Evaluating
Stormwater
Infrastructure
Funding and
Financing Task
Force

Workgroup under the
Environmental Financial Advisory Board

Draft Report

January 2020


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Contributing EFAB Members

Lori Beary
Ted Chapman ~
Rudy Chow *

Lisa Daniel
Yvette Downs
Ted Henifin ~
Craig Holland

Pam Lemoine ~
Chris Meister
Eric Rothstein
Angie Sanchez
Bill Stannard
Joanne Throwe *

* Co-Chairs
Section Leads

Invited Consultants

Bethany Bezak
Jerry Bradshaw

David Bulova
Janet Clements
Carrie Evenson
Matthew Fabry
Carol Haddock
Laurie Hawks
Lisa Kay
Drew Kleis

Prabha Kumar
Rebecca Losli
John Lundell
Ewelina Mutkowska
Fernando Pasquel
Mike Personett
Andrew Reese
Elizabeth Treadway
Chuck Walter

EPA Supporting Staff

Sonia Brubaker
Tara Johnson
Ellen Tarquinio
Britney Vazquez

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

• • •

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Table of Contents

1.0 EXECUTIVE SUMMARY	1

1.1	Stormwater Infrastructure Funding Task Force Report and Charge	1

1.2	Local Stormwater Funding Efforts	2

1.3	Federal Stormwater Funding Support	2

1.4	Recommendations	3

2.0 INTRODUCTION AND BACKGROUND	5

2.1	Stormwater Infrastructure Drivers—A New Paradigm	6

2.2	Challenges and Opportunities	7

2.3	Report Overview	8

2.4	Funding Needs Not Included in This Report	10

2.5	Key Terms	10

3.0 TASK FORCE RECOMMENDATIONS	13

3.1 Recommendation Categories	14

4.0 SUFFICIENCY OF FUNDING	21

4.1	American Support for Investments in Water Infrastructure (2019)	23

4.2	Black & Veatch Stormwater Utility Surveys (2016 and 2018)	23

4.3	Clean Watershed Needs Survey 2012 Reportto Congress (2016)	24

4.4	Florida Stormwater Association Stormwater Utility Report (2016 and 2018)	25

4.5	Georgia Stormwater Utilities Report (2017)	26

4.6	Southeast Stormwater Association Utility Report (2019)	26

4.7	The Chesapeake Stormwater Network Select Results of the MS4 Needs Survey (2016)	26

4.8	Water Environment Federation MS4 Needs Assessment Survey Results (May 2019)	27

4.9	Western Kentucky University Stormwater Utility Surveys (2013,2016,2018 and 2019)	27

5.0 EXISTING SOURCES OF FUNDING	29

5.1	The Role of the Federal Government in Funding Stormwater Programs	29

5.2	Stormwater Funding—Types and Uses of Funds	30

5.3	Availability of Funding	54

5.4	Barriers to Obtaining Funding	57

5.5	Summary of Existing Funding Sources	61

6.0 INFRASTRUCTURE AFFORDABILITY	63

6.1	Infrastructure Efficiency	63

6.2	Financial Capability	65

6.3	Customer Household Affordability	75

APPENDIX I: MUNICIPAL FINANCIAL REPORTING AND ASSET MANAGEMENT	77

APPENDIX 11: CASE STUDIES	80

APPENDIX III: STORMWATER FUNDING DATABASE	112

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Acronym List

Acronym

Definition

AWIA

America's Water Infrastructure Act

BMP

Best Management Practice

CBP3s

Community-Based Public-Private Partnerships

CSO

Combined Sewer Overflow

CSS

Combined Sewer System

CWA

Clean Water Act

CWNS

Clean Watersheds Needs Survey

CWSRF

Clean Water State Revolving Fund

DWSRF

Drinking Water State Revolving Fund

EFAB

Environmental Financial Advisory Board

ERU

Equivalent Residential Unit

FCA

Financial Capability Assessment

FCI

Financial Capability Index

FEMA

Federal Emergency Management Agency

FSA

Florida Stormwater Association

~ HEAP

Low Income Home Energy Assistance Program

LTCP

Long Term Control Plan

MHI

Median Household Income

MS4

Municipal Separate Storm Sewer System

NFIP

National Flood Insurance Program

NPDES

National Pollutant Discharge Elimination System

O&M

Operation and Maintenance

P3

Public-Private Partnerships

PRI

Program-related Investment

Rl

Residential Indicator

SRF

State Revolving Fund

USACE

United States Army Corps of Engineers

USDA

United States Department of Agriculture

USEPA or EPA

United States Environmental Protection Agency

WEF

Water Environment Federation

WKU

Western Kentucky University

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

• • •

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1.0 Executive Summary

Stormwater Funding: A National Problem That Requires Action

Effective stormwater management is as integral to American quality of life as effective wastewater
management and delivery of safe drinking water. Hence, stormwater management needs to be deemed
as a true utility service on par with drinking water and wastewater utility services —and it needs
equitable and reliable funding, just like drinking water and wastewater utilities.

In the United States, drinking water and wastewater management services, generally through the utility
structure, have matured to become reliable and effective services to the communities, and with
dedicated sources of funding. Cumulatively, Clean Water State Revolving Fund programs have provided
$133 billion in assistance, mainly in the form of low-cost financing, to a wide range of eligible borrowers.
The utility structure that is conducive to effective management and dedicated funding, which has
worked well in the drinking water and wastewater sectors, should be applied to stormwater, the next
frontier for this nation's water quality goals. But even a utility structure requires predictable and
adequate revenues and sound governance. If these two elements are in place, effective operational
capability will follow. Unfortunately, only 1,600 of the 7,550 permitted stormwater entities in the United
States have dedicated revenue sources, such as stormwater user fees (also known as stormwater
utilities where fees are based, for example, largely on impervious area), taxes, or established drainage
districts that collect dedicated funding for stormwater.

Stormwater knows no jurisdictional boundaries and crosses state, county and municipal borders. There
are no comprehensive assessments of the funding needed to construct, and adequately maintain and
operate stormwater infrastructure nationally. Recent regional, limited surveys estimate stormwater
management and infrastructure funding needs in the billions of dollars annually beyond current funding
levels. Without question, the challenges related to stormwater funding are daunting and there is a
pressing need to continue to improve estimates of the sector's needs. The dedicated stormwater
funding sources that do exist are typically insufficient for currently known stormwater needs. Given the
magnitude and cross-jurisdictional nature of the stormwater challenge, local funding efforts are not
enough. There is a need for federal investment in stormwater infrastructure, similar to the level of
investment that federal funding programs have provided in the past to begin building our interstate
highway system, upgrade our wastewater infrastructure, or deliver safe drinking water to our homes.
The federal financing and funding framework that has worked so well to support the drinking water and
wastewater sectors should be adapted to fund solutions to the stormwater challenge. This type of
federal financing and funding will support communities with stormwater permits that serve more than
80 percent of the U.S. population. Therefore, stormwater funding is a national problem that requires
action.

1.1 Stormwater Infrastructure Funding Task Force Report and Charge

This report was developed in response to Section 4101 of the 2018 America's Water Infrastructure Act

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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(AWIA), which directed the Environmental Protection Agency (EPA) to establish a Stormwater
Infrastructure Funding Task Force "to conduct a study on, and develop recommendations to improve the
availability of public and private sources of funding for the construction, rehabilitation, and operation
and maintenance of stormwater infrastructure" to meet the requirements of the Clean Water Act.

Specifically, the Task Force was charged with the following tasks:

*	Identify existing federal, state and local public and private sources of funding for stormwater
infrastructure (addressed in Section 5.0).

*	Assess how the source of funding affects affordability, including costs associated with infrastructure
finance (addressed in Section 6.0).

*	Assess whether these sources of funding are sufficient to support capital expenditures and long-
term operational and maintenance costs required to meet the stormwater infrastructure needs of
municipalities (addressed in Section 4.0).

1.2	Local Stormwater Funding Efforts

Finding funding sources has become a necessary activity for local governments and utilities that are
charged with managing stormwater programs. Several professional organizations have developed
publications and held workshops on how to develop and implement dedicated funding mechanisms.
Their advocacy efforts have also elevated the discussion on the need for funding and the importance of
affordability.

Perhaps more importantly, conversations in recent years have shifted from "how to develop stormwater
utilities" to the need for innovative funding strategies that include public-private partnerships,
incentives for private property owners to implement stormwater controls, green bonds, and trading
schemes. Innovative funding mechanisms, coupled with reliable traditional mechanisms (e.g.,
stormwater utilities, fees-in-lieu-of, drainage/taxing districts) provide local programs with additional
alternatives to fund their stormwater needs.

1.3	Federal Stormwater Funding Support

As previously stated, local funding efforts alone are not enough. Stormwater infrastructure requires
funding and it has been neglected, or inadequately funded, for far too long. There is a need for federal
investment in stormwater infrastructure, similar to the level of investment that federal funding
programs have provided in the past to, among other things, begin building our interstate highway
system, upgrade our wastewater infrastructure, and deliver safe drinking water to our homes.

The federal government can also help by allocating funding for stormwater programs from existing
related programs to ensure that infrastructure is properly maintained and that future infrastructure
planning, design and capital expenditures are conducted using industry best practices.

Municipalities and local utilities need federal and state help in defining long-term reliable funding
sources. Funding must be available in all states and be sufficient to support both capital expenditures
and long-term operation and maintenance costs.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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1.4 Recommendations

Task Force recommendations are presented as items that are practical to implement, actionable at the
federal level and understandable to the public. They present suggestions to use existing funding
mechanisms, increase accessibility to those funding mechanisms, identify additional funding
opportunities, and enhance public education. The Task Force's recommendations are grouped into the
following categories:

*	Stormwater funding education and technical assistance. Educating the public and elected officials
on the need for stormwater funding is critical to the successful implementation of and community
support for funding solutions. In addition, many communities need technical assistance related to
evaluating and securing funding and financing mechanisms.

Recommendation: Educate elected representatives, professional administrative leaders and the
general public on the need for sustainable local stormwater funding and organizational capacity
through, for example¦, the creation of stormwater utilities or the expansion of existing utilities
into the stormwater sector.

Recommendation: Provide technical assistance and funding to help communities create
sustainable funding sources. This could include assistance with funding need assessments,
organization analysis, grant applications, and/or establishing a stormwater utility fee.

*	Simplification and/or modification of existing federal grant and loan programs and affordability
support. Federal grants, loans (e.g., from State Revolving Funds) and support to enhance
affordability are needed to maintain sustainable local funding sources.

Recommendation: Provide for a common application for different federal grants across all
federal agencies.

Recommendation: The State Revolving Fund (SRF) is an integral tool among the many
infrastructure financing options available to communities. Whether stormwater receives
consideration of its own through a new SRF program, or receives less restrictive eligibility
considerations and larger appropriations within the existing Clean Water SRFs (CWSRF) or
eligible Drinking Water SRF (DWSRF) projects, it is the view of the Task Force that stormwater
would benefit from an additive - not zero-sum - recurring financial commitment from EPA. This
could be achieved by the implementation of one or more of the following, each of which is
outlined below:

o Create a new SRF program exclusive to stormwater programs and projects.

o Expand the existing Water Infrastructure Finance and Innovation Act (WIFIA) program or
fund the Army Corps of Engineers' Water Infrastructure Program also established in 2014.

o Create a specific stormwater set-aside in the existing CWSRF framework and increase
awareness/ guidance on the CWSRF for stormwater projects, including the Green Project
Reserve program.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Recommendation: Use federal funding or technical assistance to help utility customers who are
financially struggling to pay their water, sewer, and stormwater utility bills (similar to Low
Income Home Energy Assistance Program (LIHEAP)).

* Dedicated federal stormwater funding assistance. Given the magnitude of the stormwater needs
described in this report, there is a need for federal investment similar to the investments in the
National Interstate Highway system and historical wastewater treatment plant upgrades.

Recommendation: Build comprehensive national database that enumerates state barriers to
implementation of new dedicated stormwater revenue sources such as user fees or other
revenue sources, and/or any state restrictions on existing fees and charges.

Recommendation: Increase annual funding allocation for and modify the 319(h) grant program
to allow and encourage local capacity building, utility fee study and implementation, asset
management, and remove restrictions on use of grant funds for MS4 permit compliance.

Recommendation: Develop a new construction grant program specifically for stormwater
projects, similar to the federal Municipal Construction Grants Program that funded the
construction of wastewater treatment plants.

Recommendation: Given the link between agricultural pollution and mandated stormwater
pollutant reduction targets for impaired streams, a Farm Bill Federal subsidy dedicated to
stormwater programs would also be valuable. Require 10 percent of US federal farm subsidies
(all programs) be re-directed towardstormwater/nonpoint impacts in same watershed where
recipient farm is located.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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2.0 Introduction and Background

Stormwater management involves diverse activities that span both operations and maintenance (O&M)
and capital program. The O&M activities, to name a few, typically include the maintenance of
stormwater conveyance infrastructure; good housekeeping practices; land use development and
redevelopment permitting, monitoring, and inspections; public education and outreach; and
management of various other stormwater programs. The capital program management typically
includes asset management, capital projects planning and execution. Needless to say, holistic
management of stormwater O&M and capital program services requires sustainable and dedicated
funding.

Stormwater management is widely viewed as a key part of the solution to improving water quality in the
nation's waterways, reducing local flooding/drainage problems, and enhancing community resiliency.
However, the challenges related to funding stormwater infrastructure are daunting: the stormwater
sector is still maturing and has traditionally not been funded as a true "utility" operation like wastewater
and drinking water utilities. Meanwhile, EPA has identified urban stormwater runoff as the only major
growing source of water pollution across much of the country. Starting in the 1990s, EPA sought to
reduce pollution in U.S. waterways through regulations and a permit program under the Federal Water
Pollution Control Act, commonly known as the Clean Water Act (CWA). Communities with stormwater
permits include more than 80 percent of the
U.S. population—therefore, stormwater
funding is a national problem that requires
action.

There are no comprehensive assessments of
the funding needed to construct, maintain and
operate stormwater infrastructure nationally. Recent regional or limited surveys estimate stormwater
management and infrastructure funding needs in the billions of dollars, ranging from $3.3 billion over
the next 10 years in Florida alone 1 to $8.1 billion per year for only municipal separate storm sewer
system (MS4) permittee activities in the United States.2

EPA estimates that $150 billion is needed for stormwater infrastructure and program investments (MS4s
and combined sewer overflows) over the next 20 years.3 The needed investment in stormwater

1	Florida Stormwater Association. 2018. Stormwater Utility Report. https://www.florida-
stormwater.org/stormwater-utilitv-reportl

2	WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survey-Report-2019.pdf

3	U.S. EPA. 2016. Clean Watersheds Needs Survey 2012 Report to Congress EPA-830-R-15005.
https://www.epa.gov/sites/production/files/2015-12/documents/cwns_2012_report_to_congress-508-opt.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Recent regional or limited surveys
estimate stormwater management and
infrastructure funding needs in the billions
of dollars


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infrastructure is similar to the level of investment that federal funding programs have covered in the
past to initiate construction of our interstate highway system or upgrade wastewater treatment plants.

Funding needs continue to expand as the stormwater sector faces increasing challenges related to
regulatory requirements, water quality degradation, flood risk reduction, community resilience, aging
infrastructure, and more. Many communities have no sustainable source of funding for stormwater
programs. In addition, increasing stormwater management costs at the local level exacerbate the
affordability challenges that many communities face. While a more detailed analysis is needed to fully
assess the funding need, it is widely acknowledged that the stormwater infrastructure sector cannot
fully address these challenges at current funding levels.

This report was developed in response to Section 4101 of the 2018 AWIA, which directed EPA to
establish a Stormwater Infrastructure Funding Task Force "to conduct a study on, and develop
recommendations to improve the availability of public and private sources of funding for the
construction, rehabilitation, and operation and maintenance of stormwater infrastructure" to meet the
requirements of the CWA. AWIA stipulates that the Task Force comprise representatives of federal,
state and local government and private entities (including nonprofit entities). Furthermore, EPA is
required to submit a report to Congress no later than 18 months after AWIA enactment describing the
results of the Task Force's study and resulting recommendations.

The Task Force was convened under an existing Federal Advisory Committee, the Environmental Finance
Advisory Board (EFAB). 14-members of the EFAB with experience and expertise in stormwater funding
and financing are on the Task Force. EPA also initiated an open nomination process to identify expert
consultants to advise and support the Task Force. EPA selected 19 consultants to address gaps in the
Task Force's expertise and ensure the Task Force could complete the required study and
recommendations within the stipulated timeframe. Task Force members, consultants and key EPA staff
who supported the preparation of this report are presented at the beginning of this report.

Task Force members and consultants participated in two in-person meetings and in regular telephone
conference meetings to conduct research, develop the study and identify associated recommendations
for consideration by EPA. EPA also solicited and integrated public input on stormwater funding through
seven public meetings held across the country in Florida, Massachusetts, Illinois, the District of
Columbia, Virginia, Georgia, and Washington.

2.1 Stormwater Infrastructure Drivers—A New Paradigm

Before the 1990s, municipal stormwater management was driven mainly by one consideration: convey
stormwater away from our built environment. While federal regulations added a new focus on water
quality, the Task Force recognizes the need to consider both water quality and water quantity when
evaluating funding sources and needs. In fact, stormwater management is undergoing a significant
paradigm shift (Figure 1): local programs often have multiple responsibilities, including water quality,
water quantity, floodplain management, resilience planning and response, regulation of new and re-
development, multi-objective planning, ecosystem health, environmental, and increasing community
expectations. These responsibilities are relevant to stormwater management in recognition of the
broader public concern for infrastructure management and environmental stewardship.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Expanding Stormwater Drivers

Figure 1. Graphic representing the current stormwater management paradigm shift.

2.2 Challenges and Opportunities

This report identifies several potential sources of funding available to most municipalities (see Section
5.0). While the length of the list may imply that it is easy to fund stormwater management activities, the
opposite is true: the volume of options shows that there is no universal solution, and many types of
funding must be supplemented by a baseline revenue stream like that found in other municipal-level
utilities. Establishing such a baseline revenue stream for stormwater management programs—programs
that themselves are undergoing such a significant paradigm shift—is extremely challenging and faces
legal obstacles in many places. Garnering community support for an expanding program is difficult
enough. Asking a community to pay for it in the form of user fees or taxes is an even greater challenge.

A municipal stormwater program cannot be funded in a bureaucratic vacuum and in an environment
where the decision makers and the community are not fully aware of the benefits and challenges of
stormwater management. It can only succeed with the support of the local community and its elected
officials. One of the many barriers to gaining that support is the lack of public understanding about what
a stormwater program is and how it affects quality of life for the average citizen. Municipal stormwater

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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programs have focused on infrastructure and environmental stewardship but have not always done an
effective job of explaining to the community and elected officials what they are and why they are
important.

At the same time, the Task Force has observed that municipalities differ significantly with respect to the
distribution of stormwater management and regulatory compliance responsibilities due to variations in
local and state institutional frameworks. Under a new and evolving paradigm, institutional frameworks
often lag behind the functional changes brought about by the new drivers. The distribution of
responsibilities can affect cost-effectiveness, funding and affordability, creating situations with
overlapping responsibilities and a shortage of accountability or leadership for program implementation.
In addition, providing technical assistance and public outreach/education to such a dispersed
community of stormwater managers and programs is a challenge.

While these challenges are daunting, they also represent opportunities to interact with and leverage
other public investments such as transportation, flood protection, public safety, recreation and other
cultural endeavors that fit within the new stormwater paradigm. Municipalities have made great strides
to integrate stormwater projects and programs into these other areas through multi-benefit projects.
But much more must be done to move the needle on the adequacy of stormwater funding.

In summary, the local government stormwater manager is faced with multiple, costly, sometimes
conflicting responsibilities across a wide spectrum of stormwater-related demands—often with little
dedicated funding to accomplish necessary tasks. About 60 percent of the stormwater permittees
indicate that their major challenge is the lack of funding or availability of capital for implementation of
stormwater programs and design, construction and maintenance of stormwater infrastructure.4

2.3 Report Overview

The Task Force was charged with the following tasks:

Identify existing federal, state and local public and private sources of funding for stormwater
infrastructure (Section 5.0).

Assess how the source of funding affects affordability, including costs associated with infrastructure
finance (Section 6.0).

Assess whether these sources of funding are sufficient to support the capital expenditures and long-
term operations and maintenance (O&M) costs required to meet municipalities' stormwater
infrastructure needs (Section 7.0).

The report is organized based on the findings associated with these tasks, as described below.

Section 3.0: Task Force Recommendations

Section 3.0 presents the Task Force's overall recommendations. The recommendations present

4 WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survey-Report-2019.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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suggestions to enhance the use of existing funding mechanisms, increase accessibility to those funding
mechanisms, identify additional funding opportunities, and measures to enhance public education. The
Task Force's recommendations are grouped into three succinct categories:

*	Stormwater funding education and technical assistance;

*	Simplification of existing federal grant and loan programs and affordability support; and

*	Dedicated federal stormwater funding assistance.

Section 4.0: Sufficiency of Funding

Section 4.0 discusses the difficulty of assessing the capital and long-term O&M funding needed for
municipal stormwater infrastructure in the United States. This section also presents information from
several regional and national surveys that attempt to make these estimates and includes case studies of
stormwater funding challenges in more than a dozen communities across the country. Finally, Section
4.0 describes the reasons why the funding gap exists and continues to grow, as well challenges
associated with finding effective solutions to meeting stormwater funding needs.

Section 5.0: Existing Sources of Funding

Section 5.0 describes the various types of plausible funding sources such as recurring and sustainable
sources, intermittent revenue sources, capital financing sources and one-time sources of funding for
stormwater programs. Even though there are multiple types of funding sources, only a few can provide
reliable, sustainable, and dedicated revenue for holistic stormwater management. Perhaps more
importantly, without elected officials' support, to develop such dedicated sources of funding where it
currently doesn't exist, the availability of funding will continue to be limited, leaving most programs
without enough funds to meet all the stormwater community's needs.

Section 6.0: Infrastructure Affordability

Section 6.0 describes how available funding sources and financing options affect three aspects of a
municipality's stormwater management that are directly impacted by the various types of funding and
financing sources. The three aspects that this section focuses on are:

*	Effective management of Infrastructure. Industry best practices, such as adopting proactive asset
management, leveraging resources and economies of scale, building resilience, and engaging in risk
mitigation, all of which can also improve affordability.

*	Financial capability, is defined as the adequacy of a municipality's funding to meet its annual
stormwater O&M obligations and to manage its capital stormwater infrastructure needs,
determined based on delivering adequate levels of service. This sub-section discusses the impact of
different funding sources on building financial capacity and provides criteria for evaluating the
affordability impacts of different recurring, intermittent and one-time funding sources to address
capital and O&M requirements.

*	Customer household affordability, defined as the impact that the various types of financial
resources have on the users of the system. This sub-section describes traditional and emerging
concepts that are used to evaluate household affordability.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Affordability can also be impacted by the public and elected officials' lack of understanding of the need
for stormwater services and the benefits of stormwater programs. Therefore, the Task Force concludes
that educating these stakeholders can facilitate the implementation and acceptance of reliable and
sustainable funding sources.

2.4	Funding Needs Not Included in This Report

This report does not address funding needs related to the following programs or activities (which can
complement the goals of local stormwater management programs, but are typically funded by other
federal or local sources):

*	Addressing agricultural water pollution. Most local stormwater programs focus on urban areas and
the associated drainage, flooding, resilience and stormwater quality needs. These local programs
typically do not have legislation that allows them to regulate agricultural activities. Soil and Water
Conservation Districts and other U.S. Department of Agriculture programs under the Farm Bill, as
well as CWA nonpoint-source regulations, address this growing source of pollution.

*	Flood risk identification and mapping. Costs associated with the Federal Emergency Management
Agency (FEMA) flood risk identification and mapping program under the National Flood Insurance
Program (NFIP) are not included in this report, since these federal activities are funded by the NFIP
and flood insurance policy fees.

*	Large flood risk management and ecosystem restoration programs. Large programs to address
riverine flooding navigation, and ecosystem restoration programs conducted by the U.S. Army Corps
of Engineers and funded through the Water Resources Development Act are not included in this
report. In some instances, local stormwater revenue is used as the local match for these large
projects, but the bulk of the costs are paid by federal sources.

2.5	Key Terms

To frame and further refine the scope of the required study, the Task Force first agreed on a definition
for stormwater, as well as definitions of associated environmental, technical and other considerations
and drivers for stormwater services. The Task Force also determined what considerations fall outside
the scope of the AWIA charge and are not addressed in this report.

The Task Force used the following key definitions related to stormwater, stormwater services and
regulatory requirements for municipal stormwater services:

*	Municipal stormwater: Surface water runoff, snow melt runoff, and drainage from public and
private lands in urban areas, typically collected in MS4s consisting of drains, pipes, catch basins,
outfalls, and ditches and conveyed to nearby streams, rivers, lakes, estuaries, basins, wetlands and
oceans, carrying with it a variety of urban pollutants.5 Stormwater control measures (e.g.,
basins/ponds and green infrastructure—bioswales, filters, infiltrators, pollutant traps, etc.), also

5 Adapted from National Association of Flood and Stormwater Management Agencies. 2006. Guidance for
Municipal Stormwater Funding, https://www.epa.gov/sites/production/files/2015-10/documents/guidance-
manual-version-2x-2 O.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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known BMPs, are used to "treat" municipal stormwater by capturing pollutants to improve water
quality and reducing runoff to prevent flooding.

*	Municipal Separate Storm Sewer System (MS4): A conveyance or system of conveyances (including
roads with drainage systems, municipal streets, catch basins, curbs, gutters, ditches, artificial
channels or storm drains) that is owned or operated by a state, city, town, borough, county, parish,
district, association or other public body and is designed or used to collect or convey stormwater,
but is not a combined sewer and is not part of a publicly owned treatment works (POTW).sThere
are 7,550 MS4 stormwater permittees in the United States, including more than 6,500 cities.
Communities with MS4 stormwater permits serve more than 80 percent of the U.S. population or
approximately 263 million people.7

*	Phase I Municipal Stormwater Regulation (hereafter Phase I): a 1990 regulation that requires
medium-sized and large cities, or certain counties with populations of 100,000 or more, to obtain
National Pollutant Discharge Elimination System (NPDES) permit coverage for their stormwater
discharges. There are about 855 Phase I MS4s covered by 250 individual permits.7

*	Phase II Municipal Stormwater Regulation (Phase II): a 1999 regulation that requires small MS4s in
U.S. Census Bureau-defined urbanized areas, as well as MS4s designated by the permitting
authority, to obtain NPDES permit coverage for their stormwater discharges. Phase II also includes
non-traditional MS4s such as public universities, departments of transportation, hospitals and
prisons. There are about 7,000 Phase II MS4s covered by statewide General Permits; some states
instead use individual permits.8

*	Combined Sewer System (CSS): A system of conveyance that carries and conveys both sanitary
sewage and stormwater flows, in the same pipe, to a POTW. CSSs serve about 43 million people in
about 1,100 communities nationwide.9

*	Infrastructure efficiency: The ability to effectively manage the stormwater system infrastructure
and improve affordability through best management practices, including adopting proactive asset
management, leveraging resources and economies of scale, building resilience, and engaging in risk
mitigation.

*	Integrated planning; A voluntary approach to meeting multiple Clean Water Act requirements by
identifying efficiencies from formerly distinct drinking water, wastewater and stormwater programs
and sequencing investments to address the highest priority projects first. Integrated planning also
encourages multi-benefit, cross-sector sustainable and comprehensive solutions to water resource
challenges.

6	Definition from 40 CFR § 122.26.

7	U.S. EPA. 2019. Stormwater Discharges from Municipal Sources, https://www.epa.gov/npdes/stormwater-
discharges-municipal-sources

8	Ibid.

9	U.S. EPA. 1997. Combined Sewer Overflows—Guidance for Financial Capability Assessment and Schedule
Development. EPA 832-B-97-004. February 1997. https://www3.epa.gov/npdes/pubs/csofc.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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* Median Household Income (MHI): The middle-income level earned by households in a given area,
intended to represent the economic status of households in that area. Fifty percent of households in
the specified area will earn above median household income, and 50 percent will earn below.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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3.0 Task Force Recommendations

The Task Force offers recommendations on how existing funding can be used and made more accessible,
as well as on identifying additional funding opportunities. They are intended to be actionable and
understandable to the public. The recommendations are summarized in the Executive Summary and
presented in detail below.

The Task Force's recommendations fall into the following categories:

*	Stormwater funding education and technical assistance. Educating the public and elected officials
on accepting the need for stormwater funding is critical to the successful implementation of and
community support for funding sources. In addition, many communities need technical assistance
related to evaluating and securing funding and financing mechanisms.

*	Simplification of existing federal grant and loan programs and affordability support. Federal
grants, loans (e.g., from State Revolving Funds) and support to enhance affordability are needed to
maintain sustainable local funding sources. These actions would provide communities an incentive
to create dedicated funding sources to demonstrate financial capacity and capabilities, while still
retaining the flexibility and local control as to the actual method for repayment.

*	Dedicated federal stormwater funding assistance. Given the magnitude of the stormwater needs
described in this report, there is a need for federal investment similar to the investments in the
National Interstate Highway system and wastewater treatment plant upgrades. A Farm Bill Federal
subsidy dedicated to stormwater programs would also be valuable, given the link between
agricultural pollution and mandated stormwater pollutant reduction targets for impaired streams.

Several of the recommendations include direct involvement and interaction by EPA with state and local
agencies. The main goal is for federal actors to help state and local agencies, but the federal actors will
also learn about issues and barriers that confront local agencies. This two-way flow of information and
experiences will help bridge the gap between the source of clean water regulations (federal) and the
most important source of funding (primarily local). This, in turn, will also greatly benefit the overall goals
of the CWA, the involved agencies, and the public at large.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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3.1 Recommendation Categories

3.1.1 Stormwater funding education and technical assistance

Recommendation: Educate elected officials, professional administrative leaders and the public
on the need for sustainable local stormwater funding and organizational capacity through, for
example, the creation of stormwater utilities or the expansion of existing utilities into the
stormwater sector. Sustainable funding for stormwater infrastructure builds long-term financial
capacity, improves operational performance—and over time produces results for citizens and
residents. For over two hundred years, this has been the experience with drinking water and
wastewater utilities in this country. The educational goals for these three audiences will
demonstrate that stormwater management investment directly benefits the health, safety and
economic opportunity for citizens and residents through the overall improvement of water
quality.

Stormwater, along with drinking water and wastewater, must be approached as part of a
comprehensive "One Water" solution. When stormwater management, sustainable drinking water
supplies and wastewater treatment resources and goals are aligned, communities avoid costs, are
financially sustainable, are safer, are better environmental stewards, and provide better economic
opportunities and quality of life for their residents. FEMA's own hazard mitigation program generally
notes that investments in key stormwater infrastructure alone improve a community's resilience; the
return on investment is four times or even better, through cost avoidance and quicker return to
normalcy than a do-nothing scenario.

Communities with successful water resource management strategies have generally identified financial
needs over multi-year planning horizons. Implementation of "One Water" strategies supported by
appropriate financial resources provide better management of public health, safety, economic and
financial risks. Successful education will help reduce barriers, such as those that may exist under state
law, and will build support to establish forward-looking and sustainable operational capability in
stormwater management and responsible and long-term finance and capital planning. The Task Force
Recommends that EPA's Water Finance Center work with other EPA programs and Federal Agencies to
address this recommendation.

Recommendation: Provide technical assistance and funding to help communities create
sustainable funding sources. This could include assistance with funding need assessments,
organization analysis, grant applications, and/or establishing a stormwater utility fee.

Many communities would be willing to work toward greater funding self-sufficiency but lack the
support, expertise and initial resources to get started. Federal assistance can help overcome these
hurdles through technical assistance and funding to support the initial activities necessary to create
sustainable funding sources.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Technical assistance may include guidance documents, webinars, hands-on training and support. While
technology should be leveraged to make this assistance accessible to all communities with stormwater
issues, the technical assistance also needs to be proactive. Proactive programs should include reaching
out to smaller communities through circuit-rider-type programs with onsite assistance. This technical
assistance program could be established under the EPA Office of the Municipal Ombudsman established
by AWIA Section 5006.

EPA should provide funding and in the form of grants or matching funds to support the utility capacity
building, feasibility/needs assessment, grant applications and other activities needed to create
sustainable funding sources.

3.1.2 Simplification of existing federal grant and loan programs and affordability
support

Recommendation: Provide for a common application for different federal grants across all

federal agencies.

Most of the U.S. population lives in large urban or suburban areas, generally associated with
governmental units that have relatively more financial, technological and human resources. While these
areas are generally associated with governmental units that have relatively more financial, technological
and human resources, they do not always have sufficient resources to dedicate to securing necessary
stormwater funding. In addition, most individual local governments are associated with small or very
small populations (10,000 or fewer people). These communities are also often rural and often exhibit
below-average income indicators. As such, they may face particular difficulty in accessing the requisite
technical expertise and financial resources that are often needed to even apply for federal grants.

The Task Force believes all communities, especially small, rural and otherwise disadvantaged ones,
would greatly benefit from more uniformity to the federal grant application process—perhaps some
baseline commonality to all applications across the federal government irrespective of the agency or
department ultimately administering the grant program. A common application could lessen barriers for
communities if as much of the actual application as possible were exactly the same and not specific to
any particular federal agency or department. The Task Force notes that the federal Paperwork
Reduction Act (44 U.S.C. §§ 3501-3521) was established in 1980 but has not been amended since 1995,
during the infancy of the Information Age. For a comparable example, The Common App10, implemented
almost a generation ago, is now used by nearly 900 colleges and universities across all 50 states,
benefitting more than a million prospective college students. This streamlining and simplification saves
both the applicant and the associated higher education institutions significant time while breaking down
barriers of access and relieving burdens of redundancy.

10 The Common App is a college admissions application that applicants may use to apply to various universities.
More information available at: https://www.commonapp.org/.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Recommendation: The SRF is an integral tool among the many infrastructure financing options
available to communities. Whether stormwater receives consideration of its own through a new
SRF program or receives less restrictive eligibility considerations and larger appropriations within
the existing SRFs, it is the view of the Task Force that stormwater would benefit from an additive
- not zero-sum - recurring financial commitment from EPA. These would provide communities an
incentive to create dedicated funding sources to demonstrate financial capacity and capabilities,
while still retaining the flexibility and local control as to the actual method for repayment. This
could be achieved by the implementation of one or more of the following, each of which is
outlined below with the associated risks and opportunities:

I.	Create a new SRF program exclusive to stormwater programs and projects.

o Advantages

¦	Replicates programs that have been proven successful for decades.

¦	Would eliminate 'competition' with wastewater projects inherent within the
current CWSRF program.

o Disadvantages

¦	Would require the creation and passage of new enabling legislation to establish
a new SRF program.

II.	Expand the existing WIFIA program (e.g. explicit references to stormwater project
eligibility, priority points for stormwater projects, lower project minimums for bundled
stormwater projects) allowing funding for more stormwater projects, or fund the Army
Corps of Engineers' Water Infrastructure Program also established in 2014.

o Advantages

¦	Would not require new enabling legislation.

¦	WIFIA has already demonstrated the ability to leverage federal dollars many
times over the initial appropriation.

¦	The Corps' program has a stated mission to "enable local investments in projects
that enhance community resilience to flooding, promote economic prosperity
and improving environmental quality" which is already consistent with the
general aim of stormwater infrastructure.

o Disadvantages

¦	Bundling enough projects together to meet the scope of the WIFIA program.

¦	Administrative difficulty in successfully applying to the program.

III.	Create a specific stormwater set-aside in the existing CWSRF framework and increase
awareness/ guidance on the CWSRF for stormwater projects, including the Green
Project Reserve program.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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o Advantages

¦	Would not require new federal legislation.

¦	Preserves each states' ability to administer the program to maximize efficiencies
and effectiveness specific to each states' needs.

o Disadvantages

¦	Might not improve best management practices or capability of communities if
the set-aside is viewed by them as an implicit high likelihood/guarantee to get
funded.

IV. Create a "One Water" SRF with equal weighting among drinking water, clean water
and stormwater.

o Advantages

¦	Would encourage community creativity and holistic, multi-year master planning
- including resilience and integrated planning - by way of multi-purpose projects
that achieve goals aligned with the One Water principles.

¦	Might be more likely to attract private sector participation, especially if flood
control and stormwater facilities are added as a private activity bond category
as proposed by the Administration in February 2018's infrastructure stimulus.

¦	Would provide communities an incentive to create dedicated funding sources to
demonstrate financial capacity and capabilities, while still retaining the flexibility
and local control as to the actual method for repayment.

o Disadvantages

¦	Would require amending existing enabling SRF legislation.

¦	The CWSRF has been in place since 1987 and the DWSRFsince 1997; therefore
decades of policy and administrative inertia could pose an implementation
barrier.

Recommendation: Create federal funding and technical assistance (similar to LIHEAP) to help
address household affordability issues of utility customers who are economically challenged in
paying their water, sewer, and stormwater utility charges.

One of the strengths of the utility fee approach, to funding stormwater management, is that the cost of
services is distributed to properties in proportion to the stormwater that properties contribute to a
public stormwater system. This type of industry accepted fee for service approach is perceived to enable
equitable cost recovery by establishing a reasonable nexus between the demand placed on the system
and the charges that are assessed. However, the addition of a stormwater user fee, however small the
fee maybe, could create an additional burden on low-income households, including the elderly on fixed
incomes, that already struggle to pay the water and sewer utility charges.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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To address household affordability challenge, some local governments have established customer
assistance programs to help with water, sewer, stormwater utility fees, using general funds or other
non-utility resources. However, at the local level, particularly in financially stressed communities,
establishing fee assistance programs becomes burdensome, even if statutes allow such
programs. Further, subject to varying State and Local statutes, many utilities are unable to establish any
low-income customer assistance programs, as establishing utility fee assistance programs using utility
enterprise funds, is deemed to violate the fee for service concept. Due to these types of challenges,
elected officials in many communities in the US are reluctant to adopt a stormwater utility fee funding
mechanism.

The federal LIHEAP11, in place since the 1980s, helps qualifying households offset a portion of their
energy costs. Expanding LIHEAP, with additional funding, to help offset water, sewer, stormwater utility
charges and/or establishing a similar distinct federal assistance program for water/sewer utilities,
including stormwater, could remove a major barrier to the creation of dedicated user fee-based
stormwater funding, at the local level.

3.1.3 Dedicated federal stormwater funding assistance

Recommendation: Build comprehensive national database that enumerates state barriers to
implementation of new dedicated stormwater revenue sources such as user fees or other
revenue sources, and/or any state restrictions on existing fees and charges.

As part of 2020 Clean Watersheds Needs Survey, EPA should create a state-level funding evaluation
framework and request that states use that framework to identify barriers/gaps in state enabling
legislation to create new stormwater user fees and/or restrictions on fee increases. Once information is
received from states, EPA should post a compendium of findings from the evaluation in a publicly
available forum and provide educational materials for local government officials and the public. Further,
Congress should develop an incentive framework (e.g., matching 319 funds or other federal grant or
funding mechanisms) to encourage removal of state-level funding barriers, where applicable.

Recommendation: Increase annual funding allocation for and modify the 319(h) grant program
to allow and encourage local capacity building, utility fee study and implementation, asset
management; remove restrictions on use of grant funds for MS4 permit compliance.

The 319(h) grant program is an important resource to many small and medium-sized local governments,
but current allocation levels cannot meet demand. Increasing allocations will address critical needs at
the local level. The use of the funds for general operational program costs is limited to 10 percent. The
allocation, distributed to state nonpoint-source pollution programs, varies from year to year based on
budget authorizations. Therefore, there is no stable platform for grant awards at the local level. There is
a need to provide more funding support in an entire watershed, prioritized on financial capacity. Smaller
surface water management systems and systems in disadvantaged communities have limited capacity to

11 Low Income Home Energy Assistance Program (LIHEAP). US Department of Health and Human Services. More
information available at: https://www.acf.hhs.gov/ocs/programs/liheap

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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address water quality protection challenges. Investment in capacity building through technical, financial
and managerial support, directly by consultation or through use of grant funds, is of critical importance.
Expanding the programmatic criteria for use of Section 319 Grants to address technical, managerial and
financial deficiencies, along with comprehensive asset management technical and funding support, will
advance local communities' ability to effectively carry out their role in partnership with federal
permitting, state program guidance and local surface water system operation. The current program
structure does not allow the use of these grant funds for MS4 permit compliance and consideration
should be given to allow for such use, specifically targeted to allow an exception for communities with
limited capacity to address water quality protection.

Recommendation: Develop a new construction grant program specifically for stormwater
projects, similar to the federal Municipal Construction Grants Program that funded the
construction of wastewater treatment plants.

A Stormwater Construction Grants Program, similar to the Municipal Construction Grants program that
funded the construction of wastewater treatment plants in the 1970's and 80's, could be developed to
serve as a much-needed jump start to investment in stormwater infrastructure/capital investment. Such
a program could likely be managed through existing SRF programs if new funding sources are identified.
However, funding stormwater management is less straightforward than funding construction of
wastewater treatment plants. The program components outlined below could help to avoid some of the
challenges of the original Municipal Construction Grants Program and better tailor a program to
stormwater management.

*	The program could require participants to demonstrate capacity or secure financial assurances to
show that they can fund ongoing O&M for grant-funded projects. The technical assistance model
recommended by this Task Force could be used to help evaluate and provide these assurances.

*	In many communities, the greatest capital investment need is related to the renewal and/or
replacement of existing stormwater infrastructure. However, communities have indicated a need for
help in prioritizing stormwater asset maintenance and replacement and estimating associated
costs.12 To help meet this need, the construction grant program could fund development of an asset
management plan (or require communities to have one in place that meets certain requirements) as
a first tier of funding for renewal/replacement projects.

*	The grant program could require, prioritize or set aside a separate "bucket" of funds for
regional/watershed projects that result in cost savings and greater environmental benefits and help
avoid conflicts associated with implementing different methods for stormwater management across
communities. Similarly, the program could prioritize cross-sector opportunities, such as partnerships
with transportation departments, that result in significant cost savings and/or bring additional
matching funds.

12 WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survey-Report-2019.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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*	The program should not require "shovel-ready projects" and should fund design, feasibility, and
other upfront costs, particularly for small and medium-size communities.

*	To further encourage participation of small and medium-size communities, particularly those that
are economically disadvantaged, the program could waive or reduce matching fund requirements. It
should also carefully evaluate the needs of these communities and set aside appropriate funds or
tailor the program to better meet their needs.

*	The program should fund a wide range of projects and prioritize projects that result in the greatest
financial, environmental, and social benefits. Water quantity projects (flood control and mitigation)
should be eligible and be prioritized in consideration of all benefits—not subordinated to water
quality projects.

*	Many stormwater projects result in multiple benefits, particularly green infrastructure projects. The
grant program could be linked to other federal programs that provide funds for investment in
projects or programs related to these co-benefits (e.g., public health, air quality, energy savings,
economic development). For example, for projects that result in specific co-benefits, related federal
grant programs could provide the recipients' matching fund requirements. This would incentivize
these projects and stretch public dollars toward meeting multiple goals. It would require research
and coordination across relevant programs. This could also be achieved, in part, through the
common application for relevant federal grant programs/agencies, as recommended by this Task
Force.

Recommendation: Require 10 percent of U.S. federal farm subsidies (all programs) to be
redirected toward stormwater/nonpoint impacts in the same watershed as the recipient farm.

Agricultural lands in watersheds throughout the United States are major contributors to water quality
impairments from nutrient, sediment and bacteria runoff from farms and fields. The agricultural sector
has made great strides in implementing best management practices on farms but these practices have
limitations. Additionally, many of the most effective practices require taking land out of production, at
the same time as worldwide demand for food grows. Federal farm subsidies total about $20 billion per
year. Dedicating 10 percent to stormwater programs would generate nearly $2 billion annually for
stormwater program funding. Limiting eligibility to programs within the same watershed would provide
a rational connection between the funding source and the benefitting watershed.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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4.0 Sufficiency of Funding

Evaluate whether sources of funding are sufficient to support capital
expenditures and long-term operation and maintenance costs necessary to
meet the stormwater infrastructure needs of municipalities.

Determining the extent of capital and long-term O&M costs necessary to meet the stormwater
infrastructure needs of municipalities in the United States is a challenging task. Many surveys and
studies have been conducted over the past 30 years, each with its own limitations. The surveys and
studies presented below were largely developed within the last four years and represent only a few
resources from the pool. However, these resources collectively indicate the following:

*	The needs are great and the funding gap is very wide—estimated to approach $10 billion annually.

*	There are no large-scale, comprehensive, nationally representative numbers on total stormwater
capital and O&M needs.

*	The most recent attempt to estimate the need on a national scale was conducted by the Water
Environment Federation's Stormwater Institute in 2018, with a survey of MS4 permittees that
determined the total annual funding gap for stormwater programs (MS4 compliance activities only)
to be $8.1 billion nationally.

*	Other existing surveys evaluated and summarized below have estimated needs ranging from:

o A combined $1.7 billion for the next five years and $3.3 billion for the next 10 years for 137
stormwater utilities in Florida alone.13

o An EPA-estimated total of $19.2 billion for the nation over five years.14

o $9.7 billion for capital improvement over 20 years for 67 stormwater utilities in the
southeastern United States.15

The limitations of these and other surveys are discussed below and point to a potentially significant
underrepresentation of total national need. Many communities have not been able to quantify their
long-term needs or quantifying existing spending /annual revenues, which limits the ability to fully
capture funding needs.

*	Needs specific to O&M are even less well captured and defined because O&M responsibilities in
many communities are passed to property owners or homeowner's associations where the

13	Florida Stormwater Association. 2018. Stormwater Utility Report. https://www.florida-
stormwater.org/stormwater-utilitv-reportl

14	U.S. EPA. 2016. Clean Watersheds Needs Survey 2012 Report to Congress EPA-830-R-15005.
https://www.epa.gov/sites/production/files/2015-12/documents/cwns_2012_report_to_congress-508-opt.pdf

15	WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survey-Report-2019.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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stormwater systems or treatment facilities (best management practices or stormwater control
measures) are located.

*	Revenue for established stormwater programs may be largely generated from taxes or user fees,
which can vary significantly across the country, and capital improvements may be more commonly
cash-financed than debt-financed.

*	In some communities, there is a moderate to significant gap between annual revenue and capital
and O&M needs, and lack of funding and financing is a significant concern and priority for
stormwater programs/utilities.

*	Public perception of water infrastructure, including stormwater infrastructure, varies widely across
the country and in each community. In some communities there is widespread support for investing
in the water infrastructure, even if this requires moderate increases in customer charges; other
communities oppose any increase in charges.

The Task Force has clearly identified the need for a national survey of stormwater needs that includes all
costs related to managing stormwater, from water quality to flood control. The American Society of Civil
Engineers, in coordination with the Water Environment Federation's Stormwater Institute, has been
preparing report cards on the nation's infrastructure since 1998 and in the next report card will add
stormwater infrastructure as a specific category. Until that time and lacking a national measure of the
need, the Task Force believes—based on the many existing surveys on stormwater funding needs—that
the funding gap is well into the billions of dollars per year and will continue to grow if things are left on
the current course.

In addition to a review of available surveys and estimates on a broad scale, Task Force members
developed illustrative case studies of stormwater programs in more than a dozen communities across
the country (Appendix II). While not meant to be statistically representative of stormwater programs
across the nation, these case studies highlight the funding challenges faced by both large metropolitan
communities like Atlanta, Chicago and San Diego and smaller communities like Coralville, Iowa; Griffin,
Georgia; and Washtenaw County, Michigan. In nearly all these communities, significant gaps exist
between current funding levels for annual O&M programs as well as capital investment needs.
Stormwater programs align their level of service with available funding, not typically with an asset-
management-generated, data-supported program ensuring adequate maintenance levels are achieved
and adequate investment is being made in renewal and replacement of stormwater infrastructure.

Some communities acknowledge that their current programs do not address the impact of more
intense, more frequent storms and floods. These case studies can be found in Appendix II.

There are many reasons the funding gap for stormwater infrastructure exists. While there are many
federal funding programs—including the revolving loan programs, WIFIA, the various Department of
Agriculture programs, and others—the total available falls well short of the need and access can be
challenging, especially for small and disadvantaged communities. Attracting private capital continues to
be challenging, as the expected return for third party capital is mismatched with the risk profile of most
stormwater projects. Without low-cost concessionary debt, there is no compelling desire for outside,
private capital to invest.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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The gap also does not appear to be related purely to affordability. Communities across the nation have
implemented local stormwater fees that, in isolation, do not create undue financial burdens on the
majority of their customers. Affordability is, however, an issue for lower-income segments of the
population across the nation: without a safety net to ensure they can get relief from rising water costs
(for all water including drinking water, wastewater and stormwater), it will be impossible to close the
gap with local fees alone.

Perhaps the biggest obstacle to closing the stormwater funding gap is the lack of political will to increase
revenues dedicated to stormwater investment at the local, state and federal levels. Without leadership,
stormwater infrastructure investment will continue to fall short of annual needs and future generations
will be burdened with failing stormwater systems.

A detailed summary of the resources and surveys evaluated to assess the funding gap is provided below.

4.1	American Support for Investments in Water Infrastructure (2019)

In February 2019, as part of the U.S. Water Alliance's Value of Water campaign, public opinion
researchers conducted a phone-based survey of 1,000 voters in 47 states (all but Hawaii, Oklahoma and
West Virginia). The goal of the campaign was to raise awareness of the importance of water and water
challenges facing the nation. This survey focused broadly on water infrastructure through the lens of
drinking water and wastewater infrastructure and did not include an explicit stormwater component.

Of the 1,000 respondents, 79 percent ranked rebuilding America's infrastructure as "extremely to very
important," which is consistent with information gathered during similar 2017 and 2018 surveys. In
2019, 83 percent of respondents rated the water infrastructure in their local communities as "very
good" or "somewhat good" (on par with 2016 responses, accounting for reported margin of sampling
error). However, only 49 percent of respondents rated the condition of the nation's water infrastructure
as "very good" or "somewhat good," while 36 percent believe it is "somewhat bad" or "very bad."

While public opinion of the condition of water infrastructure in their own communities remains positive,
nearly four in five respondents indicated that they support developing plans to rebuild America's water
infrastructure and support an increase in federal investment to do so. Of note, 80 percent of
respondents indicated that their drinking water and wastewater rates were affordable and would be
willing to pay a modest amount more to improve local water infrastructure. Additionally, two-thirds of
surveyed voters believe that investments in comprehensive upgrades, replacements and improvement
should be made today, rather than addressed over time as the need arises. The survey did not
distinguish between investments in capital improvements and O&M.

4.2	Black & Veatch Stormwater Utility Surveys (2016 and 2018)

National consulting firm Black and Veatch has been conducting biennial stormwater utility surveys for
over 25 years. The 2016 online survey included 74 participants from 24 states. The 2018 online survey

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included 75 participants from 21 states.16 Combined, the survey included local utilities that served
populations from 86 to 1.5 million people. Respondents to the 2018 survey have a median population
served of 110,500 people and 33,000 accounts. In 2018, 28 percent of respondents indicated that their
stormwater operations were governed as a stand-alone stormwater utility, while 23 percent were
combined with a department of public works and 20 percent each with a water and/or wastewater
utility or other entities.

In the 2016 and 2018 surveys, as well as many previous surveys, respondents cited funding or
availability of capital as the most important challenge to enhancing their utilities' stormwater
management. In 2018, 94 percent of respondents reported that more than 75 percent of their revenue
is derived from user fees. Additionally, survey results showed that the majority (87 percent, on par with

2016	and 2014 responses) of capital improvement projects are cash-financed, as opposed to debt-
financed.

Respondents' 2018 annual stormwater capital improvement program budget ranged from $1,800 to
$143.9 million, with an average of about $7.6 million. According to the 2016 survey, 88 percent of
respondents indicated that they do not have adequate funding to meet all their stormwater programs'
needs, while 85 percent of 2018 respondents indicated that funding was not adequate. This aligns with
survey responses to the same question from the 2010, 2012 and 2014 reports. Neither the 2016 nor the
2018 survey explicitly discussed funding and needs for O&M activities, although 2018 survey
respondents indicated that stormwater utility budgets generally do capture costs for inlet and outfall
maintenance and best management practice inspection and maintenance.

4.3 Clean Watershed Needs Survey 2012 Report to Congress (2016)

The EPA conducted its most recent Clean Watersheds Needs Survey (CWNS) in 2012 and published in
2016. The CWNS estimates the capital investment necessary to meet the nation's stormwater and
wastewater treatment and collection needs, based on Clean Water Act requirements. Water quality
improvement investments considered in the CWNS included stormwater management. This category
captured costs associated with the planning and implementation of structural and non-structural
measures to control runoff in Phase I, Phase II and non-traditional MS4s.

This voluntary survey captures needs across most states, Puerto Rico, the District of Columbia and U.S.
Territories ("states"). While the goal of the survey is to capture 20-year need nationwide, because states
had limited documentation to demonstrate needs over this longer timespan (most projects will be
completed within a 5-year period), most of the needs captured in the 2016 report only reflect 2012 to

2017	needs.

Information provided by the states captured needs for over 27,000 wastewater facilities and water
quality projects. Of the estimated $271 billion required to meet documented needs, an estimated $19.2

16 The following states did not participate in the 2016 and 2018 surveys: AK, AL, AR, AZ, CT, HI, ID, IN, LA, MA, ME,
Ml, MS, ND, NH, NJ, NM, NV, NY, Rl, SD, UT, VT, Wl, WV, and WY. The following additional states did not
participate in the 2018 survey: NE, OK, and MD. In 2018, 33 respondents represented three states, Florida (16),
Texas (10) and Colorado (seven).

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billion was for stormwater-related needs. This represents a 60 percent decrease from the 2008 CWNS,
but this decrease is due in part to lower participation in the 2012 CWNS. Three fewer states participated
in 2012, and seven states reported no needs in 2012, which accounted for $7.2 billion of the 2008
survey's needs. Additionally, EPA's estimate only included projects that had a "storm water quality
benefit" and thus did not include needs associated with flood control projects in the estimates. As a
result, states reported that this modification made it difficult to meet EPA's documentation criteria for
stormwater in 2012. Of the $19.2 billion for stormwater needs, 45 percent is attributed to conveyance
systems, 32 percent for the treatment of stormwater runoff (e.g., ponds, manufactured devices), and
the remaining 15 percent for low-impact development and green infrastructure projects.

Additionally, the CWNS only includes projects with site-specific solutions to known water quality
problems and detailed cost information. Needs associated with water quality problems without known
solutions and cost estimates were not captured.

4.4 Florida Stormwater Association Stormwater Utility Report (2016 and 2018)

In 1995, the Florida Stormwater Association (FSA) began performing biennial Stormwater Utilities
Surveys to provide stormwater program information to state and local government managers and policy
makers. The FSA provides questionnaires to the 67 counties and 410 cities in Florida. Of those 477
entities, FSA estimates, 165 local governments have established stormwater utilities. In 2016, 124
utilities responded to the questionnaire; in, 2018 FSA received 137 responses. In 2016, 88 respondents
(71 percent) cited user fees as their primary approach to revenue generation. In 2018, 91 respondents
(66 percent) reported the same. In both surveys, about 70 percent of respondents indicated that fees
were primarily based on impervious area.

Eighty-two entities in 2016 and 89 entities in 2018 reported that their stormwater operating budgets are
funded solely by their stormwater fees. The rest (42 in 2016 and 47 in 2018) indicated their budgets
were covered by fees and other "non-fees" including, but not limited to, ad valorem taxes, sales tax and
gas tax. The 2016 survey indicated that 44 percent of stormwater capital construction programs were
funded only by fees, while the remainder was funded by fees and non-fees. Responses were very similar
in 2018.

In 2016, 66 percent of respondents reported that their operating budgets are funded only through fees.
Of the 34 percent for which fees and other non-fee funds fund their operating budgets, 45 percent
reported ad valorem taxes as the source of non-fee revenues. Responses to these questions were nearly
identical in 2018.

The 2016 report identifies the annual average revenue generated by each entity's utility fee as $3.6
million, whereas the 2018 report lists the annual average as $3.9 million. Respondents reported a
combined projected capital improvement need of $1.7 billion for the next five years and $3.3 billion for
the next 10 years (per-utility average of $14 million and $35.1 million, respectively). This represents an
increase from 2016 reported total respondent needs of $1.4 billion (five-year need) and $3.1 billion (10-
year need). Respondents were also asked whether stormwater fee revenue was sufficient to meet
administration, O&M and capital improvement needs. In 2018, 33 percent of respondents indicated that
fees were sufficient to meet all or most needs, while 26 percent reported that fees were not adequate

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to meet urgent needs. In 2016, responses to the same questions were 39 percent and 37 percent,
respectively. Respondents were not given the option to indicate whether fees were not adequate to
meet non-urgent needs.

4.5	Georgia Stormwater Utilities Report (2017)

From August 2016 to February 2017, the University of North Carolina's Environmental Finance Center
and the Georgia Environmental Finance Authority surveyed 48 stormwater utilities in 27 Georgia
counties regarding stormwater fees. Of the 48 respondents, 23 reported collecting fees through utility
bills, while 20 reported collecting fees through property tax bills and five through stand-alone bills. Of
the participants, 31.2 percent indicated they apply unique multi-family residential fee structures. In
Georgia, flat fee structures are commonly used to apply fees for multi-family and single-family
residential properties. Lastly, 93.8 percent of respondents indicated that they charge an equivalent
residential unit (ERU)-based fee for non-residential properties, which is based on the amount of
impervious surfaces on a property.

4.6	Southeast Stormwater Association Utility Report (2019)

The Southeast Stormwater Association conducted its seventh biennial survey of stormwater utilities in
2019, capturing information from 103 respondents representing stormwater utilities from 136
jurisdictions in Georgia, South Carolina, North Carolina, Alabama, Tennessee, Florida and Kentucky.
Ninety-four percent of respondents reported generating revenue from a user fee, largely based on the
amount of impervious area on a property. Annual reported revenue generated by the stormwater utility
fee ranged from $32,000 to $71.1 million, with an average of $4 million. Average monthly utility rates
ranged from $0.62 in Alabama to $5.36 in South Carolina.

Across 67 respondents, the estimated total 20-year capital improvement need is $9.7 billion, with an
average of $144.8 million in need per respondent.

4.7	The Chesapeake Stormwater Network Select Results of the MS4 Needs
Survey (2016)	

In 2016 the Chesapeake Stormwater Network surveyed Phase I and Phase II MS4 permittees within the
Chesapeake Bay watershed (Virginia, Maryland, Delaware, West Virginia, Pennsylvania, New York and
Washington, D.C.) to identify funding needs. A total of 137 respondents provided input for the survey.
Seventy-three percent of respondents indicated that their stormwater program is somewhat (45
percent) or very (28 percent) underfunded. Respondents also cited resource limitations and scale of
permit requirements as the most significant challenges to permit implementation.

The majority (65 percent) of Phase I permittees responded that they have an approximate annual
budget of over $1 million. The remaining Phase I permittees indicated the following: 8 percent operating
on a budget of less than $25,000, another 8 percent operating on a budget between $25,001 and
$100,000, 5.4 percent operating on a budget between $500,000 and $1 million, and 13 percent unsure
of their operating budget.

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The majority of Phase II permittees (36 percent) indicated that they have less than $25,000 to
implement their programs. The remaining Phase II permittees indicated the following: 21 percent
operating on a budget between $25,000 and $100,000, 8 percent operating on a budget between $500
and $1 million, 7 percent operating on a budget between $100,001 and $500,000, and another 7
percent operating on a budget of more than $1 million, and 18 percent not sure of their budget
allotment.

4.8	Water Environment Federation MS4 Needs Assessment Survey Results
(May 2019)	

The Water Environment Federation's (WEF's) Stormwater Institute conducted a national survey of MS4
permittees in 2018 to identify permittees' information and technical resource needs and better
understand the challenges facing MS4 permittees. A total of 622 respondents represented 48 states and
Washington, D.C. The sample size was statistically significant and generally representative of the
distribution of MS4 programs across the United States, including municipal, non-traditional and state
department of transportation permittees. The survey determined the total annual funding gap for
stormwater programs in the MS4 sector to be $8.1 billion nationally.

Phase I and Phase II MS4 respondents cited lack of funding or availability of capital, aging infrastructure,
and increasing or expanding regulations as the most significant challenges to their stormwater
programs. Close to 50 percent of Phase I and II municipal permittees indicated that they do not have
enough money to meet program goals, and that a respective 52 percent and 136 percent annual budget
increase is needed. Respondents also indicated a need for more information on methods for securing
funding and financing. Specifically, respondents indicated needing additional information on "leveraging
additional sources of funding based on co-benefits."

WEF indicates that the number of MS4s with inadequate annual budgets may be underrepresented due
to unwillingness to answer questions that might only raise further questions about their budgeting
process or regulatory compliance.

4.9	Western Kentucky University Stormwater Utility Surveys (2013, 2016, 2018
and 2019)

Western Kentucky University (WKU) has been conducting a regular survey of stormwater utilities since
2007. The WKU team mines publicly available online data on stormwater utilities, in addition to
conducting phone surveys. The survey aims to identify as many stormwater utilities as possible within
the United States and Canada.

The number of identified stormwater utilities has been increasing in each survey. The 2013 survey
identified 1,417 stormwater utilities in the United States, compared to 1,583 in 2016, 1,681 in 2018, and
1,716 in 2019. The 2019 survey reported that 800 of these utilities fund their programs with ERU-based
user fees. These reported monthly fees have generally increased through the years from $4.57 in 2013
to $5.85 in 2019 (median of $4.75), even though the average impervious area based on the ERU has
varied. This is largely attributed to the application of tiered fees and the fee structure that is applied to
residential and non-residential properties.

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As previously stated, the Task Force believes, based on the many existing surveys on stormwater funding
needs, that a significant gap exists, well into the billions of dollars per year and left on the current
course, that gap will continue to grow.

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5.0 Existing Sources of Funding

Identify existing federal, state and local public and private sources of funding for
stormwater infrastructure and how funding for stormwater infrastructure from
such sources has been made available, and utilized, in each state to address
stormwater infrastructure needs.

Stormwater management at the local municipal level has changed significantly within the last 20 years
as discussed in earlier sections of this report. The following are some of the factors that have raised the
average cost of stormwater programs (adjusted for inflation) over what it was 20 years ago:

*	The increased use of green stormwater infrastructure for stormwater management

*	The maturation of many water quality programs and the increase in infrastructure maintenance
needs

*	The impacts of more intense rainfall

*	The necessity for resilience planning and implementation of initiatives

*	The realization that underground stormwater systems were reaching the end of their functional
lives, requiring massive rehabilitation and replacement programs

This cost increase necessitates an evaluation of existing sources of stormwater funding, as well as ways
to either further leverage existing funding sources or identify potential new sources of funding.

5.1 The Role of the Federal Government in Funding Stormwater Programs

To date, the role of the federal government has been to provide minimal funding for selected capital
projects, often with a significant match required and for targeted and limited programs, with availability
further limited by annual appropriations. For example, for flood resiliency support, federal programs
include Housing and Urban Development Hazard Mitigation Grants, Community Development Block
Grants, FEMA Pre-Disaster Mitigation Programs and Flood Mitigation Assistance, U.S. Army Corps of
Engineers (USACE) flood risk management studies and projects, and U.S. EPA loan programs, etc. Even
though these programs provide small contributions to the construction of capital projects, they do not
provide funding for the bulk of the stormwater needs: compliance requirements, infrastructure
operations and maintenance, and additional capital expenditures. In addition, most USACE flood risk
management funding is for large projects that typically do not address the stormwater needs of small
communities.

Existing funding has proven inadequate for current and anticipated future costs associated with proper
stormwater management. Certainly, it is not expected that the federal government should meet all
funding needs—but it has opportunities to provide leadership and increased funding to allow local
communities to better address stormwater management needs. The needed federal investment in

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stormwater infrastructure is similar to federal funding programs used in the past to begin construction
of our interstate highway system and upgrade wastewater treatment plants.

Ultimately, local communities committed to raising or implementing stormwater user fees or other
dedicated and sustainable funding sources to more realistic levels, in concert with the ability to
repurpose the various existing federal programs, could go a long way in solving existing problems. In
some cases, communities can manage and fund the local stormwater collection and water quality
program. The difficulty is to find funding for communities with:

*	Extreme events and large system flooding issues.

*	Lack of resources to meet compliance requirements, environmental standards or consent decrees
that go beyond typical water quality issues.

*	Operations and maintenance needs for stormwater infrastructure (treatment and collection).

*	Vast sections of very old and inadequate stormwater piped drainage systems. In many of these
cases sources of the problem exist outside the boundaries of the community.

5.2 Stormwater Funding—Types and Uses of Funds

In the face of increasing costs, communities across the United States have implemented a wide range of
approaches to fund stormwater programs and related capital projects—but few have the revenue
capacity or one-time influx of funds to support anything beyond small capital projects or ancillary
programs. Stormwater funding tends to fall into three categories:

*	Revenue—an ongoing stable and meaningful flow of funds, including taxes of various types,
franchise fees and stormwater user fees, as well as intermittent revenue from various special fees
and charges.

*	Capital financing—targeted capital funding for a specific project, such as state and federal grants,
state and federal loan programs, general obligation or revenue bonds, and other short or long-term
loans.

*	Other resources/approaches for funding stormwater management, including development by
others—new development and redevelopment creating stormwater infrastructure or partnership
approaches, other in-kind services or volunteer programs, approaches that can shift risk or delay
payment such as public-private partnerships, market-based solutions, and other innovative
approaches.

The following table (

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Table 1) provides a stormwater funding matrix that further outlines examples of stormwater funding
currently used by communities, along with advantages and disadvantages of each. Most communities
use more than one source of funding. The following sections further explain the sources and uses of
each type of funding.

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Table 1. Funding Type Matrix, including a Description of the Funding Source and Associated Advantages and Disadvantages.

Funding Source

Description

Advantages

Disadvantages

1.0 "Revenue-Based" Funding Sources used to pay on-going Operation & Maintenance and Debt Service of the Stormwater System

l.A Recurring, Sustainable Revenue Sources for On-going Stormwater Program Funding

• Provide regular, recurring revenues to fund both operating and capital related costs

Taxes/ General
Funds

Funds raised through taxes such as
property, income, and sales that are
paid into a general fund.

•	Consistent from year-to-year

•	Utilizes an existing funding system

•	There can be significant competition for funds;

•	Tax-exempt properties do not contribute;

•	System is not equitable (does not fully reflect
contribution of

stormwater runoff)

Taxes/ Dedicated (e.g.,
local option sales tax,
Gas Tax, drainage or
special assessment
district)

Funds raised through taxes such as
property, income, and sales that are
restricted, in part or in whole, for
funding stormwater costs.

•	Consistent from year-to-year but can vary
(e.g., changes in property values or rise and
fall with economic cycles)

•	Utilizes an existing funding system

•	Can be targeted for a specific purpose (e.g.
ongoing maintenance, capital, etc.)

•	May be competition for funds if not exclusively
restricted to stormwater;

•	May require approval by vote of the local legislative
body and public if a new tax

•	Often have a "sunset" clause resulting in stable
funding only for a specified period of time (e.g., 10
years)

•	Tax-exempt properties do not contribute;

System is not equitable (does not fully reflect
contribution of stormwater runoff)

Stormwater Utility User
Fee (Enterprise Fund)

A stormwater utility generates its
revenue through user fees and the
revenues from the stormwater
charges will go into a separate fund
(e.g. enterprise fund) that can be
used only for stormwater services.

•	Dedicated funding source

•	Directly related to stormwater impacts

•	Sustainable, stable revenue

•	Shared cost

•	Equitable apportionment of costs

•	Improved watershed stewardship

•	Addresses existing stormwater issues

•	All properties served pay fee

•	Feasibility study required for implementation, fee
structure, and administration of utility

•	Requires approval by vote of the local
legislative body, in some cases public vote
required

•	Perception by the public of a "tax on rain"

•	Public acceptance for a first-time fee is difficult

•	Some states have not yet allowed SW Utilities

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Funding Source

Description

Advantages

Disadvantages

l.B Intermittent Revenue

• To recover a portion of costs related to which fee is assessed

Fees

Revenue raised through charges for
services such as inspections and
permits.

Revenue raised through developer
related fees are one-time charges
linked with new development.

•	Specific permit and inspection fees allow for
more direct allocation of costs for services
provided

•	Fees can be set to fully recover cost

•	Certain kinds of fees can provide funding for
long-term maintenance

•	Addresses potential stormwater impacts
related to new construction

•	Not available for larger projects or system-wide
improvements

•	Developer impact fees may be an unreliable source
when development slows (due to market
downturns/contractions)

•	Requires administrative framework to assess and
manage

•	Legal limitations may constrict or restrict usage

Special Charges (e.g.,
impact fees, latecomer
fees, system
development charges,
special assessments,
surcharges on other
utilities)

A number of different fees that
attempt to shift certain program
costs to provide a better cost
causation match. Payees might be
other local programs, development
interests, other local government
programs, or parties requiring a
myriad of special services or
penalties.

•	Improves cost causation equity match

•	Allows special services to be paid for by
recipients

•	Provides additional funding in a manner
acceptable to the general public

•	Recovers the cost of negative impacts of
other activities on the stormwater system

•	Level of funding is unpredictable and can vary
significantly year to year

•	Can be hard to administer

•	May be seen as discouraging development or
other desirable activities

•	May be difficult to price accurately

•	While some sources may fund certain O&M
(e.g., staff time), others, such as impact fees
and SDCs are generally restricted to capital
funding only

l.C Capital Financing Sources (Financing Vehicles, require repayment)

• Borrowing for capital projects

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Funding Source

Description

Advantages

Disadvantages

Bonds (Debt
Obligations)

Bonds are not a true revenue
source, but are a means of
borrowing money to finance capital
projects. Bonds are generally issued
with a term less than the expected
useful life of the assets financed.
Bonds may be general obligation
(GO) bonds backed by taxes, or
revenue bonds, backed by a secure
revenue source (most commonly a
stormwater user fee). "Green"
bonds are a designation of bonds
dedicated to environmentally
friendly projects, including clean
water projects.

•	Existing sources available for
stormwater-related funding

•	Can support construction-ready projects

•	Allows a community to complete large
projects sooner than revenue cashflows
become available, or a significant
stormwater capital program more quickly

•	Spreads the cost of the capital project over
time, allowing beneficiaries of the
improvements to pay over the life of the
bonds, rather than current property owners
paying up front.

•	Mitigates the risk of construction cost
escalation

•	Accelerates ability to address important
health and environmental issues

•	May require approval for each issuance, in
some cases, voter approval

•	Requires access to funding for full repayment of
principal borrowed

•	Interest costs can vary but will add to total project
cost

•	Requires dedicated repayment revenue stream

•	May require design-level documents to be
prepared in advance of debt funding

•	Cannot be used to fund O&M if they are tax
exempt bonds.

•	Will require additional funding for costs of
issuance

•	May require significant administrative preparation
to issue and for post compliance activities and
disclosures.

Loans (Debt Obligation)

Low-interest loans, for example the
SRF loans, may be secured, and are
generally used for planning and
capital
projects.

•	Existing sources available for
stormwater-related funding

•	Offers low- or no-interest financing

•	Loan interest loan programs may offer ease of
issuance relative to public offerings

•	One-time source of funds

•	Requires full repayment of principal borrowed

•	Administrative requirements can be time-
consuming

•	Loan interest loan programs may come with
inflexible mandates and restrictions

l.D One-time Sources

• Generally used for capital projects

Grants

State, federal, local and non-profit
grants provide additional funding for
water quality improvements.

•	Existing sources available for
stormwater-related funding

•	Does not require repayment

•	Competitive

•	Typically, one-time, project- specific, or time-
constrained funds

•	Often requires a funding match

•	Does not fund post-project O&M

•	Matching grant requirements and project needs
difficult

2.0 Other Resources/Approaches for Funding Stormwater Management

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Funding Source

Description

Advantages

Disadvantages

Public-Private
Partnerships (P3)/
Alternative
Service Delivery
(ASD)

Contractual agreement between a
public agency and a private sector-
generally used for capital projects.
Partnering with private enterprise
can expand access to resources and
capital and offer better economies
of scale. P3/ASD shifts both risks
and duties from the traditional
procurement and project
management context Examples
include: Design/Build,
Design/Build/Operate/Maintain/Fin
ance, Pay-for-Performance (also
sometimes referred to as Pay-for-
Success), etc. May include private
financing, or a combination of public
and private financing.

•	May be structured to require minimal to no
initial cash outlay for public sector, assuming
the private sector partner is providing
financing

•	Efficiency through bypassing bureaucracy or
economies of scale

•	Flexibility & creativity of project approach,
new technology adoption and
contracting/procurement

•	Access to flexible & creative private sector
financing

•	Significantly leverages public resources

•	Draws on private sector expertise

•	Enables transfer of compliance from one
development to another

•	Partnerships can be with not-for-profit
entities

•	Considers a project's full lifecycle, potentially
including O&M

•	Risk is shared with or passed entirely to
private entity

•	A local revenue source is needed to fund the
partnership

•	May be structured so as not to require new
funding; may rely on underlying public revenue
stream (e.g. user fees, taxes, etc.)

•	May require enabling legislation

•	Substantial education and socialization is required
to manage public perceptions related to loss of
control and escalated costs

•	Initial financing costs inherent within P3/ASD may
be higher than municipal debt.

•	A lack of public agency experience may
necessitate the need for additional resources to
complete a successful contract negotiation

Private

Development

Sites

Private sites build distributed
stormwater infrastructure (e.g. Low
Impact Development, BMP's,
conveyance, etc.) that contributes to
the overall municipal goals OR
contribute funding in lieu of
construction. Usually required by
local ordinance or conditions of
approval OR set up as a development
impact fee. The proper construction
and ongoing maintenance of these
sites constitutes a major stormwater
expenditure of significant
importance.

•	When well-regulated and inspected these
structures and systems are the first, and most
important line of defense against flooding,
erosion and pollution

•	Inspection and enforcement costs are
comparably low but with significant return on
investment

•	Capital expenditure and permitting costs are
borne by private development

•	Often required by regional NPDES permits and
enforced by municipalities

•	Political will, budget, and legal capability to enforce
long-term maintenance, and sometimes initial
construction standards may be lacking

•	Funding is only triggered when regulated
development occurs, which can be hard to plan
around and predict - particularly in a low
investment environment or with regulations that do
not capture the majority of development and
redevelopment activities

•	Development may not happen in areas of greatest
need in watershed/community

•	Additional education of Public knowledge may be
required

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This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or approved by the chartered EFAB, and does

not represent EPA policy.

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Funding Source

Description

Advantages

Disadvantages







•	Impact of such programs is hard to measure unless a
high percentage of the watershed has been
constructed with modern requirements

•	Distributed infrastructure may not be efficient in
treating and managing SW flows

•	Ensuring O&M is difficult and requires municipal
resources

•	Development impact fees requires robust needs
analysis and nexus findings (could also be an
advantage)

Volunteer
Programs

In-kind initiatives that can help
support stormwater priorities

•	No cost to stormwater program

•	Can help increase public awareness

•	Some not-for-profits come trained and ready
to work

•	Can bolster public support for a user fee

•	Limited impact from overall revenue perspective

•	Requires coordination, training and supervision

Coordination with
other Municipal
Departments and
State Agencies

Synergize with other city
departments, agencies, etc. to
leverage available community funds
for stormwater needs

•	Eliminate duplication of effort

•	Move toward a "water agency" that can
integrate water as a single resource

•	Allows easier/quicker response for
emergencies

•	Multiple funding or resources may be
harmonized; the "whole being greater the
sum of the parts"

•	Transportation projects can add SW elements
for marginal costs (sometimes)

•	State DOTs right of way limitations often
compel them to partner with municipalities to
achieve SW goals

•	Stormwater may be seen as a secondary priority
behind water and wastewater or public works focus
on roads

•	Can lose ability to react to stormwater needs if
equipment and manpower is not dedicated

•	May require additional education of personnel or
additional resources with stormwater expertise to
make stormwater decisions

•	Disparate-agency partnerships can be difficult to
manage

•	Mixing funding sources (particularly with grants) can
be challenging

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This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or approved by the chartered EFAB, and does

not represent EPA policy.

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Funding Source

Description

Advantages

Disadvantages

Market-Based
Solutions

The off-site provision of required
stormwater controls on another site,
or in another way, that is seen as
more cost effective to a property
owner or developer, but equally
effective in attainment of the
regulatory standard.

•	Creates cost efficiencies in placement of
stormwater controls

•	Can allow for aggregation for better overall
control and treatment

•	Can shift and target controls to more critical
locations

•	Can be complex to administer

•	Requires clear and enforceable policies on
ownership and maintenance

•	Markets may be not be initially viable and may need
to be jumpstarted with local funding

Newer Innovative
Approaches

A wide variety of approaches that
seek to exploit unique or unusual
funding sources: sponsorship of
stormwater or green infrastructure
sites, adopt-a-road advertising, tax
increment funding, use of private
land for public infrastructure, shared
right-of-way, seed money and
expertise, leveraging user fee
credits, philanthropy, etc.

•	Can provide funds at little cost

•	Can motivate the private sector through name
recognition

•	Can provide good return on seed money
investment when paired with private actions

•	Can be hard to administer and explain

•	May require opinions and analysis on legality

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5.2.1 Revenue-Based Funding Sources Used to Pay Ongoing Operation and
Maintenance and Debt Service of the Stormwater System

The majority of ongoing stormwater program costs must be funded with revenue from dedicated
recurring sources, making revenue-based funding the "backbone" of stormwater funding. Revenue-
based funding tends to fall into two broad categories: recurring, sustainable revenue sources and
intermittent funding.

5.2. J. J	Recurring, Sustainable Revenue Sources

Almost all activities undertaken in a stormwater program are ongoing (excluding capital costs such as
construction) and therefore must have ongoing, stable, dependable sources of revenue. Activities that
require recurring, sustainable revenue include ongoing services to plan, rehabilitate and maintain the
stormwater system, conduct programs to meet regulatory requirements, and accomplish a variety of
ancillary responsibilities related to stormwater management.

5.2.1.1.1 Taxes/General Funds

Taxes (of several types) are by far the largest source of revenue for local governments. Such taxes,
unless dedicated, are placed into a local government's "general fund." While the types of taxes
assessed, and the proportion of revenue generated from each, vary from state to state, the bulk of local
government revenue most commonly comes from property tax and income tax assessments. This is true
even though communities are increasingly looking to other revenue sources such as stormwater utility
user fees.

*	Real estate/ property taxes, also called ad valorem taxes, are charged to property owners as a
percentage of the assessed value of real estate or personal property. They are administered by local
governments and require voter approval. Property taxes are an important form of revenue for local
governments; they are often used as a funding mechanism for parks and open space measures.

*	Individual income taxes, also called personal income taxes, are assessed at the state and federal
levels (and, in some places, also at the county or municipal levels).

*	Specialized taxes can also be levied on a large number of parameters, including property transfer,
occupancy, gambling, estate, motor vehicle sales and licensing, etc.

The primary advantage of using general fund taxes to fund stormwater programs is that they can
provide a reliable (but fluctuating) revenue stream. They are also common and well understood.
However, there is significant competition for such funds, with most communities finding it difficult to
cover all general fund activities (e.g., police, fire, streets, general government) with available funding. As
a result, communities often find that stormwater programs are prioritized lower than other municipal
needs, and thus risk losing funding from year to year unless there is a dedicated source of funding for
the stormwater program. Another disadvantage is that the use of general fund tax revenue as a
stormwater funding source raises equity issues, as system revenue recovery generally bears no relation
to use of, or benefit from, a stormwater system. This causes an inequity between the level of service
provided and the cost property owners incur. In addition, tax-exempt properties do not pay general

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This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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fund taxes, causing further inequity as the costs they incur must be recovered with revenue from other
properties.

5.2.1.1.2	Taxes/Dedicated

Beyond general fund taxes, many communities use dedicated taxes to fund stormwater program costs.
These may take the form of dedicated sales taxes, motor fuel taxes or special assessments.

*	Local sales taxes are often add-ons to state general sales and use taxes. They may also exist where
there is no state sales tax. Depending on state constitutions, statutes and home rule traditions, most
local governments must seek voter approval to levy local sales taxes. State authorization processes
vary. States may give approval to all counties or communities or limit authorization to specific
localities. Local taxes are usually limited to a specified time period (i.e., a sunset provision) or a
dollar collection total, and are generally dedicated to a specific use. The dedicated revenue stream
may be used for operations and maintenance costs, to back local general obligation or revenue
bonds, or to pay for a specific stormwater program directly.

*	Motor fuel taxes are imposed at the state and federal levels and are levied on gasoline and other
fuels. All 50 U.S. states and the District of Columbia assess gasoline taxes. State gasoline tax rates
generally range from 14.65 cents to 58.7 cents per gallon.17 State and federal motor fuel tax
revenues are typically dedicated to highway construction and maintenance. Revenues from state
and federal motor fuel taxes could be earmarked to fund stormwater infrastructure related to
roadways, though competition for such funds is fierce—roadway resurfacing and repair are normally
the top priority.

*	Special assessments or special taxing districts or service/ drainage districts are recurring
surcharges levied by local jurisdictions on subgroups of the population or even the entire
population, in the case of districts that cover the entire community. Some localities levy them in the
form of taxes dedicated to stormwater management; others levy them as fees. The group paying the
recurring charges receives benefits from a stormwater service or improvement not enjoyed by
others in the area. For example, if a community wants to finance regional stormwater
improvements, residents within the protected area or the contributing area could be charged a
special assessment. Special assessments are generally charged by local governments and authorized
by local ordinance. They are often barred by legislation from use by some states. Special
assessments are used to fund water works systems, sanitary sewer systems, installation or repair of
water and sewer service lines, flood protection projects, and other purposes.

5.2.1.1.3	Stormwater Utility User Fees

Stormwater management resembles drinking water and wastewater utilities far more closely than
municipal responsibilities such as police, schools and roadway maintenance, in that the cost recovery for
utility services that are provided can be closely aligned with the service demands of the users.

17 As of 2018; excludes the federal excise tax of 18.4 cents per gallon (https://taxfoundation.org/state-gas-tax-
rates-iulv-2018/).

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This has led to the concept of a stormwater utility user fee. A stormwater user fee is similar to a
wastewater user fee in that it is developed to recover the costs of the stormwater program based on
each property's estimated use of the stormwater system. The first user stormwater fee systems
appeared in the United States in the mid-1970s, and their apparent success in generating significant,
sustainable revenue while keeping the typical homeowner's fee below a critical reactionary level led to
many other communities to follow suit. Local water quality and flood control agencies/districts or
utilities are typically responsible for designing, assessing and collecting user fees (or taxes, as noted
above) based on a property's contribution to the stormwater management system. Today there are
about 1,760 stormwater enterprise funds (stormwater utilities) employing user fees to fund their
programs and to fund revenue bonds for capital construction.

A stormwater user fee falls into the municipal revenue generation mechanism called a "service charge."
Service charges are not established
simply to generate general fund
revenue, but must be tied to the
objectives of a specific program to
which they are associated. A
stormwater utility generates its
revenue through user fees, and the
revenues generated from the
stormwater user fees is placed in a separate fund—called an enterprise fund—that can normally be used
only for stormwater services. Stormwater user charges are designed to provide a nexus between the
user fee and the service provided. As such they differ from taxes.

The amount each rate payer is charged must be related to the "use" of the system (rational nexus),
which can be interpreted as either direct use through runoff contributions or use through protection
from flooding of the property and streets by local stormwater program efforts. When a forested or
grassy area is paved, a greater flow of water (runoff) is placed on the drainage system. This is the
demand. The greater the demand (i.e., the more the parcel of land is paved or otherwise covered with
an impervious surface), the greater the user fee should be.

While there are similarities between a stormwater utility and water/wastewater utilities, a stormwater
utility differs from drinking water and wastewater utilities in several key ways:

*	There is no way to remove or discontinue services for non-payment, as long as the physical property
exists.

*	The stormwater management service is provided within the entire jurisdiction regardless of whether
one or more property deems it necessary or not. This is because stormwater management is
performed as a community-wide level of service and not distinctly as an individual property level
service (though mandatory water and wastewater service makes this difference less of a distinction).

*	The demand placed on the system can only be roughly measured or approximated, as it is not
possible to directly measure stormwater flow.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

Stormwater user fees provide the greatest
opportunity to provide communities with
sustainable, recurring revenue to fund
stormwater needs.

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* The actual service rendered to a particular property is often difficult to quantify without the use of a
reasonable and consistent approximation approach.

Despite these differences, the utility concept can be a viable and flexible revenue generation approach
to stormwater funding. According to the 2019 version of an annual survey by Western Kentucky
University, at least 1,716 stormwater utilities currently exist across 40 states and the District of
Columbia, serving a total population of nearly 115 million (35 percent of the U.S. population).18 The
authority (enabling legislation) to implement such an approach varies from state to state, and even from
municipality to municipality, depending on the details of state-granted authority or home rule
requirements. Of the 10 states that do not have utilities, three are either conducting feasibility studies
or exploring changes in state law to allow implementation of stormwater utilities.19

Even in utilities that have a dedicated user fee, which can be used to support debt service associated
with capital program financing, while a Black and Veatch 2018 biennial survey reports that most
responding stormwater utilities (87 percent) use cash financing instead of long-term debt financing for
funding their capital program investments.20 This indicates that stormwater utilities seldom use the
capital markets to augment their financial capacity, which can delay needed upgrades and/or affect the
pace of compliance programs. Further, only 15 percent of respondents indicated that utility revenue is
adequate to meet all needs. The median annual revenue per capita reported in Black and Veatch's
survey was $54, with the maximum annual per capita revenue reported being $200. WKU does not
provide annual revenue details for all utilities surveyed, but found roughly $2.2 billion in utility fees,
with 20 percent of that figure coming from one utility: Chattanooga, Tennessee. More research is
needed to provide a full accounting of all public revenue that is raised toward stormwater management
and compliance.

State statutes may prevent the creation of a stormwater user fee without a ballot measure or enabling
state legislation. This is discussed in detail later in the report.

5.2. J .2	Intermittent Funding

While it is imperative that communities have in place one or more recurring, sustainable funding
sources, there are other types of funding that while more intermittent, can provide some additional
benefit and help recover certain costs of stormwater management.

5.2.1.2.1 Special Fees

A growing common practice is the use of fees and specific charges to help fund services by local and
state government. Special fees tend to focus on specific beneficial government services, while charges

18	Campbell, C. W. 2019. Western Kentucky University Stormwater Utility Survey 2019.
https://digitalcommons.wku.edu/seas faculty pubs/1

19	Campbell, C. W. 2019. Western Kentucky University Stormwater Utility Survey 2019.
https://digitalcommons.wku.edu/seas faculty pubs/1

20	Black & Veatch. 2018. "Stormwater Rate Structure and Billing." In 2018 Stormwater Utility Survey.
https://www.bv.com/sites/default/files/2019-

10/18%20Stormwater%20Utilitv%20Survev%20Report%20WEB O.pdf

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approved by the chartered EFAB, and does not represent EPA policy.

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are defined more broadly in terms of receiving special benefit or service. "When certain services
provided especially benefit a particular group, then governments charge fees on the direct recipients of
those that receive benefits from such services." Often the size or level of the fee is derived from the
actual cost of such provision. "However, many governments provide subsidies to various users for policy
reasons, including the ability of residents or businesses to pay. Well-designed charges and fees not only
reduce the need for additional revenue sources but promote service efficiency."21

Special fees tend to fall into several categories:

*	Fees for development-related services such as plan review, inspection, environmental permit fees,
septic system inspections and other similar types of services.

*	Fees to defray the cost of specific government services such as specialized disposal (e.g., oil),
recycling, tolls, certification, bond issuance, licenses, etc.

*	Fees for government services or land, such as franchise fees, or indirect cost allocations from other
enterprise funds for general governmental purposes.

Such fees focus costs on recipients of special services and not the general public, and they address
potential stormwater impacts during the critical construction phase. On the other hand, it is often
difficult to set such fees at a level that recovers the full cost of the activity necessitating the fee. In
addition, revenues from such fees are intermittent and, thus, when that activity is not occurring no
funds are received even though local government costs (such as personnel) may be stable and ongoing.

5.2.1.2.2 Special Charges

Special charges are often not distinguished from fees in that they tend to be related to specific
government services or benefits. They do tend to be more complex or related to higher government
functions. Examples include connection fees, impact fees, special assessment or improvement districts,
tax increment funding, developer extension fees, in-lieu fees, latecomer charges, and other exactions.

Connection Fees

Connection fees, also called hookup fees, are typically charged to property owners when they connect
with existing municipal drinking water and wastewater treatment facilities. But they could be used for
stormwater as well. Connection fees are generally levied by local governments or county governments.

Impact Fees

Impact fees are often assessed on the construction of new buildings. Local governments and county
governments levy impact fees. The revenues are used to pay for improvements to services and
amenities for the occupants of new development (including expansions of police and fire stations,
wastewater and water supply systems, parks, libraries, and schools) and the building of new roads. In
addition, impact fees are often assessed based on the projected environmental impacts of a
construction project, with their revenues used to mitigate those impacts. The drawback of impact fees is

21 Government Finance Officers Association. 2018. "Establishing Government Charges and Fees."
https://www.gfoa.org/establishing-government-charges-and-fees

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approved by the chartered EFAB, and does not represent EPA policy.

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that they can only be used to improve an adequate stormwater system in the face of increased demand,
and many systems cannot be shown to be adequate. As well, they typically have sunset provisions.

Exactions

Exactions, also called proffers, are conditions or financial
obligations imposed on developers to aid local governments
in providing public services needed to support new
developments. They are administered by local governments.

Exactions can take a number of different forms. They can
include financing of existing infrastructure facilities or
infrastructure improvements; donations of in-kind services;
and donations of land, water and wastewater lines, and road
and parking facilities. Exactions can also take the form of
impact fees paid in lieu of the types of donations described
above. Exactions allow more flexibility than strict impact
fees because they are not required to be financial
contributions. They may be offered voluntarily by
developers; local governments often negotiate them with
each developer. Most localities use exactions in some form.

Some localities assign building permits competitively based
on the level of exactions offered by different developers.

Special Assessments

Special assessments are recurring surcharges levied by local
jurisdictions on subgroups of the population. Some localities
levy them in the form of taxes; others levy them in the form
of fees. The sub-group paying the recurring charges receives
benefits from a stormwater service or improvement not
enjoyed by others in the area. For example, if a community
wants to finance stormwater quality improvements that
contribute to lake cleanup, residents with waterfront
property could be charged a special assessment. Special
assessments are generally charged by local governments and
authorized by local ordinance. Special assessments are used
to fund water works systems, wastewater systems,
installation or repair of water and wastewater service lines,
stormwater and flood protection projects, and other
purposes, and are sometimes used in conjunction with a
neighborhood development to fund the construction and
ongoing maintenance of a stormwater detention pond or water quality feature.

Case Study: Five San
Francisco Bay Area
Voter-Approved Fee
Measures

Five small- to mid-sized
municipalities in the San
Francisco Bay Area put
new stormwater fee
structures out for voter
approval in 2018 and 2019
(with mixed results). Each
municipality followed a
similar approach including
developing a
comprehensive needs
study or master plan,
conducting a scientific
survey of the community's
priorities and willingness-to-
pay, and executing a
community outreach and
education process aimed
at increasing awareness
regarding local flooding;
storm drainage
infrastructure operations,
maintenance and capital
improvements; and water
quality.



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Special Assessment or Improvement Districts

Another form of local fee comes from the creation of a special assessment or improvement district. In
this case, a district is designated to need stormwater management upgrades—typically green
infrastructure or low-impact development—as part of a broader economic development strategy. The
district then creates a special tax assessment that is paid for by the property owners within the district's
geographic boundary. State and local laws differ on how these districts are created and voted into
existence, what funds are acceptable to be assessed, and how often assessments can be billed. These
assessments may be a one-time or ongoing assessment depending on their purpose. One-time
assessments tend to be raised for capital construction simultaneous to a broader economic
development process. Ongoing assessments may pay for capital construction, administration of the
entity in charge of governing the district, and operations and maintenance of district-owned projects.
Most special assessment districts are subject to periodic renewal based on a vote by their members;
some are mandated by state law to have a sunset clause (e.g., five, 10, 20 years).

Following are some of the advantages and disadvantages of Special Assessment or Improvement
Districts:

*	Advantages:

o Improve cost causation equity match,
o Allow special services to be paid for by recipients.

o Provide additional funding in a manner acceptable to the general public,
o Recover the cost of negative impacts of other activities on the stormwater system.

*	Disadvantages:

o Funds flow is not generally predictable and steady,
o Can be hard to administer.

o May be seen as discouraging development or other desirable activities,
o May be difficult to price accurately.

o Typically, cover staff time only—not funding for operation and maintenance or capital
improvements.

o Typically, cannot be used as leverage for raising debt capital.

5.2.2 One-Time Funding Sources for Financing of Capital Projects and/or Other
One-Time Initiatives

The use of one or more recurring funding sources such as user fees and charges are necessary for any
sustainable stormwater program. However, there are other types of funding sources including debt
financing, grants, and other sources that are available to communities, more and are more conducive to
funding of capital projects and/or help fund special capital program initiatives.

Repository of Funding Sources: The Task Force worked with the EPA to assist in developing a database
of existing funding sources. Sources of funding at the federal, state and local levels as well as private

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This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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funding were compiled, to the extent possible. The results of the effort are found in Appendix III. While
the database should not be construed to be comprehensive, it is an extensive database and the Task
Force feels it is mostly complete as it relates to federal funding sources. The sources identified at the
state, local and private level should be considered representative of the types of funding that may be
available. This database includes multiple Federal grant programs that may be available to stormwater
programs, through EPA, the US Department of Housing and Urban Development (HUD), US Department
of Agriculture (USDA) Rural Utility Service (RUS), and other agencies.

This funding sources database may be available to communities that are interested in examining
potential sources of funding primarily for their stormwater capital programs.

5.2.2. J	Capital Financing Sources (Financing Vehicles, Require Repayment)

Debt financing, with either short-term or long-term amortization, is an important capital financing
instrument that is available for stormwater capital program just as it is for the drinking water and
wastewater sectors.

Use of these debt financing instruments for capital
program funding requires dedicated, recurring, and
sustainable revenue source(s) for the repayment of
principal and interest associated with the debt
financing. Therefore, it is important to recognize
that the capital program debt financing funding
source is not just an [alternative] for recurring
sources of revenue but rather a valuable complement for funding capital infrastructure investments.

Debt financing mechanisms can greatly help enhance a community's ability to complete large capital
projects that would not otherwise be possible with just limited cash resources (whether generated
through user fees, taxes, or other sources), and enable a community to plan and execute a larger capital
program. Long-term financing of capital projects provides the additional benefit of spreading the costs
of projects over the life of the asset, with the principal and interest paid by those who benefit from the
project.

Following are the primary types of capital financing available to communities for stormwater capital
program management.

5.2.2.1.1 Bonds

"Municipal bonds are debt securities issued by states, cities, counties and other governmental entities
to fund day-to-day obligations and to finance capital projects" including stormwater projects.

"Generally, the interest on municipal bonds is exempt from federal income tax. The interest may also be
exempt from state and local taxes" in some states. General obligation bonds and revenue bonds are the
most common types of municipal bonds. "General obligation bonds are issued by states, cities or
counties and not secured by any assets. Instead, [they] are backed by the 'full faith and credit' of the
issuer, which has the power to tax residents to pay bondholders. Revenue bonds are not backed by
government's taxing power but by revenues from a specific project or source," which could include a

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Debt financing mechanisms can
greatly help enhance a
community's ability to complete
large capital projects that would
not otherwise be possible.


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Green Bonds

"A green bond is a bond
whose proceeds are used to
fund environment-friendly
projects...Green bonds
provide investors with a way to
earn tax-exempt income with
the benefit of personal
satisfaction, knowing that the
proceeds of their investment
are being used in a
responsible, positive manner.
The issuers of green bonds also
benefit, since the green angle
can help attract a new subset
of investors, namely younger
investors, whom the issuers can
profit from over an extended
period vs. a base of older
investors...The first entity to
issue green bonds was the
World Bank, which began the
practice in 2008 and has since
issued over $3.5 billion in debt
designated for issues related
to climate change. Ginnie
Mae and Fannie Mae have
also issued mortgage-backed
securities with the 'green'
label, as has the European
Investment Bank."

stormwater enterprise fee. "Some revenue bonds are 'non-
recourse/ meaning that if the revenue stream dries up, the
bondholders do not have a claim on the underlying revenue
source."22 "A 'double barreled' bond is a municipal bond in
which the interest and principal payments are pledged by two
distinct entities—revenue from a defined project and the
issuer and its taxing power."23

An advantage of bonding is that projects can be constructed
earlier and more rapidly; as well, the payment for the capital
project better matches the life of the project, with newer
residents participating in the payment according to their
longevity within the municipality. Disadvantages include the
potential to build up a large debt balance (limiting investment
to meet other stormwater needs), the technical and legal
requirements to obtain bonds, the limitations on bond
capacity within a local government, the potential need for
voter approval, and often the limitations on the use of the
funds to capital construction but not the full suite of life-cycle
costs.

There are many variations on the two general types of
bonding, including anticipation note s, asset-backed securities,
moral obligation bonds, special assessment bonds, and tax
increment bonds.

5.2.2.1.2 Loans

There are a few Federal, State, and private loan type funding
mechanisms —many of them originally targeted toward water
and wastewater programs— that can be leveraged for local
stormwater programs. Relative to borrowing in the bond
market, Loans can often provide a lower cost debt financing as
under special circumstances, Loans can be structured to
include features such as zero interest, very low interest, or
even in some cases principal forgiveness. Some of the loan
programs are targeted at "green" objectives and programs.

In this section, an overview of the following types of loan programs are discussed.

* Clean Water State Revolving Fund (CWSRF) and Drinking Water State Revolving Fund (DWSRF)

22	U.S. Securities and Exchange Commission, n.d. "Municipal Bonds." https://www.investor.gov/introduction-
investing/basics/investment-products/municipal-bonds

23	Chen, J. 2019. "Municipal Bond." Investopedia. https://www.investopedia.eom/terms/m/municipalbond.asp

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*	USDA Water and Waste Disposal Loan and Grant Program

*	Water Infrastructure Finance and Investment Act (WIFIA) Loan Program

*	State Based Loan Programs

*	Private Investments

CWSRF: One of the most commonly used loan programs in the wastewater sector is the CWSRF
loan. Under Title VI of the 1987 Clean Water Act, states receive federal monies to capitalize CWSRF
loan programs. Through CWSRF programs, loans are made to communities to provide low-cost
financing for a wide range of different projects

All 50 U.S. States and Puerto Rico
operate CWSRF Programs.

to protect water quality. Examples of activities
funded with these loans include nonpoint-
source pollution control, watershed protection
and restoration, estuary management, wetlands

restoration, brownfields remediation, and improvements to municipal wastewater treatment
infrastructure. Loans are made at low interest rates (0 percent to market rate) for terms of up to 20
years. In addition, states use CWSRF money to repurchase debt to get these loans to 30 years. States
may set the criteria for determining which municipalities can access the loans each year. All 50 U.S.
states and Puerto Rico operate CWSRF programs. Some CWSRF and Drinking Water State Revolving
Fund (DWSRF) loan programs make short-term loans for planning, design and initial construction in
localities that may later receive long-term CWSRF and DWSRF loans. In addition, state revolving fund
loans may be used to pre-finance other federal or state drinking water loans or grants.24

USDA Water and Waste Disposal Loan and Grant Program: This program "provides funding for
clean and reliable drinking water systems, sanitary sewage disposal, sanitary solid waste disposal,
and storm water drainage to households and businesses in eligible rural areas...Funds may be used
to finance the acquisition, construction or improvement of: drinking water sourcing, treatment,
storage and distribution; sewer collection, transmission, treatment and disposal; solid waste
collection, disposal and closure; and stormwater collection, transmission and disposal."25

WIFIA: WIFIA is the latest federal loan program administered by EPA for eligible water, sewer, and
stormwater infrastructure projects. The program funds development phase activities,
construction/reconstruction/rehabilitation/replacement, acquisition of real property or interest in
real property, environmental mitigation, construction contingencies, and equipment acquisition;
capitalized interest necessary to meet market requirements, reasonably required reserve funds,
capital issuance expenses, and other carrying costs during construction. Applicants must submit a
letter of interest, and based upon several criteria, EPA invites qualified projects to apply for the
WIFIA loan.

24	U.S. EPA. 2019. "Learn About the Clean Water State Revolving Fund (CWSRF)."
https://www.epa.gov/cwsrf/learn-about-clean-water-state-revolving-fund-cwsrf

25	U.S. Department of Agriculture, n.d. "Water & Waste Disposal Loan & Grant Program."
https://www.rd.usda.gov/programs-services/water-waste-disposal-loan-grant-program

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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*	State Based Loan Programs: There are also many state-based loan programs with a variety of
objectives and requirements. For example, the Georgia Fund Loan Program currently "supports
water, wastewater, and solid waste infrastructure improvements...[with] loans available at a low-
interest rate for a maximum of 20 years."26

*	Private Investments: Private investment can take the form of loans and/or other financial assistance
originating from sources other than commercial banks and/or finance companies. Sources of private
investment can include, but are not limited to, insurance companies, pension funds, venture capital
funds, individual venture capitalists, corporation partners and general capital investors. Private
investment funds billions of dollars' worth of new business start-ups in the United States each year.
The potential uses of private investment for supporting environmentally related businesses and/or
activities are only limited by the degree of profit associated with them: if it can be shown that an
idea or activity will make money, then private investment can be found to support it. Applying for
private investment is typically much faster than for government loan programs. Private investors
usually have no set eligibility criteria and may have no predetermined limits on the total amount of
loan capital available. Private investors tend to demand a significantly higher rate of return on their
money, though, than other sources of capital. Note that a private investment can develop into a
public-private partnership of an operational component is added to the mix.

5.2.2.1.3 Grant Type Funding

A variety of one-time grants are available for supporting specific initiatives of capital projects from
government and private foundation sources. The advantage of such grants is that there is no repayment
requirement and the amounts can be substantial. The disadvantages include the competitive nature of
the grants, the requirement for pre-positioned matching in-kind or funds for some grants, the
limitations on the use of some grant funds, the effort required to file the applications, and the need to
harmonize the grant requirements with the needs of the local government.

There are several federal and state grant programs, including both ongoing programs and one-time
opportunities. Several websites provide a good source for learning about federal grants: sites for
agencies that participate in the water world will present many opportunities, as will http://grants.gov.
For example, the 1987 amendments to the Clean Water Act established the Section 319 Nonpoint
Source Management Program. Under Section 319, states, territories and tribes receive grant money that
supports a wide variety of activities including technical assistance, financial assistance, education,
training, technology transfer, demonstration projects and monitoring to assess the success of specific
nonpoint-source implementation projects. Grantees must use these funds to implement U.S. EPA-
approved nonpoint-source pollution management programs. A 40 percent nonfederal match, in the
form of supplies, equipment, and/or funding, must be provided by grantees. Regulatory and

26 GeorgiaGov. n.d. "Environmental Loans & Tax Credits." https://georgia.gov/popular-topic/environmental-loans-
tax-credits

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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nonregulatory programs assessing the success of specific nonpoint-source pollution control projects may
be eligible for these grants. Grant totals for the last few years were in the $170 million range.27

Many types of foundations and charitable organizations have begun supporting various aspects of
stormwater-related needs through grant-making. Foundation and corporate grants are a significant and
growing source of funding for environmental protection projects. Most grants of this type fund well-
defined projects, with specified time frames, costs and deliverables that meet the immediate priorities
of the funding source and are not funded by governments. Foundation and corporate grant programs
tend to favor the most innovative environmental projects. Funding such things as green infrastructure
strictly through grants generally is not a sustainable financing strategy, but it may be a way to fund some
high-profile demonstration projects that will attract subsequent sustainable government or property-
owner financial support.

5.2.2.1.4 Other Resources/Approaches for Funding Stormwater Management
In addition to more traditional funding sources discussed previously, there are new and evolving
approaches to funding stormwater management that could be leveraged in many cases. These include
public/private partnerships, private site stormwater development, and volunteer programs. The ability
to utilize such approaches, and the impact to the stormwater program vary but are important options to
evaluate in developing a comprehensive funding strategy.

5.2.2.2	One-Time Sources

A wide variety of one-time grants are available for supporting specific initiatives of capital projects from
government and private foundation sources. The advantage of such grants is that there is no repayment
requirement and the amounts can be substantial. The disadvantages include the competitive nature of
the grants, the requirement for pre-positioned matching in-kind or funds for some grants, the
limitations on the use of some grant funds, the effort required to file the applications, and the need to
harmonize the grant requirements with the needs of the local government.

There are several federal and state grant programs, including both ongoing programs and one-time
opportunities. A number of websites provide a good source for learning about federal grants: sites for
agencies that participate in the water world will present many opportunities, as will http://grants.gov.
For example, the 1987 amendments to the Clean Water Act established the Section 319 Nonpoint
Source Management Program. Under Section 319, states, territories and tribes receive grant money that
supports a wide variety of activities including technical assistance, financial assistance, education,
training, technology transfer, demonstration projects and monitoring to assess the success of specific
nonpoint-source implementation projects. Grantees must use these funds to implement U.S. EPA-
approved nonpoint-source pollution management programs. A 40 percent nonfederal match, in the
form of supplies, equipment, and/or funding, must be provided by grantees. Regulatory and

27 U.S. EPA. 2019. "319 Grant Program for States and Territories." https://www.epa.gov/nps/319-grant-program-
states-and-territories

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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nonregulatory programs assessing the success of specific nonpoint-source pollution control projects may
be eligible for these grants. Grant totals for the last few years were in the $170 million range.28

Many types of foundations and charitable organizations have begun supporting various aspects of
stormwater-related needs through grant-making. Foundation and corporate grants are a significant and
growing source of funding for environmental protection projects. Most grants of this type fund well-
defined projects, with specified time frames, costs and deliverables that meet the immediate priorities
of the funding source and are not funded by governments. Foundation and corporate grant programs
tend to favor the most innovative environmental projects. Funding such things as green infrastructure
strictly through grants generally is not a sustainable financing strategy, but it may be a way to fund some
high-profile demonstration projects that will attract subsequent sustainable government or property-
owner financial support.

5.2.3 Other Resources/Approaches for Funding Stormwater Management

In addition to more traditional funding sources discussed previously, there are new and evolving
approaches to funding stormwater management that could be leveraged in many cases. These include
public/private partnerships, private site stormwater development, and volunteer programs. The ability
to utilize such approaches, and the impact to the stormwater program vary but are important options to
evaluate in developing a comprehensive funding strategy.

5.2.3. J	Public-Private Partnerships

Public-private partnerships (P3s) are receiving increasing attention in the United States and
internationally as an innovative way of financing a wide range of different environmental protection
initiatives. The point of P3s is that partnering with private enterprise can expand access to resources and
capital and offer better economies of scale. There are many types of P3s: design/build,
design/build/operate/maintain, pay-for-performance (interchangeable with pay-for-success),
community-based P3s, etc. They may include private financing or a combination of public and private
financing. Community-based P3s have a "commitment to social goals through setting robust
requirements for local jobs, and providing a platform for economic growth and revitalization associated
with large-scale Gl investments. Additionally, in this framework (based upon the military housing private
investment model), the community benefits through the structure of the community-based public-
private partnerships (CBP3) to reinvest savings through efficiencies in implementation back into more
'greened' acres rather than simply taking the savings as profits realized. Interest in CBP3s has been
growing across the country, as there is recognition of the universal applicability of this approach."29

In some cases, it is possible to capitalize on specific private sector resources through the use of P3s. The
availability of those resources depends upon the nature of the partnership arrangements, the resources

28	U.S. EPA. 2019. "319 Grant Program for States and Territories." https://www.epa.gov/nps/319-grant-program-
states-and-territories

29	California Stormwater Quality Association. 2019. 'The Community-Based Public-Private Partnership Approach: A
Revolution in Funding and Financing Green Infrastructure." https://www.casqa.org/asca/communitv-based-public-
private-partnership-approach-revolution-funding-and-financing-green

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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available to the private partners, the circumstances in the locations where they are set up, and other
factors. Access to sophisticated technologies and specialized expertise often allows the private sector to
provide specific types of services that the public sector may be unable to provide. In addition, private
financing can reduce the burden on public debt capacity. Private sector procurement and construction
methods sometimes save time and provide significant cost savings. Through P3s involving ownership
transfers from government entities to private companies, responsibilities for financial risk can be
transferred from the government entity to the private company.

P3s have some important limitations. Local governments may not always have the legal authority to
enter into contracts with private parties. A government jointing a P3 might lose oversight
opportunities—a major concern. When government officials cease to be involved with the day-to-day
operations of a facility, they may have to give up opportunities to monitor things such as compliance
with environmental standards and permits. In addition, public employees and unions may oppose the
use of P3s due to concerns about the loss of jobs. Finally, tax-exempt and/or other low-cost financing
that is available for (federal and state) government-run projects may not be available for P3s.

Thus, the appropriateness of a particular type of P3 for a given environmental protection initiative and
location depends on many factors, such as the type of environmental media being protected, availability
of public funding for the partnership, demographics, and the tax code.

5.2.3.2	Volunteer Programs

Volunteers can provide free labor for a variety of local stormwater program efforts. Examples include
education, technical assistance to homeowners, inspections, cleanups, adoptions of various stormwater
systems and rivers, grant writing, watchdogs, and more. Volunteers and volunteer organizations can
bolster support for stormwater programs or funding approaches. Citizen groups can assist in decision-
making and in selling decisions to the public. River-keeper-type groups can provide a sense of
stewardship of precious water resources and can serve as great allies with local governments. Some can
help run and manage programs such as rain gardens, citizen monitoring and stream cleanups.

Some volunteer groups require significant supervision and training for the perceived return on
investment, and there can be safety and liability concerns when volunteers partner with local
governments for activities.

An approach that can reduce or eliminate these problems is adoption of stormwater management
features: cases in which a group or company adopts a street, detention facility, pond, greenway or other
feature in the same way a company adopts a stadium in return for naming rights. Signage can be placed
along a road or near another feature with the adopter's name and/or logo. Such has been done by
Boeing and Starbucks.

While volunteer programs do not mitigate a substantial cost of the overall stormwater program, they do
provide valuable services and also help to engage the community and can be helpful in gaining public
understanding of stormwater management needs in the community.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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5.2.3.3	Coordination with Other Community Departments

Synergies can be gained among agencies that influence some aspect of stormwater management when
they cooperate, when a better-funded department or agency provides funding or services to a
stormwater program. Examples include:

*	A solid waste agency providing household hazardous waste assistance

*	A wastewater agency working to eliminate seepage of wastewater into the stormwater system as
part of an l&l program

*	A public affairs office helping the stormwater program implement certain activities

*	An agency that bills for service providing inserts explaining some aspect of the stormwater program

A public works or transportation department can add stormwater components or green infrastructure
features as a small part of a construction project. This can even work with different agencies or at
different levels of government.

Outside programs or organizations can incentivize such partnerships (e.g., watershed groups spanning
several local governments or DOT's) through coordination and funding efforts.

5.2.3.4	Market-Based Solutions

Local and state agencies, often in collaboration with EPA, have created market-based solutions to tackle
various water quality challenges—including nutrient reduction, volume control and wetland mitigation,
among others. These markets are designed to attract private capital, take advantage of efficiencies
gained from private delivery of projects, and/or direct solutions geographically to where they are
needed most. An internal EPA memo from February 6, 2019, reiterated the agency's support for market-
based solutions, particularly for nonpoint-source pollution (i.e., stormwater), and provided clarity to
state and local regulators and policymakers on best practices to implement locally appropriate
solutions.30 The most common form of market-based solution is through the creation of a credit or unit
of measure that denominates and quantifies an environmental outcome against a specific regulatory
mandate (e.g., Total Maximum Daily Load). The supplier of a credit is typically a non-regulated private or
public entity that has the financial wherewithal to build a project or a regulated entity that can go
beyond what is required of it. In both cases, this supplier generates additional environmental capacity
that can be sold to offset a regulated private or public entity's regulatory requirements. A functioning
market will have many buyers and sellers and a dynamic price based on what the market will bear.

Examples include wetland mitigation banking, nutrient trading, and stormwater volume trading. The last
of these, stormwater volume trading, is an emerging local solution pioneered by the District of
Columbia's Department of Energy and the Environment and profiled in a case study in Appendix II. It

30 U.S. EPA. 2019. Updating the Environmental Protection Agency's (EPA) Water Quality Trading Policy to Promote
Market-Based Mechanisms for Improving Water Quality, https://www.epa.gov/sites/production/files/2019-
02/documents/trading-policv-memo-2019.pdf

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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involves purchase of "Stormwater Retention Credits/' seen as more cost effective for regulated property
owners or developers but equally effective in attainment of the District's regulatory standard.

* Advantages:

o Create cost efficiencies in placement of stormwater controls.

o Can allow for aggregation for better overall
control and treatment.

o Can shift and target controls to more critical
locations and be combined with other
public incentives (e.g., grant programs) to
further incentivize credit suppliers to
develop projects in specific places.

* Disadvantages:

o Can be complex to administer

o Require clear and enforceable policies on
ownership and maintenance.

o Markets may be not be initially viable and
may need to be jumpstarted with local
funding.

5.2.3.5	Newer Innovative Approaches

Market-based solutions are just one of many new
approaches that can attract new forms of funding and
financing. A wide variety of approaches that seek to
exploit unique or unusual funding sources are being
explored in the stormwater space. Examples include:

*	Sponsorship of stormwater or green infrastructure
sites by private and/or public organizations, similar
to adopt-a-road advertising.

*	Tax increment financing that can be leveraged if a
new green infrastructure facility is designed to
increase surrounding property values, owners of
those properties agree to a new tax levy, and an
agency is designated legally to issue tax increment
bonds.

*	Use of private land for public infrastructure through various partnership and payment mechanisms
between public agencies and private landowners.

*	"Complete" or "green" street policies that mandate road repairs and include stormwater
management, often combined with vegetative practices or other aesthetic improvements.

Case Study: Washington, D.C.
Stormwater Retention Credit
Training

The U.S.' First Stormwater Retention
Trading Market in the Nation's
Capital

In 2013 Washington, D.C.
promulgated new stormwater
retention regulations for new
development or substantial
improvement projects. Part of these
new regulations was the
introduction of the Stormwater
Retention Credit Trading market,
which allows these regulated
projects to purchase up to 50% of
their stormwater management
requirements off site, in the form of
Stormwater Retention Credits (SRCs).
This allows regulated properties to
pursue more cost-effective
compliance methods and provides
financial incentives for properties to
voluntarily install stormwater
management practices.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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*	User fee credits that incentivize reduction in impervious area.

*	Green ratio ordinances that require developers in certain zoning districts to dedicate a percentage
of their property to natural area, which can manage stormwater runoff.

*	Various development incentives, including floor-area-ratio bonuses, expedited permitting, and
others in exchange for voluntary construction of stormwater management practices.

*	Strategic partnerships between communities and philanthropic sources to enhance public spending.

A Advantages:

o Can provide funds at little cost.

o Can motivate the private sector through name recognition.

o Can provide good return on seed money investment when paired with private actions.

A Disadvantages:

o Can be hard to administer and explain,
o May require opinions and analysis on legality.

5.3 Availability of Funding

The previous section describes the different types of funding sources for stormwater programs. Even
though there are several sources of funding, it is important to recognize several challenges that exist
when evaluating the overall stormwater funding aspect of stormwater management. In addition, only a
few funding sources can provide reliable, sustainable, and dedicated revenue for stormwater programs.
In fact, about 60 percent of the respondents to a recent survey indicate that their top challenge is the
lack of funding or availability of capital for their programs.31

5.3.1 Key Funding Challenges by Types of Funding

*	User Fees: User fees, as discussed earlier, can provide a reliable, sustainable and dedicated revenue
mechanism for stormwater programs. However, many communities need expertise, resources,
financial assistance to even plan for, develop, and launch a user fee program. Perhaps more
importantly, any public initiative to enhance stormwater funding cannot happen without the
engagement and acceptance of citizens within a local community and the support of local elected
officials.

In addition, the level of funding, which utilities that do have dedicated user fees or dedicated
stormwater tax type fees generate, is not adequate to meet all of the stormwater community needs.

31 WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survey-Report-2019.pdf

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*	Debt Financing: Despite the benefits of debt financing discussed earlier, the challenge that majority
of the communities currently face in leveraging debt financing, is that they simply do currently do
not have the annual financial capacity to repay the debt service associated with debt financing.

Consequently, stormwater programs have not leveraged capital financing sources to the extent
available. This is primarily due to the lack of a sustainable, recurring funding source to provide the
funding necessary for repayment. According to the 2018 Black & Veatch Stormwater Survey, only 13% of
stormwater utilities responding to the survey indicated that the majority of their capital program is debt
financed. 87% indicated that the majority of the capital program was cash funded. Therefore, it seems
that even where stormwater utilities (with user fees) are in place, communities are not leveraging
capital financing vehicles to the extent available.

*	Grants: Many of the grant programs are predominantly focused on specific regions (e.g.,

Appalachian Regional Commission, Region 1 Healthy Communities Grant Program, etc.); specific
type of demographics (e.g., Special Evaluation Assistance for Rural Communities and Households,
Clean Water Act Indian Set-Aside Grant Program, etc.); or specific activity (e.g., Beaches
Environmental Assessment and Coastal Health Act Grants. Hence, not all communities nation-wide
have access to grants.

Further, in most cases, grant allocations are much smaller in magnitude, and are also limited to a certain
percentage of the overall project, with matching funds required. The qualifications for each program
vary, depending upon the requirements of the specific program. In addition, normally, grants have a
window of opportunity to apply for funding each year, with the total amount available dependent upon
the level of appropriation for the year.

*	Public-Private Partnerships & Market Based Solutions: Many of the capital financing sources such
as Public-Private Partnerships, Market Based Solutions, and other such programs are still in their
infancy or just emerging, and may not be a viable option especially for smaller and rural
communities.

*	Volunteer Programs: While programs such as volunteer programs are a beneficial tool in the overall
stormwater management, those cannot contribute in any material manner to bridge the significant
funding adequacy issues that many communities face.

5.3.2 Estimate of Current Dedicated Stormwater Recurring Revenue Generation

Currently, there is no robust tracking of the annual revenue that is currently generated in the United
States from even the annually recurring and dedicated stormwater revenues sources discussed earlier in
this section. However, there are a couple of national level surveys that have gathered information on
annual revenues generated by stormwater utilities that have a dedicated stormwater user fee.
Therefore, the EPA the task force attempted to leverage the annual revenue information available from
(i) the 2019 Western Kentucky University (WKU) survey on stormwater utilities, and (ii) the 2018 Black &
Veatch Stormwater Survey of utilities that have stormwater user fees.

Out of the 1,700+ stormwater utilities from which WKU gathered user fee, population, and annual
revenue information, the annual revenue data was available only for 678 of those 1,700+ utilities. Based

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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on this available information, the median annual stormwater user fee revenue per capita was
determined to be $32.00. To the contrary, based on the annual revenue information that survey
participants reported in its survey, Black & Veatch reported a median annual stormwater user fee
revenue per capita of $54.00.

As at the time of this EPA Task Force study and report preparation, only these two sources of
information were available, the EPA Task Force deemed it appropriate to extrapolate the potential
annual revenue generation from existing 1,700+ stormwater utilities. The 1,700+ utilities identified in
the WKU survey, encompass a total population of roughly 114,850,631. So, using the median annual
revenue per capita figures determined from the two surveys, the following low end and high-end range
of annual revenue generation is estimated, at the current time, from the 1,700+ stormwater utilities
nationwide:

*	Low end annual revenue generation estimate: 114,850, 631 * $32 = 3.675 Billion (rounded)

*	Low end annual revenue generation estimate: 114,850, 631 * $54 = 6.202 Billion (rounded)

This annual revenue generation range off $3,675 to $6,202 Billion is based on the extrapolation done on
a per capita basis from the 1,700+ stormwater utilities.

However, the annual stormwater revenue generated from dedicated recurring funding source will be
higher as there are also a few utilities nationwide that have dedicated stormwater taxes and other
stormwater special assessments discussed earlier in this section. Currently, there is no readily available
information on the revenues generated from these other dedicated stormwater revenue sources, and
hence it is not feasible to estimate the aggregate annual stormwater revenues that are generated
overall from the existing revenue sources that are explicitly dedicated to stormwater management.

However, it is important to note that the revenue from dedicated stormwater funding sources such as
taxes, special assessments, etc is likely to be not significant as not many utilities in the country have
these types of dedicated stormwater revenue generation mechanisms.

Based on the annual stormwater revenues estimated just from the user fee revenues of 1,700
stormwater utilities, it is evident that there is an enormous "funding gap" between the overall
stormwater management funding needs and the level of funding that appears to be currently generated
in the United States. As described in Section 4.8 of this report, the funding gap is estimated to be
approximately $ 8 to $10 billion annually. This number is based on a national scale survey conducted by
the Water Environment Federation's Stormwater Institute in 2018. The information was obtained from
MS4 permittees to determine the total annual funding gap for stormwater programs (MS4 compliance
activities only) nationally.

To address this funding gap, diverse types of proactive measures including Federal, State, and Local
legislative actions and policies; enhanced technical and financial assistance; significant public education
and engagement; and a drive towards establishing dedicated sources of stormwater funding at the local
level, are necessary.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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5.4 Barriers to Obtaining Funding

Previous sections summarize the plethora of funding opportunities for stormwater programs. However,
this discussion would not be complete without mention of the many barriers to funding stormwater
programs in any meaningful way. As with most public funding schemes, there is a tension between the
need for funding and the access to funding—as well there should be in a public arena. Blank checks do
not exist, nor should they. But the barriers are often substantial, and thus stormwater programs across
the country are experiencing such a huge gap between needs and available funding.

This section focuses on barriers to funding from recurring, sustainable sources (such as taxes and user
fees), because they form the backbone of any funding portfolio and can be the most difficult to secure
at required levels.

5.4.1	Political Decision Making

A key principle in public governance is that it is done with the permission of those governed. Financial
support for publicly funded programs and services cannot be effectively established without substantial
buy-in from the members of the community, and equally important without the legislative action of
local elected officials.

The most common political decision-making barrier stems from each community's local political
environment. Members of local governing bodies face a wide range of competing needs and are hesitant
to increase taxes and fees due to various political, economic, and constituent obligations reasons,
reasons (not least the desire to be re-elected). The local decision makers typically refrain from proactive
stewardship for establishing a new source of funding such a new stormwater user fee or for enhancing
existing stormwater fees and charges, especially when the community has significant stormwater
management needs and the associated need for significant funding. There are many drivers for political
barriers including public perception, historical context of stormwater management and funding,
competition from other public programs, and a general cynicism for any new proposal for taxes or fees.

To garner effective support from local decision makers, stormwater program managers must engage in
extensive and timely education of its public and elected officials, and thoughtfully plan and prioritize
O&M and capital program investments so as to maximize benefits community-wide over the planning
horizon, community members and elected officials in the overall running of programs as well as
establishing funding structures.

5.4.2	Public Perception

Across the United States, there is general fatigue from taxes, fees and charges, particularly for utility
bills when water and sewer bills seem to increase much faster than other household costs. This often
translates to cynicism and limits the ability to garner stakeholder support for a new user fee or tax. The
lack of support intensifies when the population is not familiar with stormwater program and funding
needs, and don't have a clear understanding of the potential and tangible community-wide benefits.

In addition, stormwater management is often not seen as an essential service. As with water and sewer
utilities, the average citizen may not be aware of the complex network of stormwater drainage system

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or how it enhances their quality of life, safety, and, potentially, property values. In many communities,
chronic system failures may only be evident as a minor nuisance such as intersection flooding. In
addition, other common property services such as water, sewer and garbage collection have been
historically seen as essential public health services—but not stormwater management. The average
citizen actively turns on the kitchen sink faucet, flushes toilets, or puts the garbage out at the curb once
a week; stormwater services are much more passive. So it is not surprising to find a general lack of
understanding about stormwater systems.

This is the setting in which a municipality or utility may ask for a new stormwater user fee or some other
source of funding (e.g., a sales tax dedicated to stormwater). When the issue of stormwater funding and
user fee is initiated in such an environment of limited public awareness and perception, the road to
successful funding becomes challenging.

5.4.3	Competing Needs

Municipalities are one of our most potent forms of government, providing the widest array of public
services to their citizens. These typically include police, fire, parks and recreation, roads, utilities,
libraries and other facilities, and other general social services. Stormwater programs and facilities
compete for public funds in this crowded field. Whether through strategic planning, annual budget
requests or electoral politics, stormwater service is often prioritized much lower than other municipal
services.

5.4.4	Legal Barriers and Enabling Legislation

Funding for public programs must comply with a variety of legal requirements, many of which are noted
in previous sections of this report. In some cases, these legal requirements can be barriers to developing
funding for stormwater programs.

5.4.4. J	Legal Requirements

Many states have legal restrictions that supersede a local governing body's authority for imposing a
stormwater fee. For instance, until a few months ago the State of New Jersey prohibited forming a
stormwater utility or imposing fees. (The state's governor has now signed legislation giving that
authority to municipalities.) In 1996, meanwhile California voters approved Proposition 218, a
constitutional amendment making it more difficult for local government to impose taxes, fees and
assessments. One provision (clarified in a 2002 court ruling32) requires stormwater fees to be submitted
to a ballot measure requiring either a 50 percent majority of affected property owners or two-thirds
majority of registered voters to impose (or increase) a stormwater fee. Since 2002 only 31 stormwater

32 California Sixth Appellate District, Howard Jarvis Taxpayers Association versus the City of Salinas, 2002. That
decision acknowledged that Proposition 218's text is ambiguous as to whether stormwater falls under the
definition of "sewer," which did not have the ballot requirement. In 2017, the California Governor signed SB-231,
clarifying that definition to also exempt stormwater fees from the ballot requirement. The Salinas plaintiff has
vowed to sue any municipality that sets fees accordingly. However, the threat of litigation alone has caused most
cities to continue to take fees to the ballot.

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ballot measures have been pursued statewide (among more than 500 municipalities); voters have
approved about two-thirds of them.

Overall, 41 states and the District of Columbia have at least one stormwater utility each. The other nine
states have none, and legal barriers may play a part in that.

5.4.4.2	Legal Challenges

Legal challenges of new stormwater fees are a concern to many municipalities, particularly small ones
that are limited in the resources needed to sort through complex and sometimes ambiguous enabling
legislation. "Such is the case in Pennsylvania where regional approaches are being pursued in the
counties of Blair, York, Lancaster and Montgomery, but, even there, one of the major barriers to
implementation is concern about the confusing details of the enabling legislation and fear that
implementation won't confirm and will be mired in legal challenges."33

Legal challenges do occur. Previously mentioned was the Salinas case in California, which significantly
changed the stormwater funding landscape in that state. The Western Kentucky University Stormwater
Utility Survey from 2013 summarized legal challenges across the country. "We have now identified 76
legal or political challenges to stormwater utilities in the U.S....Of the 76 challenges, 44 were decided in
favor of the utility, while in 16 cases the utilities received unfavorable decisions or were struck down.
Twelve of the cases are still pending or we were unable to find whether or not a court decision had been
reached. Five challenges were successful political challenges. Stormwater utilities in Birmingham,
Alabama, Colorado Springs, Nampa, Idaho, Manitowoc, Wisconsin, and in Cumberland County, North
Carolina were repealed."34

The 2018 edition of the Black & Veatch Stormwater Utility Survey35 asked the 75 participating agencies
whether their stormwater user fees ever faced legal challenges. They found that 27 percent of the
respondents said "yes." The basis of challenge varied as follows:

4	Tax and not a user fee (38 percent)

*	Lack of authority to assess stormwater fees (24 percent)

*	Equity and fairness (17 percent)

*	Rate methodology (14 percent)

*	Rational nexus between costs and user fees (3 percent)

*	Constitutionality (3 percent)

33	Environmental Financial Advisory Board. 2016. Developing Dedicated Stormwater Revenues.

34	Campbell, C. W. 2013. Western Kentucky University Stormwater Utility Survey 2013.
https://www.wku.edu/seas/documents/western kentuckv university swu survey 2013.pdf

35	Black & Veatch. 2018. "Stormwater Rate Structure and Billing." In 2018 Stormwater Utility Survey.
https://www.bv.com/sites/default/files/2019-

10/18%20Stormwater%20Utilitv%20Survev%20Report%20WEB O.pdf

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5.4.5	Equity Issues

As many as 92 percent of stormwater utilities base their fees on relative impervious surface area.36 This
is a well-accepted method to ensure fair distribution of costs to customers, one of the distinguishing
features of a user fee (as opposed to a tax). An unintended consequence of that fee basis is the
potential of a disproportionate financial burden placed on properties in disadvantaged areas. Residential
densities tend to be higher, which is often accompanied by a much higher percentage of impervious
surfaces (and thus a higher proportion of the fee base).

Low-income areas also tend to be in low-lying, flood-prone areas where insufficient stormwater capacity
is first felt. These neighborhoods also tend to be rental properties where landlords have little incentive
to invest in green spaces or low-impact development.

Rate discounts or exemptions for low-income or seniors are sometimes difficult to provide. With no
rational basis for reducing rates based on impervious surface, some states do not permit such discounts
unless subsidized by non-stormwater funds (such as a city's general fund).

5.4.6	Administrative

Sometimes the greatest barrier to forming a stormwater utility is the agency's internal administrative
structure. This is particularly true for local municipalities where various stormwater functions have
evolved within different departments or divisions. For example, infrastructure maintenance may reside
in the streets or sewer departments, NPDES compliance in the environmental group, capital planning in
the engineering division, and financial services in the finance department. In other words, it is all too
common to find these functional units distributed throughout a municipal organization without unified
leadership or cohesive functionality.

Without such leadership, it can be very difficult to champion a cause such as initiating a stormwater user
fee. Support for change must often come from senior management in order to be implemented.

5.4.7	Limited Resources

Managing a complex municipal utility requires significant resources that are often lacking—particularly
in small/midsize municipalities or ones that are attempting to launch a stormwater utility structure for
the first time. These resources may include:

*	Strategic and financial planning

*	Asset management

*	Technology (GIS, data)

*	Public engagement (branding, outreach)

The path to a dedicated and sustainable revenue stream includes all of the above (needs analyses,
financial planning, fee study, community engagement). This can cost $300,000 to $1 million or more and

36 Ibid.

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take two or more years. In addition, competing in the grant funding arena demands that a stormwater
agency possess expertise in grant writing and grant administration.

Finally, basic NPDES permit compliance is a complex and time-consuming endeavor to which an MS4
must devote resources to keep abreast of changing regulations and implementing NPDES programs,
public education and enforcement.

5.4.8 Lack of Public/Policymaker Awareness and Understanding of Needs

The first step in establishing a stormwater utility is determining the needs and calculating the associated
costs. Once done, the bigger challenge may be communicating this need to the municipality's
policymakers and the community at large in a compelling way. "The most effective stormwater business
plans recognize community expectations. In some cases, expectations must be elevated by convincing
demonstrations that stormwater problems exist and can be solved. Stormwater management rarely
captures public support unless problems impact the daily lives of citizens. Many drainage systems are
underground and essentially invisible to the public. If they are designed, constructed, and maintained
properly, most people are unaware of them. More visible problems such as potholes in roadways
consistently rate higher than drainage problems. The most effective programs identify and publicize the
problems they must address, seek public participation and support, and orchestrate the use of various
tools and resources over time."37

This can be accomplished from the technical side with engineering and financial analyses. But moving
public opinion is much more difficult and requires expertise not often found in the ranks of stormwater
managers. A successful utility would employ public information personnel and develop an early branding
effort from which is built a full public engagement program that can begin to move the opinion of both
policymakers and the public at large.

5.5 Summary of Existing Funding Sources

Stormwater programs face many challenges to developing the resources needed to deliver programs, as
well as the projects that will achieve the goals of flood protection and clean water. Progress has been
made on many stormwater funding fronts, including many federal and state grant programs. While
primary funding remains a local municipal responsibility, it is widely recommended that any stormwater
program or utility develop a portfolio approach to funding. A solid foundation for that portfolio should
be a dedicated, sustainable revenue stream such as user fees, but it should be supplemented with a
robust array of other funding and financing mechanisms such as loans and other debt tools, grants,
partnerships, and multiple creative approaches using the resources of other like developers and private
interests.

The role of the federal government may be limited by comparison, but its presence is invaluable in
helping provide much needed capital funding for large projects, as well as in providing education,

37 National Association of Flood and Stormwater Management Agencies. 2006. Guidance for Municipal Stormwater
Funding.

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offering training, and making all opportunities to meet the challenges of funding available to all local
programs.

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6.0 Infrastructure Affordability

Identify how the source of funding affects the affordability of the infrastructure,
including consideration of the costs associated with financing the infrastructure.

Section 5.0 of this report details the types of funding sources and financial resources that are and could
be used to manage stormwater operations and infrastructure. It also presents an overview of the key
barriers municipalities face in obtaining the requisite ongoing funding for effective stormwater
management. This section of the report focuses on how the funding sources affect three aspects of a
municipality's stormwater management capabilities and household affordability: efficient management
of infrastructure, financial capability, and customer household affordability.

6.1 Infrastructure Efficiency

An integral and critical aspect of stormwater infrastructure management is how efficiently utilities
manage stormwater infrastructure. Generally, infrastructure efficiency pertains to a deliberate focus on
best practices such as proactive asset management, effective use and leveraging of resources, strategies
that help achieve economies of scale, and risk mitigation and resiliency building efforts. An area of
opportunity identified by the Task Force is the highly decentralized nature of stormwater service
provision.

The types of U.S. stormwater systems and the organization of responsibilities both significantly influence
infrastructure efficiency. The following subsections discuss these two issues.

6.1.1 Types of Stormwater Systems and Implications

Stormwater is discharged not only through MS4 conveyance infrastructure but also via CSS conveyance
infrastructure. MS4s and CSSs have similar obligations under the federal Water Pollution Control Act of
1972 (P.L. 92-500), commonly known as the CWA, and its related amendments. However, the two
systems' characteristics impose unique levels of service and infrastructure management burdens and
obligations, and consequently exert differing levels of impact on infrastructure efficiency, financial
capability and customer affordability.

Excessive wet weather (stormwater) flows in a CSS could trigger combined sewer overflows (CSOs),
where the untreated combined stormwater and sanitary sewage is directly discharged to surface
receiving waters without even primary treatment. Consequently, the environmental responsibilities and
exposure to regulatory mandates such as the Long Term Control Plan (LTCP) requirements for CSS can
be vastly more expensive, as measured in both operating expenses and capital commitments necessary
to eliminate CSOs. Further, stormwater inflow into non-CSS wastewater collection systems can cause
similar overflows conditions.

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Excessive wet weather flows also affect MS4s in a number of ways, including flooding, habitat
degradation, streams and channel erosion, and other significant water quality issues such as
sedimentation and pollution resulting from stormwater runoff. These, in turn, create the need for
stormwater treatment facilities.

Both CSSs and MS4s involve significant financial investment in the treatment and management of wet
weather flows. Typically, funding for CSS management is covered by wastewater fees. Funding for MS4
management, the subject of this Task Force, is covered by a variety of sources as described in Section
5.0; however, many municipalities have no dedicated, consistent or reliable funding mechanisms in
place.

Regardless of the types of systems and funding mechanisms, customer affordability and the public's
understanding of the need for these services are critical.

6.1.2 Delineation of Stormwater Responsibilities

The Task Force has observed significant differences among municipalities with respect to the
distribution of stormwater management and regulatory compliance responsibilities. Some of these can
be attributed to the types of stormwater management systems that exist within a jurisdictional area
(discussed above); largely, though, they can be attributed to the institutional framework established by
the state in which the municipality is located, as well as local and regional stormwater needs. The
distribution of responsibilities can affect affordability by creating situations where there are overlapping
responsibilities and limited accountability for program implementation.

In some municipalities (e.g., Philadelphia, Pennsylvania, or Newark, New Jersey), the water/sewer
utility—a city department—is responsible for managing all aspects of stormwater management
including LTCP/ NPDES and MS4 regulatory compliance; both CSS and MS4 types of stormwater
infrastructure; and all associated O&M requirements, including green infrastructure initiatives. In these
cases, the management of the entire stormwater infrastructure rests within a single entity with single
point of accountability.

Responsibility is divided in other municipalities. In Washington, D.C., for example, an independent
authority (DC Water) manages the CSS and separate sanitary sewer systems while the municipality
(specifically, the Department of Energy and Environment) is responsible for all MS4 requirements. Even
in a municipality that has only an MS4 system and a separate sanitary sewer system, the stormwater
management responsibilities may be distributed between a water/sewer utility, a department of public
works, and for example a department of transportation. In addition, in many communities, the MS4
responsibilities for developing and implementing specific permit requirements such as stormwater
pollution prevention plans or nutrient management plans are given to school districts or fire, police or
parks departments. In these cases, holistic management of stormwater infrastructure requires a clear
understanding of roles and responsibilities, delineation of ownership of stormwater assets, and effective
coordination among the various entities to enhance infrastructure efficiency. An integrated planning
framework could especially enhance efficient management of infrastructure in these situations where

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multi-entity coordination is critical. Such a framework would put municipalities in a position to optimize
capital investments—making this a concept worth the investment of grant dollars.

Such significant differences in the distribution of stormwater service responsibilities among municipal
jurisdictions also directly influence the overall financial capability aspects of stormwater management
(discussed in Section 5.0), as funding and cost recovery mechanisms differ significantly. Note also that,
in some municipal jurisdictions, the U.S. Army Corps of Engineers may support the implementation of
stormwater-management-related projects (mainly large flood risk management projects) by providing
partial funding and technical assistance.

6.2 Financial Capability

Stormwater capital infrastructure investments are driven by the need to enhance and/or maintain
existing drainage capacity, flood mitigation, repair and rehabilitation of aging infrastructure, coastal
resilience, climate resilience, and community needs. In CSS communities with consent decree
requirements to mitigate CSOs, the pressure on stormwater infrastructure investments such as tunnel
or gray infrastructure, and/or the need to enhance pumping and wastewater treatment capacities, can
be significant. The critical challenges for a municipal entity managing stormwater infrastructure (for
CCSs or MS4s), are funding availability, funding adequacy and timeliness of funding.

Municipalities tend not to have enough funding for stormwater infrastructure, though they range on a
spectrum from "no dedicated funding" to "adequate funding." For example, the national WEF
Stormwater Institute and Black & Veatch stormwater surveys38 and other state-level stormwater,
drinking water and clean water surveys indicate that utilities cite "lack of funding availability" as their
highest-ranked challenge with respect to timely infrastructure investments. While there are many
funding sources for stormwater, as described in Section 5.0, the Task Force believes the funding is
inadequate and that there are significant barriers to accessing the available funding sources.

The following subsections present four factors affecting financial capability for effective stormwater
management:

*	Stormwater financial reporting

*	Impact of various funding sources on building financial capacity

*	Implications of the financial capability assessment methodology

*	Customer household affordability

38 WEF Stormwater Institute. 2019. National Municipal Separate Storm Sewer System (MS4) Needs Assessment
Survey Results. https://wefstormwaterinstitute.org/wp-content/uploads/2019/08/MS4-Survev-Report-2019.pdf;
Black & Veatch. 2018. 2018 Stormwater Utility Survey, https://www.bv.com/sites/default/files/2019-
10/18%20Stormwater%20Utilitv%20Survev%20Report%20WEB O.pdf

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6.2.1 Stormwater Financial Reporting

Stormwater infrastructure is, generally, an entirely municipal proposition. The footprint of publicly
traded investor-owned utilities and private companies that own and operate stormwater systems is
small—not a material share of the total infrastructure universe. Therein lies a major area of opportunity:
there are roughly 42,158 units of local government,39 and while not all are directly responsible for every
category of municipal asset, they are very diverse in management and governance structures as well as
financial reporting. This makes summary observations of financial capabilities as well as affordability to
households more difficult. Municipalities generally do not produce independently audited financial
statements with the same timeliness as publicly traded companies, nor do most publish intra-year
unaudited statements such as quarterly financials.

Specifically, the differences in management and governance have direct implications for stormwater
funding and financial reporting, as follows:

*	General government (most common). When stormwater management responsibilities lie with a
general government (e.g., with its public works or streets and transportation department), the
primary source of funding is typically general tax revenues. There may not be any dedicated source
of funding for stormwater management. This governance and funding structure is usually associated
with a modified accrual basis of accounting or, worse, a cash basis. Neither includes a balance sheet
with assets and liabilities. Similarly, the statement of revenues over expenditures does not have an
explicit line item for depreciation for those assets that are even depreciable. The Task Force believes
that without a clear correlation between dedicated funding and revenue requirements, sufficient
funding for stormwater cannot be allocated through such governance structures.

*	Utility department (varies by state, but generally less common). Some municipalities have
standalone stormwater enterprise funds. However, not all local governments have state statutory
authority to establish separate and discrete stormwater utilities, meaning stormwater management
responsibilities lie within the purview of a larger water and sanitary sewer utility department within
the municipality. The primary source of ongoing funding is typically user rates and user charges.
However, the way rates and charges are levied varies from municipality to municipality. Some
utilities (e.g., Philadelphia, Pennsylvania; Portland, Oregon; Wilmington, Delaware; and Chesterfield
County, Virginia) levy a fee based on the property's actual or estimated impervious surface area to
recover the costs associated with stormwater management. Other communities levy a flat recurring
charge based on type of land use (residential, commercial, etc.). Still other municipalities—such as
New York City, where the Department of Environmental Protection is responsible for water, sewer
and stormwater management—recover costs through sanitary sewer user charges. Still, for
transparency purposes, a rate-based funding structure typically is associated with traditional
enterprise financial reporting, using an accrual basis of accounting that does include an income

39 Hogue, C. 2013. Government Organization Summary Report: 2012.

https://www.census.gov/content/dam/Census/librarv/publications/2013/econ/gl2-cg-org.pdf. (This Census
summary identifies 38,910 general purpose governments. It excludes special and school districts but does include
3,248 special districts categorized as "drainage and flood control.")

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statement, balance sheet and depreciation. This makes it less difficult to assess whether ongoing
funding is sufficient to cover stormwater needs, even without uniform reporting standards.

*	Independent authority (least common). If stormwater management responsibility lies with an
independent municipal authority or separate political subdivision, stormwater funding may have to
rely on either the taxing authority or its own rates and charges. Comparability and assessment of
financial capacity and affordability to the household is therefore subject to financial accounting and
transparency.

6.2.2 Impact of Various Funding Sources on Building Financial Capacity

The Task Force reviewed the key funding sources discussed in Section 5.0, evaluating most of those
sources' potential impact on a municipal entity's overall ability to build financial capacity, for O&M and
capital infrastructure investment.

In the summary below, the Task Force discuss the criteria for this review, summarize the findings and
present a case study examples.

6.2.2. J	Assessment Criteria

The Task Force defined the following key criteria for evaluating the ability of various funding sources to
help build a municipality's overall financial capacity:

*	Sufficiency—measures the total annual revenue that a municipality can generate from one or more
funding sources.

*	Stability/sustainability—assesses the ability of the combination of funding sources to provide
consistent and reliable levels of dedicated funding to support immediate and long-term sustained
infrastructure management including capacity expansion and to meet O&M service obligations.
These criteria also measure the sustainability of the revenue source.

*	Scalability—measures the flexibility of the utility to increase funding commensurate with increases
in revenue requirements.

*	Legislative requirements—funding options including user fees, impact fees and debt issuance often
require internal approval from boards, councils or commissions, and/or potentially voter
approval/referenda through ballot measures. These legislative requirements and challenges can
influence the ability to generate timely funding.

*	Acceptability—evaluates the benefits and risks of the various funding sources as judged by elected
officials, utility management and external stakeholders.

*	Customer equity—evaluates the measure of equity, which can be defined in a variety of ways, in
cost recovery from the customer base within the jurisdiction.

6.2.2.2 Summary Assessment of Funding Sources on O&M and Capital
Infrastructure Investments Financial Capacity

Section 5.0 summarized the various types of funding sources, along with their advantages and
disadvantages. It broke those sources into three categories:

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*	Recurring and/or intermittent revenue funding

*	One-time funding sources for capital projects and/or one-time initiatives

*	Other resources/approaches

This section further examines the impact of the first two of those categories in building a utility's

financial capacity for stormwater management.

*	Figure 2 summarizes the impact of recurring and/or intermittent funding sources on a utility's ability
to effectively fund O&M operations. All of the sources listed in Figure 2 and Table 2 are applicable to
a municipal entity's stormwater O&M revenue requirements.

*	Figure 3 summarizes the impact of the one-time sources/initiatives on a utility's ability to
adequately fund capital infrastructure investments.

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Table 2. Financial Capacity Impact of Recurring/Intermittent Funding Sources—O&M Operations.

Evaluation
Criteria

Recurring or Intermittent "Revenue Based" Funding Sources



Taxes/General
Funds

Stormwater
Dedicated Taxes

Stormwater Utility
User Fee

Other O&M Fees

Surcharges or
Special Assessments

Revenue
Sufficiency

Low: general
funds typically
have different
priorities such as
public safety

Moderate: better
transparency via
correlation
between revenues
and revenue
requirements

Moderate to high:

generally, the rates
and charges are
objectively aligned
with the revenue
requirements of the
stormwater system

Low: don't always have
a clear correlation or
justification to annual
revenue requirements
and may be fungible
with other general
government needs

Moderate: generally,
have somewhat
limited revenue-
raising ability

Stability of
Revenues

Volatile: property
and sales tax
bases can rise and
fall with economic
cycles

Volatile: property
and sales tax bases
can rise and fall
with economic
cycles

Strong: revenues are
tied to either the size
of the property's
impervious surface
area or the category of
the property, not to
economic cycles

Variable: very low
volatility if tied to a per-
parcel fee and not
subject to property
valuation, very high
volatility if tied to non-
recurring cash flows like
development

Low to moderate:

special assessments
often are tied to
property valuation
and surcharges
sometimes are
related to water
consumption

Scalability to
Meet
Increasing
Needs

Low: major line
item increases are
generally subject
to political
scrutiny

Very low:

dedicated taxes are
typically voter-
approved and may
not even exist in
perpetuity

High: a dedicated
funding source allows
the user fees to be
leveraged to address
both O&M and capital
expenditure; however,
fee increases are
typically not well
received by elected
officials or the public

Low: would mostly
likely need some kind of
authorization to scale
up the fee structure,
from a municipality or
even a homeowners'
association

Moderate: limited
ability to increase
revenues creates
finite financial
capacity

Legislative
Requirements

High: subject to
annual

appropriation,
sometimes even
voter approval

Very high: subject
to voter approval
and annual
appropriation

Low: usually only
requires a one-time
authorization via
either state general
assembly or municipal
ordinance

Very high: subject to
voter approval and
annual appropriation,
perhaps public
education to get buy-in
from the developer
community

High: likely subject to
some kind of initial
legal authorization

Community
Acceptability

High: aside from
politicization of
where in the
municipality to
fund projects,
usually not
controversial

Moderately high:

establishing a new
tax may not be
politically palatable
unless a recent
flood event is
driving the measure

High: aside from
politicization of where
in the municipality to
fund projects, usually
not controversial

Moderately high:

establishing a new tax
may not be politically
palatable unless a
recent flood event is
driving the measure,
but possibly offset by a
user-pay

Moderately high:

establishing a new
tax or fee may not be
politically palatable
unless a recent flood
event is driving the
measure

Community
Financial
Capability
Barriers

High: many states
have established
and/or

municipalities
have self-imposed
limitations related
to taxation

Moderate:

comparably easier
to assess financial
capacity and assign
resources even if
that capacity may
be statutorily
limited

Low: a dedicated,
user-based, non-tax
revenue stream
creates dedicated
financial capabilities
and improves ability to
do multi-year planning

Moderate: if there is a
high degree of revenue
fluctuation, it may be
difficult to appropriate
funding to retain
dedicated full-time
equivalent staffing;
municipality could lose
institutional knowledge

Moderate:

comparably easier to
assess financial
capacity and assign
resources even if
that capacity may be
statutorily limited

Household

Affordability

Impact

High: property
taxes are generally
deemed as
regressive

High: property
taxes are generally
deemed as
regressive

Low: User fees are still
somewhat regressive
but usually much
smaller in actual
dollars compared to
water and sewer
charges

Low: if tied to a "user
pay" levy, would mostly
likely be borne by those
directly benefitting
from the infrastructure

Moderate: not as

regressive as a pure
tax but still
correlated to
property valuation
without explicit
income recognition

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Acceptability

Financial Capability
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OTaxes/General Funds OStormwater Dedicated Taxes Stormwater Utility User Fee OOtherO&M Fees ©Surcharges or Special Assessments

Figure 2. Impact of recurring and/or intermittent funding sources on a utility's ability to effectively fund O&M operations.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or approved by the chartered EFAB, and does

riot represent EPA policy.

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Sufficiency	Cost of Borrowing flexibility in Use of	Acceptability	Financial Capability Affordability Impact

Impacts	Fundi	Barriers

OGrants OBonds Low-inter est Loans QCapital Revenue Fee O Developer Contribution

Figure 3. Impact of one-time sources/initiatives on a utility's ability to adequately fund capital infrastructure investments.

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Table 3. Financial Capacity Impact of One-Time Financing Sources—Capital Infrastructure

Evaluation
Criteria

One-Time Financing Sources for Capital Projects/Initiatives



Grants

Bonds

Low-Interest Loans

Capital Revenue
Fees

Developer
Contribution

Revenue
Sufficiency

Moderate: will
usually be
sufficient for a
single project but
rarely for an
entire system on a
recurring basis

Strong: allows for
payment over
extended period,
creating ability to pay
for larger projects and
still have cash flow for
ongoing O&M;
however, a dedicated
funding source is
needed to pay the
bond commitments

Strong: allows for
payment over extended
period of time, creating
ability to pay for larger
projects and still cash
flow for ongoing O&M;
however, a dedicated
funding source is
needed to pay the loan

Low: generally,
municipalities
earmark this revenue
stream for pay-as-
you-go infrastructure
investments, and
capital plan needs in
any given year may
exceed that

Low: generally tied
to economic
development or
redevelopment,
which can be very
volatile

Cost of

Borrowing

Impacts

Moderate:

typically requires
somefinancial
commitment or
cost share by the
municipality,
which is

sometimes itself a
barrier

High: interest
expense, ongoing
disclosure
requirements and
debt and financial
management
obligations recur
through the life of the
bonds

Moderately high:

typically rates are
subsidized and below
market; has fewer
disclosure and other
recurring requirements,
but still requires good
debt and financial
management practices

None: generally
municipalities
earmark this revenue
stream for pay-as-
you-go infrastructure
investments

None: one-time
cash inflow, against
which

municipalities
generally do not
borrow or pledge
toward debt

Flexibility in
the Use of
Funds

Low: federal and
maybe even state
grants require
single audit and
related
verification

High: if the bonds are
tax exempt, the main
restrictions are those
related to IRS
requirements

High: generally the only
restriction is that the
project must be
associated with the
lender agency's mission

Very high: local,
internally generated
revenues generally
do not have
restrictions

High: only
restriction might be
that contributions
be used for growth-
driven investments
in the immediate
area of
development

Legislative
Requirements

Almost none:

grants are well-
established tools
that may only
require formal
approval and
acceptance by the
municipality

Low: while some
states and many
municipalities impose
some guidelines or
limits, generally local
governments are not
restricted to use
bonds

Low to moderate: some
lending agencies
require more collateral
or a pledge of a
supplemental revenue
stream, which may
require further
authorization by the
municipality

Low: there may in
some states be a
requirement to
justify based on cost
of service

Low: political
willingness to
implement impact
fees (or equivalent)
is generally the only
barrier

Community
Acceptability

High: assuming
the local match is
not a barrier,
municipalities
generally
welcome grants

Moderate to high:

there may be some
aversion to debt in the
community but
generally this does not
preclude bond
issuance

High: federal or state
agencies may also be
more willing to work
with a financially
distressed community
than the capital market
creditors

Moderate:

introduction of fees
may be more
politically palatable
than taxes

Moderate: may

galvanize resistance
among the
developer
community as
being disruptive to
their business
model

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Evaluation
Criteria

One-Time Financing Sources for Capital Projects/Initiatives



Grants

Bonds

Low-Interest Loans

Capital Revenue
Fees

Developer
Contribution

Community
Financial
Capability
Barriers

High: many
communities lack
the institutional
knowledge or
funding for grant
application
writers and grant
administrators

High: generally
bonding relies on
access to credit
markets, which can be
a barrierto poor or
small municipalities
and requires good
financial management

Moderate: still requires
good financial
management practices
but federal and
especially state
agencies often can
provide technical and
administrative
assistance that small,
poor or rural
communities might not
otherwise be able to
access

Moderate:

recommended best
practices include
segregated financial
accounting and
reporting to show
citizens revenues are
being deployed as
represented—a
potential barrierfor
small, poor or rural
communities without
the requisite staff

Moderate: requires
financial and
technical expertise
to properly track
and account for
these non-recurring
revenues

Household

Affordability

Impact

Low: one of the
most favorable
weighted cost of
capital options

High: borrowing, even
at favorable interest
rates, is still the
highest cost of capital

Moderately high: few

programs offer pure
"zero interest"
borrowing

Low: capital-related
fees are often small
in absolute dollars

None: in most
cases, developers
typically bear the
upfront costs, and
many cities require
"growth pays for
growth" so that
costs are not
subsidized by the
general rate base

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6.2.2.3	Case Study Example: Flexibili

The Iowa SRF program has funded stormwater
projects, without affecting user fees, through the
Water Resource Restoration Sponsored Projects
program. A CWSRF project can carve out 1
percent of the interest that would have otherwise
been paid to the CWSRF program on its
infrastructure loan, using that money for a
nonpoint-source project. The SRF program allows
about $100,000 per $1 million CWSRF loan to be
used for water quality projects. Through this
overall interest rate reduction, the utility's
ratepayers do not pay any more than they would
have for just the wastewater improvements.

Stormwater projects including permeable
paving, bioswales, rain gardens, streambank
restoration and soil conservation projects on
agricultural lands have been funded. About $50 million for these projects have been approved for
funding.

6.2.3 Implications of Financial Capability Assessment Methodology

Financial capability assessments (FCAs) are distinct from various measures of household or individual
customer affordability (discussed below) in that an FCA relates to the ability of a community (or
permittee) to finance infrastructure investments. For a broad array of purposes, EPA has used a static,
two-phase methodology to conduct FCAs. Phase I involves calculation of a residential indicator (Rl),
which examines the average per household cost of services relative to a benchmark of 2 percent of
service-area-wide median household income (MHI).

Phase II involves the calculation of a financial capability index (FCI), a simple arithmetic average of scores
for six economic indicators:

*	Bond rating

*	Net debt as a percentage of full market property value

*	MHI

*	Local unemployment

*	Property tax revenues as a percent of full market property value

*	Property tax collection rate within a service area

ty in the Use of CWSRF

$¦ jcaocom



¦	Loan Costs
(interest and fees)

¦	Sponsorec project
principal

~ Wastewater
principal

S1 miion CWSRF H million loan with
ban	sponsored project

Figure 4. Graphic representing the current stormwater
management paradigm shift.

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A higher FCI score suggests relative economic strength; a lower FCI indicates weak economic conditions
and relatively lower financial capability. EPA's existing FCA guidance40 has been subject to extensive
review and critique for a variety of reasons that are particularly resonant for application to stormwater
related infrastructure financing. For example, the diversity of governance structures and financial
reporting protocols noted above makes even baseline evaluation of current funding complicated.
Financing stormwater infrastructure is often less straightforward than issuance of the revenue bonds
assumed to be available in EPA guidance. And profound complexities may be involved in assigning the
residential vs. non-residential flow contribution responsibilities required in EPA's matrix methodology.

Emerging concepts to address the limitations of EPA's current FCA methodology could also improve
evaluation of community financial capabilities to fund stormwater infrastructure (though the diversity of
governance configurations will continue to impose complexities). For FCAs, these concepts call for a
direct evaluation of a community's (or communities', in cases where stormwater services involve
multiple jurisdictions) financing capacity through cash-flow analyses. Current and potential new
methods for funding stormwater infrastructure would require explicit recognition (rather than being
subsumed within general government financial reporting). Projected tax or fee cost impacts on
individual households and non-residential entities may be calculated and gauged in relation to various
income metrics (e.g., median and lowest quintile, gross and disposable). Financial capabilities would be
assessed in terms of the community's ability to fund O&M expenses and capital spending given tenable
annual adjustments to stormwater-dedicated tax and fees. The pace and magnitude of these tax or fee
increases would be established by reference to new measures of household or individual customer
affordability as discussed below.

6.3 Customer Household Affordability

In the context of water and wastewater services, customers' hardships include various costs associated
with challenges in paying service bills, including even service interruptions. For stormwater services,
such customer affordability issues may manifest less explicitly or dramatically, but they nevertheless are
important considerations for stormwater finance policy development. And, as with FCA, both how
household affordability is measured and what constitutes burdensome levels of cost are being
reconsidered as concerns rise about water (i.e., drinking water, wastewater and stormwater)
affordability across all water-resource-related services.

Historically, EPA has measured water and wastewater service cost affordability largely in terms of how
estimates of annual household costs compared to MHI as reported by U.S. Census data. EPA's
historically used FCA matrix methodology may render a determination of "High Burden" for
communities where household costs are above 2 percent of MHI. Logically, though rarely done, the
same methodology can be applied to evaluation of stormwater service costs—especially (or at least
more easily) if such costs are explicitly calculable by reference to stormwater utility rates or fees rather
subsumed within general government funding sources. The historical underfunding of stormwater
management costs (even if recovered through separately established fees and charges) means that
stormwater management costs are unlikely to be deemed as currently imposing an undue burden using

40 U.S. EPA. 1997. Combined Sewer Overflows—Guidance for Financial Capability Assessment and Schedule
Development. EPA 832-B-97-004. February 1997. https://www3.epa.gov/npdes/pubs/csofc.pdf

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historically applied metrics referencing MHI. In addition, the use of MHI as an affordability metric has
been widely criticized.41

Emerging concepts related to household water affordability measures (like those for FCAs) offer new
measures and methodologies for assessing water resource management costs beyond reference to MHI.
Cost as a percentage of lowest quintile income is advocated for its focus on the economically
disadvantaged; cost as a percentage of a measure of disposable incomes is advanced as a means to
gauge whether households will face undue substitutions of health care, food or other essential services.
Most importantly, these concepts call for inclusion of stormwater-management-related costs (incurred
via separate charges or through general taxes and fees) in the pantheon of claims imposed on
households for water resource management services.

41 AWWA. 2013. Affordability Assessment Tool for Federal Water Mandates.
httpsV/www.awwa.org/Portals/O/AWWA/ETS/Resources/AffordabilitvAssessmentTool.pdf

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Appendix I: Municipal Financial Reporting and Asset
Management

In 1999, in a document known as Statement 34,42 the Governmental Accounting Standards Board paved
the way for a fairly large shift in the way public sector entities produce financial reports.

Statement 34 discussed infrastructure assets: "long-lived capital assets that are normally stationary in
nature and normally can be preserved for a significantly greater number of years than most capital
assets. Examples of infrastructure assets include roads, bridges, tunnels, drainage systems [emphasis
added], water and sewer systems, dams, and lighting systems. Buildings, except those that are an
ancillary part of a network of infrastructure assets, should not be considered infrastructure assets for
purposes of this statement."

In the excerpt below, Statement 34 encourages asset management:

[Depreciation expense] may be calculated for (a) a class of assets, (b) a network of assets,1 (c) a
subsystem of a network," or (d) individual assets...

Infrastructure assets that are part of a network or subsystem of a network1" (hereafter, eligible
infrastructure assets) are not required to be depreciated as long as two requirements are met. First,
the government manages the eligible infrastructure assets using an asset management system that
has the characteristics set forth below; second, the government documents that the eligible
infrastructure assets are being preserved approximately at (or above) a condition level established
and disclosed by the government.™ To meet the first requirement, the asset management system
should:

a.	Have an up-to-date inventory of eligible infrastructure assets

b.	Perform condition assessments7 of the eligible infrastructure assets and summarize the results
using a measurement scale

c.	Estimate each year the annual amount to maintain and preserve the eligible infrastructure assets
at the condition level established and disclosed by the government.

1 A network of assets is composed of all assets that provide a particular type of service for a
government. A network of infrastructure assets may be only one infrastructure asset that is
composed of many components. For example, a network of infrastructure assets may be a dam
composed of a concrete dam, a concrete spillway, and a series of locks. [This footnote

" A subsystem of a network of assets is composed of all assets that make up a similar portion or
segment of a network of assets. For example, all the roads of a government could be considered a
network of infrastructure assets. Interstate highways, state highways, and rural roads could each
be considered a subsystem of that network.

42 Governmental Accounting Standards Board. 1999. Basic Financial Statements—and Management's Discussion
and Analysis—for State and Local Governments.

http://www.gasb.org/cs/ContentServer?site=GASB&c=Document C&pagename=GASB%2FDocument C%2FGASBD
ocumentPage&cid=1176160029121

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III	If a government chooses not to depreciate a subsystem of infrastructure assets based on the
provisions of this paragraph, the characteristics of the asset management system required by this
paragraph and the documentary evidence required by paragraph 24 [which leaves documentation
to professional judgment] should be for that subsystem of infrastructure assets.

IV	The condition level should be established and documented by administrative or executive policy, or
by legislative action.

v Condition assessments should be documented in such a manner that they can be replicated.
Replicable condition assessments are those that are based on sufficiently understandable and
complete measurement methods such that different measurers using the same methods would
reach substantially similar results. Condition assessments may be performed by the government
itself or by contract.

The Louisiana Division of Administration spoke for the vast majority of public sector entities across the
U.S. when it recommended in 1999 that the state "...choose the alternative, to depreciate the
capitalized infrastructure assets. We feel that this is the most cost-effective approach for reporting since
there would not be any significant burden involved in depreciating the infrastructure assets once they
have been identified and capitalized. The schedules of capitalized infrastructure assets would simply
include a column to compute the amount of annual depreciation. Under the modified approach, the
capitalization requirements are the same as under the depreciation alternative. However, the cost and
effort to follow the requirements of the modified approach would be significant and therefore more of a
burden than depreciating the infrastructure assets. In addition, with the uncertainty of state funding to
cover the additional costs of maintaining the state's infrastructure at specified condition levels as
prescribed in the modified approach, it is possible that the state would have to revert to the
depreciation alternative at some point in the future and face a qualification in the year we fail to
maintain at the designated level."43

To date, less than 10 percent of the roughly 42,15844 units of government are estimated to be using the
modified approach. Municipal finance officials already face burdensome reporting and financial
statement preparation requirements that greatly inhibit their ability to produce independently audited
financial statements much before 120 to 180 days from the end of the previous fiscal year. Assuming
infrastructure assets have an expected useful life of 10 to 30 years, this completely ignores changes over
time in inflation, labor, building materials and technology and potentially introduces a very material gap
between "book value" and replacement cost. In a 2017 piece of research, RBC Capital Markets noted, "A
comprehensive inventory of public assets is a critical prerequisite to identifying opportunities to create
new value."45 Reliance instead on a depreciation-based, historical cost reckoning of infrastructure assets

43	Louisiana Division of Administration, n.d. "GASB Statement 34 Implementation Issues: Infrastructure
Reporting—Modified Approach vs. Depreciation."

http://www.doa.la.gov/osrap/librarv/gasb34/infrastructure%20reporting.pdf

44	Hogue, C. 2013. Government Organization Summary Report: 2012.

https://www.census.gov/content/dam/Census/librarv/publications/2013/econ/gl2-cg-org.pdf. (This Census
summary identifies 38,910 general purpose governments. It excludes special and school districts but does include
3,248 special districts categorized as "drainage and flood control.")

45	RBC Capital Markets and HR&A Advisors. 2017. "Unlocking Value from Public Assets: Leveraging Private-Sector
Expertise to Generate New Public Benefits." p. 46.

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rather than an assessment that explicitly correlates asset condition to financial value not only introduces
public policy-making risk but also makes it more challenging to establish a baseline FCA.

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Appendix II: Case Studies

1.	Washington, D.C. Stormwater Retention Credit Trading:

The U.S.'s First Stormwater Retention Trading Market in the Nation's Capital

2.	Four San Francisco Bay Area Voter-Approved Fee Measures:

Stormwater Infrastructure User Fees

3.	Stormwater Utility Goodlettsville, TN:

Watershed Protection through Stormwater Management

4.	Los Angeles Parcel Tax Approved by Voters in 2018 (Measure W):

Stormwater Infrastructure User Fees

5.	How Operation and Maintenance Costs Effect Resiliency in Coralville, Iowa:

Managing Flooding and Quality of Life

6.	Stormwater Utility, Downers Grove, IL:

Flood Risk Reduction, Erosion Control, Water Quality Protection, and Drainage
Infrastructure Management

7.	Watershed Protection in Austin, TX:

Flood Risk Reduction, Erosion Control, Water Quality Protection, and Drainage
Infrastructure Management

8.	Stormwater Program Implementation in Atlanta, GA:

Water Quantity (Aging Infrastructure, Flood

Management, Drainage) Water Quality (Regulatory Compliance, TMDLs), Expanding
Expectations (public outreach, multi-use areas)

9.	Washtenaw County, Michigan:

Summary Report of Stormwater Program Needs

10.	City of Raleigh, North Carolina:

Basin Master Planning

11.	City of Bellevue, WA Storm and Surface Water System Plan 2015:

WQ, Flood, Infrastructure, WIPs, Drainage

12.	City of San Diego:

Watershed Asset Management Plan (2013)

13.	Grand Rapids, Ml:

Flood Protection, Sediment Reduction, and Stormwater Quality Compliance in Water
Quantity (MS4 Permit and TMDLs Compliance)

14.	Griffin, GA:

Stormwater Pipe Assessment: Water Quantity (Infrastructure, Drainage)

15.	Ventura County, CA:

Flood Protection and Stormwater Quality Compliance

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Water Quantity (Flood Protection) and Water Quality (MS4 Permit and TMDLs
Compliance)

16.	Stormwater Utility, Lawrence, KS:

Flood Risk Reduction, Erosion Control, Water Quality Protection, and Drainage
Infrastructure Management

17.	Metropolitan Water Reclamation District of Greater Chicago:

Working hard to manage stormwater, clean wastewater and recover valuable resources,

18.	Stormwater Environmental Utility, Sarasota, FL:

Control water quantity, enhance water quality, effectively manage stormwater

Figure 5. Map depicting the location of various utilities included in the case studies.

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Washington, D.C.
Stormwater Retention
Credit Trading

The U.S.'s First Stormwater Retention
Trading Market in the Nation's Capital

In 2013 Washington, D.C. promulgated new

stormwater retention regulations for new development or substantial
improvement projects. Part of these new regulations was the introduction
of the Stormwater Retention Credit Trading market, which allows these
regulated projects to purchase up to 50% of their stormwater
management requirements offsite, in the form of Stormwater Retention
Credits (SRCs). This allows regulated properties to pursue more cost-
effective compliance methods and provides financial incentives for
properties to voluntarily install stormwater management practices. The
underlying regulation and the new market are designed to help the
District meet its MS4 permit requirements and 2025 TMDL goals in a cost-
effective way, using private investment and private property.

Challenges

County or Municipality
Washington, D.C.

Population
702,445

Annual Rainfall
40.78 inches

Land Area
68.34 square miles

Poverty Level
17.4%

Total Identified Need
$10 billion?

Annual Capital Budget
$10 million?

Annual O&M Budget
N/A

Polluted stormwater runoff is a primary threat to water quality
nationwide and is one of the biggest threats to the Chesapeake Bay. The
Chesapeake Bay is the largest and most productive estuary in North
America. Economists value fishing and hunting, tourism, and shipping
activities along with increased property values in the Bay at over $1 trillion
per year. Stormwater runoff represents the second largest source of
nutrient and sediment pollution and is the only sector in the Chesapeake
watershed growing in its impact, due to population growth and land
development. At the same time, many cities are struggling to finance the water infrastructure
improvements needed to prevent stormwater runoff.

Washington, D.C. is 43% impervious and is a major source of this stormwater runoff, which impacts the
local Anacostia River, Potomac River and Rock Creek as the water flows out to the Chesapeake Bay.
However, getting retrofits installed to serve the 43% of D.C.'s land area that is impervious is a difficult
challenge. The majority of this impervious surface achieves little or no retention, is not required to
retrofit, and does not have financing available to support a retrofit.

Further, Washington, D.C.'s Department of Energy and the Environment (DOEE) estimates that to meet
its permit requirements and achieve its water goals, $10 billion in investment is necessary. However,
DOEE only collects ~$10 million in revenue per year.

Solution

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DCs Department of Energy and the Environment (DOEE) has developed a first-of-its-kind in the country
stormwater retention credit trading program for new development and major renovations. This
program requires new projects to retain the stormwater generated from their development. However,
to help land-constrained property owners meet these requirements, the city instituted a credit market
for stormwater, which allows these regulated projects to purchase up to 50% of their stormwater
management requirements offsite, in the form of Stormwater Retention Credits (SRCs). The SRC market
was designed with two goals in mind: i) provide a cost-effective solution for developers to meet their
retention requirements, while achieving significant co-benefits for the city; and ii) allow the District to
meet its own green infrastructure goals at a lower cost than it could using only public land and financing.
Currently, SRCs are trading at close to half the cost of public delivery of equivalent infrastructure and it
is estimated that the 2013 rule and subsequent SRC activity will increase spending on stormwater
mitigation by lOx historic public investment. Further, DOEE recently introduced a public purchase
program, Price Lock, whereby the District purchases projects at a market rate that best meet DOEE's
clean water goals. These public purchases reduce the cost of compliance for the District and help bolster
development of credit supply in parts of the District where stormwater mitigation is most needed.

Mitigating runoff at the cheapest cost possible is a major hurdle for jurisdictions in the Bay and around
the country. Washington, DC is using the SRC market to prove that market forces can accelerate the
deployment of green infrastructure through private investment and in doing so, obviate the need for
future public gray infrastructure spending to reduce stormwater runoff.

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Stormwater Utility
Goodlettsville, TN

Watershed Protection through
Stormwater Management

Overview

GOODLETTSVILLE

The City of Goodlettsville, TN is located in the North Central area of
middle Tennessee. In 2013, the City completed a Stormwater
Management Master Plan identifying the city's drainage basins and
recommended the enactment of a stormwater utility fee as a
dedicated funding source.

History

The Stormwater Utility Ordinance, implemented in 2013, is organized
into three main sections: Capital Improvements, Capital Maintenance,
and Engineering review. The utility is responsible for all activities
related to the operation and maintenance of the stormwater system,
including master planning, the capital improvement program, and
inspections.

As one of the first stormwater utilities created in middle Tennessee,
the City of Goodlettsville has been a leader among local governments
in developing such a program. The City of Goodlettsville assesses its
residential customers on Equivalent Residential Units (ERU's) which are
based on the effective impervious area of the average single-family
parcel of $3.67 per month. The assessment of Commercial and
Industrial properties are based on the actual impervious surface with
on ERU equivalent to 2900 sq. ft. at $5.50 ea. per month.

County or Municipality
City of Goodlettsville, Tn.

Population
16,859 (2018)

Annual Rainfall
62.3 inches

Land Area
14,1 sq. mi.

Poverty Level
18.1%

Total Identified Need
$1,250,000.00

Annual Capital Budget
$400,000.00

Annual O&M Budget
$850,000.00

Flooding Level of Service is intended to protect habitable structures up to the 100-year, 24-hour rain
event. Water quality requirements from regulatory ordinances include all new development or re-
development of greater than one acre, or less than one acre if part of a larger common plan.

Capital Needs

To-date, the City has collected $3,200,000 in stormwater utility fees and has spent $1,400,000.00 in
stormwater flood improvements, operations and maintenance throughout the city. Since
implementation of the program, a rate increase has not occurred and the program has not taken out
loans to fund projects. Future projects include Drainage Basin Area Study, Box Culvert Replacement and
Upgrades, Major Roadway Drainage Study, and completion of a Flood Mitigation Program

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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How Operation and
Maintenance Costs Effect
Resiliency in Coralville,
Iowa

Managing Flooding and Quality of Life

The City of Coralville funds the operation and
maintenance of stormwater infrastructure through a
local stormwater utility fee, property taxes, and
federal/state road use tax.

Operation and maintenance activities related to local
water quality include compliance of the City's MS4
permit, which consists of staff time, training, and maintenance of water
quality practices installed as part of public infrastructure projects
(roadway projects); street sweeping; and catch basin cleaning.

Operation and maintenance activities related to flood control and
water quantity include staff time and training, maintenance of the
flood protection system (pump stations, permanent flood
walls/barriers, earthen berms, and detention basins), and maintenance
of the storm sewer system (catch basins, pipes, and outfalls).

In the last 25 years, Coralville has experienced two major flooding
events on the Iowa River. In 1993, a flood described as a "100 year
event" devastated homes and businesses, and caused millions of
dollars in damage. Of the businesses affected, 20% chose to not
rebuild. In 2008, the Iowa River flooded again. This time, it was a 500
year event with costs totaling $21 million for commercial properties, $4
million for residential properties, and $7 million in damages to public
infrastructure. After the 2008 flood, 40% of the businesses chose to
not rebuild.

County or Municipality
Coralville, Iowa

Population
21,664

Annual Rainfall
37"

Land Area
12 Sq miles

Poverty Level
14% of citizens are
considered impoverished

Total Identified Need
3 Million

Annual Capital Budget
$0

Following the 2008 flood, Coralville was awarded $65 million in federal

and state grants to create a flood control system, which the City implemented. This permanent flood
control system is essential to protecting our community. Maintaining the floodwali and stormwater
pump stations accounts for 40% of the total stormwater budget. The remaining budget covers staff and
all other operations and maintenance-related activities mentioned above, leaving a deficiency in
maintenance objectives and very little funding for capital improvement projects. One of the largest
deficits can be seen in the maintenance of our regional detention ponds. These ponds protect residents

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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from localized flooding events driven by heavy rainfall. This maintenance cost is estimated at 3 million
now with an annual expense of $50,000 in continuing unmet need.

One of the largest complaints Coralville receives from residents is related to localize flooding concerns
on their property. Residents expect their municipality to protect them from flooding, whether it is from
the Iowa River or stormwater in the roadway or behind their home. Maintaining regional detention
ponds and the local storm sewer system is essential for reducing the risk of localized flooding. The
maintenance of local detention ponds is not being completed due the deficit in the stormwater budget.

Over the past five years, the Iowa Flood Center has observed a 40% increase in the precipitation
amounts of large rain events. We see that data in action. We are experiencing an increased need to
protect our community during these heavy rain events. We project that the ongoing maintenance
requirements of our system will increase as our storm events become larger and more destructive.

None of our stormwater systems are large enough to carry the rain events we have been experiencing.
The oldest sections of town, where the storm systems tend to be the most undersized also coincide with
our most impoverished and vulnerable populations.

Without additional funding to support the operation and maintenance cost of our stormwater system,
we will continue to fall further behind. As storm events increase in size, these systems will be essential
to protecting the quality of life of our residents.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Stormwater Utility,

Downers Grove, IL

Flood Risk Reduction, Erosion Control,

Water Quality Protection, and Drainage
Infrastructure Management

Overview

The Village of Downers Grove, IL is located 22 miles
west of Chicago. In 2006, the Village adopted a Stormwater
Master Plan that provided information about the existing
stormwater problems in the Village, the condition of the
stormwater system, the adequacy of system components, and
estimated costs for necessary maintenance, capital improvements
and regulatory requirements at the time of publication,

A Stormwater Utility Fee was established in 2012 to provide a
dedicated revenue for the identified stormwater management
needs.

History

This 2006 Master Plan document provided the Village with
information for establishing strategies for future infrastructure
management, identifying preliminary budgetary needs, and
identifying alternatives for financing an adequate stormwater
program.

Prior to the Stormwater Utility, operating costs for the
stormwater system were funded primarily through property
taxes. Shifting the source of funding to a utility/fee-based system
resulted in a reduction in the property tax levy by approximately
$2.48 million, beginning with the 2012 levy.

The Stormwater Utility Fee model represents an equitable
method to collect revenue from those properties that place a
demand on the system. Revenue is generated by charging all
property owners a monthly stormwater fee, based on the
property's impact to the stormwater system. The Village has
created a plan that increases revenues over a 15-year period,
allowing the Village to move from the current level of service to
the recommended level within that time frame.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

• • •

87

County or Municipality
Village of Downers Grove, Illinois

Population
49,649

Annual Rainfall
38" (Illinois)

Land Area

•	Approximately 7,000

drainage structures
• 315 stormwater detention
facilities

• 130 miles of storm sewer
pipes

• 12 miles of streams

•	140 miles of roadway

ditches

• 47,000 feet of culverts.

Poverty Level
5.39%

Total Identified Need
$340M

Annual Capital Budget
FY19 Budget includes $7.08M for
stormwater capital projects.

Annual O&M Budget
$2M


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The plan calls for annual increases in the stormwater utility fee of approximately 8.5% per year, which
would increase the annual revenue available for stormwater management fees from the level of $4.6
million to about $11.4 million in 2028.

Capital Needs & Funding Sources

The 2007 Watershed Infrastructure Improvement Plan identified estimated cost of $340 million for
stormwater management projects. The more recent 2014 Stormwater Project Analysis identified 17
non-floodplain and 3 floodplain projects to provide 95% protection for the 21 areas throughout the
Village that were identified as significantly impacted by the April 2013 floods. The estimated cost to
complete the 17 non-floodplain projects is $11.6M and they are planned to be completed in 2020. The
annual cost for stormwater maintenance activities are $2.0M each year. However, it would cost about
$4 million per year to perform the recommended annual maintenance activities.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Watershed Protection in
Austin, TX

Flood Risk Reduction, Erosion Control,
Water Quality Protection, and Drainage
Infrastructure Management

Overview

The mission of the City of Austin's Watershed Protection
Department (WPD) is to protect the lives, property, and
environment of the community by reducing the impacts of
flooding, erosion, and water pollution. The department provides
services for the City of Austin and its extraterritorial jurisdiction
through a combination of capital improvement projects,
operating programs, and regulations. The department also serves
as the City's drainage utility—it is responsible for the operation,
maintenance, renewal, and upgrade of the public stormwater
infrastructure system. This includes the inspection and
maintenance of assets that convey, store, and treat stormwater
runoff while complying with state and federal regulatory
requirements, such as the Municipal Separate Storm Sewer
System (MS4) permit issued by the Texas Commission on
Environmental Quality (TCEQ).

Over the years the City of Austin has received numerous awards
for its watershed protection and management programs. In
2017, the Watershed Protection Department was the highest
scoring Phase I MS4 program nationally among those submitting
nominations for the annual Water Environment Federation /
USEP MS4 awards program. Austin was also received gold-level
recognition that year for innovation and for program
management.

History

For more than three decades, WPD has been recognized as a
national leader in watershed protection. The two most important
events that helped shape the City's watershed protection
program were uncontrolled development in the late 1970s and
the Memorial Day Flood of 1981 In the late 1970s, sediment
from widespread construction visibly entered Lake Austin, the
City's water supply, and Barton Creek, a beloved community

City of Austin, Texas
Watershed Protection
Department

Population (Jan 2019)
981,035

Average Annual Rainfall
34 inches

Estimated Rainfall in 24-
hour Storm Event
25-year: Up to 9 inches
100-year: Up to 13+ inches

Land Area
326 sq. mi.

Poverty Level (Jan 2018, U.S.

Census)
15.4%

Total Identified Capital Need
(10-Year Planning Estimate)
$2 billion

Annual Capital Budget
(FY19)

$35 million annual transfer +
developer mitigation fees +
bonds

Annual O&M Budget (FY19)
$104 million

Workforce (FY19)
349 full time employees
26 temporary employees

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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swimming and hiking area. Public concern led to calls for improved environmental protection through
water quality and erosion controls for development. Around the same time, the Memorial Day Flood of
1981 underscored Austin's geographic location in what is known as America's "Flash Flood Alley"—an
area of unusually intense flooding events. In response to the storm's devastating effects and loss of life,
the City implemented a Drainage Charge in 1982 to provide funding for an expanded stormwater
management program. In 1991, the City established a Drainage Utility to oversee and directly fund its
stormwater management programs. The Watershed Protection Department (WPD) was created in 1996
through the merging of the flood and erosion programs in Public Works with the water quality
protection programs of the Environmental and Conservation Services Department.

Capital Needs and Funding Sources

To fund its capital projects, WPD utilizes a combination of funding sources, including general obligation
bonds, drainage fees, payment-in-lieu developer mitigation programs, and Certificates of Obligation
from tax increment financing.

The department has identified more than $2 billion in capital needs to address the City's most severe
flood, erosion, water quality, and infrastructure maintenance needs over the next 10 years. With an
estimated capital budget of approximately $700 million over that same timeframe, the department
utilizes principles defined in the department's Watershed Protection Master Plan, Strategic Asset
Management Plan, and City of Austin Long-Range CIP Strategic Plan to prioritize solution
implementation within its budget.

The department continues to evaluate and update its best practices for stormwater management and
CIP prioritization by incorporating community priorities, policy decisions, and the latest technical data,
such as the Atlas 14 historic rainfall study.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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EFAB Stormwater Case Studies

Stormwater Program Implementation in
Atlanta, GA

Water Quantity (Aging Infrastructure, Flood
Management, Drainage), Water Quality (Regulatory
Compliance, TMDLs), Expanding Expectations (public
outreach, multi-use areas)

The City of Atlanta is a regional center located in the
Southeastern United States. Situated in the headwaters of
two river basins, the City provides drinking water,
wastewater, and watershed management services to nearly
half a million people within the City's jurisdictional
boundaries and some areas outside the boundaries. The
Department of Watershed Management (DWM) is
responsible for the NPDES MS4 permit in addition to state
and regional requirements. DWM stormwater functions
include watershed improvement planning, drainage
improvements, asset management, water quality
improvements, regulatory compliance, and public education
and outreach. The City has a combined sewer system (CSO),
which has resulted in increased emphasis on stormwater
infiltration practices to reduce the stormwater runoff load
to the CSO.

Stormwater Program Funding

County or Municipality
City of Atlanta, GA

Population
498,044 (2018 US)

Average Annual Rainfall
49.71 inches (NOAA)

Land Area
136.7 sq. mi.

Poverty Level
22.4% (U.S. Census)

Total Identified Needs
FTEs -122

Annual Operating Costs - $12 million
Annual Capital Costs - $18 million
Annual Total Costs - $30 million

Current Capital and O&M Budget
FTEs - 60.5

Annual Operating Costs - $6.6 million
Annual Capital Costs - $12.5 million
Annual Total Costs - $19 million

The City of Atlanta does not have a dedicated funding
source for stormwater management activities and
stormwater management is currently limited to meeting
regulatory mandates and addressing emergency repairs.

Much of the existing stormwater drainage infrastructure
within the City is nearing the expected lifespan and will
need to be repaired or replaced. In addition, many

customer requests for stormwater infrastructure improvements have not been addressed due to the
lack of adequate funding.

Increasing stormwater-related regulatory requirements, changing weather patterns, more frequent
nuisance flooding issues, and aging infrastructure needs have prompted the DWM to consider a
dedicated funding source and develop annual operating and capital funding needs. An evaluation of
future resource needs identified 122 full time equivalent (FTE) employees, $12 million in annual
operating costs, and $18 million in annual capital expenditures to meet stormwater program

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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requirements and level of service. This is an approximately 50% increase over current resource and
funding levels.

Extent of Service Area

Stormwater services will be provided for the following areas:

*	Municipally owned rights of way

*	Municipally owned drainage easements

*	Municipally owned ponds and structural stormwater control facilities

*	Rivers and streams on municipally owned property or the ROW

The City's inventory within municipally owned property or within public Right of Way includes an
estimated 150 miles of stormwater pipe; 9,500 catch basins; 10,000 headwall, manholes, outfalls,
culverts, and other miscellaneous stormwater structures. A significant portion of this stormwater
infrastructure is not maintained on a routine basis; is reaching the normal engineering lifespan and is in
need of repair or replacement. Stormwater facilities on private property are excluded from the City's
Extent of Service.

The City of Atlanta is a leader in implementing green infrastructure programs and developing creative
funding solutions such as MOST, grants, and an Environmental Impact Bond. However, meeting the
identified funding needs gap will take additional creative planning, coordination, and communication
with local and national stakeholders.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Washtenaw County Michigan

Summary Report of Stormwater Program Needs

We have completed Master Plans for some of our larger sub-
systems (8 of some 550). We have an asset management plan
(AMP), but no predictable means of planning capital work due
our organizational structure as a special assessment agency by
statute. Our current goal is to increase annual spending on
minor, pro-active preventative maintenance where we have
authority (we can spend $0.97 per foot of drain without a
petition). We are working to raise awareness of capital needs to
achieve a goal of petitions that result in $5-$10M of capital
projects annually. Information from our AMP suggests that
we could proceed for 10-15 years in this fashion (working on
whatever people are willing to ask us to work on at their
expense) without compromising any logical sequence of
capital improvements.

Our system replacement value is estimated at $430M in
today's dollars. Our data source is our Asset Management
Plan which indicates that about 15% of our system is in
immediate need of replacement due to complete lack of
function. We are currently seeking to raise awareness of
these and other poorly performing sections of infrastructure
with those who would pay. Our only mechanism for capital
project initiation is by petition, so long-range planning is a
challenge. Because we can receive a petition from either a
group of citizens or as a Resolution from a municipal agency,
we have started a process of seeking regular approval of
major maintenance on an annual basis with municipalities
within our jurisdiction. We have currently done this with 6 of
the 28 municipalities and hope to use this process for capital
work also. We have currently done a 5-year plan with each.
The idea is to annually have an approved one-year budget
and acceptance of a rolling 5-year budget forecast - for most
of our municipalities.

County or Municipality

Washtenaw County, Ml

Population

360,000

Annual Rainfall

35 inches

Land Area

446 square miles

Poverty Level

14.5% population below poverty level

Total Identified Need

$64.5 million

Annual Capital Budget

Varies by petitions received

Annual O&M Budget

$4.1 million

Due to having systems that pre-date current water quantity management design standards, all of our
capital work focuses on improving water quality while striving to maintain the quantity management of
the original system. In some cases, the water quality measures (such as extended storage) may provide
an ancillary quantity benefit in smaller storms (85th percentile or smaller, so first flush to one-year
storm sizes may have quantity benefit).

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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The County does include MS4 permittees, but not the entire system as our service area includes
urbanized and rural census tracts. Generally, our enclosed pipes in our urbanized area are designated
MS4s and open ditches are not. Our biggest problems are in the urbanized areas but those are generally
not available for federal or state funding for improvements, because we are supposed to be responsible
for those through the unfunded mandate of MS4. (Incidentally, the Ml State Supreme Court ruled that
MS4 regulations were NOT an unfunded mandate, stating that [paraphrased] "municipalities have never
been mandated to provide drainage systems, so MS4 regulations only apply to those communities who
have chosen to have stormwater systems.").

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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City of Raleigh, North
Carolina

Basin Master Planning

We have developed a preliminary estimate of citywide needs
related to stream stabilization/restoration, which has not
been included in past studies. The preliminary estimate for
citywide stream stabilization/restoration needs is approximately $120 million, which is beyond stream-
related projects identified in the basin studies. Within the past several years, the City's Stormwater
Program has also expanded its scope and assumed responsibility for City owned/operated Stormwater
Control Measures (SCMs) and Dams. Approximately $10 million in capital repair needs has been
identified for dams while assessment continues for both SCMs and Dams.

Annual O&M Budget
$14.3 million

The City of Raleigh has performed and completed a number
of past drainage basin and watershed-based studies.
Approximately % of the city area has been covered by basin
studies, although some of these were completed more than
twenty years ago. The studies have looked primarily at
infrastructure hydraulic capacity and flood hazard reduction
needs and projects. Some studies have also reviewed water
quality-related needs with projects identified including lake
restoration/retrofit and stream stabilization/restoration
opportunities along with other water quality-oriented
projects. Recently (earlier in 2019) the City completed the
first phase of a multi-phase integrated watershed master
planning project. As part of this recent work, the City asked
its consultant to identify and summarize stormwater projects
identified from past basin studies but not yet constructed. In
this context, the total of stormwater projects identified from
past basin studies is approximately $280 million, escalated to
2019 dollars.

In addition to this, the City has approximately $60 million of
projects that are assumed to be beyond what has been
identified from past studies. The current CIP plan includes
master planning, water quality retrofits, flood hazard
reduction, lake-related projects, stream restoration, and
neighborhood and street drainage system repair projects.

County or Municipality
Raleigh, NC

Population
458,862

Annual Rainfall
46 inches

Land Area
145.98 square miles

Poverty Level
16.8% households under $25K income

Total Identified Need
$470 million

Annual Capital Budget
$11.1 million

In summary based upon the above, a preliminary estimate of capital improvement program needs for
the City's Stormwater Management Program is approximately $470 million.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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The planning period for this portfolio is assumed as 20 to 30 years, although implementation will be a
function of future stormwater program revenues that may be available over time. (Note this
preliminary planning level CIP total does not include the estimated annual needs for MS4 operation,
maintenance, and MS4 repairs and rehab from a developing asset management perspective. The annual
needs related to asset management are included within the response to Question #3.)

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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City of Bellevue, WA Storm and Surface Water
System Plan 2015

WQ, Flood, Infrastructure, WIPs, Drainage

The City's Storm and Surface Water plan evaluates the
operational management of the Utility, providing a
"roadmap" for future planning. It is a tool to help the
City meet federal, state, and regional regulations. Key
focus areas include: control damage from storms (100
year, 24 hour storm event), protect surface water quality
support fish and wildlife habitat and protect the
environment.

Primary challenges include aging infrastructure, reduced
forest cover, global climate change and a new class of
pollutants has emerged as a potential threat to aquatic
and human health over the last decade. Pharmaceuticals
and endocrine disrupters (found in some pesticides or
other products applied to the landscape) are increasingly
being detected in receiving water bodies. Stormwater
has been identified by the Puget Sound Partnership as a
primary pressure impacting the health of Puget Sound.

Bellevue does not have widespread flooding problems.

The City is in 100% compliance with Phase II NPDES
Municipal Permit

2016 - 2019). No debt funding

Rate Structure: Accounts are billed at different rates

depending on the intensity of development	Annual O&M Budget

(undeveloped, lightly developed (20%), moderately	$13.4 million (average $12.5 2016 - 2019)

developed (40%), heavily developed (70%), very heavily
developed (over 70%) and wetlands). 2019 rates include

billing charge $5.88, plus charge per 2,000 square feet depending on intensity of development noted
previously, $0 wetlands, $.098 undeveloped, $7.08 lightly developed, $8.84 moderately developed,
$13.26 heavily developed and $17.65 very heavily developed.

Bellevue has a successful and established asset management program.

The Renewal and Replacement (R&R) reserves were established by the City Council in 1995 to better
position the City for the future by planning for the inevitable replacement of the utility system
The Utilities Department has assets with a replacement value of over $3.5 billion in 2010 dollars, and
about half of this aging infrastructure is past mid-life.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

County or Municipality

City of Bellevue, WA

Population

147,599 (recent US census estimates)

Annual Rainfall

42 inches of rain, on average

Land Area

86.66 (33.46 square miles)

Poverty Level

7.37% of overall population. Median
household income 2019 $105,000

Total Identified Need

$275 million next 20-years

Annual Capital Budget

$13.5 million annual rate funded capital
from operations and asset replacement
account funding (average $11.5 million

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Accumulating R&R reserves in a measured way to pay for the proactive replacement of aging systems
before they fail. Managing reserves that fund the replacement of that infrastructure is critical to
financial sustainability. R&R reserves ensure that the Utilities Department is financially prepared to
respond to emergency events. Use of R&R reserves is governed by state law and the Utilities financial
policies (established by City Council resolution in 1995; see Chapter 4 Policies).

R&R needs are projected using asset management data to determine the timing and estimated cost of
replacing systems over time. Annual revenues set aside for infrastructure replacement are based on
projected replacement cash flow needs over a 75-year forecast period less projected interest earnings.
In 2015, the storm and surface water repair and replacement fund had a balance of $43.8 million and
projected to increase to $70 million by 2044 (Figure 6).

Recommendations include:

Continue investing in the Flood Control Capital Program to reduce or eliminate local flooding caused by
insufficient public drainage system capacity. Continue to use King County Flood Control Zone District
Sub-Regional Opportunity funds. Invest in cost-effective water quality projects. Consider emerging
technologies and techniques that improve water quality for pilot projects. Continue to invest in the Fish
Passage Improvement Program to remove fish passage barriers created by impassable culverts, debris
jams, or accumulated sediment, which opens spawning and rearing habitat for salmon populations.
Continue to invest in the Stream Channel Modification Program to construct habitat improvements on
stream channels. Invest in the Stream Restoration for Mobility and Infrastructure. Continue to invest in
the Stormwater System Conveyance Infrastructure Rehabilitation Program to rehabilitate or replace
defective storm drainage pipelines and ditches identified in the condition assessment program.
Continue to invest in Minor (Small) Storm and Surface Water Capital Improvement Projects, to resolve
deficiencies, improve efficiencies, or resolve maintenance problems. When possible, complete in
conjunction with other Bellevue programs such as the transportation overlay program.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Description

20-Year Total % of Total

Minor Storm & Surface Water Capital Imp. Projects

$

2,052,000

0.75%

Storm WaterSystem Conveyance Infrastructure Rehabilitation

$

10,457,000

3.80%

Replace Coal Creek Pkwy. Culvert at Coal Creek

$

26,000

0.01%

Replace NE 8th St Culvert at Kelsey Creek

$

136,000

0.05%

Stormwater Pipeline Video Inspection Enhancement

$

246,000

0.09%

Long-Term R&R- Mains

$

97,492,738

35.41%

Long-Term R&R - Facilities

$

348,166

0.13%

Long-Term R&R - Additional Costs

$

6,852,242

2.49%

Long-Term R&R- Contingency (40% of Aging Infrastructure)

$

39,136,362

14.21%

Fish Passage Improvement Program

$

2,533,000

0.92%

Stream Channel Modification Program

$

3,642,000

1.32%

Flood Control Program

$

5,790,000

2.10%

Stream Restoration for Mobility & Infrastructure Initiative

$

108,000

0.04%

Lower Coal Creek Flood Hazard Reduction

$

6,128,000

2.23%

Storm Water Quality Retrofit in Kelsey Creek

$

342,000

0.12%

Long-Term Environmental Preservation Projects

$

36,752,063

13.35%

Long-Term Mobility & Infrastructure Projects

$

63,295,219

22.99%

Long-Term Mandate Compliance Projects

$

-

0.00%

Total

$

275,336,791

100.00%

Figure 6. 2015 stormwater-related budget for the City ofBellevue, WA.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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City of San Diego

Watershed Asset Management Plan (2013)

In order to anticipate and justify current and projected
costs of complying with federal, state, and local
stormwater regulations, the City of San Diego developed
an integrated Watershed Asset Management Plan
("WAMP") for its stormwater management system. The
WAMP was finalized in 2013 and aims to lay the
groundwork for meeting regulatory requirements by
'annualizing' long-term compliance needs as well as documenting
and communicating expectations of citizens regarding functions of
the storm drain system and the quality of water and related
services. The first element of the WAMP assesses the current
inventory, costs, and condition of the City's stormwater system.

Assets are categorized as "hard," "natural," or "soft" and valuated
accordingly. After assessing the current state of City-managed
assets, the WAMP goes on to quantify a long-range forecast of
funding necessary to maintain a baseline level of service. The
projections are calculated using a custom-built database which
balances refurbishment and replacement costs to keep assets
functionally above a minimum acceptable threshold. The result of
this forecasting projected a 100 year need of nearly $20 billion (in
2013 dollars); equating to about $200 million per year, accounting
for regulatory compliance, capital, and O&M costs. Lastly, the plan
articulates various potential funding sources and scenarios for
achieving targeted levels of service. Scenarios range from current
budget to full funding attainment and lay out resulting backlog of
needed infrastructure upgrades that would result from each
scenario. Developing a WAMP is an iterative process requiring
continual input from stakeholders, new or improved data, and
updates to fiscal modelling efforts as awareness of costs becomes
more sophisticated, particularly in accounting for effects of climate

change. Currently, the City is undertaking a comprehensive update of its WAMP in order to reflect new
regulations, assets, and cost estimates. The process of developing a WAMP can also serve to inform the
regulatory process. In particular, an asset management perspective in context of a TMDL could
substantiate reasonable compliance schedules for water quality attainment. In the context of
stormwater permitting, an asset management plan could be used as a compliance mechanism
alternative to meeting water quality-based limitations.

1	E-l Population Estimates. Demographics. California Department of Finance website.

2	Western Regional Climate Center website

3	2018 Census Gazetteer Files-Places. United States Census Bureau website

4	United States Census Bureau website-QuickFacts City of San Diego.

City of San Diego Watersheds

County or Municipality
San Diego, California

Population
1,419,845 million-

Annual Rainfall
10.13 inches2

Land Area
325 square miles3

Poverty Level
14.5%4

Total Identified Need
$3,128,424,9385 (FY2019-35)

Annual Capital Budget
$2,666,667 (FY2020)

Annual O&M Budget
$51,967,670 (FY 2020)

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Grand Rapids, Ml

Flood Protection, Sediment Reduction, and Stormwater Quality Compliance
Water Quantity (MS4 Permit and TMDLs Compliance)

The Environmental Services Division (ESD) is responsible for managing stormwater within the City of
Grand Rapids. The primary goals of the City's
stormwater program are to reduce the impacts of
flooding and erosion (water quantity) and to improve
water quality in local rivers, lakes, and streams. This
includes complying with the City's MS4 permit and
TMDL requirements for E. coli and biota. To help meet
these goals, the City developed a stormwater master
plan that incorporates a 20-year asset management
plan and capital improvement plan (CIP), as well as
other stormwater- and sustainability-related City
initiatives.

County or Municipality

City of Grand Rapids Environmental Services

Division, Ml

Population

198,829 (2017)

Annual Rainfall

37 inches

Land Area

45.3 square miles

The City's asset management plan identifies four level
of service scenarios for stormwater management,
including three new levels of service (A, B, and C) and
the existing level of service. The new levels of service
were designed to meet regulatory requirements, goals
for infrastructure renewal and replacement, and
operations and maintenance. In addition, each
scenario allocates a percentage of capital investment
to green infrastructure practices. Under the City's plan,
level of service A represents the highest level of
service, while B and C result in subsequently lower
service requirements.

Poverty Level

15.8% (persons in poverty, 2017 1-year

estimate)
MHI $48,521

Annual Revenue

$599,986 (FY 2018) - from licenses and
permits, state grants, charges for services

Annual Budget*

$3,867,433

Total Identified Need

$6,509,567 per year (through 2033)

Based on an evaluation of existing stormwater assets

and a comprehensive risk assessment, the City developed a 20-year CIP for level of service B, which
represents the mid-range level of service from the asset management plan. The City estimated that total
annual funding requirements for this desired level of service would amount to $14.7 million per year (for
20-years). However, due to funding constraints, the City is now aiming to achieve the levels of service
associated with scenario C of the asset management plan, which will require $10.4 million in annual
expenditures. This compares to annual funding requirements for maintaining existing levels of service of
$3.6 million.

In Michigan, it is difficult to establish a stormwater utility because of legal circumstances. Thus, the
City's stormwater program is funded from the City General Fund, as well as the Local and Major Streets,
Refuse, and Vital Streets Funds. The Vital Streets program, which includes green infrastructure and other

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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stormwater components as part of comprehensive street improvement projects, has been funded for
the last 15-years through a voter-approved income tax.

In FY 2018 the City's budget for stormwater management and maintenance was $2.7 million, while the
capital budget amounted to $1.2 million (including approximately $674,00 from the General Fund and
$536,000 from Vital Streets). The total $3.87 million budget is below the funding needed to meet the
City's level of service goals. While the City continues to make progress and has been recognized
nationally for its excellence in service and innovation,46 bridging this funding gap will require additional
sources of funds and/or a longer timeline for achieving the City's goals.

46 In 2017, the City of Grand Rapids received a gold recognition in program management award through the Water
Environment Federations' National MS4 and Green Infrastructure Awards Program.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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Griffin, GA

Stormwater Pipe Assessment: Water
Quantity (Infrastructure, Drainage)

The City of Griffin lies on the continental divide with
watersheds draining to two different basins. Located about
an hour south of Atlanta, this small MS4 Phase 2
community created the first stormwater utility in the state
of Georgia and has been on the forefront of
stormwater management for many years.

The City prepared a condition and risk assessment of
all stormwater infrastructure within the City
boundaries in 2016. The assessment included 6,792
pipes and associated infrastructure. Condition
assessment was developed using a standardized
approach and defined criteria. Only infrastructure in
the poor category were considered for replacement
estimates as a capital expense. Not included in the
estimate is on-going maintenance expense associated
with clearing pipes blocked with debris. Up to 30% of
the stormwater infrastructure is considered blocked in
some areas, reducing the effectiveness of the
conveyance system and increasing maintenance costs.

Risk assessment criteria included FEMA floodzones,
proximity to buildings, and road classification.
Infrastructure determined to be high risk and poor
condition will be prioritized for maintenance and/or
replacement.

County or Municipality
Griffin, GA

Population
22,878 (US Census 2018)

Annual Rainfall
49.7 inches (US Climate Data)

Land Area

square miles (US Census 2018)

Poverty Level
31.4% (US Census 2018)

Total Identified Need
$23 million

Annual Capital Budget
$443,000

Annual O&M Budget
N/A

As part of this study, a replacement cost estimate was
developed based on comparable construction costs

and included factors such as pipe material, pipe diameters, and replacement method. Only for
stormwater infrastructure determined to be in poor condition, the replacement cost is estimated to be
$23 million.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Ventura County, CA

Flood Protection and Stormwater Quality
Compliance

Water Quantity (Flood Protection) and
Water Quality (MS4 Permit and TMDLs
Compliance)

The Ventura County Public Works Agency's Watershed
Protection District (VC WPD) is the regional flood protection
service provider in Ventura County in addition to local
systems in ten incorporated Cities of Camarillo, Fillmore,
Moorpark, Ojai, Oxnard, Port Hueneme, Ventura, Santa
Paula, Simi Valley and Thousand Oaks. VC WPD is also
leading collaborative efforts by the County of Ventura and
ten incorporated Cities to implement requirements of the
Ventura 2010 Municipal Separate Storm Sewer System
(MS4) Stormwater Permit No. CAS004002 since 1992, when
Ventura County Board of Supervisors adopted a benefit
assessment levy for stormwater and flood management in
Ventura County. Since passage of Proposition 218 in 1996,
the assessment rates have not changed, because voter
approval is required. Consequently, annual revenue of
approximately $40,499,155 has not changed, while the
recent annual budget for MS4 Permit/TMDLs compliance
and VC WPD's flood control was over $74 Million* (this
amount does not include Cities' flood control budgets). The
funding gap is supported by the County and Municipal
General Funds, Grant funding, and fund balance, which are
highly variable sources due to competing needs for General
Fund funding, competitive nature of grant programs, and
short-term availability of fund balance. In addition, fees for
municipal services, e.g., inspections of businesses, industrial
facilities, and construction sites, help fund MS4 compliance
activities.

County or Municipality
County of Ventura, Ventura County
Watershed Protection District, and ten
incorporated Cities of Camarillo,
Fillmore, Moorpark, Ojai, Oxnard, Port
Hueneme, Ventura, Santa Paula, Simi
Valley and Thousand Oaks, California

Population
850,967

Annual Rainfall
18 inches

Land Area
2,208 square miles

Poverty Level
9.5% (persons in poverty)
MIHI $81,972

Annual Revenue
$40,499,115

Annual Budget*
$74,129,564

Total Identified Need
$2,305,178,303 (2021-2050 CIP)
$87,530,290/year (O&M after 2050)

Flood protection needs in the County are driven by aging
infrastructure and flood risk reduction. It is estimated that

over 50% of facilities will need to be replaced or rehabilitated within the next 30 years at a significant
cost not supported by current revenues.

The Ventura MS4 Permittees are subject to 16 Total Maximum Daily Loads (TMDLs), of which 13 TMDLs

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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are enforceable after incorporation into the MS4 Permit in 2010. Compliance with the upcoming new
Permit and approaching TMDL deadlines will require for planning and implementation of costly
stormwater treatment structural best management practices (BMPs).

The roughly estimated structural BMP implementation cost for Ventura MS4s are driven by the three
effective and assumed two future watershed-wide Bacteria TMDLs. In particular, the wet weather
compliance is very expensive undertaking for each watershed in Ventura County. Significant new CIP
funding is already needed to meet upcoming 2023, 2026, and 2029 deadlines for existing Bacteria
TMDLs. Past the year of 2050, anticipated as final compliance deadline for future TMDLs and completion
of flood control improvements, the annual operation and maintenance (O&M) cost was estimated at
approximately 3% of the total estimated CIP costs. As discussed with regulatory agencies, the current
and future funding gap continues to be a significant challenge for Ventura MS4s.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Stormwater Utility,
Lawrence, KS

Flood Risk Reduction, Erosion Control,
Water Quality Protection, and Drainage
Infrastructure Management

Overview

The City of Lawrence, KS, is located 35 miles northwest
of Kansas City. In 1996, the City adopted a Stormwater
Management Master Plan that analyzed the performance
capability of the existing drainage system, recommended
improvements to the facilities, and recommended the
creation of the Stormwater Utility and corresponding
stormwater fee.

History

The 1996 master plan provided a framework for the City to
create and operate a Stormwater Utility. The utility is
responsible for all activities related to the operation of the
stormwater system, including planning, capital facility
construction, street sweeping, and educational programs.

The plan also recommended the implementation of a
stormwater fee to provide a dedicated source of revenue.
The impervious area fee is an equitable means of collecting
revenue from users in proportion to their demands on the
system. In 1996, the fee was set at $2.00 per equivalent
residential unit; this fee was increased to $4.00 by 2003 and
was not adjusted again until 2016. Currently the fee is $4.37.

The City has recently begun a comprehensive stormwater
rate study and financial plan in anticipation of increasing the
size of the utility's capital program and completing the
capital projects identified in 1996.

County or Municipality
City of Lawrence, KS

Population
97,286

Annual Rainfall
39.92"

Land Area
26.3 square miles
17 main watersheds

Poverty Level
21.8%

Total Identified Need
$62 million

Annual Capital Budget
$1.3M

Annual O&M Budget

$1.9 M

Annual Stormwater Revenue
$3,233,000

Capital Needs

The initial master plan identified 41 individual projects at a total cost of approximately $62 million (2019
dollars), while implementing a stormwater fee that would generate approximately $1.2 million per year.
Average revenue has been $2.9 million since 2003, which has been sufficient for annual operating costs
and debt service but left little for new capital facilities. The current five-year capital improvements plan

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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identifies projects totaling $26 million, which the utility plans to meet after paying off its outstanding
debt in 2018 and establishing a program of regular rate increases.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Metropolitan Water
Reclamation District of
Greater Chicago

Working hard to manage stormwater,
clean wastewater and recover
valuable resources.

Overview

History

Annual Capital Budget

For years, stormwater management in Cook County had been a	(fY19 Budget)

patchwork of efforts by local, regional, state and federal

agencies. In 2004, the Illinois General Assembly enacted Public

Act 93-1049 allowing for the creation of a comprehensive

stormwater management program in Cook County under the

supervision of the Metropolitan Water Reclamation District of Greater Chicago (MWRD).

The Metropolitan Water Reclamation District of
Greater Chicago (MWRD) serves approximately 10.35 million
people each day, residents of Chicago and 128 suburban
communities.

Through a variety of engineered solutions, both green and gray,
and flood-prone property acquisitions, MWRD's Stormwater
Management Program addresses both regional and local flooding
problems throughout Cook County.

In 2015, the MWRD adopted a Green Infrastructure Plan to
increase the acceptance and investment of Gl throughout Cook
County. Since that time, the MWRD has partnered with dozens of
agencies to fund Gl projects such as rain gardens,
bioswales/bioretention areas, permeable pavement systems, and
rain water harvesting systems. These projects will provide up to 5
million gallons of stormwater runoff storage to over 1,400
benefiting structures.

County or Municipality
Metropolitan Water Reclamation
District of Greater Chicago, Cook
County

Population
10.35 Million Service Area

Annual Rainfall
38" (Illinois)

Land Area
822.1 sq. mi.

Poverty Level
15.9% (Cook County)

Total Identified Need

The Act required MWRD to develop the Cook County Stormwater Management Plan. The Cook County
Stormwater Management Plan provides the framework for the stormwater management program,
including its mission, goals, and program elements.

The MWRD's countywide Stormwater Management Program's mission is to provide Cook County with

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

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approved by the chartered EFAB, and does not represent EPA policy.

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effective rules, regulations and capital improvement projects that will reduce the potential for
stormwater damage to life, public health, safety, property and the environment.

Under the plan, the MWRD established Watershed Planning Councils and completed Detailed
Watershed Plans for all six major watersheds in Cook County.

MWRD has made significant investments in developing over 140 capital stormwater projects since it
assumed the authority for stormwater management in 2004. These projects, which range in both size
and scope, provide flood protection for thousands of homes, businesses, and critical infrastructure.

Capital Needs & Funding Sources

Public Act 93-1049 gives MWRD the authority to levy a tax and to issue bonds for the development and
administration of countywide stormwater management. Although the District's authority for the
program applies to all of Cook County, the tax levy is only applicable to commercial and private property
located within the District's corporate limits. The District's stormwater management program is
currently funded by the stormwater tax levy.

The District utilizes the stormwater tax levy and additional funding mechanisms to finance the
countywide program.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Stormwater Environmental
Utility, Sarasota, FL

Control water quantity, enhance water
quality, effectively manage stormwater

Overview

The County of Sarasota, FL, is located in the coastal plain of
southwest Florida. In 1987, the County completed a
Stormwater Management Master Plan that identified the county's
drainage basins and recommended the enactment of a stormwater
utility fee as a dedicated funding source.

History

The Stormwater Environmental Utility (SEU) was established in
1989 and is organized into four main sections: Master planning,
Capital improvements, Maintenance, and Development review. The
utility is responsible for all activities related to the operation of the
stormwater system, including master planning, the capital
improvement program, inspection and maintenance of the
stormwater management system, and the proper use, storage,
disposal of sediments, herbicides and other materials.

County or Municipality
Sarasota County, FL

Population
419,689

Annual Rainfall
52.99"

Land Area
725 square miles
6 main watersheds

Poverty Level
18.6%

Total Identified Need
$400 million

Annual Capital Budget
Varies

Annual Stormwater Revenue
$21,000,000

The assessment methodology has gone through several legal
challenges and changes since its inception in 1989. As one of the
first stormwater utilities created in Florida, Sarasota County has
been a leader among local governments in developing such a
program. In contrast to the engineering practice of impervious and
flow rate calculations, the rate structure was changed in 1994 to a
system that considers the pervious and impervious areas of each
parcel as the method of assessment (all lands act like impervious
surfaces during 5-yr, 25-hr rain events). The Sarasota County SEU

assesses its customers based on Equivalent Stormwater Units (ESU's) that are based on the effective
impervious area of the average single-family parcel.

Flooding level of Service (LOS) is intended to protect habitable structures up to the 100-yr, 24-hr rain
event. Water quality expectations from regulatory pressures are significant and reach beyond the
Stormwater Environmental Utility to include wastewater treatment and reuse water for irrigation.

Capital Needs

To-date, the SEU has spent about $600,000,000 in stormwater LOS flood improvements, operations and

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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maintenance. Water quality expenditures for the SEU have been approximately $20,000,000. Current
Total Maximum Daily Load (TMDL) requirements are forecast to have an unmet need of $400,000,000
that will be distributed to various sources of nutrient loading in the County over the next 20 years.
Various sources of local funding are being exercised in public dialog. All typical sources are under
consideration to include sales tax, ad-valorum and special assessments.

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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Appendix III: Stormwater Funding Database

As part of its charge, the Task Force lead the development of a database of funding and financing
sources commonly used by communities and municipalities to fund their stormwater infrastructure. The
database is not a comprehensive list of all sources; rather, it is the most commonly used sources at the
federal and state level. Local funding sources, which are often used by municipalities and communities
were not captured in this effort. It was decided by the Task Force that local source vary year to year, and
from community to community so greatly that they would not be able to accurately capture local
options. The complete database can be found on the EPA's Water Finance Infrastructure and Resiliency
Finance Center webpage ( https://www.epa.gov/waterfinancecenter) and has been uploaded to the
Water Finance Clearinghouse.

Data Sources

This section summarizes the variety of sources used to populate the Stormwater Funding Database.
Water Finance Clearinghouse

The Water Finance Clearinghouse, which is a web-based portal that contains information and resources
on drinking water, wastewater, stormwater infrastructure, and other areas within the water sector, was
developed by EPA's Water Infrastructure and Resiliency Finance Center. Within the Water Finance
Clearinghouse, funding sources were pulled by applying a "stormwater" filter to narrow the results to
377 sources, which were then uploaded to Microsoft Access. The data was reviewed for duplicates and
all national federal programs were limited to one entry, since some federal grants were listed several
times but in relation to only one state. The State Revolving Fund (SRF) grants, however, were broken
down into several entries, one for each state/territory.

Federal Funding Programs - Stormwater and Green Infrastructure Projects

The EPA had previously developed this table containing all known federal funding programs that involve
stormwater and/or green infrastructure project components. The sources pulled from the Water
Finance Clearinghouse were cross referenced to this table and any missing data was added.

Stormwater Infrastructure Funding Task Force

The Task Force provided recommendations and documentation of potential sources to include in the
database.

Technical Approach

This section summarizes the different variables, or fields, that were used in the database as well as the
procedure for entering and quantifying the data.

The Water Finance Clearinghouse provided many fields of data that were narrowed down to what was
relevant to the charge, as seen in the table below. A few fields were also added to directly provide

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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information to help answer some of the charges. A few of the fields were limited to the options
provided in bullets below to simplify filtering the data by source type, agency, funding use, etc. For the
funding amounts, if the source does not have a range and only has a fixed amount allocated each year,
the amount was placed in the max field and the min field was left blank.

Program Name

Name or brief description of source

Source

Who is providing the funds?

Source Type

*	Taxes/general funds
A Fees

*	Stormwater utility

*	Grants

*	Bonds

*	Loans

*	Public-private partnerships

Agency

*	Federal

*	State
A Local

*	Private (including non-profit)

Website

URL

State

State or National

How Funds are Issued

*	Application process

*	Fund allocation to states and localities

*	Competitive vs. non-competitive process

*	Long-term programs vs. one-time allocation

*	Grant vs. loan programs

How Funds are Used

*	Capital

*	O&M

*	Compliance

How Funds are Utilized

How are funds coordinated with other sources of
funding?

Funding Amount Min

What is the typical annual minimum amount of
funding amount for this program?

Funding Amount Max

What is the typical annual maximum amount of
funding amount for this program?

Funding Requirements

What are the requirements for receiving these
funds?

Environmental Financial Advisory Board (EFAB) Draft Working Paper—Do Not Cite or Quote

This draft is a work in progress; it does not reflect consensus advice or recommendations, has not been reviewed or
approved by the chartered EFAB, and does not represent EPA policy.

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