
participants.
Expensive.
Types of wastes usually
limited to waste oil, paint,
or certain hazardous wastes
such as explosives and
corrosive wastes in corroded
containers.
Point of purchase
Residents return HHW to retail
stores where the products were
originally purchased.
Low cost.
Deposit requirement on
purchase may enhance public
participation.
Types of wastes are limited
(usually car batteries and
waste oils).
country, most include both educational and collection components. Public education about
HHW is necessary no matter what collection/disposal strategyis used. Education can focus
on:
How HHW contributes to pollution.
Which kinds of products contain hazardous constituents.
Which alternative products contain fewer or no hazardous constituents.
I How to reduce the amount of HHW generated in the home (such as using up household
products or giving away what cannot be used).
I How to properly store, handle, and dispose of products in the home containing
hazardous constituents.
Communities usually begin a HHW program by designating a specific day for residents
to drop off HHW. Organizing a collection event, perhaps with neighboring communities,
is an important first step in reducing and managing risks associated with HHW. Options
for HHW collection are shown in Table 5-7.
Chapter 5: Finding Feasible Solutions for Your Community 59
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Finding Solutions: Nonpoint Source Pollution
Nonpoint source (NFS) pollution comes from many different sources and affects both
surface water and ground-water quality. NFS pollution can especially be a problem when
it affects drinking water supplies. Even water bodies that are not used for drinking water,
however, can become so degraded that they can no longer be used for desirable purposes,
such as fishing and swimming.
Because of the strong relationship between drinking water and NFS issues, many of the
technology and management options presented in this chapter for drinking water are also
useful for NFS pollution. NFS pollution control should be part of wellhead and watershed
protection programs. The most important aspects of NFS pollution control programs are:
Identifying sources of NFS pollution.
Developing management strategies to control NFS pollution. As with wellhead and
watershed protection, this includes regulatory strategies, nonregulatory strategies, and
financing strategies, as well as control methods that the local government can use
directly.
Educating the community on NFS pollution problems and strategies to reduce those
problems.
Sources of IMPS Pollution
Many different activities and land-use patterns create NFS pollution. Commonly, NFS
pollutants are carried by rain and snowmelt that run into lakes, streams, and other water
bodies. Stormwater runoff can carry soil, fertilizers, pesticides, oil and other car fluids,
trash, and other materials that affect water quality. Runoff increases when natural vegeta-
tion, which captures and uses much of the rainwater, is removed. Problems also occur when
natural lands are developed and covered with houses and hard surfaces such as asphalt that
do not absorb water. Rainwater that falls on these surfaces quickly runs into surrounding
areas. This problem is worsened when contaminants on these surfaces, such as antifreeze
leaked from cars, are washed with the runoff into surrounding water bodies.
Runoff is also a major problem on surfaces that cannot absorb water quickly enough, such
as exposed soil. This is a particular concern because runoff over bare soils causes erosion,
which increases water quality problems and wastes valuable soil resources.
Air pollution also contributes to NFS water pollution. Contaminants that are released to
the air settle or are ultimately washed out of the air by rain or snow.
60 Chapter 5: Finding Feasible Solutions for Your Community
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Management Strategies for IMPS Pollution
There are two practical ways to reduce NFS pollution:
Reducing contaminants that are applied to the soil or released to the air.
Keeping stormwater runoff to a minimum.
For small communities some of the most common contaminants that contribute to NFS
pollution are pesticides and fertilizers. Most pesticides contain toxic substances that can
contaminate drinking water and poison plant or animal life. Fertilizers can cause excessive
levels of nitrate in ground water and can cause excessive algae growth in surface water
bodies. Too much algae reduces the oxygen and sunlight available in the water, which
harms naturally growing plants and animals. When too much of a pesticide or fertilizer is
applied to plants or soils, the excess is washed away into receiving waters. When pesticides
and fertilizers are used before a rainstorm, much of what has been applied can be
immediately washed away. Using too much of these substances and using them at the wrong
time also wastes money.
The best way to reduce NFS pollution is to reduce the amount of nonabsorbent and
minimally absorbent ground cover. A good approach is to surround areas such as parking
lots with plant-covered strips that can capture and soak up runoff. Finally, exposed or bare
soil should be limited as much as possible. Stalks, leaves, and other plant residue can be
left to cover the soil after crops are harvested, or quick-growing plants such as grasses can
be planted on exposed soils. These methods protect the soil for the next growing season
and help reduce pollution of nearby water bodies.
Examples of regulatory, nonregulatory, and financing strategies available to small commu-
nities for NFS pollution control are presented in Table 5-8.
Educating the Community
Because NFS pollution control strategies can help both the environment and community
residents, educational programs can be extremely successful. Before people will change
their actions to reduce NFS pollution, they need to be made aware of how their activities
affect local water bodies. They also need to be educated on how to best reduce NFS
pollution. You can make a big difference by educating community residents. Use public
service announcements and press releases to spread the word about the causes of NFS
pollution problems. Set up a committee that can provide advice to local residents on how
best to reduce NFS pollution and save money at the same time. Send out pamphlets that
outline the problems and possible solutions.
Educational programs can be both popular and powerful. Communities around the
country have used educational programs to spur actions that protect their valued water-
ways. People are willing to help once they are armed with the knowledge they need.
Chapter 5: Finding Feasible Solutions for Your Community 61
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Table 5-8
Reducing Nonpoint Source Pollution: Options for Small Communities
Program Type
Description
Advantages
Disadvantages
Protective zoning
Areas within the community
are separated into land-use
zones and districts. Sensitive
areas, such as wetlands and
strips along rivers, lakes, and
other water bodies, are
identified. Potentially
damaging activities in these
areas, such as excessive
pesticide use and
development, are restricted.
Water bodies susceptible to
NPS pollution can be directly
protected.
Environmentally beneficial
land-use practices can be
encouraged, while land-use
practices that cause
environmental problems can
be discouraged or eliminated.
Does not affect current land-
use practices that are causing
pollution.
Can be controversial because
it affects how residents can
use their land.
Requires significant admini-
stration and enforcement.
Acquisition
Sensitive areas, or buffer
zones around sensitive areas,
are purchased by the
community. The community
can then directly control
activities in these areas to
reduce NPS pollution.
Offers the most direct
protection for water bodies
susceptible to NPS pollution.
Can achieve other goals,
such as flood management,
creation of open space for
recreation, and preservation
of ecologically important
settings.
Potentially high costs.
Tax incentives
Landowners that keep their
land in a state that reduces
NPS pollution, such as forest
land, are taxed at a lower rate
than those that develop their
land.
Promotes environmentally
beneficial land-use practices
while discouraging practices
that cause environmental
problems.
Limits local government
intervention.
Might result in lost tax
revenue for the community.
Requires significant
administration, assessment,
and bookkeeping.
Landowners might still
develop their lands, despite
the program.
62 Chapter 5: Finding Feasible Solutions for Your Community
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Finding Solutions: Underground Storage Tanks
Thousands of small and rural governments own and operate underground storage tanks
(USTs). Eighty percent or more of the USTs in small towns are made of unprotected steel
and might leak after as few as 10 years in the ground. Leaking tanks pose a major threat
to ground water. In 1992, corrective action costs for a spill or leak contaminating only soil
ranged from $10,000 to $125,000. Cleanup costs involving ground water can range from
$100,000 to over $1 million, depending on the extent of contamination.
Your community should develop a list of private existing and abandoned underground
storage tanks, as well as those owned and operated by the community. Contact your state
regulatory agency to see if it has a list of USTs in your area.
A community has two basic options for reducing the potential risks associated with owning
an UST
Closing existing USTs. This option eliminates potential future liabilities. The cost of
removing old tanks and assessing the site ranges from $5,000 to $10,000. Table 5-9
shows a number of options that small communities can choose if they close existing
USTs. More than one of these options can be used at the same time.
Upgrading existing community-owned USTs through repair and installation of re-
quired systems that protect against leaks and spills. This may be a very expensive option
—$20,000 to $30,000 for equipment and labor and $2,000 to $6,000 annual operating
costs—and does not relieve the community of liability for future leaks and spills.
Chapter 5: Finding Feasible Solutions for Your Community 63
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Table 5-9
Options for Communities That Close Existing USTs
Costs*
Option
Using
commercial
supplies
I. Using
alternative
fuels
Description
Maximize use of
nearby commercial
petroleum product
suppliers.
Use alternatives to oil
(such as electricity or
natural gas) for
heating purposes.
Advantages
If conveniently
located suppliers
are available,
eliminates future
liability with only
slightly higher costs.
i Potential added
benefit of reduced
pollution.
Disadvantages
Depends on the
availability and
long-term stability
of the suppliers.
Slight increase in
fuel costs.
Fuel costs may be
substantially higher.
i O&M costs may
be changed.
Conversion costs
can be substantial.
Category
Additional fuel
costs.
Conversion and
operating costs.
Range
$0.05-$0.20
more for each
gallon of fuel
purchased.
Determined
by type of
alternative.
Regionaliza- Several communities
tion share one large,
centrally located
facility with one or
several USTs and
close some or all
their USTs.
Has some of the
advantages of
closing existing
USTs.
Communities share
the cost of compli-
ance and liability.
Not practical in
sparsely settled areas.
Possible
inconvenience due
to travel distance
and time.
New ta n k Determi ned by
installation and facility size
operating costs, and complexity.
Privatization Community signs
of USTs lease agreement with
a private vendor;
under agreement,
the vendor constructs,
operates, and owns
the facility.
Reduces or
eliminates liability.
Capital costs are
spread out over the
term of the lease.
Used where #1 is
not feasible.
Higher costs per
unit of storage
capacity.
Typical annual $9,000-
lease payments $15,000
for 5 years. annually.
Above- Construct storage
ground tanks tanks above the
ground.
Reduces many
environmental risks
associated with USTs.
Lower O&M
and possibly
capital costs.
Easy leak detection
and remediation.
Subject to more
dangerous
explosions from
vapor leaks.
Safety issues may
result in prohibition
of construction in
certain areas.
Tank installation. $20,000-
$50,000.
Installation
of new USTs
Install state-of-the-art
UST for best
performance and
management.
Protection against Most expensive
leaks and spills. option.
Still liable for spills
and leaks.
Typical $2,000-
operating costs. $6,000
(annual only).
Typical $25,000-
installation costs $50,000.
(equipment and
labor) per tank.
* Costs are in addition to the $5,000-$! 0,000 cost of closing existing USTs (removing old tanks and assessing sites).
64 Chapter 5: Finding Feasible Solutions for Your Community
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Ruraltown Narrows the Options:
Septic Tank Problems
eptic systems are a serious problem in certain areas of Ruraltown,
causing high coliform counts in nearby private wells. Some septic
systems had been installed in areas where they could never accept the
wastewater properly because the soil was too shallow or impermeable.
After discussion with the local extension agent and a state official, the
planning team obtained soil maps for the area. Overlaying the septic system
failures revealed that certain areas of the town were unsuitable for the use
of these systems, with the areas of failures generally matching the areas
with unsuitable soils. Other, outlying areas had good soils for septic systems,
and the overlay revealed few problems there.
The planning team drew up a list of possible options to address this problem
and eliminated some from consideration. Where conventional onsite septic
systems wouldn't work, the team learned, some other types of onsite systems
(such as mound systems) might be feasible for the soil conditions in the
area. Conveying wastewater from a number of homes via a small diameter
effluent sewer to a "cluster" treatment facility (large soil absorption system
or sand filter) might also be possible on a suitable site a short distance
away. The team ruled out conventional sewers and centralized wastewater
treatment for the homes in question because of the large distances between
homes and between these homes and the existing underused collection
system, which would have resulted in prohibitive costs. Low-cost sewers,
however, could be used to carry wastewater to the existing mains.
The Ruraltown team narrowed the options in this manner for each of the
problems and needs it had identified. The list of feasible options is shown
on the next page.
Chapter 5: Finding Feasible Solutions for Your Community 65
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Feasible Solutions to Ruraltown's Problems
Problem
Solution
Drinking water samples exceed
coliform MCL
Obtain outside assistance (such as a circuit rider or
contract O&M) to provide on-the-job training and
supervision for Ruraltown's operators/administrators.
• Improve chlorination equipment (upgrade mixing system
and contact tank).
Implement wellhead protection program.
• Hire engineering firm to evaluate long-term needs.
Inadequate drinking water system
capacity
Conduct full professional evaluation.
Upgrade current treatment facility.
Dig new wells in protected areas.
Replace portions of distribution system.
Implement water supply program (water conservation,
leak detection, new rate structure, and public education).
Drinking water plant does not
meet all monitoring requirements
• Determine and conduct all required monitoring.
• Investigate possibility of monitoring waiver for some
contaminants.
• Seek agreement with other communities to pool
samples to reduce costs of commercial laboratory, or
consider using an academic institution in area.
High coliform counts in
private well supplies near septic
systems in areas with high ground
water
Install new onsite mound systems (for problem systems).
Install cluster collection and treatment facility.
Add point-of-use and point-of-entry disinfection units
at problem locations.
Pesticide use near drinking water
wells
• Set limits on type and amount of pesticides applied in
wellhead protection areas.
• Encourage farmers and homeowners to use less
hazardous chemicals with more efficient application.
• Provide hazardous waste collection system for area.
Aging underground storage tanks
owned by town
Close all underground petroleum tanks.
Get petroleum products from nearby commercial
sources.
Replace tanks.
66 Chapter 5: Finding Feasible Solutions for Your Community
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Feasible Solutions to Ruraltown's Problems (continued)
Problem
Solution
Poor wastewater treatment plant
performance; effluent exceeds
organic matter and suspended
solids limits
Conduct full professional treatment plant evaluation.
Obtain circuit rider assistance and training.
Implement water supply program (water conservation,
leak detection, new rate structure, and public education).
Failing septic tank systems
Replace with new onsite systems where soils acceptable.
Collect with low-cost sewers to cluster disposal system.
Collect with low-cost sewers to existing sewer mains.
Landfill doesn't meet state design
requirements; almost full
Construct a new landfill with new required design.
Close landfill and build transfer station.
Implement a source reduction program with public
education; charge residential customers by the bag and
review results annually.
Enter regional agreement to build new disposal facility
and materials recovery facility.
Pollution of surface water by
fertilizers (nitrates and phosphates)
Educate farmers on use of grassy strips and other
means to contain runoff pollutants.
Educate farmers, commercial appliers, and residents
on more efficient use of fertilizers in the watershed
protection area.
Leaf burning
Encourage yard waste composting by residents.
Initiate townwide yard waste collection and composting.
Household hazardous waste
(including used oil) contaminating
ground water near landfill
Start public education program about household
hazardous waste and used oil.
Identify or provide a market/use for used oil.
Ask the gas station to collect used oil.
Start periodic household hazardous waste collection
days with neighboring communities (e.g., once or twice
per year).
Chapter 5: Finding Feasible Solutions for Your Community 67
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Feasible Solutions to Ruraltown's Problems (continued)
Problem
Solution
Might be asbestos in elementary
school
Make sure school is inspected.
If asbestos is found, see if containment option is feasible.
Lead paint in homes
Start educational program through schools about what
the hazards are and how to minimize them.
Radon in homes
Determine if radon exists in planning area; if so, start
educational program about what the hazards are and
how to check for and minimize them.
Runoff from construction sites and
tannery
Notify construction companies and tannery about NPS
pollution regulations and provide information on storm-
water best management practices (BMPs) alternatives.
Monitor their implementation of these practices and
keep authorities informed of violations.
68 Chapter 5: Finding Feasible Solutions for Your Community
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Putting
the Plan
Together
Py this point, you have gathered
together the information you need to
put together your community environ-
mental plan. You have defined your
community's vision for the future, your
community's environmental problems and
needs, and feasible solutions. Now it's time ///x ^H^^ /"*"••
to set priorities for action and produce a coherent plan—your road map and your schedule
for reaching your goals.
To create your community environmental plan, three steps remain:
Target the most important problems for your community to solve.
Set priorities for action and choose the solutions to implement.
Put the plan together, making sure that all the solutions fit together
(including coordinating with regulatory agencies to make sure that they agree).
Targeting the Problems
At this step, the planning team needs to decide which problems to target. You have already
laid much of the groundwork for this in Chapter 4, when you determined the greatest
hazards to people and the environment, determined the regulatory requirements you have
to meet, and evaluated how effective your environmental facilities are.
You should target the problems your planning team considers to pose the highest risk,
since protecting the health and environment of your community's residents is your first
priority. If your community is notin compliance with regulations covering other problems,
however, it is in your community's best interest to consider these regulations as you put
your plan together. Make sure that you discuss this situation with your state agency as early
as possible. Explain your community's desire to solve the high-risk problems first. Letthem
know that, in your plan, you will address how and when your community will meet the
regulatory requirements that cover the other problems. Be willing to discuss a timetable
for compliance. If you have a clear plan for addressing the regulatory requirements in the
69
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future, regulatory agencies should be able to negotiate with you to develop a long-term
agreement and exercise some flexibility in their enforcement roles. The state can be a
valuable ally in your efforts to "do the right thing."
If you have facilities that are not performing well, you might want to target those problems
too, even if they don't yet pose a high risk or cause you to be out of compliance with
regulations. Poorly working environmental facilities waste money and other resources and
are likely to cause bigger problems in the future.
Finally, your community probably has other important considerations besides risks,
regulations, and performance of environmental facilities. These might be social or eco-
nomic goals, such as:
I Attracting businesses to the community.
I Making the community a nicer place to live.
Promoting tourism.
Each community has its own set of considerations and priorities. For some communities,
these other considerations might even be more important than reducing risk. This would
be a good time to revisit your community vision to see what goals residents value the most.
At this stage in the planning process, you should rearrange the list of your community's
needs and problems according to the considerations that are most important to your
community. Since some will probably be equally pressing, you can arrange them in
categories, such as "action is urgent," "action is necessary," and "action is desirable." The
box entitled "Ruraltown's Priorities" shows how Ruraltown grouped its needs and prob-
lems.
Setting Priorities for Action
Which solutions will you implement to address your problems and needs? Which will you
implement now, and which will you implement farther down the road?
You should already have a handle on which solutions are feasible for your community, how
quickly or easily they can be implemented, approximately how much they cost, and what
they can achieve (see Chapter 5). List these solutions, along with key information about
them, next to the problems.
70 Chapter 6: Putting the Plan Together
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Ruroltown's Priorities
The Ruraltown planning team grouped its environmental problems as shown
below. The "urgent" problems were those that presented the highest risks to
human health. Those grouped under "action is necessary" were high or medium
risks, or were regulatory violations. Those grouped under "action is desirable"
were not regulatory issues and had lower or longer term risks.
In its discussions with state officials, the Ruraltown team learned that the town
might be able to obtain "use waivers" from the expensive drinking water monitoring
requirements for certain organic and inorganic chemicals. States can grant these
waivers when it can be shown that a contaminant has not been used, manufactured,
or stored in the wellhead area. The state agreed to help the team develop a plan
to apply for a waiver and comply with all other monitoring requirements.
Action Is Urgent Drinking water samples exceed coliform MCL
High coliform counts in wells near septic systems in areas with high
ground water
Landfill doesn't meet state design requirements; almost full
Action Is Necessary Poor wastewater treatment plant performance
Failing septic tank systems
Inadequate drinking water plant capacity
Drinking water plant does not meet all monitoring requirements
Improper disposal of used oil and household hazardous waste
Pesticide use near private drinking water wells
Might be asbestos in elementary school
Pollution of surface water by fertilizers
Aging underground storage tanks owned by town
Lead paint in homes
Runoff from construction sites and tannery
Radon in homes
Leaf burning
Chapter 6: Putting the Plan Together 71
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Setting your priorities for action requires a balancing act. You want to solve as many of
the most urgent problems as you can with the resources you have. You might also want to
address problems that don't necessarily pose a high risk but that have easy and inexpensive
solutions. For example, littering generally does not pose a great hazard to public health or
to ecosystems. The littering problem, however, might be easily solved by providing trash
cans in public places, having school children make posters that can be displayed throughout
town asking people not to litter, or even getting local law enforcement involved, if
necessary. Activities that involve a broad spectrum of your community help generate public
support for the overall environmental program.
Also, keep in mind that your resources might not be as limited as you think. Chapter 7
provides some information about obtaining resources to implement your plan, including
how to draw on the resources of other communities and the private sector. Be creative
when making your choices, and be open to new resource possibilities.
Give special attention to solutions that can address more than one problem. For example,
you might decide that leaf burning is a low-priority problem in your community, while
managing solid waste is a high priority. Yard waste composting is a solution for reducing
solid waste that also helps discourage leaf burning and its associated air pollution problems.
The matrix below can help you set short-term priorities for action. Keep in mind that your
community is likely to have longer term needs that might require substantial resources to
solve.
Remember, this is the environmental plan for your community. Only the people in your
community know what the priorities for action should be. So take charge, be creative, and
do your best to juggle your options to solve as many of your community's environmental
problems as possible while maintaining public support and using resources wisely.
Solutions Require Few
Resources
Solutions Require Many
Resources
Problem Is Very Important
for the Community to Solve
Include solutions in the plan
Include as many solutions as
possible in the plan
Problem Is Less
Important for the
Community to Solve
Probably include solutions
in the plan
Don't include solutions in
the plan
Looking at the Big Picture
At this stage in the planning process, your community environmental plan will be pretty
well hammered out. The only thing left to do is to look at the big picture. For each of the
problems that are priorities for action in your environmental plan, try to predict the full
outcome of using the solution (or solutions). See if any of the solutions you have chosen
might cause new problems or interfere with one another. Say, for example, that your
community decides to expand its ground-water supply system. This could mean that the
"zone of contribution" for the well—the area of an aquifer that recharges the well—could
72 Chapter 6: Putting the Plan Together
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expand to encompass more septic tank leachfields or other potential sources of contami-
nation. Talk to your local experts and county, state, and federal contacts. Ask them if they
foresee any problems with how the solutions fit together.
Community support will be crucial to the success of your plan. As you look at each solution,
ask yourselves questions about how much support it will have in the community:
How concerned is the community about the problem that the solution addresses?
I Do you have local leadership necessary to undertake and complete the needed changes?
Can you draw on local capabilities, equipment, and ingenuity to implement the
solution?
Consider that the county, state, and federal governments have to protect the broader public
interest and might find your plan too narrow. Keeping an eye on environmental problems
that you might be exporting to other communities will help you anticipate and avoid
conflicts with higher levels of government.
Finally, never lose sight of your community vision. Looking at each problem indepen-
dently can make it difficult to see how it all fits together. Throughout the process, stop
and consider what you are really trying to accomplish.
Chapter 6: Putting the Plan Together 73
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Ruraltown Puts Together Its
Environmental Plan
The Ruraltown planning team, with the assistance of representatives from
the state environmental agency, selected the solutions to implement based
on several factors. After reviewing the list of feasible solutions, the team clearly
saw that lower cost strategies emphasizing pollution prevention and public
education would provide major benefits for the town. In several cases, the team
selected educational strategies over more coercive methods. For example, the
team decided to provide information to farmers and residents about ways to
reduce pollution from pesticides and fertilizers. In its work with residents, the
team found several people who were enthusiastic about developing education
programs for the community.
Despite the benefits of voluntary efforts, Ruraltown still needed major im-
provements to its environmental facilities. To address the failing onsite septic
systems in areas with unsuitable soils, the team determined that a new cluster
treatment system would be the most cost effective of the feasible options. The
team contacted local construction companies about using equipment to help
construct such a system. A civic organization and the residents who would be
served by the systems agreed to donate time to the project to help reduce costs.
For the drinking water and wastewater treatment plants, the team decided to
obtain circuit rider assistance to improve operator skills in the short term
(instead of hiring a trained full-time operator) and to plan for major capital
improvements over the next 5 years, hi the long term, the plants may have to
be upgraded and expanded to accommodate growth in the area (if the growth
demand exceeds water savings due to the new rate structure designed to dis-
courage unnecessary water use.) Ruraltown would fund a professional evaluation
of the long-term needs of both plants after the immediate programs have been
in place long enough for the town to assess their effects.
Finally, the town would pursue a regional agreement to build a new disposal
facility and materials recovery facility. The team determined that in the long
run this would be less expensive than building and using a transfer station,
especially since several other towns in the county were also experiencing prob-
lems managing their solid waste.
74 Chapter 6: Putting the Plan Together
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Ruraltown Chooses Priorities for Action
Drinking water samples
exceed coliform MCL
High coliform counts in
wells near septic systems
in areas with high ground
water
Landfill doesn't meet state
design requirements;
almost full
Poor wastewater treatment
performance; effluent
exceeds organ ics and
suspended solids limits
Failing septic tank systems
Inadequate drinking water
system capacity
Drinking water plant does not
meet monitoring requirements
/ Obtain assistance from a circuit rider (immediately)
Improve chlorination equipment
Take the first steps in setting up a wellhead protection program;
determine low-cost ways to protect ground water (immediately)
Hire engineering firm to evaluate long-term needs (later)
Install new onsitc mound systems
Have engineers design and install cluster collection and treatment
facility
Install point-of-use/point-of-entry disinfection units in affected homes
(temporary)
Construct a new landfill with new required design
Close landfill and build transfer station
Enter regional agreement to build new disposal facility and materials
recovery facility
Implement source reduction program with public education; including
yard waste collection/composting
Charge residential customers by the bag and review results annually
/ Conduct full professional treatment plant evaluation
Obtain circuit rider assistance/train ing
Implement water supply program (water conservation, leakdetection,
new rate structure, and public education)
Replace with new onsitc systems where soils arc acceptable
/ Collect with low-cost sewers to cluster disposal system (see above)
Collect with low-cost sewers to existing sewer mains
/ Conduct full professional evaluation
Begin planning capital improvements (5 years) to upgrade current
treatment facility and replace portions of distribution system
Dig new wells in protected areas
Implement water supply program (see above)
Apply for monitoring waiver for contaminants not present or used in
the area
/ Conduct all other monitoring
Seek agreement with other communities to pool samples to obtain
better analytical rate from commercial laboratory or academic
institution in area
Chapter 6: Putting the Plan Together 75
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Ruraltown Chooses Priorities for Action (continued)
Household hazardous
waste (including used oil)
contaminating landfill
leachate and ground water
Start public education program about household hazardous waste
and used oil disposal
Identify or provide a market/use for used oil
Ask the gas station to collect used oil
Start periodic household hazardous waste collection days with
neighboring communities (once or twice per year)
Pesticide use near private
drinking water wells
Might be asbestos in
elementary school
Set limits on type and amount of pesticide application in wellhead
protection areas
Encourage farmers and homeowners to use less hazardous chemicals
with more efficient application
/ Provide hazardous waste collection system for area (see above)
Make sure school is inspected
/ If asbestos is found, determine if containment solution is feasible
Pollution of surface water
by fertilizers (nitrates and
phosphates)
Educate farmers on use of grassy strips and other means to contain
runoff pollutants
Educate farmers and residents on more efficient use of fertilizers in
the watershed protection area
Aging underground
storage tanks owned by
town
Close the community-owned underground petroleum tanks
Get petroleum products from nearby commercial sources
Replace tanks
Lead paint in homes
Start educational program through schools about what hazards are
and how to minimize them
Action Is Desirable
Runoff from construction sites
and tannery
Radon in homes
Leaf burning
Notify construction companies and tannery about NPS pollution
regulations and provide information on stormwater BMPs
Monitor their implementation of these practices and keep state
authorities informed of violations
Determine if radon exists in planning area; if so, start educational
program through schools about what hazards are and how to check
for and minimize them. If not, no action necessary
Encourage yard waste composting by residents
/ Initiate town-wide yard waste collection and composting
76 Chapter 6: Putting the Plan Together
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Implementation:
Putting the Plan Into Action
keeping It On Tra
ow you have your community
I environmental plan—your
I road map to the destination
your community wants to
reach. But even the best map will be
worthless if you never buy your
vehicle, gas it up, and hit the road.
You'll need a maintenance schedule
to keep things running smoothly. And don't forget—no matter how good your road
map is, detours, flat tires, and accidents might force you off course. You need to check
your progress regularly and see whether you need to change your route.
This chapter is about implementation: putting the plan into action, evaluating how well
the plan works, and revising the plan as you need to. In your environmental plan, your
community has outlined the solutions itwants to use to manage environmental issues. Now
it is time to iron out the approach for implementing the plan, which includes:
Developing a schedule for putting the plan into action.
I Financing the plan.
I Determining the role your local government and other governments and organizations
will play.
Determining the role individuals in your community will play.
Evaluating and revising the plan as necessary.
Developing a Schedule for Putting the Plan Into Action
To begin implementing the plan, develop a step-by-step approach for each solution your
community has chosen. Start by making a list of concrete actions that must be taken, in
the order in which they should be taken, for each solution. Once these step-by-step
approaches have been ironed out, draw up a schedule for taking the steps. The schedule
should include a start date and a completion date for each step, when possible. Sometimes,
however, the actual dates will have to be established after other actions are completed. An
77
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approximate target date should be included in these situations. In some cases, the solutions
will take only days or weeks to complete. In other cases, however, completion will take
years. A schedule is especially important for issues that involve regulatory requirements;
you will need to show regulatory agencies when you will be able to comply with those
regulations.
After the schedule has been drawn up, determine who is responsible for "making things
happen." List those responsible for completing each step. This way, you can easily check
with the right people to see if the plan remains on schedule and to determine what should
be done if the schedule slips. Check the schedule regularly to make sure things are
happening as planned. If not, take steps immediately to keep up the momentum.
Your community should also set up a way to measure the plan's successes and failures. For
each solution, specific goals should be given. For example, a specific goal might be to cut
the amount of trash each family produces from three to two bags a week.
Your community might consider focusing on one major project in your plan that addresses
a key concern—such as beginning a water conservation program—and mobilizing the
community to get results. This can help build momentum and community support for
other actions specified in your plan, and can help you identify and correct weaknesses in
one project before you've gone far on other projects.
Financing the Plan
The approach your community uses to implement its environmental plan must include a
strategy for how to pay for solutions. Your community must cover both the operating
costs and the capital costs of any equipment and facilities included in your plan.
Generally, different types of financing are used for operating costs than for capital costs.
You will need to choose which combination of financing options you will use to cover both
of these costs. Some excellent guides to financial management for small communities are
listed in Appendix D.
Common operational costs include the costs of employee salaries and benefits; supplies; fuel,
utility, rent, and insurance bills; maintaining equipment; monitoring; and interest pay-
ments on loans. Another type of operational cost that all communities face, but many do
not think about, is depreciation, the reduction in value of a facility or piece of equipment.
All of the equipment and facilities that your community uses are getting older. The older they
get, the less valuable they are because they are more likely to break down. Each piece of
equipment has a useful life, which is the duration of time that the equipment is expected
to last before it must be replaced. Financially preparing to replace equipment when its
useful life is over is important. Although depreciation is an operational cost, replacement
is a capital cost, which is discussed on the next page.
Operational costs tend to stay about the same from year to year, although they can rise
because of the age of equipment and because of inflation. A steady flow of funds should
therefore be used to finance operational costs. Small communities usually generate these
funds through local taxes and fees.
78 Chapter 7: Implementation
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Capital costs are different from operating costs because they involve a one-time investment
that is usually relatively large. Common capital financing options are grants, loans, bonds,
and notes. For many of these options, the useful life of the equipment or facility must be
considered when choosing a financing option and the level of debt. If the equipment or
facility must be replaced before the debt is repaid, your community will be carrying more
than one debt for the same service.
Table 7-1 presents information about common financing options for both operational and
capital costs.
Another important alternative is saving money. Saving money allows your community to
become more efficient and provide services at a lower cost. A community can save money
in many ways, such as by using local people, equipment, and financial resources (including
business donations and volunteer help); increasing employee productivity; properly main-
taining equipment; running equipment at times when electrical costs are lower; and buying
supplies in bulk with other towns at a discount. Although financing minor capital costs
with money saved is possible, this rarely happens. Instead, savings are usually used to fund
operational costs and to avoid the need to raise taxes or fees.
The affordability of your environmental solutions depends on community involvement as
well as the funding available. If community residents have not participated in shaping the
environmental plan, its affordability may well be reduced, because residents will be less
willing to pay for changes in which they have had no role.
Roles of Government and Other Organizations
Your local government has three basic choices about the role it will play when implement-
ing your community environmental plan: implement solutions alone, cooperate with other
local governments, or form a partnership with private companies. Your community does
not have to choose just one of these roles; you can mix and match roles to implement
different solutions. For example, your local government can implement an underground
storage tank program alone, become partners with other local governments to build and
operate a wastewater treatment plant, and contract with a private company to collect and
dispose of solid waste.
Working Alone
Working alone may be the easiest role for your community to play because it does not
require you to develop any special arrangements. Working alone may be an option if the
solutions you choose are inexpensive and do not require advanced technology. When more
complicated systems or facilities are needed, you should consider cooperating with other
communities or forming a partnership with private companies.
If local government organizations are understaffed or do not have the expertise to
implement the new solutions, new organizations might be necessary. In these cases, your
community can set up committees or agencies and delegate the power to perform certain
functions. The members of the committee can also be specially trained to deal with the
solution they are implementing. For example, many communities have set up wellhead
protection committees that work with state agencies or local experts to define wellhead
Chapter 7: Implementation 79
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protection areas, identify sources of ground-water contamination in those areas, and
implement strategies to protect the community's ground-water resources.
Cooperating With Other Local Governments
Cooperating with other local governments can be the best way to implement some of the
solutions in your community environmental plan. Small communities can cooperate
through joint ownership and operation of drinking water, wastewater, and solid waste
management facilities. Communities can also cooperate by sharing personnel who do
certain common jobs, such as billing customers, purchasing supplies, maintaining equip-
ment, and testing samples. To cooperate with other local governments, decide the role
each community will have, how conflict among the communities will be resolved, and how
the cooperative activity or facility will be paid for.
There are many advantages to cooperation. For example, communities can pool funds so
that they can afford facilities or technologies that individual communities cannot afford
alone. Providing a service to a small number of people is often more expensive per person
than providing a service to a large number of people. Economies of scale allow you to
increase the number of people that are served to achieve lower costs per person. Finally,
larger operations are often more efficient than smaller operations because they allow full
use of staff who otherwise are not fully occupied by a single smaller operation.
The major disadvantage to cooperation is some loss of local control. When you are
cooperating with other communities, your community will no longer be able to act alone.
Negotiations will have to occur to make any changes to the ways in which environmental
services are provided. In addition, when communities are far apart or there is rugged terrain
between them, increased costs for distribution pipes or transporting wastes can outweigh
some of the savings achieved through economies of scale and increased efficiency.
Table 7-2 shows the different options for formally cooperating with other communities,
along with their advantages and disadvantages.
Forming a Partnership With the Private Sector
In many cases, there are advantages to the private sector rather than the public sector
providing environmental services. Your community might therefore want to consider
forming a public-private partnership. The five main types of public-private partnerships
are:
Contract Services. The community contracts with a private company to provide a service
(such as garbage collection) or to run a facility that is owned by the community (such
as a wastewater treatment plant). Firms or experts also can be contracted with to
perform specific duties, such as accounting or maintenance of electrical systems.
Turnkey Facilities. The community owns a facility but contracts with a private company
to design, construct, and operate the facility. The community is responsible for funding
the facility, while the private company is responsible for providing a certain level of
service or regulatory compliance.
80 Chapter 7: Implementation
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Leasing. The community pays rent to a private owner in exchange for using a facility
for a specified period. The community controls the facility until the lease is over, when
the facility is returned to the owner. With a finance lease, however, the community pays
to lease a facility but then owns the facility at the end of the lease.
Developer Financing. A private developer finances construction or upgrading of a facility
to gain the right to build homes, stores, or other buildings.
I Privatization. A private firm owns, builds, operates, and partially or totally finances a
facility or service. The local community decides it wants the facility or service, and
might partially fund it.
Merchant Facility. This is similar to privatization except that the private firm also decides
to provide the service. The local community plays no role at all.
Just like cooperating with other communities, the main disadvantage of public-private
partnerships is some loss of local control. To get rid of the headaches of responsibility, you
also have to be willing to allow someone else to make most of the decisions. Partnerships
also take work: Legal issues have to be ironed out, and the actions of the private company
have to be overseen. Public-private partnerships aren't the right choice for all small
communities because many communities do not need to use sophisticated technologies,
or they are not located close enough to a company that provides the services they need.
If your community decides to use a private company to implement part of your environ-
mental plan, you should choose that company carefully. Try to identify companies with
experience working with small communities with problems similar to yours. Ask those
communities about the company to make sure that it has a good track record. The
companies should also have experience with the type of technologies you are interested
in. In many cases, you can also find companies with experience helping small communities
get the financing that they need. Finally, try to choose the company that can give the best
service for the best price. (The state utility commission must approve rates, an important
protection for the ratepayer.)
Some Reasons To Form a Public-Private Partnership
A public-private partnership can help your • Giving your community ways to finance
community by: environmental services using private
• Allowing your community to use a more capital.
sophisticated technology that the private Letting your community know exactly how
company uses. much the service will cost, because the
cost is written into the contract.
Chapter 7: Implementation 81
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Table 7-1
Financing Plan Options
Financing
Method
Description
Advantages
Disadvantages
Taxes
Property taxes (e.g., on
buildings, land, and/or
vehicles) are the most common
type of taxes used by local
governments.
Easy to administer.
Generate a relatively steady
flow of funds, therefore good
for financing operational costs.
Tax burden is spread over
a small number of people in
a small community.
Taxes are unpopular and tax
increases may require formal
approval by those affected.
Hotel taxes, rental taxes, and
taxes on other tourist activities
(such as restaurants,
nightclubs, and guided tours)
can be used by communities
with high tourist populations.
Can increase revenues
without placing a higher burden
on permanent residents.
Higher taxes might
discourage tourism.
Amount of revenue varies
according to the number of
tourists during a season.
Fees
Service fees can be charged
for using an existing service
(such as billing customers for
the drinking water they use) or
demanding a service (such as
charging homeowners to be
hooked up to the wastewater
treatment system). Fees can be
flat fees (everyone who uses
the service pays the same
price) or graduated fees
(based on the amount each
person uses).
Generate a steady flow of
funds, therefore better for
financing operational costs.
Graduated fees could provide
customers with incentives to use
less if fee rates are increased
as more water is used.
Flat fees discourage
conservation and promote
wasteful use.
Service fees might be
unpopular.
Fees based on how much
water is used could
discourage industries and
other businesses from
locating in an area.
Punitive or corrective fees can
be charged to people or
businesses that pollute (e.g.,
releasing chemicals into
wastewater treatment systems).
The community can also give
special fee reductions for
industries that start out with
water conservation and
pollution prevention measures.
Generate revenue while
discouraging pollution.
In some cases, avoid
noncompliance with permit
requirements caused by
industrial pollutants.
Cannot be relied upon as
a source of income.
If too stringent, could lose
industry to another location
or encourage illegal
avoidance fees.
Recreational fees can be
charged for hunting and
fishing licenses or privileges.
Only paid by those who
participate in certain activities.
The money raised can be
earmarked to protect the
environment and maintain
recreational areas.
Generate a relatively small
amount of money.
If recreational fees are too
high, they might encourage
illegal activities.
82 Chapter 7: Implementation
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Table 7-1
Financing Plan Options (continued)
Financing
Method
Description
Advantages
Disadvantages
Fees (continued)
Impact fees can be charged to
developers, who will create
demand for local infrastructure.
Only paid by those who profit.
Money can be used to offset
costs.
Might reduce potential for
development.
Grants
Grants are funds that are
provided by the federal
government, states, or other
organizations to pay for
special projects (e.g., U.S.
Department of Agriculture's
Rural Development
Administration, the U.S.
Department of Housing and
Urban Development [HUD]).
Small communities may be
eligible for many different
grants to build or upgrade
their environmental facilities.
Grants do not have to be
paid back.
Most grants have specific
eligibility requirements that
a community must meet.
Grants tend to be very
competitive. Your community
must invest time and money
to apply for a grant that you
might not get.
Grant use requirements may
be expensive.
Loans
A loan is money lent with
interest. Low-interest loans
might be available through the
state (e.g., State Revolving
Funds) or federal government
(e.g., from the Rural
Development Administration or
HUD). If federal and state loans
are not available, your small
community can borrow from a
commercial bank.
A long-term, low-interest loan
will allow your community to
pay for capital expenses that
require a large one-time
investment.
Loan payments can be spread
out over time so that repayment
is manageable.
Loans can be used for shorter
term financing while waiting for
grants or bonds.
Unlike a grant, a loan must
be repaid. Over time, both
interest and principal must be
repaid with money collected
through taxes, fees, or money
previously saved.
State Revolving Fund loans
require adherence to federal
rules and regulations.
Commercial bank loans may
be difficult to obtain without
adequate collateral.
Revolving Funds
Revolving funds are self-
sustaining funds set up to
provide loans to communities for
construction and modification of
facilities. As the loans are
repaid, the money is returned to
the fund so that it can be
borrowed by other communities.
State Revolving Funds currently
finance wastewater treatment
plants, but can be used for NFS
pollution control and drinking
water facilities.
Offer below-market interest
rate loans.
Are often targeted toward the
improvement of environmental
facilities in communities.
Legal requirements can limit
the use of funds.
Most communities have legal
limits on the amount of debt
they can accrue, including
through revolving fund loans.
Privatization Under privatization, a private
firm owns, builds, operates,
and partially or totally finances
a facility or service.
Reduces or eliminates debt
needed to provide service.
Reduces local government
responsibility for providing
service.
Some loss of local control
occurs.
Oversight of private firm is
necessary.
Legal issues must be
resolved.
Chapter 7: Implementation 83
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Financing
Method
Description
Table 7-1
Financing Plan Options (continued)
Advantages
Disadvantages
Bonds
A bond is an interest-bearing
certificate of public or private
indebtedness, often sold to
finance long-term projects with
high capital costs.
Bonds typically are used for
financing capital costs.
The community only has to
make interest payments until
the bond is due.
Issuing bonds can be
complicated and may require
the help of a financial advisor.
Bonds are usually only used
when large amounts of money
are needed for long periods.
General obligation bonds are
secured by the taxing power of
the community, which means
that the community pledges to
pay back the interest and
principal through taxes (if
necessary).
General obligation bonds
should be used, when possible,
to save money in interest
payments.
Most communities have legal
limits on the amount of
money they can borrow
through general obligation
bonds, and voters often must
approve of using these bonds.
Because of the limits placed
on them, general obligation
bonds are usually used for
facilities that do not generate
revenues.
Revenue bonds are secured by
money that will be generated
by the use of the loan, such as
user fees from a wastewater
treatment facility that will be
built or upgraded.
Most communities do not have
a limit on the amount of money
they can borrow with revenue
bonds.
Revenue bonds are appropriate
for environmental facilities since
most can generate revenues
through user fees and tipping
fees.
The interest rates for revenue
bonds are usually higher
than for general obligation
bonds.
Many states now have bond
banks from which communities
can obtain bond money. The
state uses its taxing power to
secure a large bond issue that
can be divided among its
communities.
Because the state has more
taxing power than individual
communities, it can get a bond
at a lower interest rate.
Because the costs of issuing a
bond are about the same no
matter how big the bond is,
bond banks also save money
by spreading out the costs of
issuing the bond.
With a state bond bank, the
state can issue the bond in
anticipation that its communities
will need it, reducing the time it
takes for each community to get
bond money.
Many communities compete
for a limited amount of
available bank bond funds.
84 Chapter 7: Implementation
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Financing
Method
Description
Table 7-1
Financing Plan Options (continued)
Advantages
Disadvantages
Certificates of Certificates of participation
Participation (COPs) can be issued by a
community instead of bonds.
Unlike bonds, COPs are issued
to several lenders that all
"participate" in the same loan.
Costs and risks of the loan are
spread over several lenders.
Where authorized under
state law, COPs may be issued
when bonds would exceed debt
limitations.
Requires complicated
agreements among the
participating lenders.
Notes
A note is a written promise to
pay a debt. The community
promises to pay the principal
and the interest at a specified
time. Notes are a short-term
option usually used to finance
costs during construction.
Grant anticipation notes are
secured by a community's
expectation that it will receive a
grant. In essence, it allows the
community to "borrow against"
the grant. (You should never
request a grant anticipation note
for more money than the grant.)
Bond anticipation notes are
secured by the community's
ability to sell its bonds. Your
community must therefore satisfy
all legal requirements for issuing
a bond before it applies for a
bond anticipation note.
Notes can be used as a short-
term financing option while you
are waiting for money from
grants or bonds.
Grant anticipation notes
should only be used when the
organization giving the grant
has made a firm commitment
that your community will get
the grant, and when you need
money immediately and you
don't expect to receive the
grant for some time.
Voters usually have to
approve a general obligation
bond, making a bond
anticipation note very risky
unless the community has
shown overwhelming support.
Roles of Community Members
Once your community has a picture of which organizations will play a role in implementing
the plan, you'll need time to figure out how individuals will be involved. Your community
should decide who is responsible for making the solutions work and what their specific
responsibilities are. Some people on the planning committee might continue to be involved
as the plan is implemented. Stay on the lookout for new people who might step forward
to help carry out new programs and activities.
When the approach to implementing the environmental plan calls for community resi-
dents to play a role, they should be knowledgeable about their new responsibilities. If the
plan includes a used oil program, for instance, the people of the community must be
provided with clear instructions on how to collect their oil and where to bring it for
recycling or proper disposal.
Actively seek volunteers to donate both time and materiel. The more you involve people in
implementing the plan, the greater the support from the community and the fewer the problems.
Chapter 7: Implementation 85
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Option
Table 7-2 Options for Cooperating With Other Communities
Advantages Disadvantages
Authorities—Communities and counties
can establish an authority to finance,
build, and operate a public facility or
system that generates revenues. The
authority is a corporate body with a
charter that must be approved by the state
legislature. Authorities operate outside the
regular structure of government and are
financed through user fees or other
revenues.
Local debt ceiling doesn't affect
financing.
Voter approval of financing isn't
necessary.
Local politics are less likely to affect
service because private citizens, rather
than government officials, are on the
board.
Can increase efficiency by avoiding
government budgeting and
administration.
Revenues can make the service self-
supporting.
Capital financing is tax-exempt.
Financing can be complex to
administer.
Government or public control can be
too limited.
In some areas, authorities can compete
with private industry.
Special districts—Communities can
establish a special district to perform a
single function, such as drinking water
treatment. The special district acts as a
government agency outside the regular
structure of government and uses special
taxes for financing. Special districts must
respond to local needs and cooperate
with local jurisdictions to be successful.
The residents to which the district is
responsible are a distinct constituency.
Elected officials can serve on the board
for the district to give the local
government some say.
State statutes limit powers.
Financing requires special taxes that
must be approved by voters.
Might not be as responsive to residents
as arrangements where voters elect the
board.
Nonprofit public corporations—These are
similar to authorities except that they must
be approved by all member communities
and state officials, as required by law.
They are financed by issuing bonds, and
directors of the corporation must be local
government or state officials.
Local debt ceiling doesn't affect
financing.
Voter approval of financing isn't
necessary.
After bonds are paid, the corporation
gives assets to member communities.
Not subject to real estate or federal
taxes.
Capital financing is tax exempt.
It is difficult to get out of the
corporation if better service becomes
available.
The corporation cannot use taxing
power of local governments to secure
financing.
Local government and state officials
might exert political influence.
Multicommunity cooperatives—This is a
way to gain cooperation between
governments without legal charters or
agreements. Communities agree to work
together to build a facility or provide a
service. Usually, one community takes the
lead.
These have less restrictive legal and
institutional structure than other
multicommunity options.
Communities can pool resources to
provide services that they may not be
able to provide alone.
Member communities lose
independence and must cooperate in
making decisions about how the service
will be provided, where the facility will
be sited, etc.
Interest rates on loans or bonds could
increase if leader community is not as
financially strong as other communities.
Intergovernmental agreements—Formal
and informal agreements can be made
between two or more local governments
to provide services. Contracts are the most
commonly used type of intergovernmental
agreement.
Contracts are flexible, predictable,
and enforceable.
Basic government structures are not
affected.
Saves time because no new structures
are necessary.
Because each community, rather than
a single unit, must borrow money, it
may be more difficult to get financing.
Misunderstandings may occur if the
agreement is not spelled out in detail in
a contract.
Each participant must reach agree-
ment every time a new issue comes up.
86 Chapter 7: Implementation
-------
Evaluating and Revising the Plan
No matter how much thought your community has put into the environmental plan, you
might find that some of the solutions you have chosen just don't work out. Other solutions
might work, but not as well as your community had hoped.
When solutions do not meet expectations, it's time to reevaluate your community envi-
ronmental plan. In some cases, your community will decide not to do anything because
the flaws in the plan are not big enough to justify the money and time it would take to fix
them. For example, if trucking solid waste to the landfill costs more than you expected,
building a more central landfill would probably not be a better solution.
Sometimes your community will have to modify solutions only slightly. If your plan
includes wellhead protection and people are still accidently polluting the wellhead area,
the only change that might be necessary is to increase public education and post signs that
tell people what they can't do in the wellhead area. Unfortunately, in some cases major
changes to the plan might be necessary. Some of Ruraltown's solutions, for example, relied
on voluntary action by residents. To address surface water pollution by nitrates, the
community got the local extension agent to explain to farmers the value of using fertilizers
more efficiently and using grassy strips to contain runoff. If problems with nitrate
pollution of surface water continue, the town might have to take stronger action to reduce
fertilizer use.
Even if your community finds that all of the solutions in its environmental plan are
effective, the plan might still have to be revised in the future. Changes outside the
community might affect your plan. For example, new technologies might be developed
that can better solve environmental problems, and new regulations might be made on how
communities should handle environmental issues. Your community should be aware of
these changes so that its environmental plan can be updated when revisions make sense.
Changes within your community might also affect the environmental plan. As your
community grows, for example, solutions might have to be revised to handle unforeseen
problems. Also, growth might allow you to implement solutions that previously were too
expensive for a smaller community. Finally, the people in the community might develop
new priorities, and your plan will need to change to reflect those priorities.
Just as water, soil, and air are connected, so are creating the plan and implementing it.
What your community does with one will continue to affect what happens to the other.
Chapter 7: Implementation 87
-------
Ruraltown Sets a Schedule
After Ruraltown chose the solutions it would implement in its environmental
plan, the planning team filled out an implementation worksheet (page 89).
First, the team drew up a detailed schedule for implementation. The schedule
included the specific goals to be achieved, a step-by-step approach for each solution,
and a list of people responsible for the plan. The team also listed the financing
methods it would use for each solution.
The state environmental agency, which had helped the team throughout this proc-
ess, approved Ruraltown's priorities for action and the schedule the team had set.
The state agreed that, if the town implemented the strategies according to the
schedule the team developed, no enforcement actions would be taken regarding
temporary, intermittent violations of effluent permit limits or drinking water re-
quirements. To keep the plan on track, the team decided to meet every 3 months
to review the schedule and progress with the plan. The team also agreed that the
goals listed in the implementation worksheet would help them in the evaluation
and review process.
88 Chapter 7: Implementation
-------
Ruraltown's Implementation Worksheet
Problem/Specific Goals
Solutions
Step-by-Step Approach
Start/Completion Date
Person(s) Responsible
Financing Method(s)
ACTION IS URGENT
nking
water exceeds coliform
MCL
GOAL: Consistently
provide safe drinking
water
Obtain
assistance from a circuit
rider.
N- Improve
chlorination equipment.
Begin
setting up a wellhead
protection program,
and determine low-cost
ways to protect ground
water.
Hire
engineering firm to
evaluate long-term
needs.
• Call circuit rider to set up meeting.
• Hold meeting to discuss problems.
• Follow appropriate
recommendations of the circuit rider.
• Research alternatives.
• Review research, rank alternatives,
and present to town council.
• Purchase and install new equipment.
• Form a wellhead protection team.
• Conduct research to delineate the
wellhead protection area.
Delineate wellhead protection area.
Identify and locate potential sources
of contamination.
• Develop strategies to
prevent/minimize contamination,
focusing on low-cost alternatives.
Present to town council.
• Research firms in the area
specializing in drinking water plants.
• Review research and interview firms.
• Choose and hire best firm.
• Complete evaluation.
• Review firm's evaluation, discuss,
and present to town council.
SOLUTION: Follow appropriate recommendations from the
engineering firm's evaluation.
• Tomorrow (2/6/95).
• ASAP (target date 2/9/95).
ASAP (target date depends on
recommendations).
2/13/95-2/20/95.
2/21/95-3/1/95.
When received (target date 4/21 /95).
• 2/14/95-2/28/95.
3/7/95 - 4/4/95.
• 4/4/95 - 4/25/95.
4/25/95-5/16/95.
• 5/16/95-6/13/95.
Depends on strategies chosen by town
council (target date 8/1 /95).
2/22/95-3/1/95.
• 3/2/95-3/16/95.
• 3/17/95.
• 9/20/95.
• 9/20/95-10/4/95.
• Target date depends on recommendations
(goal is to implement all
recommendations by 2001 ).
• Public works director.
Planning team (including public works
director).
Depends on recommendations.
Drinking water plant personnel and planning
team.
Public works director.
Drinking water plant personnel.
• Led by the planning team.
• Wellhead protection team.
• Wellhead protection team.
• Local volunteers led by the wellhead
protection team.
• Wellhead protection team.
Depends on strategies chosen.
• Planning team.
• Public works director.
• Public works director.
Engineering firm.
Planning team (including public works
director).
Depends on recommendations.
Free.
Temporary fee increase.
• Apply for federal assistance
under EPA's Wellhead
Protection Demonstration
Project.
• Enlist volunteer help.
Graduated fee increase.
Depends on
recommendations.
-------
«o
o
o
a
-o
VI
3
3_
5'
Solutions
Step-by-Step Approach
Start/Completion Date
Person(s) Responsible
Financing Method (s)
PROBLEM: Wastewater
treatment plant perform-
ance is poor: effluent
sometimes exceeds or-
ganic matter and sus-
pended solids
limits.
GOAL: Consistently meet
all effluent limits by 2005.
Implement
water supply program.
Conduct
full professional
treatment
plant evaluation.
• Form a water supply team.
• Quantify all water users in
Ruraltown.
• Conduct water leak detection
study.
Develop a plan to reduce water
usage, including a revised fee
structure.
Create a fact sheet describing the
water conservation plan.
Send the fact sheet out with the
water bills.
Develop and distribute a press
release on the water conservation
plan.
Research and purchase modern
leak detection and repair
equipment.
Research firms in the area
specializing in Wastewater facility
evaluations.
Review research, and interview
firms.
Choose and hire best firm.
• Complete evaluation.
Review firm's evaluation and
present to town council.
SOLUTION: Follow appropriate recommendations from the
professional treatment plant evaluation.
6/1 0/96 - 6/24/96.
• 7/1/96-7/22/96.
7/1 /96 - 7/22/96.
• 7/29/96 - 9/9/96.
• 9/16/96-9/30/96.
10/1/96.
• 1 0/1 /96 - 1 0/1 5/96.
10/15/96- 10/28/96.
4/1/96-4/15/96.
• 4/1 6/96 - 4/30/96.
• 5/1/96.
• 8/4/96.
• 8/4/96 - 9/1 /96.
• Target date depends on recommendations
(goal is to implement all
recommendations by 2001 ).
• Led by the planning team.
• Water supply team.
Public works division.
• Water supply team.
• Member of the water conservation team.
Drinking water plant personnel.
• Member of the water supply team.
Public works director.
Planning team and Wastewater plant
personnel.
Planning team.
• Town council.
• Consulting firm.
Planning team (including the public works
director).
Depends on recommendations.
• Water fee revenue increase.
• Enlist volunteer help.
• If possible, a loan from the
State Revolving Fund. If not,
a general revenue bond.
• If possible, a loan from the
State Revolving Fund. If not,
a general revenue bond.
-------
PROBLEM: Leaf burning.
GOAL: Prevent disposal
of yard waste with
municipal solid waste.
Solutions
Initiate a
townwide yard waste
composting program.
Step-by-Step Approach
Form yard waste team.
• Research yard waste composting
alternatives.
• Identify a composting site.
• Develop a pamphlet that describes
the benefits of composting and
explains to residents how to
participate in the composting
program.
Mail the pamphlet to all town
residents.
Begin yard waste composting.
Start/Completion Date
• 1 17/97 - 1 /21 /97.
• 1 728/97 - 3/1 1 /97.
• 3/18/97-4/15/97.
• 3/28/97 - A/15197.
4/26/97.
5/14/97.
Person(s) Responsible
• Led by the planning team.
Composting team.
Composting team.
• Member of the composting team.
Composting team.
Member of public works department who is
in charge of composting.
Financing Method(s)
Loan.
• Enlist volunteer help.
0
Q
3"
—t
V|
-------
Appendix A:
Environmental Community Agreement
Between the Kenai Peninsula Borough
and the Alaska Department of
Environmental Conservation
a. Introduction
The goal of the Alaska Department of Environmental Conservation (DEC) is to protect
public health and the environment through cost-effective environmental problem solving.
In the spirit of achieving this goal DEC and the Kenai Peninsula Borough (KPB) agree to
develop, maintain, and update a cooperative working agreement to identify public health
and environmental issues.
This agreement is not to be construed as an enforceable document, but rather as a checklist
for identifying issues, and solving problems within reasonable timeframes.
This agreement is limited to programs and activities that are the primary responsibility of
the Department of Environmental Conservation.
b. Purpose Statement
By this agreement, KPB and DEC establish a common agenda to work together on
environmental protection objectives and specific goals. This will include efforts to solve
environmental problems in the KPB in a cost-effective manner.
c. Changes to the Agreement
The signatories will review this document annually from the effective date of this agree-
ment. Amendments or additional appendices may be developed and implemented by
mutual agreement at any time, without renegotiating the entire environmental community
agreement.
93
-------
d. Effective Date of Agreement
This agreement is effective March 20, 1992.
e. Contact Persons
The contact persons for initiating any of the activities defined in this agreement are: for
DEC, Les Buchholz, the DEC District Manager (or his successor) located in Soldotna;
for KPB, the Mayor or his designee.
f. Schedule and Purpose of Meetings
The contact people for KPB and DEC will meet at least once every two months at a
mutually agreeable location. The purpose of these regular meetings is to identify and
address environmental concerns within the KPB.
g. Regulations Assistance Workshops
DEC is available to conduct a regulations assistance workshop on state environmental
regulations that affect the KPB. The workshop agenda can be expanded to allow partici-
pation from other communities and state and federal agencies. DEC expects to conduct
the workshops on various regulation topics and issues in central locations around the state.
h. Pollution Prevention
KPB agrees to promote pollution prevention practices that focus on eliminating or
reducing pollution to the air, land, and water rather than on controlling pollution after it
has been created. In order to minimize present and future threats to human health and
the environment KPB, with assistance from DEC, agrees to the pollution prevention
hierarchy as local policy, declaring that:
1. pollution should be prevented or reduced at the source to the maximum extent
possible;
2. pollution that cannot be prevented should be recycled in an environmentally
safe manner;
3. pollution that cannot be prevented or recycled should be treated in an environ-
mentally safe manner; and
4. disposal should be employed only as a last resort and should be conducted in an
environmentally safe manner.
i. Pollution Prevention Technology Roundtable for Local Governments
KPB agrees to designate one or more local governmental personnel to attend Pollution
Prevention Technology Transfer Roundtable meetings as they occur. The next scheduled
meeting will occur in Anchorage on April 9 and 10, 1992. The Roundtables were
established by DEC in cooperation with the Alaska Municipal League. The purpose of
the Roundtable is to transfer information to local governments about opportunities to
prevent pollution through waste reduction and recycling in their communities.
94 Appendix A: Environmental Community Agreement
-------
j. KPB Comprehensive Planning Effort
DEC is available to assist in developing environmental quality goals and objectives for the
KPB Comprehensive Plan and to also assist in incorporating state regulations with
borough regulations.
k. Areas of Agreement
The following pages will outline the programs that KPB and DEC have agreed to initially
address as priority issues. The programs are ranked in the order of their priority.
I. Other Programs
Pursuant to the authority granted to DEC by A.S. Title 46 and the authority granted to
KPB by A.S. Title 29, and their respective regulations and ordinances, other programs
may be identified and added to the list of priority issues.
The department is available to assist KPB in these program areas.
Village Safe Water (Facility Planning, Construction, and Operations)
Safe Drinking Water
Domestic & Industrial Waste Water Treatment
Solid & Hazardous Waste
Water Pollution Prevention
Animal Health and Dairy
Pesticides
Radiation Protection
Underground Storage Tanks
Pollution Prevention (waste reduction and recycling)
Environmental Health
The following consent to the above agreement for the mutual benefit of the State of Alaska
and to the Kenai Peninsula Borough.
Appendix A: Environmental Community Agreement 95
-------
Don Gilman, Mayor
Kenai Peninsula Borough Date
Jon Sandor, Commissioner
Alaska Department of Environment Conservation Date
Svend Brandt-Erichsen
Regional Administration
Southcentral Regional Office
Alaska Department of Environment Conservation Date
Les Bucholz
Kenai District Manager
Alaska Department of Environment Conservation Date
96 Appendix A: Environmental Community Agreement
-------
Present Situation
Strategy
Goals
1. Oil and Hazardous Substance
Spills
There have been a number of
hazardous substance spills in the
KPB.
DEC recognizes local concern
about hazardous substance spill
prevention and response.
2. Solid Waste and Disposal
The KPB has responsibility for
solid waste disposal throughout
the entire borough. KPB operates
a number of landfill sites with
DEC permits.
3. Leaking Underground
Storage Tank Program
There are leaking underground
storage tanks in the KPB area.
4. Treatment/Disposal of
Contaminated Soils
There are contaminated soils at
many and scattered locations
within the borough but there is
no place to store or dispose of
this material.
5. Household Hazardous Waste
(Spring Cleanup)
Residents and small businesses
generate hazardous wastes.
6. Air and Water Quality
There are concerns regarding
existing and the future quality
of air and water resources.
Assist KPB with development of a local
emergency plan.
If the Emergency Response Commission
approves the local emergency plan, then
an amendment to this agreement will be
developed which assures that DEC will
reimburse KPB for expenditures that may
occur in the event KPB participates in oil
spill or hazardous substance discharge
response and cleanup.
DEC will process applications for solid
waste disposal permits as efficiently as
possible, assist the city in public meeting,
and provide suggestions for different
techniques for disposing of wastewater
and solid wastes.
DEC will meet regularly and coordinate
activities with other State agencies, local
governments within the KPB to assist in
problem identification and to promote
compliance. Assist tank owners to remain
in compliance with all applicable State
and federal regulations to maintain
eligibility for participation in the State's
Underground Storage Tank Assistance
Fund Program.
Assist in locating an acceptable site for
disposal of contaminated soils. Assist in
developing methods for treatment of
contaminated soils.
Since 1983 DEC has funded an annual
hazardous waste cleanup. The strategy is
to first determine how much waste exists
and to divert as much hazardous wastes
from landfills.
Continue to identify sources of pollution
and provide monitoring assistance.
Assist KPB with implementation of the
local emergency plan after it is approved
by the SERC. Ongoing.
Assist in long-range planning for
operation of solid waste sites in a cost-
effective and environmentally safe
manner.
Cleanup of existing leaks and spills,
prevent future leaks from UST systems in
order to prevent the public from
contamination of drinking water and to
protect the environment.
To provide an environmentally safe
location for storage/disposal of
contaminated soils. To assist in
development of treatment methods.
Continue to fund KPB for this year and
divert as much residential and small
business waste as possible from the
landfills. In the future DEC wants to bring
this service to more communities.
Work toward improving and
maintaining high quality of air and
water resources.
Appendix A: Environmental Community Agreement 97
-------
Present Situation
Strategy
Goals
7. Subdivision Plan Review
There are conflicting interpreta-
tions of the subdivision review
process.
8. Hazardous Waste Sites
There are a number of hazar-
dous waste sites located in the
KPB.
9. Septage Disposal and Small
Incinerators
The KPB is concerned about the
number and impact of small
incinerators as well as the
impacts of septage disposal.
10. Public Relations
The amount of information pro-
vided to the public and the KPB
regarding environmental issues
and regulations is limited.
11. Oil and Hazardous
Substance Release and
Response Fund (OHSRRF)
Limited information is available
regarding the expenditure of
OHSRRF monies.
Cooperate in resolving procedural
problems regarding subdivision plat
reviews and approvals.
The ADEC will provide to the KPB
quarterly copies of the Hazardous Site
Status Report and provide the KPB with
further guidance and assistance to
determine the impacts of these sites.
A continued dialogue will be maintained
with the KPB with regard to incinerator
sites and impacts from septage disposal
to ensure that actions serve the public
purpose.
Provide for continued dialogue with the
KPB to ensure adequate transfer of
information and enhance the relationship
and understanding between the KPB and
the ADEC.
Develop a Kenai Environmental Advisory
Board to provide community input and
guidance regarding local environmental
issues.
Provide the KPB a statement of
accounting for this fund upon request.
To ensure that new parcels created by
subdivisions are adequate to support
onsite septic systems.
A detailed impact assessment of existing
hazardous waste sites as identified in the
Kenai cleanup inventory is needed.
Ensure that ADEC actions meet with
goals of the KPB and serve the public
purpose.
Ensure that the KPB and the public are
kept informed about changes to and new
environmental regulations and issues in
their community.
Ensure that the KPB has adequate
information regarding the expenditure of
OHSRRF monies.
98 Appendix A: Environmental Community Agreement
-------
Appendix B:
What Environmental Regulations
Affect Your Community?
This appendix is a starting point for determining which federal regulations affect your
community. Not all of the regulations described here will apply to your community,
and many others, not described here, might affect you. In addition, state and local
regulations might differ from the federal regulations listed here. The best approach
is to contact your state environmental or health agency to find out how their regulations
differ. Staying in contact with your state regulatory agency also will help keep you informed
about any new regulations that might affect your community in the future.
Finally, remember the U.S. Environmental Protection Agency's (EPA's) first rule of thumb:
Prevention is the best medicine. The best way to protect people's health and your
community's environment is to reduce the amount of waste and pollution created in the
first place. Pollution prevention should be a priority for every community.
Drinking uality
Congress passed the Safe Drinking Water Act in 1974 to make sure that the drinking
water supplied to the public is safe. In 1986, Congress strengthened the Act because of
concerns about the growing number of threats to the safety of the nation's drinking water.
The Safe Drinking Water Act applies to your community if you have a public water system
with at least 15 service connections (homes and businesses that receive water from your
system) or that regularly serves at least 25 people. In most states, the State Department
of Health or Environmental Protection provides technical and regulatory assistance for
public water systems.
99
-------
The Safe Drinking Water Act also applies to privately owned public water systems such
as mobile home parks and water companies, noncommunity systems, such as factories,
schools, and campgrounds with their own water supply, also fall within the regulations.
Compliance is the responsibility of the owner/operator of these nonmunicipal systems,
but people will probably turn to local officials if something is wrong with their water
system. Therefore, if such systems exist in your community, it's a good idea to be aware of
the requirements for these systems and workwith the systems' owners/operators to provide
safe drinking water. These systems may also benefit from consolidation with the municipal
system.
As a local official responsible for a community water system, you need to do several things
to make sure that your community is in compliance with the Safe Drinking Water Act:
Make sure that a certified operator runs your public water system. Most states have
mandatory certification for operators.
I Make sure that your operator takes advantage of training opportunities by the state
and others.
Your operator is responsible for water quality testing. Make sure that your operator is
taking water samples correctly and sending them to a state-certified laboratory for analysis.
Test results must be reported to the state agency within 10 days of receiving them. If samples
exceed safe levels of a regulated contaminant, the operator must notify the state within 48
hours and the public as soon as possible and begin efforts to correct the problem.
According to the Surface Water Treatment Rule, if your water system uses surface
water (an intake in a river or lake) or ground water that is under the direct influence of
surface water (your state agency will determine this), you must disinfect your water.
Your state agency can tell you if your system also requires filtration. If your drinking
water source is surface water, you may also want to work with the state to protect the
watershed area from contamination.
If your drinking water source is ground water, find out more about wellhead protec-
tion. Work with your state to protect wellhead areas from contamination. Also consider
working with private water systems in your community to implement wellhead protection.
Some communities find that forming partnerships with neighboring communities to
share the cost of needed monitoring, improvements, or qualified personnel is a good
way to save money.
What Contaminants Does My Community Need To Test For?
EPA has established maximum contaminant levels (MCLs) based on estimated health
risks that many contaminants might cause. Eighty-three substances are regulated by the
Safe Drinking Water Act, and the list is growing. Most of these substances fall into one of
the following categories: coliform bacteria, disinfection byproducts, inorganic
chemicals, synthetic and volatile organic chemicals, fluorides, lead and copper,
radionuclides, nitrate/nitrite, and asbestos. Information about each of these categories
100 Appendix B: What Environmental Regulations Affect Your Community?
-------
is provided below. In addition, basic monitoring requirements for these categories are listed
in the table on page 106. Contact your state agency to find out more information about
drinking water standards as they apply to your community.
Coliform Bacteria
Total coliform bacteria are known as "indicator organisms" because they are easily
measured and serve to "indicate" if disease-causing bacteria (pathogens), such as fecal
coliform, are present.
Most community water systems, as well as most noncommunity water systems (public
water systems that do not serve residential populations), must submit samples for coliform
bacteria on a regular monthly basis. You are required to submit at least one routine sample
per month for your system depending on its size. Follow procedures for sampling provided
by your testing laboratory or state agency.
If your system does not test positive for total coliforms:
Continue to submit regular samples and review results.
I Maintain a good operation and maintenance program for your water system, including
regular line flushing at fire hydrants and on dead ends.
If your system has a positive total coliform sample result:
I Immediately call your state agency and ask for help in repeating sampling and analysis
and locating any possible sources of contamination.
Follow the state agency's direction in issuing public notices and any state emergency
measures that may be required.
Correct any problems causing contamination immediately. Contact one of the resource
agencies listed in Appendix D of this book if you need technical support or help in
financing arrangements.
Disinfection Byproducts
Disinfectants (such as chlorine) are the primary defense against diseases caused by
microbiological contaminants in public water systems. The disinfectants themselves,
however, have the potential to react with organic materials in the water and form
byproducts that can contaminate the water. All public water supply systems are required
to disinfect their water, although exceptions may be granted if the water comes from
sources that are determined not to be at risk from microbiological contamination. Indi-
vidual states will determine if monitoring for disinfection byproducts is necessary, depend-
ing on each system's vulnerability to byproduct development. At present, four disinfection
byproducts are regulated, but only in community water supplies serving populations of
10,000 or greater. New rules are under development that might include smaller systems.
Appendix B: What Environmental Regulations Affect Your Community? 101
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Contact your state agency for more information about monitoring for disinfection bypro-
ducts.
Inorganic Chemicals
Even if your community has little pollution, inorganic chemicals are likely to enter your
water naturally from the rocks and soil surrounding the water supply. Exposure to high
levels of certain inorganic chemicals can cause damage to the liver, kidneys, nervous system,
and circulatory system.
EPA has setMCLs for 17 inorganic chemicals. All community water supply systems must
monitor for regulated inorganic chemicals in their water supplies. Under the present rules,
sampling for inorganic chemicals is required every 3 years from each sampling point for
ground-water supplies and every year from each sampling point for surface water supplies.
Contact your state agency to obtain more detailed information about sampling require-
ments and MCLs for inorganic chemicals.
Nitrates/Nitrites
Nitrates and nitrites are inorganic compounds that can occur naturally or can be intro-
duced into drinking water from feedlots, fertilizers, and wastewater. Community water
systems must monitor annually for nitrates/nitrites if they use ground-water sources and
quarterly if they use surface water sources. Contactyour state agency for more information
about nitrate/nitrite monitoring requirements.
Synthetic and Volatile Organic Chemicals
Synthetic organic chemicals are human-made compounds used for a variety of industrial,
manufacturing, and agricultural purposes. For testing purposes, synthetic organic com-
pounds are divided into two groups: volatile synthetic organic chemicals (VOCs) and
nonvolatile synthetic organic chemicals (SOCs), depending on how easily they are released
into the atmosphere. The effects of these chemicals include damage to the nervous system
and kidneys, as well as possible cancer risks.
Unless you are granted a waiver by the state, all public water supply systems are required
to test for SOCs, such as pesticides and polychlorinated biphenyls (PCBs). All small water
systems (defined as less than 150 service connections) must monitor for 21 regulated
VOCs. Contact your state agency for more specific information on monitoring require-
ments and MCLs for both SOCs and VOCs.
102 Appendix B: What Environmental Regulations Affect Your Community?
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Fluoride
Fluorides are compounds that contain the element fluorine. They occur naturally in many
water sources and are added in the treatment process by many public water supply systems.
In small amounts (between 1.0 and 1.5 milligrams per liter), fluoride helps reduce tooth
decay; amounts greater that 2.0 milligrams per liter can have harmful health effects.
All community public water systems must test for fluoride at every entry point to the
distribution system after treatment. Tests must be made every 3 years for ground-water
supplies and/or every year for surface water supplies. Contact your state agency for
information about fluoride sampling requirements.
Lead and Copper
Lead and copper are inorganic chemicals that often come from pipes or plumbing fixtures
in water systems that have corrosive water. Lead can cause damage to the nervous system
and kidneys, and can be very toxic to infants and pregnant women. Copper causes stomach
and intestinal problems.
In June 1991, EPA published new rules requiring tests at customer taps. Monitoring must
be conducted in "high-risk" homes (those with newer lead solder, lead pipes, or lead service
lines). High levels of lead and copper require treatment to reduce the corrosiveness of the
water, and possibly replacement of lead service lines. Ask your state agency for more
information about monitoring, treatment, and public education requirements.
EPA also banned the use of solder and flux with more than 0.2 percent lead and the use of
pipes containing more than 8.0 percent lead in new plumbing installed in facilities
connected to the public water supply. This law only applies to plumbing that distributes
drinking water and does not require the removal of existing solder. Check with your state
agency for more information about the Lead Materials Ban.
Radionuclides
Radionuclides are radioactive particles that occur naturally in areas of uranium and radium
deposits and also are found in nuclear waste. Radionuclides that can occur in drinking
water include gross alpha, gross beta, radium 226 and 228, uranium, and radon. Radionu-
clides, even in very small concentrations, pose a cancer risk. Radon, for example, can occur
in almost all ground-water supplies, and concern exists about possible cancer risks from
air exposure to radon volatilized through shower heads or laundry.
All community public water supply systems must test for radionuclides (except radon and
uranium) every 4 years. Check with your state agency to find out if there have been any
changes to the monitoring requirements.
Appendix B: What Environmental Regulations Affect Your Community? 103
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Asbestos
Asbestos fibers in drinking water are a suspected cancer-causing agent. Asbestos occurs
naturally in some water supplies, or it can enter water in the distribution system as a result
of corrosive action on asbestos cement water pipes. All public water supply systems must
monitor for asbestos. If asbestos is not likely to occur in your water source, you do not
have asbestos cement pipes, or your water is noncorrosive, you could be eligible for a
waiver from your state agency. Contact your state agency for more information about
asbestos monitoring requirements and waiver eligibility.
What Should I Do if Test Results Exceed MCLs?
In all cases, if the level of a contaminant in the public water supply is higher than the
MCL, you should:
Notify your state agency as soon as possible.
Notify the public of the violation as directed by your state agency.
Work with your state agency and/or an engineer to find the source of contamination
and the best way to reduce the amount of the contaminant in your water supply.
Work with your state agency to see if your community can continue to use the water
supply while you explore solutions to the contamination.
I Ask your state agency and other assistance agencies (listed in Chapter 8) for help in
finding the financial resources you need to make the necessary changes in the water
system.
Public Notification
The Safe Drinking Water Act requires that all owners or operators of public drinking
water systems notify their customers when drinking water standards are violated. The
purpose of public notification is to inform consumers of any potential adverse health
effects, and to tell them what steps they can take to minimize their impact. Always notify
your state agency of the violation first, and ask their direction in proceeding with public
notification.
Where Are the Regulations Published?
The regulations implementing the Safe Drinking Water Act can be found in the Code of
Federal Regulations, Title 40, Parts 141, 142, and 143.
104 Appendix B: What Environmental Regulations Affect Your Community?
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Wellhead Protection
The best way to avoid contamination and expensive cleanup procedures is to prevent your
water supply from becoming polluted in the first place. The 1986 Amendments to the Safe
Drinking Water Act ask each state to develop a wellhead protection program to protect
public water supply wells and wellfields from contamination. The law specifies that all
states participate; however, there are no penalties for states that do not participate, nor are
there funds available to help states develop these programs. In addition, EPA has no
authority to set up a wellhead protection program if a state chooses not to establish one.
According to the 1986 Amendments, each state must develop a wellhead protection
program that:
Specifies roles and duties of local governments, state agencies, and public water
suppliers with respect to the state's wellhead protection program.
I Establishes a wellhead protection area for each wellhead.
I Identifies the sources of contamination at each wellhead.
I Develops ways to protect the water supply within wellhead protection areas from those
contaminants.
I Develops plans for each public water supply to respond to well or wellfield contamina-
tion.
An effective wellhead protection program requires the participation of all levels of
government. Your responsibilities as a local government official depend on the specific
requirements of your state's wellhead protection program. Frequently, local governments
are responsible for ensuring that the wellhead areas are properly protected from contami-
nation. Typical practices used by local governments to protect ground-water quality include:
I Implementing zoning ordinances that protect wellhead areas, such as ground-water
protection districts, and implementing restrictions on certain types of land uses.
Developing land-use plans, such as a regional or local master plan.
I Developing health regulations that prohibit certain activities, such as the use of
underground fuel storage tanks or chemical septic cleaners, within the wellhead
protection area. Local health regulations also can require businesses using hazardous
materials to register with local authorities, who can inspect these facilities periodically
to ensure proper handling of those materials.
If your state adopts a wellhead protection program, you will be required to enforce your
state's specific requirements for your area. Even if your state does not adopt a wellhead
protection program, it is in your community's interest to do everything possible to protect
your water supply. To find out more about protecting the quality of your community's
water supply, contact your state agency.
Appendix B: What Environmental Regulations Affect Your Community? 105
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Drinking Water Regulations
What Should Be Done To Comply With
Substance the Regulation?*^
How Often Do I Need To Take Samples?
Coliform
bacteria
Test for total coliform bacteria.
Work with state to establish a "sample-siting
plan" for your community that lists where
samples should be taken each month.
Complete a sanitary survey of your water
system at least once every 5 years. This is
usually done by the state agency. The initial
survey must be conducted by June 29, 1994.
Take and submit at least one sample per month. The
number of samples required depends on your system's
size.
If the sample tests positive for total coliform, collect
four repeat samples within 24 hours of notification of
the positive result. Repeat samples must be collected
within five service connections of the original sample,
with at least one at the original location, one upstream
and one downstream. Analyze the positive sample for
fecal coliform (E. coli).
After the state reviews the sanitary survey, it can
change the monitoring frequency, which may reduce
the number of routine samples required. Without the
sanitary survey, you need to collect five routine samples
every month.
Inorganic
chemicals
Test water for inorganic chemicals.
If levels of inorganic chemicals in your
water are low, apply for a waiver from your
state agency to reduce required testing.
Nitrate/nitrite sampling requirements cannot
be waived.
Test surface water systems yearly and ground-
water systems every 3 years.
With waiver, test every 9 years (from 1 993).
For nitrates, test surface water systems quarterly
and ground-water systems yearly.
Every public water system must sample for nitrites
once. The state then determines whether and how
often systems must do repeat sampling.
SOCs
Cooperate with your state agency to
determine your water supply's vulnerability
to SOCs. If your system is not vulnerable,
apply for a waiver from the state exempting
you from sampling requirements until 1996.
If your system is vulnerable, work with your
state agency to take the first round of samples.
Vulnerable systems must be sampled every 3 months,
beginning in 1993.
If no SOCs are found in the first round of sampling,
repeat sampling as follows:
Population Served Number of Samples
> 3,300 Two samples every 3 years
< 3,300 One sample every 3 years
With a waiver, no monitoring is required until 1 996.
Before 1996, the vulnerability assessment must be
updated and a new waiver must be granted for the
next compliance period.
VOCs
Conduct initial sampling and repeat
sampling, if necessary, for regulated
VOCs in the water supply.
Inform your customers if you find out
that your public water supply has VOCs
violations or a monitoring waiver.
For initial sampling, take one sample every 3 months
for 1 year before 1996. Your state will designate
either 1 993, 1994, or 1 995 as the year in which
your system will be required to take samples.
For repeat sampling, take yearly samples for both
ground-water and surface water systems.
Conduct a "vulnerability assessment" and use data
from initial sampling or previously collected data to
apply for a waiver for additional sampling requirements.
If MCL is exceeded, see "What Should I Do If Test Results Exceed MCLs?" on page 1 04.
Contact your state agency for more detailed and up-to-date information on drinking water regulations affecting your
community.
106 Appendix B: What Environmental Regulations Affect Your Community?
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What Should Be Done To Comply With
Substance the Regulation?**
Drinking Water Regulations (continued)
How Often Do I Need To Take Samples?
Fluoride
Test water at every entry point to the
distribution system after treatment.
If fluoride levels are over 2.0 mg/L, ask your
state agency and/or engineer how to lower
the fluoride level, and notify the public about
the health effects of fluoride.
Test surface water systems yearly and ground-water
systems every 3 years.
Lead and
copper
Complete a "materials evaluation" of the
distribution system.
Collect tap water samples from high-risk
places (homes with lead pipe, lead service
lines, and copper pipe with lead solder
installed after 1982). Contact your state
agency for sampling procedures.
If the system exceeds either action level in
more than 10 percent of tap samples, addi-
tional monitoring, corrosion control, and public
education requirements apply. Your state will
help you.
Collect one tap sample from the following number of
sites every 6 months:
Population Number of Sites
<100 5
<500 10
501-3,300 20
Collect samples from each entry point into the
distribution system every 6 months.
If the system meets the action levels for copper and
lead for two consecutive monitoring periods, check
with your state agency about reducing the sampling
frequency to once per year. If the system continues to
meet action levels for 3 years, sampling frequency
may be further reduced.
Radionuclides Test for gross alpha particle activity and
combined radium 226 and 228.
For initial sampling, take one sample every 3 months
for 1 year.
Unless the average of initial tests results shows
radionuclide levels above or near the MCL, repeat the
test once every 4 years.
A revised regulation, which will include monitoring
requirements for uranium and radon, is scheduled to
be published in April 1 995. Contact your state agency
to find out how the new regulation will affect your
community.
Asbestos
Cooperate with the state agency to perform
a vulnerability assessment.
If you have asbestos cement pipes, take
samples from the tap.
If you have asbestos in the source water only,
take samples from each entry point to the
distribution system.
If asbestos is unlikely to be in your
system, apply for a waiver from your state
agency to avoid unnecessary testing.
Test for asbestos once every 9 years (at least once
before 1996).
With an asbestos waiver, no testing for asbestos is
required.
If MCL is exceeded, see "What Should I Do If Test Results Exceed MCLs?" on page 104.
Contact your state agency for more detailed and up-to-date information on drinking water regulations affecting your
community.
Appendix B: What Environmental Regulations Affect Your Community? 107
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Wastewater Treatment
Federal regulations have been developed to govern various aspects of wastewater treat-
ment. These regulations cover:
Pretreatment of industrial wastewaters.
Limitations on the level of pollutants in wastewater discharged into waterways.
I Management of the solid materials removed from the wastewater during the treatment
process (sludge).
Each of these topics, and the federal regulations governing them, are discussed below.
Pretreatment of Industrial Wastewater
Pretreatment of industrial wastewaters refers to the steps that industries take to remove
pollutants from wastewater before they discharge it into the public sewer system. Pretreat-
ment must remove toxic and hazardous pollutants from wastewaters, which could either
pass through or interfere with the community treatment plant. The Clean Water Act of
1977 setNational Pretreatment Standards to control pollutants that cannot be removed
by or might interfere with wastewater treatment processes.
The National Pretreatment Standards specify quantities or concentrations of pollutants
that may be discharged to a treatment plant by industrial users. In addition, the National
Pretreatment Standards prohibit everyone, including the public, from putting the follow-
ing pollutants in their wastewater:
Flammable, corrosive, solid, or viscous pollutants.
Any pollutant released at a high concentration that can interfere with the collecting
sewer and the treatment process.
Petroleum oil, nonbiodegradable cutting oil, and products of mineral oil origin.
Pollutants that result in toxic gases or vapors.
Any trucked or hauled wastes, except at discharge points designated by the publicly
owned treatment works (POTW).
Does This Regulation Apply to My Community?
Traditionally, small wastewater treatment plants with a design flow of less than 1 million
gallons per day are not required to establish local pretreatment programs. Very small
communities often have few, if any, industrial users.
108 Appendix B: What Environmental Regulations Affect Your Community?
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If your community does have industrial users (such as sawmills, food processing plants,
and metal finishers) that discharge the type of pollutants described on the previous page,
which could pass through or interfere with your treatment facility, your community might
have to implement a pretreatment program to satisfy the National Pollutant Discharge
Elimination System (NPDES) permitrequirements. EPA or approved state environmental
control agencies have the responsibility for administering these permits. (NPDES permits
are discussed later in this section.) In addition, state agencies will implement pretreatment
programs for communities that are too small to implement their own.
What Action Should My Community Be Taking?
To determine whether you are required to set up a pretreatment program in your
community, contact your state water quality agency. If such a program is necessary, the
agency will assist you in its development. Make sure that all affected industries are aware
of the pretreatment standards that they need to meet.
If you are required to establish a pretreatment program, you must establish local ordinances
and other procedures to implement program requirements. You must also identify per-
sonnel who will be responsible for administering and enforcing the program.
Finally, any time you suspect a problem caused by a nondomestic wastewater producer, notify
your treatment works operator, county sanitarian, and appropriate state agency or department.
Where Are the Regulations Published?
The regulations for pretreatment of industrial wastewater are in the Code of Federal
Regulations, Tide 40, Part 403.
The National Pollutant Discharge Elimination System
In response to the nation's growing concern about water pollution, major federal laws were
passed in the 1970s that required the restoration and maintenance of clean water for
residential, commercial, recreational, and agricultural uses. The 1972 Amendments to the
Water Pollution Control Act, which was later amended and renamed the Clean Water
Act in 1977, set federal water quality standards and cleanup schedules for meeting
pollution control requirements. One way in which the goals of these acts are achieved is
through NPDES permits, which set limits on the level of pollutants allowed to be
discharged. These permits, issued mostly by state agencies but in some cases by EPA, are
issued to operators that discharge any pollutant from point sources to a navigable waterway,
such as a lake, river, stream, wetland, or ocean.
Under the Clean Water Act, states must determine how each body of navigable water is
to be classified. This classification designates the water body for one or more of the
Appendix B: What Environmental Regulations Affect Your Community? 109
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following uses: drinking, fishing, swimming, and deep water ports. The water quality standards
used to develop NPDES permits are intended to maintain the designated use or uses of the
water body. For example, permits are likely to be less restrictive for a facility that is discharging
wastewater into a river that is not used for drinking water or recreational purposes than for a
facility that is discharging into a recreational lake that is designated for fishing and swimming.
New permits also will include residuals quality. These same regulations also govern the disposal
of septic tank pumpings (septage) for unsewered communities.
NPDES permits are required for wastewater treatment plants that discharge into waterways.
For most wastewater treatment plants, their NPDES permit requires that they must (at a
minimum) meet secondary treatment standards. Secondary treatment means that the plant
must install technologies that go beyond the settling of solids to remove 85 percent of the
conventional pollutants (materials that deplete oxygen from the water) and control acidity.
Do These Regulations Apply to My Community?
Every community deals with the issue of wastewater. Not all communities, however, have
to comply with the surface water quality standards established under the Clean Water Act.
Thousands of towns and communities are subject only to state and local requirements,
since they use septic tanks or communitywide systems that do not discharge treated
wastewater into navigable waters.
All wastewater treatment facilities that discharge to U.S. waters, however, must comply
with the NPDES requirements. Most of these plants need only meet the secondary
treatment standards, but plants that discharge into high-quality waters may have to meet
more stringent standards.
What Action Should My Community Be Taking?
To make sure that your community complies with the wastewater regulations established
by the Clean Water Act, you should do the following:
If your community has a wastewater treatment facility that discharges into a body of
water, make sure that you have an NPDES permit for operating the treatment plant.
Make sure that the treatment plant operator meets all permit requirements, such as
monitoring pollutant discharge quantities and reporting the results to state authorities.
I If you suspect that your community has a problem with wastewater or water pollution
and might need to install a wastewater treatment plant, contact your state environ-
mental agency to find out information about technology options, NPDES permits, and
potential funding sources.
110 Appendix B: What Environmental Regulations Affect Your Community?
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Where Are the Regulations Published?
The regulations governing the NPDES permitting process are in the Code of Federal
Regulations, Title 40, Parts 122 to 125. The Secondary Treatment Regulations are in Title
40, Part 133.
Sludge Management
Sewage sludge (biosolids) is removed from wastewater during the treatment process.
Federal regulations require that sludge be handled properly when it is used for beneficial
purposes (such as for a soil conditioner or fertilizer) or when it is disposed of in a landfill,
other surface disposal site, or an incinerator. Different requirements apply for sludge that
is used for beneficial purposes and sludge that is disposed of. Sludge can be stored on site
for up to 2 years before use or disposal. Sludge that remains on site for more than 2 years
must meet disposal requirements.
Do These Regulations Apply to My Community?
These regulations apply to all communities that use a central wastewater treatment plant
or mechanical plant, including a lagoon, which produces sludge.
What Action Should My Community Be Taking?
If your community generates sludge through its wastewater treatment process, you should:
Contact the water division of your EPA regional office to find out about obtaining a
permit for sludge generation and management. You will have to apply for a sludge
permit during your next NPDES permit renewal.
Collect representative samples of the sewage sludge and test for regulated metals.
I Properly dispose of the sludge. Sludge may not be placed in unlined surface areas when
arsenic, chromium, and nickel levels are above regulatory pollutant levels.
If your community uses sludge for beneficial purposes, you should be aware of and follow
proper methods for the agricultural and nonagricultural land application of sludge. The
use of contaminated sludge can threaten the health of the residents of your community.
Where Are the Regulations Published?
Sewage Sludge Program Regulations are contained in the Code of Federal Regulations, Title
40, Parts 122, 123, and 501. Technical regulations for sewage sludge use and disposal are
in Title 40, Parts 258 and 503.
Appendix B: What Environmental Regulations Affect Your Community? Ill
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Wetlands Protection
"Wetlands" are marshes, swamps, bogs, and other similar wet areas. Wetlands can be
coastal or inland, saltwater or freshwater. They are an important resource because they
help improve water quality, reduce flood and storm damages, provide important fish and
wildlife habitats, and support hunting and fishing activities. The two most important laws
dealing with wetlands protection are Section 404 of the Clean Water Act and the
Swampbuster Section of the Food Security Act
Under Section 404, EPA and the U.S. Army Corps of Engineers established a permit
program to control the release and dumping of dredged or fill materials into most wetlands.
As a result, you need to apply for a permit for almost any type of activity that affects or
might affect wetlands, such as dumping or building on or near a wetland. The Swampbuster
program withholds federal farm program benefits from anyone who:
I Plants a crop on a wetland that was converted into farm land after December 23, 1985.
I Converts a wetland to use as farm land after November 28, 1990.
Does This Regulation Apply to My Community?
Wetlands can be found in almost every county of every state in the United States. Although
there are many exceptions, especially for farmers, you should always assume that you need
a permit and check with someone from the U.S. Army Corps of Engineers before you
begin any activities that might affect a wetland. The U.S. Army Corps of Engineers will
be able to tell you if you need an individual permit or not. Anyone who violates Section
404, either by not getting a permit or by disregarding the conditions of a permit, may have
to pay to restore the area, pay fines, and/or go to jail.
What Action Should My Community Be Taking?
To comply with Section 404 of the Clean Water Act, you should:
I Find out where wetlands are located in your community by ordering wetland maps
(800-USA-MAPS).
I Before beginning any projects that might affect wetlands in your area, check with the
U.S. Army Corps of Engineers to see if a Section 404 permit is needed.
Inform your community about the requirements of Section 404 of the Clean Water Act
through public education, particularly directed to land developers and builders, so that
correct procedures are used and costly violations are avoided.
112 Appendix B: What Environmental Regulations Affect Your Community?
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Where Are the Regulations Published?
The regulations implementing Section 404 of the Clean Water Act are in the Code of Federal
Regulations, Title 40, Part 230.
Nonpoint Source Pollution
Nonpoint source (NFS) pollutants—such as grease and oil from streets and parking lots,
pet wastes, lawn fertilizers, pesticides, chemicals from agricultural and industrial sites, soil
from construction sites—can enter ground water and surface waters, causing problems
with water quality in your community. NFS pollutants are typically carried over and
through the ground by rainfall and snowmelt. Rivers, lakes, estuaries, coastal waters, and
wetlands all experience major negative effects as the result of nonpoint source pollution.
NFS pollution is difficult to regulate because it comes from a variety of sources and often
results from the ordinary and necessary things that we do, such as farming and building
houses. EPA has decided that flexible state and local decision-making is the best way to
control NFS pollution. The National Nonpoint Source Program under Section 319 of
the Clean Water Act requires states to identify:
Any navigable waters that are affected or threatened by NFS pollution
The pollution sources affecting those same waters
How Do NFS Pollution Control Regulations Affect My Community?
Control of NFS pollution is voluntary for most small communities. If NFS pollution is having
a major effect on the water quality of your community, it is in your best interest to control the
problem. EPA's system for choosing a plan to control NPS pollution is calledbest management
practices (BMPs). BMPs can be cost effective and easy to use if they are prudently applied.
What Action Should My Community Be Taking?
As a local official, you are responsible for finding out if your state has laws regulating NPS
pollution. You should:
I Contact your state environmental agency to ask if any navigable waters in your
community are affected or threatened by NPS pollution.
Appendix B: What Environmental Regulations Affect Your Community? 113
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I If your community has a problem with NFS pollution, cooperate with your state
environmental agency to develop BMPs. Many states already have carefully planned
management strategies to control NFS pollution and protect water quality. Your state
agency will help you develop a BMP program that considers local environmental,
economic, and geographic factors as part of the solution.
I Keep informed about new stormwater regulations that could affect small communities. For
more information on stormwater regulations, call the Stormwater Hotline at 703-821 -482 3.
Where Are the Regulations Published?
The stormwater regulations are containedin the Code ofFederdReguktions, Title 40, Parts 122 to 124.
Solid Waste Management
Municipal solid waste is nonhazardous waste generated by people in their homes, offices,
schools, restaurants, and other places. Solid waste that is not recycled must be disposed of
and landfilling is still the most common disposal method. The regulations affecting
municipal solid waste disposal facilities (landfills) are the Resource Conservation and
Recovery Act (RCRA) Subtitle D, Municipal Solid Waste Landfill Criteria.
The purpose of Subtitle D is to prevent solid waste from polluting the soil or ground water
by being disposed of improperly. Subtitle D regulates the location, design, operation,
ground-water monitoring, and closure and postclosure care (including financing) for both
old and new municipal landfills.
Subtitle D applies if your community owns and operates a landfill, is planning to build a landfill,
or is disposing of solid waste anywhere except in a landfill. If you have questions about the
regulations and whether they apply to your community, contact your state environmental
agency for help. Also contact your state agency to discuss your options, and cooperate with
neighboring communities to find an appropriate solid waste management solution.
Planning for New Landfills
RCRA Subtitle D restricts the construction of new landfills in floodplains, wetlands, fault
areas and seismic zones, unstable areas, and in the vicinity of airports. According to Subtitle
D design requirements, in states with EPA-approved permitting programs, landfills must
be designed to ensure that federal drinking water standards are not exceeded in the ground
114 Appendix B: What Environmental Regulations Affect Your Community?
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Operation
water. In states without EPA-approved programs, landfills must be designed with a
composite liner (made of synthetic material) covering a 2-foot clay liner and a collection
system to capture and treat leachate.
Small community landfills are exempt from the design requirements of the regulation if
they receive less than 20 tons of solid waste each day (based on a yearly average), show no
evidence of ground-water contamination, and meet one of the following conditions:
Weather or other causes make it difficult for community residents to get to a regional
landfill for 3 months in a row of every year.
There are no practical alternatives for solid waste disposal, and there is less than 25
inches of precipitation each year.
Your state agency must approve of the design before a landfill can be built or structural
changes to an old landfill or dump can be made.
All landfills must have monitoring wells to detect any ground-water contamination. If
ground water is contaminated, the owner/operator is required to clean it up to acceptable
standards to protect people's health and the environment.
Check with your state agency to learn the schedule you must follow to comply with the
ground-water monitoring requirements.
Owners and operators of both new and existing landfills must observe the following
operating criteria:
Keep out hazardous waste.
I Cover each day's waste with soil to prevent the spread of disease by rats, flies,
mosquitoes, and other animals.
I Monitor for methane gas. If emission levels in the landfill are over a certain limit, notify
your state agency and develop a plan to solve the problem.
I Restrict access to the landfill to preventillegal dumping and other unauthorized intrusions.
Control stormwater runoff and discharge to surface waters.
I Refuse bulkor noncontainerized liquid waste, such as from tank trucks or in 55-gallon drums.
I Control air emissions. Emissions from landfills may not violate state and federal clean
air laws and regulations. Open burning of waste is prohibited at landfills.
Keep records.
Appendix B: What Environmental Regulations Affect Your Community? 115
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Closure and Postclosure Care
Landfills can close for many reasons. Eventually every landfill becomes full and cannot
accept more solid waste. Landfills also may be required to close if they violate a require-
ment, such as location or design, or if the presence of the landfill has become a threat to
people's health or the environment in the area. When a landfill closes, the owner and
operator must follow very specific procedures to prevent the closed landfill from causing
health or environmental problems:
Prepare, in advance, a written plan that describes all of the steps that will be taken to
close the landfill.
Develop a plan to pay for the maintenance, closure, and postclosure care of the landfill.
Owners and operators need to prepare a detailed written cost estimate of how much it
would cost to hire someone else to complete the closure, postclosure care, and any
necessary cleanup. They need to assure the state that they will set aside at least that
much money. Each owner or operator should consult with the state agency about the
best way to do this.
Notify the state agency of the intention to close the landfill.
Complete closure activities within 180 days of starting closure.
I Install a final cover over the landfill to prevent rainwater from getting into the landfill
and to prevent as much erosion as possible.
Hire an engineer to verify that the closure has been completed according to the closure
plan.
I Make a note on the property deed to inform anyone who might buy the land in the
future that the land had been used as a landfill and therefore its use is restricted.
Prepare, in advance, a written plan for postclosure that includes:
— A description of the required monitoring and maintenance equipment.
— The name, address, and telephone number of the person or office to contact about
the landfill during the postclosure period.
— A description of the planned uses for the property during postclosure.
The owner or operator is also responsible for postclosure care of the landfill area for 30
years after the landfill closes. Postclosure care includes:
I Maintaining the final cover, including making repairs caused by erosion or any other
damage.
Maintaining and operating the leachate collection system, if there is one.
Monitoring the ground water as necessary.
I Maintaining and operating a gas monitoring system.
I Hiring an engineer to inspect the landfill at the end of the postclosure period to verify
that everything has been done according to the postclosure plan.
116 Appendix B: What Environmental Regulations Affect Your Community?
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What Action Should My Community Be Taking?
To comply with the Subtitle D Municipal Solid Waste Landfill Criteria, you should contact
your state agency to find out if your community's landfill is exempt from any of the Subtitle
D regulations. Then follow the regulations that do apply.
In addition, as a community leader, you should try to reduce the amount of solid waste
that your community produces by:
I Conducting public education programs that encourage people to buy reusable products
and products with less packaging.
Evaluating a recycling program for materials such as glass, aluminum, plastic bottles,
white paper, and newspaper, either alone or in cooperation with other communities in
your area.
Considering the pros and cons of a community program for composting yard wastes.
I Educating your community about the proper way to deal with wastes that should not
be taken to the landfill, such as tires, batteries, used motor oil, and many hazardous
household products. Contact your state agency about ideas for collecting these mate-
rials.
Where Are the Regulations Published?
The Municipal Solid Waste Landfill Criteria can be found in the Code of Federal Regula-
tions, Title 40, Part 2 58.
Hazardous Waste Management
RCRA, as amended in 1984, regulates the disposal of all household, municipal, commer-
cial, and industrial waste, including hazardous waste. The main goals of RCRA are:
To protect people's health and the environment from the potential hazards of waste
disposal.
To reduce the amount of waste generated, including hazardous waste.
To conserve energy and natural resources.
To ensure that wastes are managed properly.
A hazardous waste is a waste that poses a potential danger to people's health and/or the
environment when improperly treated, stored, transported, disposed of, or otherwise
Appendix B: What Environmental Regulations Affect Your Community? 117
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managed. RCRA Subtitle C regulates hazardous waste from the moment the waste is
generated until its ultimate disposal.
There are three categories of hazardous waste generators under the RCRA program
requirements:
Large Quantity Generator—Facilities that generate more than 1,000 kilograms
(2,200 pounds) of any hazardous waste each month, or more than 1 kilogram (2.2
pounds) of any acute hazardous waste. Large quantity generators are subject to all
RCRA requirements.
I Small Quantity Generator—Facilities that generate between 100 and 1,000 kilograms
(220 to 2,200 pounds) of hazardous waste each month. Small quantity generators
generally may accumulate hazardous waste on site for up to 180 days, and may not
accumulate more than 6,000 kilograms on site at any one time.
I Conditionally Exempt Small Quantity Generators—Facilities that generate less
than 100 kilograms of any hazardous waste each month. These facilities are exempt
from most RCRA hazardous waste requirements. Conditionally exempt small quantity
generators, however, must identify waste to determine if itis hazardous; treat or dispose
of the waste in either a recycling or permitted hazardous waste facility; and not
accumulate more than 1,000 kilograms of hazardous waste at any given time.
= 1 barrel = about 55 gallons or 200 kilograms of hazardous waste
Does This Regulation Apply to My Community?
The requirements of RCRA Subtitle C apply to hazardous waste generators, transporters,
and storage, treatment, and disposal facilities. Some types of hazardous wastes might be
generated by businesses in your community or by your municipal facility operations
themselves. A waste is considered hazardous if it has been listed by EPA as a hazardous
waste or if the waste has any of four hazardous characteristics:
Ignitability—Wastes that are easily combustible or flammable, such as paints or
solvents.
I Corrosivity—Wastes that dissolve metals or other materials, or burn the skin. Exam-
ples are rust removers, acid or alkaline cleaning fluids, and battery acid.
Reactivity—Wastes that are unstable or undergo violent chemical reactions, such as
explosions, and/or release toxic fumes, gases, and vapors when mixed with water or
other materials.
Toxicity—Wastes that are harmful or fatal when eaten or absorbed. When toxic wastes
are disposed of on land, contaminated liquid can drain (leach) from the waste and pollute
118 Appendix B: What Environmental Regulations Affect Your Community?
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ground water. Toxicity is identified through a laboratory test called the Toxicity
Characteristic Leaching Procedure (TCLP).
EPA regulations require all waste generators to evaluate whether their wastes have any of
the four hazardous characteristics. Wastes that have any of these characteristics are subject
to Subtitle C hazardous waste regulations. In addition, some wastes are considered to be
"acutely hazardous."These are wastes thatEPAhas determined to be very dangerous, even
in small amounts, such as certain pesticides and wastes containing dioxins.
The following wastes are among those not included in the RCRA hazardous waste
regulations:
Domestic sewage.
I Irrigation return water or industrial wastewater effluent permitted under NPDES (see
the section on wastewater treatment).
Household hazardous wastes.
I Agricultural wastes generated by the growing or harvesting of crops or raising of
animals (including animal manures) that are returned to the soil as fertilizer.
Wastes from businesses that generate fewer than 100 kilograms (220 pounds) of
hazardous waste each month.
If you are not sure if a business, industry, or municipal facility in your community is
generating a hazardous waste or is subject to the RCRA hazardous waste regulations,
contact your state agency or the RCRA Hotline at 800-424-9346.
Where Are the Regulations Published?
The hazardous waste regulations can be found in the Code of Federal Regulations, Title 40,
Parts 260-272.
Underground Storage Tank Safety
There are several million underground storage tanks (USTs) in the United States that
contain petroleum or hazardous chemicals. As many as 20 percent of all USTs might now
be leaking, and many more are expected to leak in the future. Leaking USTs can cause
fires or explosions that threaten people's safety. They also can contaminate nearby ground
water and cause problems with drinking water quality.
Appendix B: What Environmental Regulations Affect Your Community? 119
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Congress responded to the problem of leaking USTs by adding Subtitle I to RCRA. The
goals of the UST regulations are to:
I Prevent leaks and spills.
Find, correct, and clean up leaks and spills.
I Make sure that owners and operators of USTs can pay for fixing the problems caused
by their leaks.
Does This Regulation Apply to My Community?
These regulations apply to you if you own or operate a UST storing either petroleum or
certain hazardous chemicals. A UST is one or any combination of tanks, including
underground piping connected to the tank, that has at least 10 percent of the volume
underground.
Some kinds of tanks are not covered by these regulations:
Farm and residential tanks holding 1,100 gallons or less of motor fuel used for
noncommercial purposes.
Tanks storing heating oil that is used on the premises where it is stored.
Tanks on or above the floor of underground areas, such a basements or tunnels, where
it is possible to physically inspect the tank for leaks.
Septic tanks and systems for collecting stormwater and wastewater.
Tanks holding 110 gallons or less.
Emergency spill and overfill tanks.
If you are unsure whether or not the UST regulations apply to you, contact your state
environmental agency or the RCRA Hotline at 800-424-9346.
What Are the Specific Requirements of RCRA Subtitle I?
RCRA Subtitle I regulates the installation, maintenance, monitoring, and closure of both
new and existing USTs. The regulations also give specific instructions for the proper way
to deal with leaks and spills, including corrective action. According to the regulations, new
USTs are those installed after December 22, 1988, and existing USTs are those installed
on or before December 22, 1988. All new USTs must comply with the regulations before
installation. Existing USTs will eventually need to comply with the same regulations as
new USTs. The deadlines for compliance, however, are spread out over time. The
requirements for petroleum and chemical USTs are very similar, although there are a few
special requirements for chemical USTs.
120 Appendix B: What Environmental Regulations Affect Your Community?
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Installation
Subtitle I requires that you:
Use qualified installers who follow industry codes.
Certify on a notification form (available from your state agency) that you have used a
qualified installer who can assure you that your UST has been installed correctly.
Corrosion Protection, Spill/Overfill Prevention, and Leak
Detection
The box on page 122 lists the regulations regarding corrosion protection, spill/overfill
prevention, and leak detection for new and existing USTs. Existing tanks must be equipped
with leak detection by December 1993 and must have corrosion protection and spill/over-
fill prevention by December 1998. All existing piping must comply with corrosion
prevention requirements by December 1998 and with leak detection requirements by
December 1993; however, spill/overfill prevention requirements do not apply to piping.
Leaks and Spills
There are several requirements for both reporting and correcting leaks and spills. In
general, here is what you should do when you have a leak or spill:
Stop the leak or contain the spill immediately.
Within 24 hours, notify your state agency of the leak or spill. Report all underground
leaks. Report petroleum spills and overfills of 25 gallons or more, or any that cause an
"oil slick" on nearby surface water. If you are not sure of the amount, report it.
I Identify and mitigate fire, explosion, and vapor hazards. Ask your local fire department
to test for explosive conditions and to help you decide how to deal with any poisonous
vapors or flammable liquids and how to go about cleaning up the leak or spill.
Contact professionals who might be able to help you determine the extent of contami-
nation, prepare a cleanup plan, and clean up the site.
Keep detailed records of the actions you have taken or plan to take:
— Report your progress to your state agency or regulatory authority no later than 20
days after the leak or spill.
— Report whether the leak has damaged or might damage the environment within 45
days of the leak or spill, including how you plan to remove leaked petroleum.
You must repair your UST system in accordance with a national code of practice, which
generally requires retesting of repaired cathodic protection within 6 months, replacement
of all damaged metal piping, and lifetime recordkeeping. Chemical leaks and spills have
the added requirements of also reporting the spill or overfill to the National Response
Center at 800-424-8802 or 202-267-2675 if they exceed "reportable quantities." You can
Appendix B: What Environmental Regulations Affect Your Community? 121
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Underground Storage Tank Requirements:
Corrosion Protection, Spill/Overfill Prevention, and Leak Detection
Corrosion Protection
New tanks (Three choices)
Coated and cathodically protected steel.
Fiberglass.
Steel tank clad with fiberglass.
Existing tanks (Four choices)
Same options as for new tanks.
Add cathodic protection system.
Interior lining.
Interior lining and cathodic protection.
New piping (Two choices)
Coated and cathodically protected steel.
Fiberglass.
Existing piping (Two choices)
Same options as for new piping.
Cathodically protected steel.
Spill/Overfill Prevention
All tanks
Catchment basins and one of the following:
— Automatic shutoff devices.
— Overfill alarms.
— Ball float valves.
Leak Detection
New tanks (Two choices)
Monthly monitoring.*
Monthly inventory control and tank tightness testing every 5 years
(only an option for 10 years after installation).
Existing tanks (Three choices)
Monthly monitoring.*
Monthly inventory control and annual tank tightness testing (only an
option until December 1998).
Monthly inventory control and tank tightness testing every 5 years
(only an option for 10 years after adding corrosion protection and
spill/overfill prevention or until December 1 998, whichever date is
later).1
New and existing pressurized piping
(Choice of one from each set)
One of the following:
Automatic flow restrictor.
Automatic shutoff device.
Continuous alarm system.
And one of the following:
Annual tightness testing.
• Monthly monitoring (except
automatic tank gauging).*
New and existing suction piping
(Three choices)
Monthly monitoring (except automatic tank gauging).*
Tightness testing every 3 years.
No requirements (if the system has the characteristics described in
the regulations).
Chemical USTs
Interstitial monitoring (monitoring between the layers of double-
walled tanks and pipes) and secondary containment.
* Monthly monitoring includes: automatic tank gauging, vapor monitoring in soil, interstitial monitoring (i.e., monitoring between the
layers of double-walled tanks and pipes), ground-water monitoring, statistical inventory reconciliation, and other approved methods.
Very small tanks may also be able to use manual tank gauging.
122 Appendix B: What Environmental Regulations Affect Your Community?
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get information about the "reportable quantities" by calling the RCRA Hotline at 800-
424-9346.
Closure
If you close your UST, you must follow the requirements for permanent closure. Notify
your state agency 30 days before you plan to close your UST. Your state agency will help
you decide how to meet all local requirements for closure. Although USTs can also be
closed temporarily, the requirements are difficult. Details of temporary closure require-
ments can be obtained from your state agency.
Reporting and Recordkeeping
As noted above, you will need to report to your state agency at the beginning and end of
your UST's operating life, and in the case of a leak or spill. You will also have to keep
records that can be provided to an inspector during an onsite visit that prove your facility
meets certain requirements. These records must be keptlong enough to showyour facility's
compliance status in four major areas:
Keep the following leak detection records:
— Last year's monitoring results and the most recent tightness test.
— Copies of performance claims provided by leak detection manufacturers.
— Records of recent maintenance, repair, and calibration of leak detection equipment
installed on site.
Keep records showing that the inspections of the corrosion protection system were
carried out by properly trained professionals.
Keep records showing that repairs and upgrades to the USTs were properly con-
ducted.
For at least 3 years after closing an UST, keep records of the site assessment results
required for permanent closure.
Check with your state agency about the particular recordkeeping requirements in your
area. The general rule of thumb for recordkeeping is: When in doubt, keep it.
Financial Responsibility
Owners and operators of USTs are required to show, through insurance coverage or other
acceptable financial mechanisms, that they can pay for the cost of cleanups and third-party
damages resulting from any leaks that might occur. The other acceptable mechanisms for
compliance include state assurance funds, letters of credit, surety bonds, a financial test of
self-insurance, guarantees, and trust funds. Four additional mechanisms are available for
Appendix B: What Environmental Regulations Affect Your Community? 123
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local government entities: bond tests, government guarantees, local government funds
(trust funds), and a local government financial test.
As of January 1994, 40 states had state assurance funds that can be used as partial or even
full mechanisms for compliance with the financial responsibility regulations. For addi-
tional information about these funds, call your state regulatory agency.
The compliance deadline for petroleum marketers and nonmarketers was December 31,
1993, and the deadline for local government entities was February 18, 1994.
Contact the RCRA Hotline (800-424-9346) for more information.
Where Are the Regulations Published?
The Underground Storage Tank regulations are contained in the Code of Federal Regula-
tions, Title 40, Part 280.
Emergency Response to Hazardous Substance Spills
In 1986, Congress passed the Emergency Planning and Community Right-to-Know
Act (EPCRA, also known as SARA Title III) to help U.S. communities deal safely and
effectively with the many hazardous substances that are used throughout our society. The
law has two main purposes:
To encourage and support emergency planning for responding to chemical accidents.
To provide local governments and the public with information about possible chemical
hazards in their communities.
EPCRA requires facilities to notify communities and states immediately if there is a
chemical spill. In addition, the act requires all facilities—large or small, manufacturing or
nonmanufacturing, industrial or government—to report information about the amounts,
location, and potential effects of certain hazardous chemicals present above the threshold
levels specified by EPA.
Does This Regulation Apply to My Community?
Yes, every community in the United States must be part of a comprehensive plan for
responding to chemical emergencies. The governor of your state has appointed a State
124 Appendix B: What Environmental Regulations Affect Your Community?
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Emergency Response Commission (SERC). Each SERC, in turn, has divided its state
into local emergency planning districts and appointed a Local Emergency Planning
Committee (LEPC) for each district. At a minimum, each committee must include
representatives of state and local government; law enforcement officials; firefighters; first
aid, health, hospital, environmental, and transportation workers; community groups;
broadcast and print media; and owners and operators of industrial plants and businesses.
The LEPC is responsible for:
Developing a plan to prepare for and respond to chemical emergencies in its district
and reviewing the plan annually.
Receiving emergency release and hazardous chemical inventory information from local
facilities and making this information available to the public upon request.
Visiting facilities in the district to find out what they are doing to reduce hazards and
prepare for accidents.
Serving as an informal source of information and discussion about hazardous sub-
stances, emergency planning, and health and environmental risks for the community.
What Chemicals Must Be Reported Under the Act?
Over 1,000 chemicals are considered to be hazardous or extremely hazardous sub-
stances that could represent an immediate danger to the community if they are spilled or
released into the environment. Releases of these substances must be reported immediately
to the SERC and LEPC. Thousands of other chemicals are considered to be hazardous
or toxic chemicals that represent a significant physical or health hazard when present in
critical amounts. Facilities need to inventory these chemicals and submit specific informa-
tion about these materials to the SERCs, LEPCs, and local fire departments (the fire
department, paid or volunteer, that serves your community). For more information on
how to comply with these regulations, contact your SERC or LEPC.
What Action Should My Community Be Taking?
As a local official, you are responsible for making sure that all public facilities in your
community (such as hospitals, schools, wastewater or drinking water treatment plants)
comply with the act by immediately reporting any hazardous or extremely hazardous
substances that they release or spill to the SERC and LEPC.
In addition, you should take the following steps to ensure that your community is prepared
to respond to chemical accidents:
Learn who represents public institutions (hospitals, schools, state and local govern-
ment) on the LEPC, and contact that person to find out the information that affects
your community.
Appendix B: What Environmental Regulations Affect Your Community? 125
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Make sure that the local fire department is familiar with the emergency response plan
for your community and that the LEPC is satisfied with its preparedness.
Use the information collected by the SERC and LEPC to find out about hazardous
chemicals in your community to help identify any potential risks to people's health and
the environment.
Encourage public facilities in the community to voluntarily report inventories of the
hazardous chemicals present at these facilities. Even though public facilities are not
required by law to provide this information, this effort would ensure that the local
responders (fire departments, law enforcement officials, etc.) would be better informed
of the hazards present in the community. This information could also be incorporated
into the local community planning efforts for emergencies.
Where Are the Regulations Published?
The regulations implementing EPCRA can be found in the Code of Federal Regulations,
Title 40, Parts 300, 350, 370, 372.
Asbestos-Containing Materials in Buildings
The Asbestos Hazard Emergency Response Act (AHERA) of 1986 requires schools
to inspect buildings for materials containing asbestos and to develop a plan to properly
manage asbestos-containing materials in all school buildings. The management plans were
submitted to state agencies in May 1989, and school districts and individual private schools
began implementing their plans in July 1989. School districts and individual private schools
should update their management plans to reflect any actions that they have taken.
Under the National Emission Standards for Hazardous Air Pollutants (NESHAP),
all public buildings must be inspected for asbestos-containing materials before any reno-
vation or demolition occurs. The owner must notify the appropriate regulatory agency for
all demolition activities, even if asbestos is not found. If asbestos is found in a building to
be demolished, NESHAP establishes certain work practices, waste disposal methods, and
recordkeeping requirements that must be followed. For renovations, the owner must only
notify the regulatory agency and meet work practice, waste disposal, and recordkeeping
requirements if the quantities of asbestos-containing materials exceed 160 square feet, 260
linear feet, or 35 cubic feet. In addition, the 1990 amendments to AHERA mandate that
if a building owner renovates or demolishes a building regulated under NESHAP, people
accredited under AHERA must be used to inspect, design, and conduct all asbestos-related
activities.
126 Appendix B: What Environmental Regulations Affect Your Community?
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Finally, under the Asbestos Abatement Projects Worker Protection Final Rule
(WPR), employers of public employees that are handling friable asbestos-containing
materials must comply with provisions to protect their employees from exposure to
asbestos fibers. Employers must monitor the air, use specific engineering controls and work
practices, provide medical surveillance and training to employees, and notify the EPA
regional asbestos coordinator of their activities.
Do the Asbestos Regulations Apply to My Community?
Every local public school system or nonprofit private school (K-12) must designate and
train one person to oversee asbestos-related activities, including:
Conducting inspections in every school building for asbestos-containing materials.
Reinspections are required every 3 years.
Preparing and submitting management plans to the state agency. A management plan
includes maintenance, repair, encapsulation, enclosure, and removal, if absolutely
necessary. The plan should include a time frame for implementation of recommended
actions.
Ensuring that only properly authorized people conduct inspections, develop the asbes-
tos management plan, and design and conduct any asbestos-abatement actions.
Informing custodial and maintenance workers about the location of asbestos and
posting warning labels.
Providing appropriate training for custodial and maintenance staff.
I Notifying parents, teachers, and other school employees about the asbestos inspection
and the fact that they have the right to review the school's management plans.
Keeping records of all asbestos-related activities in the plan and making them available
for public review.
All small communities involved with the renovation or demolition of buildings must
comply with NESFEAP and AHERA accreditation requirements. In addition, if public
employees are used to handle friable asbestos-containing materials, the community must
also follow the WPR.
What Action Should My Community Be Taking?
As a local official, you should ensure that:
Any school district within your community has complied with AHERA.
You have the names of people who are responsible for all asbestos-related activities in
the district and trained and certified asbestos inspectors and removers in the area.
Appendix B: What Environmental Regulations Affect Your Community? 127
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The proper regulatory agency is notified before the demolition of any buildings.
Public employers are aware of their responsibilities under the WPR and have notified
the regional asbestos coordinator.
Where Are the Regulations Published?
The Asbestos-Containing Materials in Schools Rules and the Worker Protection Rule are
in the Code of Federal Regulations, Title 40, Part 763. The NESHAP rules for asbestos are
in Title 40, Part 61.
Radon Gas in Homes and Other Buildings
Radon is a radioactive gas that comes from the natural breakdown (radioactive decay) of
uranium in soil, rocks, and water. The U.S. Surgeon General has warned that radon is the
second leading cause of lung cancer in the United States today. Radon moves up through
the ground and enters homes and other buildings through the basement or foundation. In
almost 1 out of every 15 homes in the United States, indoor radon levels are estimated to
exceed levels recommended by EPA to protect people's health.
In 1988, Congress enacted the Indoor Radon Abatement Act (IRAA) with the goal of
reducing indoor radon levels to those found in outside air. In response to IRAA, EPA has:
Published the Citizen's Guide to Radon and other documents describing suggested
procedures for testing homes, schools, and buildings.
Completed national surveys on radon exposure in homes and schools.
I Drafted suggested standards and techniques for controlling radon in new buildings. A
draft of these guidelines will be available for public comment soon.
Set up programs to train radon professionals.
IRAA also provided funds for state governments and Native American tribes to help local
governments and communities encourage residents to test for and reduce radon levels.
Does the Indoor Radon Abatement Act Apply to My Community?
Your community might have homes, day care centers, schools, or commercial buildings
with indoor radon levels higher than the federal guidelines. Most radon-related policies,
128 Appendix B: What Environmental Regulations Affect Your Community?
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Predicted Average Indoor Screening Levels For Radon in the United States (by County)
indoor
Zorw i counties have a p«did:»d average
*;!»ennj level ol mor* lhan 4 pCii
Zone 2 courrli« hive a prsdcted avufage indocr
screeomg Wwl oC betweefi 2 and 4 pCVL
Zon* 3 canoes ftaw a prwlcled awsrage \nHoot
screening lave* or less lha
awrage I
n 2 pQ/L
however, are not federal laws. EPA, state, and local governments have focused their
energies on educating the public about the health risk of radon and encouraging voluntary
testing of homes and buildings. Some states have developed radon regulations, however,
including training and certification of radon experts and required testing of all public
schools.
What Action Should My Community Be Taking?
To protect your community from the harmful effects of indoor radon, you should contact
your state radon office. Ask them to give you public information about radon, including:
The Citizen's Guide to Radon.
Appendix B: What Environmental Regulations Affect Your Community? 129
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Lists of EPA- or state-certified radon experts who can test homes and other buildings
for radon levels.
Information on state radon regulations.
Use this information to educate your community about the risks of radon and encourage
voluntary testing. Make the list of EPA- or state-certified radon inspectors available for
anyone in your community who would like to test for radon.
ollution
The Clean Air Act Amendments of 1990 give EPA the authority to set national outside
(ambient) air quality standards to protect people's health and the environment from air
pollutants. Most air pollution comes from stationary sources (e.g., factories, power
plants, and smelters) or from mobile sources (e.g., cars, buses, planes, trucks, and trains).
Do the Clean Air Act Amendments Apply to My Community?
Most provisions of the Clean Air Act Amendments will not affect very small communities.
Some communities, however, might have wood burning or particulate problems that will
need to be solved. In addition, the act contains several new requirements that are of
particular concern to small businesses, including:
I Lower emissions from small industrial and service companies that contribute to
ground-level ozone pollution (smog).
Reduce automotive emissions by establishing tailpipe inspections and maintenance
programs for motor vehicles, and by expanding the development of cleaner automotive
fuels.
Sharply curb emissions of 189 toxic air pollutants from hundreds of industries.
Prevent or minimize the risks from the accidental release of very hazardous chemicals
into the air.
Recycle and eliminate the production and use of products and substances that destroy
the earth's upper ozone layer.
Require many sources affected by the Act to have a permit listing their air pollution
control methods.
This is a general list of the typical kinds of small businesses that will be affected by one or
more of the air pollution control programs under the 1990 Clean Air Act Amendments:
130 Appendix B: What Environmental Regulations Affect Your Community?
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Agricultural chemical applicators Asphalt manufacturers/applicators
Auto body shops • Bakeries
Distilleries I Dry cleaners
Foundries Furniture manufacturers and repairers
Gasoline service stations Hospitals
Laboratories • Lawnmower repair shops
• Lumber mills • Metal finishers
Newspapers Pest control operators
Photofinishing laboratories Printing shops
• Refrigerator/air conditioning services Tar paving applicators
Textile mills • Wood finishers
All small businesses should consult their state pollution control agency for more details
about the specific controls required in their area.
What Action Should My Community Be Taking?
Before taking any action on air pollution issues, contact your state air pollution agency or
county health department and your regional EPA small community coordinator for
guidance. If problems with air pollution exist, meet with your state air pollution agency or
regional EPA office to discuss problems and possible solutions.
Where Are the Regulations Published?
The regulations implementing the Clean Air Act Amendments can be found in the Code
of Federal Regulations, Title 40, Parts 1 to 99.
Floodplain Zoning
Floodplain zoning is part of the federal government's national flood insurance program.
Flood insurance is not available through private insurance companies. If a community
wishes to be part of the national flood insurance program, it is required to follow certain
Appendix B: What Environmental Regulations Affect Your Community? 131
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building and zoning requirements set by the Federal Emergency Management Agency
(FEMA). FEMA is responsible for:
I Publishing floodplain maps.
I Preparing minimum standards for development within floodplain zones, including
building codes and zoning ordinances.
I Requiring communities that apply for national flood insurance to adopt these standards.
FEMA has prepared flood insurance maps for every community in the country. These
maps outline the flood hazard areas in each community. To order a map of the floodplains
in your area, call the Flood Map Distribution Center at 800-333-1363.
Does Floodplain Zoning Affect My Community?
Floodplain zoning is not a federal regulation. If your community wants to be covered by
the national flood insurance program, however, it must meet the minimum standards set
by FEMA's building codes and zoning ordinances to qualify.
What Action Should My Community Be Taking?
As a local official, you need to decide whether your community is at risk for flood damage
and if your community could benefit from being a part of the national flood insurance
program. You should:
I Call FEMA's Flood Map Distribution Center to get a map of flood hazard areas in your
community.
I Contact your state environmental agency or state department of natural resources to
discuss floodplain zoning requirements for your community.
I If your community is already part of the national flood insurance program, make sure
that it meets FEMA zoning requirements.
132 Appendix B: What Environmental Regulations Affect Your Community?
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Appendix C:
Assessing Risks from Environmental
Problems in Your Community
This appendix presents information about how to assess potential risks to public health,
the environment, and the quality of life in your community. In addition, it lists states
and cities that have undertaken or are planning projects using "comparative risk" to
help set priorities in environmental decision-making. Information from one of these
projects in your state or a nearby city might be valuable in your efforts to identify
"high-risk" problems in your community.
Much of the information in this appendix is adapted from Richard Minard and Ken Jones,
Comparative Risk Lab Manual, Northeast Center for Comparative Risk.
Questions to Help You Assess Risks to Health,
Ecosystems, and Quality of Life
Answers to the following questions will help you assess risks to health, ecosystems, and
quality of life in your community:
What harmful effects can the substance or activity cause to public health, the environ-
ment, or the quality of life? Examples include cancer, gastrointestinal illnesses, or a
decline in the number offish or birds in the area.
Are the effects permanent or reversible?
What are the effects at different levels of exposure?
133
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How much of the substance do people (or ecosystems) in your planning area come in
contact with? How many people are affected (or how widespread an area)? Information
for answering these question can come from many different sources, such as results of
environmental monitoring (e.g., for drinking water or surface water quality); discharge
limits set by permits; reports made by businesses under the Title III "Right to Know"
law about how much of certain substances they discharge to air, water, and land; and
mathematical models that estimate the distribution of hazardous substances in air and
water.
Is there evidence of harm to people, ecosystems, or quality of life in your planning area?
For example, do data about human health and natural resources in your community
point to any areas of concern (such as a higher rate of certain diseases than the national
average)? What pollutants are known to contribute to these conditions? Federal, state,
and county agencies have useful data on these issues.
Assessing Human Health Risks in Your Community
Chemicals and biological contaminants in the environment can cause a variety of health
problems. Some of these health effects are temporary or easily treated, such as headaches,
nausea, diarrhea, or rashes. Other health effects can be permanent and difficult or
impossible to treat, such as learning disabilities, chronic pain, or disabling heart or
respiratory problems. Some stressors* can cause cancer.
Individual health risk depends on two variables, hazard and exposure, as shown by the
following equation:
Risk = Hazard x Exposure
Hazard—Toxicity, a measure of the stressor's potency or ability to cause health
problems.
Exposure—How much of the stressor individuals come in contact with, and over
what period of time.
Many chemicals and organisms in the home or outside environment pose little or no risk
because they are nontoxic: they have no effect on biological processes. Other stressors are
very hazardous but may pose little health risk if individuals are not exposed to them.
In assessing the risk of a chemical, scientists examine all the available scientific data for
that chemical, including data from animal studies, human data (when available), and results
of tests with isolated human cells or microorganisms. They use this information to estimate
whether and to what degree the chemical poses a human health risk.
*The term "stressor" refers to many different types of pollution, including any material, organism, radiation, temperature change, or activity that puts a
stress on human health, the environment, or quality of life.
134 Appendix C: Assessing Risks from Environmental Problems in Your Community
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For noncancer effects, scientists usually assume there is a threshold of exposure. Below
this threshold level, the harmful effect will not occur, and above it, the exposed individual
is at risk. Risk information for noncancer effects is usually expressed as an estimate of daily
exposure of a chemical that is likely to have no significant harmful effects during an
individual's lifetime (estimated at 70 years).
For cancer, scientists assume that any dose of the substance poses some degree of risk, and
that risk increases as exposure increases. Risk information for cancer is usually expressed
as a mathematical factor that relates the level of exposure to the number of additional cases
of cancer that are expected to be caused by that exposure.
To get an idea of the potential health risk of a chemical in your community, you'll need to
know (1) the level of actual exposure to that chemical in your community, and (2) risk
information on the degree of hazard that particular chemical poses. Local emergency
response coordinators should have complete listings of hazardous chemicals in the area,
along with material safety data sheets with information on toxic and hazardous charac-
teristics of those chemicals. A public health expert or toxicologist can help you obtain
available risk information, assess local risks by comparing your community's exposure with
the chemical's estimated hazard level, and provide perspective that will be useful in
constructively interpreting the risk information for your community. To locate this
assistance, start by contacting your state agency or local college or university.
Assessing Ecological Risks in Your Community
Ecological risks are threats to ecosystems themselves: the health and diversity of plants,
animals, and natural communities.
When considering ecological damage, four measures can be used. The measures help
distinguish between localized problems and those that threaten much larger areas, and
between problems that cause short-term damage and those that cause permanent damage.
The measures also focus on whole natural communities rather than individual species. The
four measures are:
Structure—The diversity and interrelationships of species inhabiting or using an
ecosystem.
Function—Ecological processes, such as the conversion of energy and nutrients into
plants and animals, decomposition, and movement of water.
Recovery time—How long it takes an ecosystem to recover from stress or damage
after the stressor is removed.
Space or scale—The size of the area affected by an environmental stressor.
Appendix C: Assessing Risks from Environmental Problems in Your Community 135
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Below are three examples of how a community might consider the ecological risks of
human activities:
EXAMPLE: A Chemical Spill
A chemical spill in a small river might kill many of the fish and insects living downstream.
For a time, the complex balance among fish, insects, aquatic plants, birds, and mammals
may be disrupted, leaving only a few pollution-tolerant species alive. This sharp reduction
in the river's diversity would be a fairly severe structural change, but it might have little
impact on some of the river's basic ecological functions, which include transporting water
and breaking down biological debris.
The polluted stream may recover quickly. Flowing water will immediately dilute the chemical
spill and push it downstream. When the water chemistry returns to normal, plants and animals
from upstream will probably move back into their own niches, replicating the system's original
structure. If the same chemical had spilled into a pond, the recovery time might be much
longer because the chemical might persist in the standing water or bottom sediment, and
because some lake species are less mobile than river species. If the spill affects a drinking water
supply, it will pose health as well as ecological risks.
EXAMPLE: Filling a Wetland
Filling a substantial wetland to create developable land would cause both structural and
functional changes. The diverse community that thrives in wetland soils would be replaced
by a much simpler system. The area also would lose its ability to absorb pollutants from
flood water in a storm.
A drained and filled wetland will likely never recover, even if the fill were removed. Most
ecologists agree that wetlands soils and their connections with ground-water systems are
so complex that they are extremely difficult to repair or recreate.
EXAMPLE: Building a New House
The ecological impact of building a new house depends on where it is built. If it is built in
the woods at the edge of a forest, the house may have a tiny local impact: a few trees may
be lost, but the health of the forest community is un diminished. If the same house consumes
a deer-wintering yard, however, it may affect the deer population in the whole region. If
the construction were to destroy a unique habitat, it would have a wider impact.
Natural environmental stressors, such as droughts, floods, forest fires, or even beavers,
also can have dramatic effects on ecosystems. Today's ecosystems have evolved in response
to natural and human-made stressors.
136 Appendix C: Assessing Risks from Environmental Problems in Your Community
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Assessing Risks to Quality of Life in Your Community
Environmental problems can degrade a wide range of resources, activities, or intangible
values that are important to people. The costs may be direct or indirect, monetary or
emotional. These risks come under the broad heading of "Quality of Life."
One way to look at quality-of-life risks is to consider how environmental problems threaten
the following seven broadly held values:
Aesthetics Negative impacts include:
Reduced visibility.
Noise, odors, dust, and other unpleasant sensations (e.g., water weeds or turbidity in a
lake, grime on buildings).
Economic Negative impacts include:
Well-Being
I Higher out-of-pocket expenses or taxes to fix, replace, or buy support services (such as
higher waste disposal fees, cost of replacing a well, higher housing costs) without any
improvements in those services.
I Net loss of jobs, higher health care costs, or lost productivity.
Fairness Negative impacts include:
Unequal distribution of costs and benefits (costs and benefits may be related to
economics, health, aesthetics, etc.).
Negative impacts include:
Generations
Shifting the costs (economic costs, health risks, ecological damage, etc.) of today's
activities to people not yet able to vote or not yet born.
Peace of Mind Negative impacts include:
Feeling threatened by potentially risky structures or facilities (such as hazardous waste
sites).
Recreation Negative impacts include:
Loss of access to recreation lands (public and private).
Degraded quality of recreation experience (spoiled wilderness, fished-out streams,
dammed whitewater, etc.).
Appendix C: Assessing Risks from Environmental Problems in Your Community 137
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Sense of Negative impacts include:
Community
Development that changes the appearance and characteristics of a town.
Loss of mutual respect, cooperative spirit, or willingness to solve problems together.
Individual liberty exercised at the expense of the common good.
Community authority exercised at the expense of individuals.
These seven values are intangible and therefore are extremely difficult to measure. However, they focus attention
on issues of importance to whole communities (or large parts of communities), and so are useful tools for
understanding and comparing risks.
Status of Comparative Risk Projects:
States, Cities, and Tribes
Projects with California: Dan Liebermann, Project Administrator, at 510-849-5211; and Michael
Completed DiBartolomeis, Office of Health Hazard Risk Assessment, 2151 Berkeley Way, Annex 11,
Rankings Berkeley, CA 94704; 510-540-2665.
Colorado: Gerard Bulanowski, Colorado Department of Health, Office of Environment
B-2, 4300 Cherry Creek Drive South, Denver, CO 80222-1530; 303-692-3004.
Guam: Mike Hammet, Center for Development Studies, Social Science Research Insti-
tute, Porteus Hall 719, University of Hawaii, Honolulu, HI 96822; 808-956-7469.
Louisiana: Chuck Killebrew, Office of the Secretary, Department of Environmental
Quality, P.O. Box 82263, Baton Rouge, LA 70884; 504-765-2726.
Michigan: Keith Harrison, Environmental Administration Division, Department of
Management and Budget, P.O. Box 30026, Lansing, MI 48909; 517-335-3666.
Seattle, WA: Steven Nicholas, Room 200, Seattle Municipal Building, 600 Fourth
Avenue, Seattle, WA 98104; 206-684-8377.
Vermont: Doug Kievit-Kylar, Pollution Prevention Division, West Office Building,
Agency of Natural Resources, 103 South Main Street, Waterbury, VT 05676; 802-241-
3888.
Washington: Dee Peace Ragsdale, Dept. of Ecology, P.O. Box 47600, Olympia, WA
98504-7600; 206-407-6986.
Wisconsin Tribes: John Haugland, U.S. EPA Region 5, Planning and Management
Division, 77 West Jackson Boulevard (ME-19J), Chicago, IL 60604-3507; 312-886-9853.
138 Appendix C: Assessing Risks from Environmental Problems in Your Community
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Projects Under Alabama: Marilyn Elliott, Alabama Department of Environmental Management, 1751
Way Congressman W.L. Dickenson Drive, Montgomery, AL 36130; 205-271-7715.
Arizona: Pat Mariella, Department of Environmental Quality, 3033 North Central
Avenue, Phoenix, AZ 85012; 602-207-4603.
Florida: Nancy Muller and Gil Bergquist, Florida Center for Public Management, Florida
State University, B-149, Tallahassee, FL 32306-4025; 904-922-8042.
Atlanta, GA: Eric Wilson, Atlanta Department of Planning and Development, 5 5 Trinity
Avenue SW, Suite 1450, Atlanta, GA 30335-0308; 404-330-6348.
Hawaii: Patrick Felling, Department of Health, Environmental Planning, 500 Ala Moana
Boulevard, Suite 250, Honolulu, HI 96813; 808-586-4337.
Illinois: Bob Liebermann, Office of Research & Planning, Illinois Department of Energy
and Natural Resources, 325 West Adams, Springfield, IL 62704; 217-785-0124.
Jackson, MS: Scott McDonald, Public Policy and Administration Program, Jackson State
University, 3825 Ridgewood Road, Jackson, MS 39211; 601-982-6405.
Kentucky: Karen Armstrong Cummings, Kentucky Natural Resources Environmental
Protection Cabinet, 4th Floor, Capital Plaza Tower, Frankfort, KY 40601; 502-564-3 350.
Maine: Cindy Bertocci, Maine Department of Environmental Protection, State House
Station 17, Augusta, ME 04333; 207-287-7842.
Maryland: Matt Thayer, Maryland Department of the Environment, 2500 Broening
Highway, Baltimore, MD 21224; 410-631-3114.
Ohio: Michelle Morrone, Ohio Environmental Protection Agency, 1800 Watermark
Drive, Columbus, OH 43266-0149; 614-644-3638.
Greater Cleveland (OH) Area: Norman Robbins, Department of Neurosciences,
School of Medicine, Case Western Reserve University, 10900 Euclid Avenue, Cleveland,
OH 44106-4975; 216-368-2194.
Columbus, OH: Richard Hicks, Columbus Health Department, 181 Washington Boule-
vard, Columbus, OH 43215-4096; 614-645-6189.
Oregon: Dick Nichols, Environmental Partnership for Oregon Communities, 2020 SW
4th, Suite 400, Portland, OR 97201-4987; 503-229-5323.
Texas: Wendy Gordon, Texas Water Commission, P.O. Box 13087, Austin, TX 78711-
3087;512-463-8448.
Houston, TX: John D. Wilson, Houston Advanced Research Center, Center for Global
Studies, 4800 Research Forest Drive, The Woodlands, TX 77381; 713-363-7913.
Utah: Bruce Slater, Utah Department of Environmental Quality, P.O. Box 144810, Salt
Lake City, UT 84114-4810; 801-536-4480.
Charlottesville Area, VA: Mike Collins, Thomas Jefferson Planning District, 413 East
Market Street, Suite 102, Charlottesville, VA 22901; 804-972-1720.
Appendix C: Assessing Risks from Environmental Problems in Your Community 139
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Elizabeth River, VA: Marjorie Mayfield, Elizabeth River Project, 100 West Plume Street,
Suite 220, Norfolk, VA 23510; 804-625-3648.
Western Tribes: Mike Frost, Southern Ute Tribe, Box 737, Ignacio, CO 81137; 303-563-
0135.
Projects in the Alaska: James Powell, Division of Environmental Quality, 410 Willoughby Avenue, Suite
Planning Stages 105, Juneau, AK 99801-1795; 907-465-5260.
Arkansas: Dick Cassat, Department of Pollution Control & Ecology, P.O. Box 8913, Little
Rock, AR 72219-8913; 501-570-2131.
Minnesota: Paul Schmiechen, Minnesota Pollution Control Agency, 520 Lafayette Road
North, St. Paul,MN 55155; 612-296-7795.
Mississippi: Sam Mabry, Chief, Hazardous Waste Division, Mississippi Department of
Environmental Quality, P.O. Box 10385, Jackson, MS 39289-0385; 601-961-5545.
Missouri: David Bedan, Missouri Department of Natural Resources, P.O. Box 176,
Jefferson City, MO 65102; 314-751-4533.
New Hampshire: Kate Hartnett, Water Supply and Pollution Control Division, New
Hampshire Department of Environmental Services, P.O. Box 95,6HazenDrive, Concord,
NH 03301; 603-271-2989.
New Jersey: Martin Rosen, Division of Science and Research, Department of Environ-
mental Protection and Energy, CN 409, Trenton, NJ 08625-0409; 609-984-5312.
New York: Mary Werner, Pollution Prevention Unit, New York State Department of
Environmental Conservation, 50 Wolf Road, Albany, NY 12233; 518-457-2480.
North Dakota: Teri Lunde, North Dakota Department of Health and Consolidated
Laboratories, P.O. Box 5520, Bismark, ND 58502-5520; 701-221-5150.
Hamilton County (Cincinnati), OH: Walter S. Handy, Jr., Cincinnati Department of
Health, Community Services Division, 3101 Burnet Avenue, Cincinnati, OH 45229;
513-357-7271.
Allegheny County, PA: David Piposzar, Allegheny County Health Department, 3333
Forbes Avenue, Pittsburgh, PA 15213; 412-578-8030.
Tennessee: Angie Pitcock, Tennessee Department of Environment and Conservation,
Division of Pollution Prevention and Environmental Awareness, 401 Church Street, 14th
Floor, Nashville, TN 37243-1551; 615-532-0736.
Wisconsin: Tim Mulholland, Bureau of Environmental Analysis and Review, Department
of Natural Resources, 101 South Webster Street, Madison, WI 53707-7921; 608-266-
0061.
140 Appendix C: Assessing Risks from Environmental Problems in Your Community
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Comparative Risk Projects: July/August 1994
Seattle
* Western Tribes
* Wisconsin Tribes
* Charlottesville
* Elizabeth River
Implementing Under Way Planning Uncommitted
Appendix C: Assessing Risks from Environmental Problems in Your Community 141
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Appei
Where To Turn
for \
This guide provides general information about environmental issues facing your
community and offers suggestions for dealing with many of these issues. After reading
the guide, you will still have questions about what your community can and should
do. In addition, you will need technical help to accomplish many of the things that
this guide suggests. This chapter tells you about some places and resources where you can
find more help. These listings are up-to-date as of mid-1994.
U.S. Environmental Protection Agency
Regional Small Community Contacts
EPA's small community contacts are designated by the Agency to provide assistance to
small communities. They will provide assistance directly or refer you to others within their
offices who are best suited to provide the help you need.
EPA Region 1
• JFK Federal Building, Room 2203
Boston, MA 02203
617-565-3412
Connecticut, Massachusetts, Maine, Neiv
Hampshire, Rhode Island, Vermont
EPA Region 2
26 Federal Plaza
New York, NY 10278
212-264-7834
New Jersey, New York, Puerto Rico, Virgin
Islands
EPA Region 3
841 Chestnut Street
Philadelphia, PA 19107
215-597-9072
Delaware, Maryland,
Pennsylvania, Virginia, West Virginia,
District of Columbia
EPA Region 4
345 Courtland Street, NE
Atlanta, GA 30365
404-347-7109
Alabama, Florida, Georgia, Kentucky, Mississippi,
North Carolina, South Carolina, Tennessee
143
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EPA Region 5
77 West Jackson Boulevard
Chicago, IL 60604
312-353-6218
Illinois, Indiana, Ohio, Michigan,
Minnesota, Wisconsin
EPA Region 6
1445 Ross Avenue, 12th Floor, Suite 200
Dallas, TX 75202
214-655-2203
Arkansas, Louisiana, New Mexico, Oklahoma,
Texas
EPA Region 7
726 Minnesota Avenue
Kansas City, KS 66101
913-551-7768
Iowa, Kansas, Missouri, Nebraska
EPA Region 9
215 Fremont Street
San Francisco, CA 94105
415-744-1568
Arizona, California, Hawaii, Nevada,
American Samoa, Guam, Trust Territories of
the Pacific
EPA Region 8
One Denver Place
999 18th Street, Suite 500
Denver, CO 80202
303-294-7009
Colorado, Montana, North Dakota,
South Dakota, Utah, Wyoming
EPA Region 10
1200 Sixth Avenue
Seattle, WA 98101
206-553-1138
Alaska, Idaho, Oregon, Washington
Other Organizations
American Petroleum Institute
1220 L Street, NW
Washington, DC 20005
202-682-8000
Provides information and technical assis-
tance to communities on how to set up used
oil collection programs and encourage used
oil recycling.
USDA Extension Service
United States Department of Agriculture
14th & Independence Avenue SW
Room 3 547 S
Washington, DC 20250-0992
202-720-0987 (or see your local directory
for your local or county extension agent)
Provides education in wastewater and other
environmental subjects for local officials
and residents.
International City/County
Management Association
777 North Capitol Street, NE, Suite 500
Washington, DC 20002
202-289-4262
Provides information and training for local
governments on a variety of issues. Sets up
peer matches for people to learn from one
another.
144 Appendix D: Where To Turn for Help
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Northeast Center for Comparative Risk
Vermont Law School
P.O. Box 96
Chelsea Street
South Royalton, VT 05068
802-763-8303
or
Western Center for Comparative Risk
5398 Manhattan Circle
Boulder, CO 80303
202-494-6393
Work with EPA to help states and cities use
comparative risk. Can provide small com-
munities with publications on comparing
environmental risks.
National Association of Towns and
Townships
1522 K Street, NW
Washington, DC 20005
202-737-5200
Offers educational services, technical assis-
tance programs, and public policy support
to local governments.
National Environmental Training Center
West Virginia University
P.O. Box 6064
Morgantown, WV 2 65 06
800-624-8301
Develops training materials on water, waste-
water, and solid waste issues.
National Recycling Coalition
1101 30th Street, NW
Suite 305
Washington, DC 20007
202-625-6406
Answers requests for information on recy-
cling; maintains lists of state recycling asso-
ciations and market development contacts.
National Rural Water Association
2715 M Street, NW
Suite 300
Washington, DC 20007
202-333-8830
Provides training and technical assistance to
small water and wastewater systems. Con-
tact the national NRWA office to find out
about the Rural Water Association in your
state.
Rural Community Assistance
Program
602 South King Street
Suite 402
Leesburg,VA 22075
703-771-8636
A national network of nonprofit organiza-
tions assisting rural and small communities
with drinking water, wastewater, and solid
waste management.
Rural Development Administration
United States Department of
Agriculture
14th and Independence Avenue, NW
Washington, DC 20250
202-720-9589
Provides loans for rural water and wastewa-
ter systems and communities with popula-
tions less than 10,000.
Small Towns Environment Program
The Rensselaerville Institute
Rensselaerville, NY 12147
518-797-3783
Helps small towns solve water and wastewa-
ter problems. Provides tools for local ac-
tion, self-help approaches to design and
construction, nonbureaucratic low-interest
loans, and technical support.
Appendix D: Where To Turn for Help 145
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Solid Waste Association of North
America
P.O. Box 7219
Silver Spring, MD 20907
800-677-9424
Works to improve solid waste management
services to the public and industry via train-
ing, education, technical assistance, and
technology transfer. Also maintains infor-
mation on local government issues as they
relate to solid and hazardous waste manage-
ment.
United States Department
of Housing and Urban
Development
451 7th Street SW
Washington, DC 20410
202-708-2690
Provides grants to drinking water treatment
utilities through the Community Develop-
ment Block Grant Program.
Technical Support Centers and Hotlines
Control Technology Center (CTC)
Radiation Hotline
919-541-0800
Provides technical support and information
on air pollution emissions and control tech-
nology.
National Radon Hotline
800-767-7236
Hotline callers receive a brochure on radon
health effects and home testing.
Emissions Measurement Technical
Information Center
919-541-1060
Provides information on air emissions test-
ing methods and federal testing and moni-
toring requirements.
Hazardous and
Solid Waste
Solid Waste Assistance
Program
800-677-9424
Provides information on all aspects of solid
waste management.
Hazardous Waste
Ombudsman Program
800-262-7937 (202-260-9361 for District
of Columbia callers)
Assists the public and regulated communi-
ties in resolving problems concerning any
program or requirements under EPA's haz-
ardous waste program.
National Response Center
800-424-8802
Receives notification of oil, hazardous
chemical, biological, and radiological
releases, and passes them on to a federal
On-Scene Coordinator, who coordinates
cleanup efforts.
Resource Conservation and Recovery
Act (RCRA)/Superfund/Emergency
Planning and Community Right-to-
Know Act (EPCRA) Hotline
800-424-9346
800-535-0202
Provides general assistance and information
on solid and hazardous waste management
and on EPCPvA.
146 Appendix D: Where To Turn for Help
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Pesticides and
Toxics
Asbestos Ombudsman
Clearinghouse/Hotline
800-368-5888 (703-305-5938 for Virginia
callers)
Provides the public sector with information
on handling and abatement of asbestos in
schools, workplaces, and homes.
Toxic Substances Control Act (TSCA)
Information Service
202-554-1404
Provides technical and general information
on TSCA regulations.
Asbestos School Hazard Abatement
Act Hotline
800-462-6706
Provides information about the Asbestos
School Hazard Abatement Act loan and
grant program, which provides funds to
public and private schools to aid in asbestos
abatement.
Pollution Pollution Prevention Information
Prevention Clearinghouse
703-821-4800
Provides technical, policy, programmatic,
legislative, and financial information about
reducing industrial pollutants.
Underground
Storage Tanks
RCRA/Superfund/EPCRA Hotline
800-424-9346
800-535-0202
Provides general assistance and information
regarding underground storage tanks.
Water and AWWA Small Systems Technical
WasteWOter Assistance Line
800-366-0107
Provides technical support for operators of
drinking water systems serving fewer than
3,300 persons. Sponsored by the American
Water Works Association.
Clean Lakes Clearinghouse
800-72 6-LAKE
Provides information on lake and watershed
restoration, protection, and management.
National Drinking Water Clearinghouse
West Virginia University
P.O. Box 6064
Morgantown, WV 2 65 06
800-624-8301
Assists small communities by collecting,
developing, and providing timely informa-
tion about drinking water issues.
National Small Flows
Clearinghouse
800-624-8301
Provides information for small communi-
ties about wastewater management.
Appendix D: Where To Turn for Help 147
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Water and
WasteWOter
(continued)
National Water Efficiency Clearinghouse
6666 West Quincy Avenue
Provides information on water conservation
and water efficiency issues.
EPA Water Resource Center
401 M Street, SW
Washington, DC 20460
202-260-7786
Distributes EPA Office of Water
publications.
Safe Drinking Water Hotline
800-426-4791
Assists public water systems and the public
with their understanding of the regulations
and programs developed in response to the
Safe Drinking Water Act Amendments of
1986.
Wetlands Information Hotline
800-832-7828
Responds to requests for information about
the value and functions of wetlands and op-
tions for their protection.
General m U.S. EPA Center for Environmental Re-
search Information (CERI) Publications
26 West Martin Luther King Drive
Cincinnati, OH 45268
513-569-7562
Distributes brochures, reports, handbooks,
newsletters, and manuals based on the scien-
tific and technical environmental informa-
tion produced by EPA.
U.S. EPA National Small Community
Contact
U.S. EPA-OROSLR (1502)
401 M Street SW
Washington, DC 20460
202-260-0244
Coordinates efforts within EPA related to
small communities.
U.S. EPA Public Information
Center (PIC)
401 M Street, SW
Washington, DC 20460
202-260-2080 or 202-260-7751
Distributes a wide variety of general, non-
technical information about EPA and its
programs.
148 Appendix D: Where To Turn for Help
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Publications
Air and EPA's The Clean Air Act Amendments of 1990: A Guide for Small Businesses is available from
Radiation the EPA Control Technology Center at 919-541-0800.
Citizen's Guide to Radon (OPA-86-004) and other information on how to find and reduce
radon in homes is available from EPA's Radon Hotline (800-767-7236).
Solid Waste Decision-Makers Guide to Solid Waste Management (EPA-530/SW-89-072), The Solid Waste
Dilemma: An Agenda for Action (EPA/530/SW-89-019), The Consumer's Handbook for
Reducing Solid Waste (EPA/53 O/K-92-003), Environmental Fact Sheet: Yard Waste Composting
(EPA/530-SW-91-009), and Recycling Works! State and Local Solutions to Solid Waste Man-
agement Problems (EPA/530-SW-89-014) are available from the RCRA/Superfund Hotline
(800-424-9346).
Why Waste a Second Chance? A Small Town Guide to Recycling (1989) is available from the
National Association of Towns and Townships (202-737-5200).
Criteria for Solid Waste Disposal Facilities: A Guide for Owners/Operators (EPA/53Q-SW-91-
089) and Safer Disposal for Solid Waste: The Federal Regulations for Landfills (EPA/53 0-SW-
91-092) are available from CERI Publications (513-569-7562).
Solid Waste Disposal Facility Criteria: Technical Manual(EPA/53Q-R-93-017, PB94-100-450)
is available from the National Technical Information Service (703-487-4650).
Hazardous Solving the Hazardous Waste Problem: EPA's RCRA Program (EPA/53O-SW-86-037),
Understanding the Small Quantity Generator Hazardous Waste Rules: A Handbook for Small
Businesses, (EPA/530-SW-86-019), Household Hazardous Waste Management: A Manual for
1-Day Community Collection Programs, (EPA/530-R-92-026), and Household Hazardous
Waste: Steps to Safe Management (EPA/530-F-92-031) are available from the RCRA/
Superfund Hotline (800-424-9346).
Toxic Substances Chemicals in Your Community: A Guide to the Emergency Planning and Community Right-to-
RnoivActt^JS. EPA, 1988) can be ordered from the Emergency Planning and Community
Right-to-Know Information Hotline (800-535-0202).
Accidents Will Happen—A Small Town Guide to Planning for Hazardous Materials Response is
available from the National Association of Towns and Townships (202-737-5200).
Managing Asbestos in Place: A Building Owner's Guide to Operations and Maintenance Programs
for Asbestos-Containing Materials, The ABC's of Asbestos in Schools, and 100 Commonly Asked
Questions About the New AHERA Asbestos-in-Schools Rule can be ordered from the Toxic
Substances Control Act Hotline (202-554-1404).
Appendix D: Where To Turn for Help 149
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Underground
Storage Tanks
Musts for USTs, a summary of regulations for USTs, is available from the U.S. Government
Printing Office, Washington, DC 20402, (202-783-3238). Stock no. 055-000-00294-1.
Also available in Spanish.
Dollars and Sense (a summary of financial responsibility regulations for USTs), Leak Lookout
and Straight Talk on Tanks (summaries of leak detection methods for petroleum USTs), and
Oh No! (a brochure on what to do in the case of petroleum leaks and spills) are available
from the National Center for Environmental Publications and Information (513-891-
6561).
Getting Out From Under: Underground Storage Tank Alternatives for Small Towns, National
Center for Small Communities (1991), is available from the National Association of Towns
and Townships (202-737-5200).
Recommended Practices Package on Tank Management (Video) is available from the American
Petroleum Institute (202-682-8000).
Ground Water
and Drinking
Water
Environmental Pollution Control Alternatives: Drinking Water Treatment for Small Communi-
ties (EPA/625/5-90/025) is available from CERI Publications (513-569-7562).
The Local Decision-Makers' Guide to Groundwater and Wellhead Protection, Small System Guide
to the Safe Drinking Water Act, Small System Guide to Risk Management and Safety, Small
System Guide to Financial Management, Small System Guide to Board Responsibilities for
Operation and Maintenance, Small System Guide to Developing and Setting Water Rates, and
The Board Guide to Small System Policies (1993) are available from Community Resource
Group, Inc./Southern RCAP, 2705 Chapman, Springdale, AR 72762 (501-756-2900).
Why Do Wellhead Protection? and Protecting Local Ground-Water Supplies Through Wellhead
Protection are available from the National Drinking Water Clearinghouse (800-624-8301).
Seminar Publication: Wellhead Protection—A Guide for Small Communities (EPA/62 5/R-
93/002) can be ordered from CERI Publications (513-569-7562).
The Watershed Protection Approach—Annual Report 1992 (EPA 840-S-93-001) is available
from the National Center for Environmental Publications and Information (513-891-
6561).
Pocket Sampling Guide for Operators of Small Water Systems (EPA/814-B-92-001 for Phase
I volatile organic chemicals, total coliform rule, surface water treatment rule, and lead and
copper rule; EPA/814-B-94-001 for Phase II and Phase V chemicals) is available from
CERI Publications (513-569-7562).
Tapping Your Own Resources—A Decision-Maker's Guide for Small Town Drinking Water is
available from the National Association of Towns and Townships (202-737-5200).
150 Appendix D: Where To Turn for Help
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Water
Conservation
and Leak
Detection
Decision-Makers' Guide to Water Supply Management (EPA 570/9-80-003, PB158-973) is
available from the National Technical Information Service (703-487-4650).
Leaks in Water Distribution Systems (1987), Water Conservation (1987), Water Conservation
Strategies (1980), Before the Well Runs Dry (Volumes I and II) (1984), Water Resources Audit
(1988), and Water Audits and Leak Detection (1990) are available from the American Water
Works Association, 6666 West Quincy Avenue, Denver, CO (303-795-2449).
An Introduction to Water Loss and Leak Detection (1988) is available from the National Rural
Water Association (405-252-0629).
Wastewater It's Your Choice: A Guidebook for Local Officials on Small Community Wasteivater Management
Options (EPA 430/9-87-006) is available from the National Small Flows Clearinghouse
(800-624-8301).
Treat It Right: A Local Official's Guide to Small Toivn Wasteivater Treatment (1989) can be
ordered from the National Association of Towns and Townships (202-737-5200).
Manual: Wasteivater Treatment/Disposal for Small Communities (EPA/62 5/R-92/005) is
available from CERI Publications (513-569-7562).
Wetlands America's Wetlands: Our Vital Link Between Land and Water (U.S. EPA, 1988) can be
ordered from the Wetlands Protection Hotline (800-832-7828).
Protecting Coastal and Wetlands Resources: A Guide for Local Governments (EPA 842-R-92-
002) is available from EPA's Water Resource Center (202-260-7786).
Nonpoint Managing Nonpoint Source Pollution (EPA-506/9-90) is available from EPA's Water
Source Pollution Resource Center (202-260-7786).
Development and Water Quality: A Decisionmaker's Guide to Protecting the Urban Environment
(1994), DecisionmakersStorm.'water Handbook (1992), Urban Runoff and Stormwater Manage-
ment Handbook (1990), and Lake Smarts: The First Lake Maintenance Handbook (1994) are
available from the Terrene Institute, 1717 K Street, NW, Suite 801, Washington, DC
20006(202-833-8317).
Financial
Management
and
Intergovern-
mental
Cooperation
A State and Local Government Guide to Environmental Program Funding Alternatives
(EPA841-K-94-001) is available from CERI Publications (513-569-7562).
Building Together: Investing in Community Infrastructure (1990) is available from the
National Association of Counties (202-393-6226).
Decision-Makers Guide to Solid Waste Management (EPA/53 O-SW-89-072) is available from
the RCRA/Superfund Hotline (800-424-9346).
Small System Guide to Financial Management is available from the Rural Community
Assistance Program (703-771-8636).
Appendix D: Where To Turn for Help 151
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Public-Private Partnerships for Environmental Facilities: A Self-Help Guide for Local Govern-
ments (EPA/20M-2003) is available from the National Center for Environmental Publi-
cations and Information (513-891-6561).
Helping Small Systems Comply With the Safe Drinking Water Act: The Role of Restructuring
(EPA/812-K-92-001) is available from the National Center for Environmental Publica-
tions and Information (513-891-6561).
Restructuring Manual (EPA/570-9-91-035) is available from the National Center for
Environmental Publications and Information (513-891-6561).
The Self-Help Handbook by Jane W. Schautz is available from Rensselaerville Institute,
Rensselaerville, NY (518-797-3783).
Innovative Grassroots Financing—A Small Town Guide to Raising Funds and Cutting Costs is
available from the National Association of Towns and Townships (202-737-5200).
Touching All the Bases: A Financial Management Handbook for Your Wastewater Treatment Project
(EPA/430-9-86-001) is available from the Safe Drinking Water Hotline (800-426-4791).
Affordability of Major Wasteivater Systems Improvements for Small Montana Communities is
available from the Montana Department of Commerce (406-444-3757).
Electronic Bulletin Boards and Databases
Drinking Water Information Exchange
Bulletin Board System (DWIE-BBS),
Phone 800-624-8301, Modem 800-932-
7459 or 304-293-7108.
The National Drinking Water Clearing-
house's electronic bulletin board service,
which provides information regarding
drinking water systems in towns of up to
10,000 people.
WATERNET, Phone 303-794-7711
The American Water Works Association's
database of information on water conserva-
tion; utility management; drinking water
quality, analysis, and treatment; water pollu-
tion; wastewater treatment; and legal issues.
Wastewater Treatment Information Ex-
change Bulletin Board Service (WTIE-
BBS), Phone 800-624-8301, Modem
800-544-1936.
The National Small Flows Clearinghouse's
forum for discussion and exchange of infor-
mation about small-scale wastewater systems.
Solid Waste Information Clearinghouse
(SWICH), Phone 800-677-9424, Modem
301-585-0204.
Provides information on all aspects of solid
waste management.
Nonpoint Source Information
Exchange, Phone 703-385-6000 or
301-589-5318, Modem 301-589-0205
A bulletin board that provides information
about nonpoint source water pollution and
other water environment-related issues.
Alternative Treatment Technology In-
formation Center (ATTIC), Phone 800-
424-9346, Modem 703-908-2138.
Provides information on innovative treat-
ment technologies for hazardous waste
cleanup.
152 Appendix D: Where To Turn for Help
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Environmental Financing Information
Network (EFIN), available through the
Local Exchange (202-626-2400), LEGIS-
NET (303-830-2200), and the Government
Finance Information Network (312-977-
9700).
A service of EPA's Office of Water that pro-
vides access to an on-line search of financial
materials and publications and information
about environmental programs and events.
EPA Office of Research and Develop-
ment Bulletin Board System (ORD-
BBS), Phone 513-569-7272, Modem
513-569-7610.
A forum for exchange of scientific and tech-
nical research information. Includes a data-
base of all ORD publications produced
since 1976.
Tools
Farm*A*Syst
B142 Steenbock Library
550 Babcock Drive
Madison, WI 53706
608-262-0024
A voluntary program in which states, in con-
junction with the Cooperative Extension
Service, the Soil Conservation Service, and
EPA, conduct farmstead assessments to
identify potential sources of and solutions
to ground-water pollution.
Waterplan 1.0. Available from California
Department of Water Resources, P.O. Box
942836, Sacramento, CA 94236.
A software package that allows planners to
evaluate the costs and benefits of more than
75 water conservation measures.
Optimizing Water Treatment Plant Per-
formance Using the Composite Correc-
tion Program (EPA/625/6-91/027).
Available from CERI Publications (513-569-
7562).
Provides procedures for evaluating and im-
proving the performance of drinking water
treatment facilities. Includes methods to
optimize existing unit process without ma-
jor capital improvements.
Drinking Water Treatment Plant
Advisor. Available from CERI Publications
(513-569-7562) or from EPA's Office of
Research and Development Bulletin Board
System.
A software product for evaluating the per-
formance of small-to-medium drinking
water treatment plants. Can help optimize
plant performance to achieve compliance
with the surface water treatment rule.
POTW Self-Assessment: Mechanical
Wastewater Treatment Facility (April
1993) and Non-Mechanical Wastewater
Treatment Facility (November 1993).
Available from Water Management Divi-
sion, U.S. EPA Region 8, Denver, CO.
Guidance and workbook materials to help
POTWs achieve compliance with NPDES
permit limitations.
Retrofitting POTWs (EPA/625/6-
89/020). Available from CERI Publications
(513-569-7562).
Describes methods for evaluating and
improving the performance of wastewater
treatment facilities. Focuses on optimizing
existing facilities without major capital ex-
penditures.
Appendix D: Where To Turn for Help 153
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POTW Expert, Version 1.1: An Advisory
System for Improving the Performance of
Wastewater Treatment Facilities
(EPA/625/11-90/001). Available from CERI
Publications (513-569-7562).
A software program designed to help opera-
tors identify causes of inadequate wastewater
treatment plant performance using the Com-
posite Correction Program (CCP) approach.
TANKMAN, Version 1.0 (U.S. Army Envi-
ronmental Center. ATTN: SFIM-AEC-ECS,
Mr. Durant S. Graves, Aberdeen Proving
Ground, MD 21010-5401).
A management and reporting software tool
developed for the U.S. Army's underground
storage tanks (USTs). Allows the user to track
a wide range of information about their
USTs, including physical characteristics, com-
pliance status, historical data, and budget
information.
Solid Waste Management Options
(SW-Options) for Municipal Planners,
Version 1.0, 1992. Available from CERI Pub-
lications (513-569-7562) or from EPA's Office
of Research and Development Bulletin Board
System.
A user-friendly computer software package
for people responsible for evaluating and
selecting municipal waste options.
Environmental Compliance Assessment
System (U.S. Army Corps of Engineers Con-
struction Engineering Research Laboratories,
1992).
Contains procedures developed for U.S.
Army installations and facilities to determine
compliance with federal environmental
regulations. Brings together environmental
regulations, good management practices,
and risk management issues in easy-to-use
checklists.
RISK * ASSISTANT (Available from Thistle
Publishing, P.O. Box 1327, Alexandria, VA
22313).
A software system designed to evaluate hu-
man health risks associated with chronic expo-
sures to chemicals. Provides analytical tools
and databases covering approximately 500
chemicals, and information-handling capabili-
ties for risk assessment tailored to individual
sites or situations.
154 Appendix D: Where To Turn for Help
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