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entitled 'Clean Water Infrastructure: A Variety of Issues Need to Be 
Considered When Designing a Clean Water Trust Fund' which was released 
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Report to Congressional Requesters: 

United States Government Accountability Office: 
GAO: 

May 2009: 

Clean Water Infrastructure: 

A Variety of Issues Need to Be Considered When Designing a Clean Water 
Trust Fund: 

GAO-09-657: 

GAO Highlights: 

Highlights of GAO-09-657, a report to congressional requesters. 

Why GAO Did This Study: 

The Environmental Protection Agency (EPA) has estimated that a 
potential gap between future needs and current spending for wastewater 
infrastructure of $150 billion to $400 billion could occur over the 
next decade. A number of entities are involved in planning, financing, 
building, and operating this infrastructure. Some of these stakeholders 
have suggested a variety of approaches to bridge this potential gap. 
One such proposal is to establish a clean water trust fund. In this 
context, GAO was asked to (1) obtain stakeholders’ views on the issues 
that would need to be addressed in designing and establishing a clean 
water trust fund and (2) identify and describe potential options that 
could generate about $10 billion in revenue to support a clean water 
trust fund. In conducting this review, GAO administered a questionnaire 
to 28 national organizations representing the wastewater and drinking 
water industries, state and local governments, engineers, and 
environmental groups and received 22 responses; reviewed proposals and 
industry papers; interviewed federal, state, local, and industry 
officials; and used the most current data available to estimate the 
revenue that could potentially be raised by various taxes on a range of 
products and activities. 

GAO is not making any recommendations. While this report identifies a 
number of funding options, GAO is not endorsing any option and does not 
have a position on whether or not a trust fund should be established. 

What GAO Found: 

In designing and establishing a clean water trust fund, stakeholders 
identified three main issues that would need to be addressed: how a 
trust fund should be administered and used; what type of financial 
assistance should be provided; and what activities should be eligible 
to receive funding from a trust fund. While a majority of stakeholders 
said that a trust fund should be administered through an EPA 
partnership with the states, they differed in their views on how a 
trust fund should be used. About a third of stakeholders responded that 
a trust fund should be used only to fund the existing Clean Water State 
Revolving Fund (CWSRF), which is currently funded primarily through 
federal appropriations, while a few said it should support only a new 
and separate wastewater program. A few stakeholders supported using a 
trust fund to support both the CWSRF and a separate program, while 
others did not support the establishment of a trust fund at all. In 
addition, more than half of the stakeholders responded that financial 
assistance should be distributed using a combination of loans and 
grants to address the needs of different localities. Finally, although 
a variety of activities could be funded, most stakeholders identified 
capital projects as the primary activity that should receive funding 
from a clean water trust fund. 

A number of options have been proposed in the past to generate revenue 
for a clean water trust fund, but several obstacles will have to be 
overcome in implementing these options, and it may be difficult to 
generate $10 billion from any one option by itself. Funding options 
include a variety of excise taxes as shown in the table below. 

Table: Estimated Revenue from Excise Taxes on Products That May 
Contribute to the Wastewater Stream (in millions of 2009 Dollars): 

Product groups: Beverages; 
Tax base: $95,551; 
1% tax: $956; 
5% tax: $4,778; 
10% tax: $9,555; 
Tax rate to generate $10 billion: 10.5%. 

Product groups: Fertilizers and pesticides; 
Tax base: $26,088; 
1% tax: $261; 
5% tax: $1,304; 
10% tax: $2,609; 
Tax rate to generate $10 billion: 38.3%. 

Product groups: Flushable products, including soaps, detergents, 
cooking oils, and toiletries; 
Tax base: $63,241; 
1% tax: $632; 
5% tax: $3,162; 
10% tax: $6,324; 
Tax rate to generate $10 billion: 15.8%. 

Product groups: Pharmaceuticals; 
Tax base: $156,069; 
1% tax: $1,561; 
5% tax: $7,803; 
10% tax: $15,607; 
Tax rate to generate $10 billion: 6.4%. 

Product groups: Water appliances and plumbing fixtures; 
Tax base: $25,517; 
1% tax: $255; 
5% tax: $1,276; 
10% tax: $2,552; 
Tax rate to generate $10 billion: 39.2%. 

Source: GAO analysis of U.S. Census Bureau data from the 2006 Annual 
Survey of Manufactures and Foreign Trade Division. 

[End of table] 

In addition, Congress could levy a tax on corporate income. An 
additional 0.1 percent corporate income tax could raise about $1.4 
billion annually. Congress also could levy a water use tax. A tax of 
0.01 cent per gallon could raise about $1.3 billion annually. 
Regardless of the options selected, certain implementation obstacles 
will have to be overcome. These include defining the products or 
activities to be taxed, establishing a collection and enforcement 
framework, and obtaining stakeholder support for a particular option or 
mix of options. 

View [hyperlink, http://www.gao.gov/products/GAO-09-657] or key 
components. For more information, contact Anu Mittal at (202) 512-3841 
or mittala@gao.gov. 

[End of section] 

Contents: 

Letter: 

Background: 

Stakeholders Identified Three Key Issues That Would Need to Be 
Addressed in Designing and Establishing a Clean Water Trust Fund: 

Various Options for Funding a Clean Water Trust Fund Could Generate a 
Range of Revenues, but Each Option Poses Certain Obstacles: 

Agency Comments: 

Appendix I: Scope and Methodology: 

Appendix II: Summary of Stakeholder Responses to Questionnaire: 

Appendix III: Stakeholders Responding to Questionnaire on a National 
Clean Water Trust Fund: 

Appendix IV: Estimated Tax Bases for Excise Tax Funding Options: 

Appendix V: GAO Contact and Staff Acknowledgments: 

Tables: 

Table 1: Product Groups that May Contribute to the Wastewater Stream: 

Table 2: Tax Bases for Product Groups and Estimated Revenue from Range 
of Excise Tax Rates, in Constant 2009 Dollars: 

Table 3: Stakeholder Support for Excise Taxes: 

Table 4: Stakeholder Views on the Extent of the Connection between 
Wastewater Infrastructure Use and Product Groups: 

Table 5: Stakeholder and Industry Reasons for Support or Opposition to 
Excise Taxes on Specific Product Groups Along with Views of Utility 
Operators: 

Table 6: Stakeholder Views on Administration: 

Table 7: Stakeholder Views on Use of a Trust Fund: 

Table 8: Stakeholder Views on Funding Distribution: 

Table 9: Stakeholder Views on What Activities Should be Eligible for 
Funds: 

Table 10: Stakeholder Views on Eligible Capital Costs: 

Table 11: Stakeholder Views on Eligibility for Funds: 

Table 12: Stakeholder Support for Funding Options: 

Table 13: Stakeholder Views on Funding Options: 

Table 14: Estimated Tax Bases for Excise Tax Funding Options: 

Figure: 

Figure 1: Stakeholder Views on How a Trust Fund Should Be Used: 

Abbreviations: 

CBO: Congressional Budget Office: 

CEIT: Corporate Environmental Income Tax: 

Census: U.S. Census Bureau: 

CWSRF: Clean Water State Revolving Fund: 

EPA: Environmental Protection Agency: 

EPCRA: Emergency Planning and Community Right to Know Act: 

IRS: Internal Revenue Service: 

NAICS: North American Industry Classification System: 

NPDES: National Pollutant Discharge Elimination System: 

TRI: Toxics Release Inventory: 

USGS: United States Geological Survey: 

[End of section] 

United States Government Accountability Office: 
Washington, DC 20548: 

May 29, 2009: 

The Honorable James L. Oberstar: 
Chairman: 
The Honorable John L. Mica: 
Ranking Member: 
Committee on Transportation and Infrastructure: 
House of Representatives: 

The Honorable Eddie Bernice Johnson: 
Chairwoman: 
Subcommittee on Water Resources and Environment: 
Committee on Transportation and Infrastructure: 
House of Representatives: 

The Honorable Earl Blumenauer: 
House of Representatives: 

More than 220 million people in the United States are served by 
wastewater systems that are composed primarily of a network of sewer 
pipes and treatment plants that carry and treat wastewater before it is 
discharged into surface water. Many of these systems were constructed 
more than 50 years ago and are reaching the end of their useful lives. 
In addition to the deterioration in the condition of this 
infrastructure, some of these systems also lack the capacity to 
adequately treat increasingly large volumes of wastewater, particularly 
during periods of wet weather. As a result, these systems are releasing 
large quantities of untreated wastewater into surface waters, which can 
pose a threat to human and aquatic health. For example, according to 
Environmental Protection Agency (EPA) estimates, wastewater systems 
annually discharge over 850 billion gallons of untreated sewage into 
U.S. surface waters. Although federal, state, and local governments 
invest billions of dollars annually in wastewater infrastructure--a 
total of about $40 billion in 2006--EPA and others have estimated that 
current spending levels may not be adequate to cover the costs of 
maintaining and replacing pipes, treatment plants, and other parts of 
this infrastructure. According to EPA's estimates, a potential gap of 
about $150 billion to $400 billion between projected future 
infrastructure needs and current levels of spending could occur over 
the next decade.[Footnote 1] Without additional investment in the 
nation's wastewater infrastructure, EPA and other groups have asserted 
that the environmental and public health gains made under the Clean 
Water Act[Footnote 2] during the last three decades could be at risk. 

A variety of approaches have been proposed to help bridge a potential 
gap between projected future infrastructure needs and current levels of 
spending. For example, one approach would be to increase federal 
funding for the Clean Water State Revolving Fund (CWSRF) program, which 
is the largest source of federal assistance for wastewater 
infrastructure. About $689 million was appropriated in both fiscal 
years 2008 and 2009 for the CWSRF program, and an additional $4 billion 
was appropriated by the American Recovery and Reinvestment Act of 2009. 
[Footnote 3] Under the CWSRF program, EPA provides capitalization 
grants to the states, which in turn use these funds to make loans to 
local communities or utilities for various water quality projects. As 
loans are repaid, the funds are cycled back into the state-level 
programs to fund additional projects. New funding for the CWSRF program 
is dependent on federal appropriations. In addition, EPA has promoted 
its sustainable infrastructure initiative for water infrastructure 
management, called the Four Pillars, to help meet infrastructure needs. 
Among other things, the Four Pillars calls for wastewater and drinking 
water utilities to charge rates for the service they provide that are 
high enough to enable them to fund future capital needs in addition to 
their routine operations and maintenance. Still another approach that 
has been considered to bridge a potential gap between projected future 
infrastructure needs and current spending levels is to establish a 
clean water trust fund. In general, federal trust funds collect revenue 
and distribute funds that have been set aside for specific purposes. A 
clean water trust fund would provide a dedicated source of funding for 
wastewater infrastructure that would be similar to some of the trust 
funds that Congress has established for other infrastructure and 
environmental programs, such as highway infrastructure construction and 
coastal wetlands restoration. Some of the revenue for federal trust 
funds is generated through federal excise taxes on specific products 
and services.[Footnote 4] 

In this context, you asked us to provide information on the issues that 
would need to be addressed if Congress decided to establish a clean 
water trust fund to help meet the potential gap between projected 
future wastewater infrastructure needs and current spending levels. 
Specifically, this report (1) describes stakeholders' views on the 
issues that would need to be addressed in designing and establishing a 
clean water trust fund and (2) identifies and describes potential 
options that Congress could consider that could generate revenues of 
$10 billion annually to support a clean water trust fund. 

To determine stakeholders' views on the issues that would need to be 
addressed in designing and establishing a clean water trust fund, we 
reviewed past legislative proposals and wastewater industry position 
papers on establishing such a fund. In addition, we interviewed a 
variety of stakeholders, both individuals and groups, with knowledge of 
wastewater infrastructure issues, including those from the wastewater 
industry and federal, state, and local government. Based on the 
information gathered from these interviews, we developed and 
administered a questionnaire to obtain the views of these and other 
stakeholders on the issues that need to be addressed in designing and 
establishing a trust fund. We sent this questionnaire to national 
organizations representing the wastewater industry, drinking water 
industry, state and local governments, engineers, and environmental 
groups. We sent out 28 questionnaires and received 22 responses, for a 
response rate of 79 percent. Some stakeholders did not answer all of 
the questions on the questionnaire, so the number of responses for each 
question can vary. We also reviewed reports and documents on the CWSRF 
and interviewed federal and state officials responsible for 
implementing this program to gain an understanding for how this program 
might interact with a clean water trust fund. Finally, we visited three 
states--Arizona, Maryland, and Wisconsin--and the District of Columbia, 
where we interviewed state and local officials about their wastewater 
infrastructure needs and how a clean water trust fund could be designed 
to meet these needs. We chose these locations because they were 
geographically dispersed, had different wastewater infrastructure 
needs, and used various approaches to finance wastewater projects. 

To identify potential options for funding a clean water trust fund that 
could generate $10 billion annually, we reviewed past legislative 
proposals and position papers from wastewater industry groups that 
discussed specific funding options. We also reviewed reports on how 
existing federal environmental and infrastructure trust funds are 
funded and conducted Internet searches to identify funding options that 
states are using to finance wastewater projects. We used our 
questionnaire to gauge stakeholders' support for various funding 
options for a clean water trust fund and to obtain their views on the 
extent of the connection between these funding options and wastewater 
infrastructure use. In addition, we interviewed federal and state 
officials to identify the challenges likely to be associated with 
implementing these funding options. To estimate the revenue that these 
options could potentially generate, we used the most recent government 
data available to estimate the value of products or activities that 
could be subject to a federal tax and applied a range of tax rates to 
these values based on current or past taxation policies. The estimates 
presented in our report are not official revenue estimates as would be 
prepared by the Joint Committee on Taxation, and they are subject to 
various limitations. For example, we did not model or estimate consumer 
or market responses to these funding options, possible noncompliance, 
or the cost of implementing and enforcing these options. As a result, 
our revenue estimates may be higher than actual receipts that would be 
generated from these funding options. Moreover, we do not endorse any 
option and do not have a position on whether or not a clean water trust 
fund should be established. 

A more detailed description of our scope and methodology is presented 
in appendix I. We conducted our work from June 2008 to May 2009 in 
accordance with all sections of GAO's quality assurance framework that 
are relevant to our objectives. The framework requires that we plan and 
perform the engagement to obtain sufficient and appropriate evidence to 
meet our stated objectives and to discuss any limitations in our work. 
We believe that the information and data obtained, and the analysis 
conducted, provide a reasonable basis for any findings and conclusions. 

Background: 

Americans rely on wastewater systems to protect public health and the 
environment. These systems are composed of a network of pipes, pumps, 
and treatment facilities that collect and treat wastewater from homes, 
businesses, and industries before it is discharged to surface waters. 
EPA sets standards for the quality of wastewater that can be discharged 
under the Clean Water Act.[Footnote 5] Under this law, the National 
Pollutant Discharge Elimination System (NPDES) program limits the types 
and amounts of pollutants that industrial and municipal wastewater 
treatment facilities may discharge into the nation's surface waters. 
During the wastewater treatment process, solid materials, such as sand 
and grit; organic matter from sewage; and other pollutants are removed 
from wastewater before it is discharged to surface waters. This 
treatment helps to ensure that the quality of surface water is not 
degraded and that it can continue to be used for drinking water, 
fishing, and swimming. About 16,000 publicly owned wastewater treatment 
plants exist in the United States, and the American Society of Civil 
Engineers estimates that between 600,000 and 800,000 miles of sewer 
pipe help to deliver wastewater to these treatment plants. These 
systems are primarily publicly owned and provide wastewater service to 
more than 220 million Americans. 

Local communities have the primary responsibility to provide funding 
for wastewater infrastructure. According to U.S. Census Bureau (Census) 
estimates, in fiscal year 2006[Footnote 6] local communities spent 
about $38 billion on wastewater operations and capital projects, while 
states spent about $1.3 billion. In addition, the federal government 
provides financial assistance for wastewater infrastructure, with EPA 
providing the largest amount through its CWSRF program. Under the CWSRF 
program, which was established in 1987, the federal government provides 
capitalization grants to states, which in turn must match at least 20 
percent of the federal grants. The states then use the money to provide 
low-interest loans to fund a variety of water quality projects, and 
loan repayments are cycled back into the program to be loaned out for 
other projects. In 2007, states provided CWSRF loans totaling about 
$5.3 billion to communities and other recipients. 

Several studies have documented the deterioration in the condition of 
the U.S. wastewater infrastructure. According to EPA, the majority of 
the nation's sewer pipe network was installed after World War II and is 
reaching the end of its useful life. Similarly, many of the wastewater 
treatment plants that were upgraded in the 1970s to comply with the 
Clean Water Act are aging and will need to be upgraded or replaced in 
the future. The American Society of Civil Engineers recently described 
the condition of the nation's wastewater infrastructure as "poor," and 
cited a lack of investment in critical components of this 
infrastructure as a contributing factor to this condition.[Footnote 7] 
The deteriorating condition of the nation's wastewater infrastructure 
has direct impacts on human and aquatic health. Specifically, many 
older wastewater systems lack the capacity to treat increasingly large 
volumes of wastewater, particularly during periods of wet weather. In 
addition, cracks in sewer pipes allow rain or snowmelt to enter the 
wastewater system and overwhelm its capacity to adequately treat 
wastewater. Untreated wastewater can be released during the resulting 
sewer overflows associated with these wet weather events and introduce 
significant levels of pollution into local water bodies, which can pose 
risks to human health and result in beach closures and fish kills. EPA 
estimates that over 850 billion gallons of untreated wastewater are 
released annually into U.S. surface waters. 

Although local, state, and federal governments have invested billions 
in wastewater infrastructure over the years, studies by EPA and the 
Congressional Budget Office (CBO) suggest a potential gap exists 
between what is currently being spent on wastewater infrastructure and 
estimated future infrastructure needs. EPA's 2002 analysis estimated a 
potential gap for wastewater infrastructure capital improvements, along 
with operations and maintenance, of about $150 billion to $400 billion 
over the period from 2000 to 2019.[Footnote 8] CBO estimated a gap of 
about $60 billion to $220 billion in capital funding alone over this 
same period.[Footnote 9] Without additional investment in the nation's 
wastewater infrastructure, EPA and other groups have asserted that the 
environmental and public health gains made under the Clean Water Act 
during the last three decades could be at risk. However, these studies 
by EPA and CBO note that this gap is not inevitable, and policy makers 
and wastewater groups have proposed a variety of approaches to help 
bridge this gap, including the following:[Footnote 10] 

* Implement EPA's Sustainable Water Infrastructure Initiative. This 
initiative, which is called the Four Pillars, encourages wastewater and 
drinking water utilities to improve the management of their systems, to 
systematically plan ahead for infrastructure needs, and to charge the 
full cost of the service they provide to customers. Charging the full 
cost would require utilities to charge prices that reflect the costs of 
building, maintaining, and operating a wastewater system over the long 
term.[Footnote 11] 

* Increase funding for the CWSRF. Federal CWSRF capitalization grants 
to the states had been declining in recent years, despite growing 
wastewater infrastructure needs. In both fiscal years 2008 and 2009, 
$689 million was appropriated for the CWSRF program, which was below 
the average from 2000 to 2007 of about $1.2 billion. Some proponents of 
the CWSRF have recommended increasing federal appropriations for this 
program and the program has recently received additional federal 
funding. The American Recovery and Reinvestment Act of 2009 
appropriated $4 billion in funding for the CWSRF program, and the 
President's budget request for fiscal year 2010 asks for an increase in 
funding for the program. In addition, some have suggested increasing 
the pool of available CWSRF funds by encouraging more states to use 
their federal capitalization grants as collateral in the public bond 
market.[Footnote 12] This practice, known as "leveraging" allows states 
to borrow additional money to lend out through the CWSRF. Currently, 
about 27 states leverage their capitalization grants. 

* Establish a national infrastructure bank. Three bills were introduced 
in the 110th Congress that proposed establishing a national 
infrastructure bank or other entity that would provide financing for a 
variety of infrastructure projects, including wastewater infrastructure 
projects.[Footnote 13] This entity would independently evaluate 
projects and determine the most appropriate way--through loans, grants, 
or other financial tools--to finance them. 

* Encourage public-private partnerships. Historically, wastewater 
infrastructure has commonly been owned and operated by public entities, 
such as local municipalities. However, other approaches exist where 
private entities can provide services such as designing, constructing, 
or operating infrastructure projects, including wastewater systems. In 
recent years, these partnerships have become more common in the 
transportation sector.[Footnote 14] 

* Lift private activity bond restrictions on wastewater projects. 
Private activity bonds are tax-exempt bonds issued by state or local 
governments to provide special financing benefits for qualified 
projects. These bonds are used to provide financing to private 
businesses for certain facilities, such as airports, electric and gas 
distribution systems, mass transit systems, solid waste disposal sites, 
and wastewater plants. Because private activity bonds are exempt from 
federal tax, states and municipalities can borrow money at lower 
interest rates. However, states are limited in the amount of private 
activity bonds that they can issue annually. While certain projects 
such as airports and solid waste disposal facilities are exempt from 
this cap, wastewater infrastructure facilities are subject to this cap. 
Removing this restriction could increase the level of low-interest 
financing available for wastewater projects.[Footnote 15] 

* Create a federal clean water trust fund. Establishing a clean water 
trust fund could help to provide a dedicated source of federal funding 
for wastewater infrastructure. Federal trust funds, such as the Highway 
and the Airport and Airways Trust Funds, are used to account for funds 
that are dedicated for spending on a specific purpose. Unlike trustees 
of private trust funds, a federal agency may exercise a greater degree 
of control over its trust fund. As authorized by law, the federal 
government may control the fund as well as its earnings and raise or 
lower future trust fund collections and payments or change the purposes 
for which collections are used. 

Stakeholders Identified Three Key Issues That Would Need to Be 
Addressed in Designing and Establishing a Clean Water Trust Fund: 

Three main issues would need to be addressed in designing and 
establishing a clean water trust fund, according to stakeholders. 
[Footnote 16] These issues include: how a trust fund should be 
administered and used; what type of financial assistance should be 
provided for projects; and what activities should be eligible for 
funding. 

Administration and use of a trust fund. Stakeholders told us that 
designing a clean water trust fund would involve deciding what agency 
or entity would administer the fund and whether the trust fund would be 
used to fund the CWSRF or a separate program. A majority of 
stakeholders (15 of 20) responding to our questionnaire expressed the 
view that a trust fund should be administered through an EPA-state 
partnership like the current CWSRF program.[Footnote 17] However, as 
figure 1 shows, stakeholders differed in their views on how a trust 
fund should be used. 

Figure 1: Stakeholder Views on How a Trust Fund Should Be Used: 

[Refer to PDF for image: horizontal bar graph] 

Stakeholder view: Only to fund the CWSRF; 
Number of stakeholders: 7. 

Stakeholder view: To fund a separate and distinct program; 
Number of stakeholders: 3. 

Stakeholder view: To fund both the CWSRF and a separate and distinct 
program; 
Number of stakeholders: 5. 

Stakeholder view: A trust fund should not be created; 
Number of stakeholders: 3. 

Stakeholder view: Other; 
Number of stakeholders: 2. 

Source: GAO analysis of stakeholder responses. For additional 
information on stakeholder views, see appendix II. 

[End of figure] 

About a third of stakeholders (7 of the 20) expressed the view that a 
trust fund should be used only to fund the existing CWSRF. Stakeholders 
cited several reasons for this view, including their interest in 
building on the success of the CWSRF program, avoiding the redundant 
administrative costs associated with establishing a new wastewater 
infrastructure program, and providing a dedicated funding source to 
increase available funding for the CWSRF program. 

Three of 20 stakeholders that responded to our questionnaire said that 
a trust fund should not be used to support the existing CWSRF, but 
rather to fund a separate and distinct wastewater infrastructure 
program. One of these stakeholders told us that the CWSRF does not 
prioritize funding to wastewater systems with the greatest needs. 
Stakeholders we interviewed said that CWSRF loan amounts can sometimes 
be inadequate to meet the needs of large urban areas that have large 
and costly infrastructure projects and that smaller communities may 
lack the administrative capacity to go through the process of applying 
for a CWSRF loan. In addition, our past work has found that states vary 
in the way they allocate CWSRF funds for small or economically 
disadvantaged communities and that some states have placed limits on 
the amount of CWSRF funding any one borrower can receive in a single 
year.[Footnote 18] 

Twenty-five percent of questionnaire respondents (5 of 20) supported 
using a trust fund to both fund the CWSRF and establish a separate and 
distinct program. These stakeholders said the CWSRF needed a dedicated 
source of funding, but that the flexibility of a new program could help 
to address some of the CWSRF's limitations. 

Finally, 3 of 20 stakeholders responding to our questionnaire were 
opposed to the creation of a clean water trust fund to support the 
nation's wastewater infrastructure. According to these stakeholders, 
utilities should be self-sustaining through the rates they charge their 
customers and by more efficiently managing their systems. These 
stakeholders also attribute the potential gap between projected future 
wastewater infrastructure needs and current spending to the reluctance 
of wastewater utilities to charge the full cost of the services they 
provide. Charging the full cost would require utilities to charge 
prices that reflect the costs of building, maintaining, and operating a 
wastewater system over the long term. Our past work has highlighted 
similar concerns with the management of local wastewater utilities. 
Specifically, we found that many utilities were not routinely charging 
the full cost for wastewater services and that the practice of 
systematically identifying and planning for infrastructure 
improvements, known as asset management, could help utilities better 
address their infrastructure needs.[Footnote 19] 

Type of financial assistance. Another design issue that stakeholders 
identified was specifying the type of assistance--grants or loans--that 
a clean water trust fund would provide. Over half of the stakeholders 
responding to our questionnaire (13 of 21) favored distributing funding 
to wastewater infrastructure projects using a combination of loans and 
grants. According to many of these stakeholders, the type of assistance 
provided by a trust fund should be tailored to the applicant's needs 
and capacity. Some of these stakeholders explained that while some 
communities can take on debt and pay back loans for wastewater 
projects, others may need grants because they are unable to pay back 
loans. Other stakeholders who we talked to also stated that loans 
impose discipline on borrowers, who are responsible for repayment, but 
that grants may be needed for certain communities that cannot make loan 
repayments, such as those with declining or low-income populations. 
These stakeholder views are consistent with some of the policy debate 
surrounding the reauthorization of the CWSRF, in which certain groups 
have supported the distribution of grants, as well as loans, for 
certain wastewater projects, through the CWSRF as is currently allowed 
under the Drinking Water State Revolving Fund. A provision allowing 
some funding to be distributed as grants would be similar to recent 
legislation; specifically, some of the funding provided to the CWSRF by 
the 2009 American Recovery and Reinvestment Act can be distributed in 
the form of grants. 

In contrast, 3 of 21 stakeholders who responded to our questionnaire 
told us that funding to support wastewater infrastructure projects 
should be distributed using loans only while 2 said that only grants 
should be used. The stakeholders supporting the use of loans said that 
the funds from the repayment of these loans provide a source of funding 
to meet future infrastructure needs, and that below-market interest 
rates can be offered on these loans as an affordable way for 
communities to fund wastewater infrastructure. One of the stakeholders 
who said that funding to support wastewater infrastructure projects 
should be distributed using grants stated that a grant program will 
help lower costs for municipalities and allow them to offer more 
affordable wastewater utility rates. 

Eligible activities. Finally, stakeholders said that designing and 
implementing a clean water trust fund would involve determining the 
type of wastewater infrastructure activities that the fund would 
support. Most stakeholders who responded to our questionnaire supported 
using a trust fund for planning and designing wastewater projects (18 
of 21) and for capital costs (19 of 21). Some stakeholders noted that 
these two activities are closely linked--planning and designing are 
essential components of carrying out capital projects. Stakeholders 
that supported using the trust fund for capital costs identified many 
of the activities that are currently eligible for funding under the 
CWSRF as those that should be eligible to receive support under a clean 
water trust fund. These activities include expanding wastewater systems 
to meet existing needs, replacing or rehabilitating wastewater 
collection systems or treatment facilities, and correcting wastewater 
overflows from wastewater systems. Many of these stakeholders said that 
capital costs should be given priority because these are major costs 
and represent the most pressing needs for utilities. Moreover, 
according to some stakeholders, capital costs should be eligible for 
funding because communities may incur significant costs when upgrading 
or rehabilitating their wastewater systems in order to comply with 
Clean Water Act requirements or other federal mandates. In addition to 
capital costs, stakeholders identified other activities that should be 
eligible for funding, including providing rate-payer assistance to low- 
income households, supporting green infrastructure and nonpoint source 
pollution projects, and training wastewater plant operators. Only 2 
stakeholders responded that a trust fund should be used to support 
operations and maintenance for wastewater utilities. 

Appendix II provides the full range of stakeholder responses to the 
questionnaire on design issues. Appendix III provides a list of 
stakeholder groups that responded to our questionnaire. 

Various Options for Funding a Clean Water Trust Fund Could Generate a 
Range of Revenues, but Each Option Poses Certain Obstacles: 

Although a variety of options have been proposed in the past to 
generate revenue for a clean water trust fund, generating $10 billion 
from any one of these alone may be difficult. In addition, each funding 
option poses various implementation challenges, including defining the 
products or activities to be taxed, establishing a collection and 
enforcement framework, and obtaining stakeholder support. 

A Variety of Options Are Available That Could Generate a Range of 
Revenue to Support a Trust Fund: 

Various funding options, including excise taxes on products that may 
contribute to the wastewater stream, an additional tax on corporate 
income, a water use tax, and an industrial discharge tax, could 
generate a range of revenues for a clean water trust fund. However, it 
may be difficult to raise $10 billion for a clean water trust fund from 
any one of these options because of the small size of the tax bases of 
many of these options. 

Excise Taxes on Products That May Contribute to the Wastewater Stream: 

Excise taxes on products that may contribute to the wastewater stream 
could be used to generate revenue for a clean water trust fund. These 
products include beverages, fertilizers and pesticides, flushable 
products, pharmaceuticals, and water appliances and plumbing fixtures. 
While past proposals for funding a clean water trust fund have 
identified these products as contributing to the wastewater stream, 
limited research has been done on their specific impact on wastewater 
infrastructure, according to EPA.[Footnote 20] See table 1 for a 
description of these product groups and how these products may 
contribute to the wastewater stream. 

Table 1: Product Groups that May Contribute to the Wastewater Stream: 

Product group: Beverages; 
Description: Products include soft drinks, bottled water, ice, beer, 
wine, and liquor. After consumption, beverages as well as their 
containers can end up in the wastewater stream. 

Product group: Fertilizers and pesticides; 
Description: Products include substances used to fertilize soil or 
control plant or animal pests. Fertilizers and pesticides can 
contribute to nonpoint source pollution--pollution that comes from 
diffuse sources when rain or snowmelt washes pollutants off the ground. 
For example, fertilizers can introduce large amounts of nutrients such 
as nitrogen and phosphorous into water bodies, leading to excessive 
growth of algae, which in turn blocks out sunlight and decreases 
dissolved oxygen in water, a necessity for plants and other aquatic 
life. Pesticides can introduce harmful chemicals into water bodies as 
well. In 2009, EPA reported that agriculture was a leading source of 
water impairments in a sample of the nation's rivers, streams, lakes, 
ponds, and reservoirs.[A] 

Product group: Flushable products; 
Description: Products include soaps and detergents; cooking oils; and 
shampoos, lotions, and perfumes. Some of these products can introduce 
pollutants into the wastewater stream. For example, some dishwashing 
detergents contain phosphorous, a nutrient that in excessive quantities 
can lead to excessive growth of algae in surface waters. In addition, a 
2002 study by United States Geological Survey (USGS) detected household 
chemicals found in detergents, soaps, and cosmetics in streams that 
received discharge from wastewater treatment plants.[B] Cooking oils 
also can cause pipe blockages. 

Product group: Pharmaceuticals; 
Description: Products include over-the-counter and prescription drugs. 
When consumed, pharmaceuticals are not entirely absorbed by the body 
and can be excreted into wastewater. In addition, some pharmaceuticals 
are flushed down the toilet for disposal. According to EPA, studies 
have shown that pharmaceuticals are currently present in our water 
bodies, and some may cause ecological harm. For example, a 2002 study 
by USGS detected chemicals, including pharmaceuticals, in streams that 
receive discharge from wastewater treatment plants.[B] Currently, 
wastewater systems are not equipped to remove pharmaceuticals, and 
additional research is needed to better understand the impact of 
pharmaceuticals on wastewater and the environment. 

Product group: Water appliances and plumbing fixtures; 
Description: Products include dishwashers, washing machines, and other 
plumbing fixtures. These products typically introduce wastewater into 
the system. The volume of wastewater that a utility must treat impacts 
the capacity of the wastewater plant needed. 

Source: GAO summary of EPA and USGS reports along with interviews with 
stakeholders. 

[A] EPA, National Water Quality Inventory: Report to Congress 2004 
Reporting Cycle (Washington, D.C., January 2009). 

[B] USGS, Pharmaceuticals, Hormones, and Other Organic Wastewater 
Contaminants in US Streams, USGS Fact Sheet FS-027-02, June 2002. 

[End of table] 

The tax base for each group of products in 2006--the value of products 
manufactured domestically as well as those imported, but excluding 
exports--varied from about $26 billion for water appliances and 
plumbing fixtures to about $156 billion for pharmaceuticals, after 
adjusting these tax bases to 2009 dollars. In addition, raising $10 
billion from a tax on any individual product group would require tax 
rates varying from a low of 6.4 percent for pharmaceuticals to a high 
of 39.2 percent for water appliances and fixtures.[Footnote 21] 
Alternatively, a lower tax rate could be levied on a number of these 
product groups that would collectively generate about $10 billion. 
Table 2 shows the tax bases for the product groups along with the 
revenue that could be generated from a range of tax rates. Appendix IV 
presents additional information on the tax bases for these funding 
options. 

Table 2: Tax Bases for Product Groups and Estimated Revenue from Range 
of Excise Tax Rates, in Constant 2009 Dollars (Dollars in millions) 

Product groups: Beverages; 
Tax base: $95,551; 
1% tax: $956; 
5% tax: $4,778; 
10% tax: $9,555; 
Tax rate to generate $10 billion: 10.5%. 

Product groups: Fertilizers and pesticides; 
Tax base: $26,088; 
1% tax: $261; 
5% tax: $1,304; 
10% tax: $2,609; 
Tax rate to generate $10 billion: 38.3%. 

Product groups: Flushable products, including soaps, detergents, 
cooking oils, and toiletries; 
Tax base: $63,241; 
1% tax: $632; 
5% tax: $3,162; 
10% tax: $6,324; 
Tax rate to generate $10 billion: 15.8%. 

Product groups: Pharmaceuticals; 
Tax base: $156,069; 
1% tax: $1,561; 
5% tax: $7,803; 
10% tax: $15,607; 
Tax rate to generate $10 billion: 6.4%. 

Product groups: Water appliances and plumbing fixtures; 
Tax base: $25,517; 
1% tax: $255; 
5% tax: $1,276; 
10% tax: $2,552; 
Tax rate to generate $10 billion: 39.2%. 

Source: GAO analysis of U.S. Census Bureau data from the 2006 Annual 
Survey of Manufactures and Foreign Trade Division. 

[End of table] 

Alternatively, a per unit excise tax could be levied on these products. 
For example, according to the Container Recycling Institute, there were 
about 215 billion bottled and canned beverages sold in 2006.[Footnote 
22] Levying a 1 cent tax on these bottles and cans could yield about 
$2.2 billion, and raising $10 billion would require a tax of about 5 
cents. 

Additional Tax on Corporate Income: 

Another option that could be used to fund a clean water trust fund is 
to levy an additional tax on the incomes of corporations. This tax 
would be similar to the Corporate Environmental Income Tax (CEIT) that 
helped fund the Superfund program until 1995.[Footnote 23] Increasing 
the current corporate income tax by levying an additional 0.1 percent 
on the $1.4 trillion in corporate taxable income reported in 2006, 
after adjusting for inflation, could raise about $1.4 billion annually. 
Higher tax rates would need to be levied to generate a larger amount of 
revenue. For example, a 0.5 percent tax could raise $6.9 billion and to 
raise $10 billion from this option, an additional tax of about 0.7 
percent would need to be levied. However, this level of taxation would 
exceed the 0.12 percent CEIT that was in place under Superfund when it 
expired in December 1995. 

Water Use Tax: 

Another option to fund a clean water trust fund is a tax on water 
usage. A tax on water use could involve a volume-based charge or a flat 
charge added to local residential, commercial, and industrial water 
utility rates paid by water customers. For a volume-based charge, 
levying a tax of 0.01 cent per gallon on the 13.4 trillion gallons of 
water that were delivered to domestic, commercial, and industrial users 
from public supplies in 2000 could raise $1.3 billion annually, while a 
tax of about 0.1 cent per gallon could raise about $13 billion 
annually.[Footnote 24] Alternatively, a flat charge could be added to 
household wastewater bills, similar to Maryland, which charges 
households $30 annually to help fund wastewater infrastructure in the 
state.[Footnote 25] At a national level, imposing a flat charge of $30 
annually on the approximately 86 million households that receive 
wastewater service from wastewater utilities could raise about $2.6 
billion annually. Raising $10 billion from a flat charge on households 
would require a charge of about $116 per year per household.[Footnote 
26] Based on EPA estimates from 2003, American households paid about 
$474 annually for water and wastewater services; therefore, imposing an 
annual charge of $116 on households would represent an approximately 25 
percent increase in customers' water and wastewater bills. 

Industrial Discharge Tax: 

A final option that we identified that could raise revenue to fund a 
clean water trust fund is an industrial discharge tax. A tax on 
industrial discharge could potentially be levied in two ways. The first 
would be to levy a fee on National Pollutant Discharge Elimination 
System (NPDES) permits. These permits, required under the Clean Water 
Act, allow a point source to discharge specified pollutants into 
federally regulated waters. A second approach would be to levy a tax on 
toxic chemical releases to water reported by industrial facilities to 
the Toxics Release Inventory (TRI), which contains data on the 
quantities of toxic discharges to air, water, or land for 581 chemicals 
and 30 chemical categories.[Footnote 27] However, it is unclear what 
level of taxation could be levied to generate $10 billion from either 
of these approaches because of data limitations. Specifically, EPA 
lacks complete and reliable data on the number of NPDES permits issued 
nationwide. Similarly, EPA does not have complete data on all of the 
toxic releases because TRI data are based on self-reporting by 
facilities that release chemicals above certain thresholds. In 
addition, these reports can be based on estimates of their toxic 
releases instead of actual measurements.[Footnote 28] 

Each Funding Option Poses Certain Implementation Challenges: 

Implementing any of the funding options discussed above poses a variety 
of challenges, including defining the products or activities to be 
taxed and establishing a collection and enforcement framework, 
according to interviews we had with agency officials and other 
stakeholders. 

Excise Taxes on Products That May Contribute to the Wastewater Stream: 

According to Internal Revenue Service (IRS) officials, implementing 
excise taxes on products requires the agency to develop clear and 
precise definitions of the products to be taxed, as authorized by 
Congress. These definitions determine whether taxpayers are required to 
pay excise taxes and how much tax they owe. In implementing excise 
taxes in the past, the IRS has developed these definitions after 
receiving comments from relevant industries. As part of this process, a 
decision also would need to be made regarding whether the tax would be 
levied on a per unit basis or a percentage of sales basis. Of the $71.3 
billion that the federal government collected from federal excise taxes 
in 2007, many items are taxed on a per unit basis--a gallon of 
gasoline, for example--but some items are taxed on a percentage of 
sales--such as an airline ticket, which is taxed at 7.5 percent of the 
ticket price. The larger the number of taxable products covered by an 
excise tax, the greater the challenge of defining these products, 
according to IRS officials. In addition, any exemptions to the excise 
tax would also need to be defined. According to IRS officials, a large 
number of exemptions could present additional implementation challenges 
because the agency would have to process applications from taxpayers 
seeking refunds for taxes paid on exempted products. IRS officials told 
us that the administrative costs associated with designing and 
implementing any new excise taxes could be substantial and this process 
could take more than a year to complete. 

In addition, once the taxable product(s) have been defined, IRS also 
would need to modify its excise tax collection and enforcement 
framework. Implementing new excise taxes would require the IRS to 
update the forms currently used to submit excise taxes and its computer 
systems to document these receipts, as well as training agency staff on 
administering the new excise taxes. Moreover, implementing new taxes 
would increase the auditing and enforcement responsibility of the IRS. 
In addition, to increase compliance the IRS conducts outreach to those 
who would be required to pay these excise taxes. All of these 
activities--making changes to forms and computer systems, training 
staff, and conducting outreach--would need to occur well in advance of 
the start of the tax filing season to eliminate possible confusion and 
could increase the agency's administrative costs, according to IRS 
officials. In addition, the challenge in collecting and enforcing 
excise taxes can be impacted by the point at which the tax is collected 
and the number of taxpayers. According to IRS officials, collecting and 
enforcing an excise tax at the manufacturing level is preferable 
because it involves fewer taxpayers than a tax that is levied at the 
retail level. 

Additional Tax on Corporate Income: 

According to IRS officials, implementing an additional tax on corporate 
income would require defining the types of corporations and the 
portions of their income that would be subject to this tax. For 
example, under Superfund, the CEIT was levied only on corporations that 
had income in excess of $2 million.[Footnote 29] In addition, while the 
current collection system for corporate income taxes could be used to 
collect this additional tax, this change would need to be communicated 
to both corporate taxpayers and IRS tax examiners to promote 
compliance. 

Water Use Tax: 

Implementing a tax on water use also would pose challenges such as 
developing a collection system, deciding how to structure the tax, and 
determining the tax base or which users to tax. Collecting this tax 
could be difficult, because according to water and wastewater officials 
we spoke with, it would most likely involve relying on some of the 
billing systems in place for the nation's existing 50,000 community 
water systems and over 16,000 publicly owned wastewater plants along 
with other local government entities.[Footnote 30] However, all of 
these water and wastewater suppliers do not uniformly bill their 
customers based on the volume of water use. Instead, some charge a flat 
fee or have other types of rate structures. Some stakeholders said that 
a flat charge on households would be easier to administer, but that a 
volume-based charge on water use would be more equitable. In addition, 
decisions would need to be made regarding which users of the system-- 
households, commercial, and industrial--would be subject to the tax. 

Industrial Discharge Tax: 

Implementing an industrial discharge tax also could be difficult 
because there is no federal system currently in place to charge and 
collect such a tax. As a result, key steps, including defining the tax 
base--whether to tax discharge permits or actual discharge--determining 
a tax rate, and developing a collection and enforcement framework, 
would need to be completed before such a tax could be implemented. 
These efforts would likely be complicated by a lack of complete and 
accurate data on the number of permit holders and quantity of 
industrial discharge. Implementing such a tax would include the 
following specific challenges: 

* Permit-based tax. Determining which of the two types of NPDES 
permits--individual or general--would be taxed and setting a tax rate 
could be difficult.[Footnote 31] Individual permits are typically 
issued for single facilities, such as wastewater treatment plants, 
while a single general permit can cover multiple facilities that are 
engaged in similar types of activities and located in a specific 
geographic area, such as construction sites. According to EPA 
officials, the types of effluent and levels of discharge covered by 
these two types of permits can vary significantly and charging a flat 
tax to all permit holders may not be equitable. In addition, because 
EPA currently does not collect any taxes or fees on NPDES permits, the 
agency would have to develop a basis for establishing a tax rate and 
put in place a collection and enforcement framework before a permit- 
based tax could be implemented. 

* Discharge-based tax. Currently, EPA does not collect any taxes on 
industrial discharges, and to implement such a tax would require EPA to 
put in place a collection and enforcement framework. Developing such a 
framework could be difficult because EPA does not have complete data on 
the industrial discharges that are occurring or on the environmental 
and human health hazards posed by such discharges. For example, while 
the TRI has information on approximately 265 chemicals that are 
discharged to water, these data are based on annual reports submitted 
by industrial facilities. Moreover, EPA has limited national data on 
the discharge of conventional pollutants to water because many 
facilities that discharge these pollutants are not required to report 
this information to EPA.[Footnote 32] In addition, determining a basis 
for a tax rate could be difficult because of the potentially large 
number of chemicals and their varying characteristics. While EPA has 
developed toxic weighting factors that provide a relative measure of 
the toxicity for most of the TRI chemicals, EPA officials told us that 
there are inherent scientific difficulties in using existing toxicity 
weighting systems to compare toxicity among chemicals. Specifically, 
they told us that these systems may not adequately distinguish between 
cancer and non-cancer hazards and considering all such hazards together 
can be misleading. In addition, EPA has not developed toxic weighting 
factors for all chemicals in the TRI. EPA officials pointed out that 
these weighting factors were not developed for taxation purposes, and 
they expressed concern that using the TRI for this purpose could 
potentially discourage industries from reporting their full discharges 
to the TRI. Such an outcome would be a significant concern given that 
one of the TRI program's primary goals is to increase the public's 
access to the best available information on toxic chemical releases in 
their communities. 

Obtaining Stakeholder and Industry Support for Funding Options Could 
Pose Additional Challenges: 

Consideration of stakeholders' and industry views is important in 
developing a new taxation system, because voluntary compliance with any 
tax is influenced by whether taxpayers view a tax as being transparent, 
credible, and logical. While a majority of stakeholders supported three 
of the eight funding options, we identified some stakeholders who had 
not yet taken a position on these options, making it difficult to gauge 
their level of support for these options.[Footnote 33] In addition, 
industry groups representing most of the product groups that we 
identified as potential funding options were generally opposed to 
levying excise taxes on these products. Furthermore, obtaining 
widespread stakeholder support may be difficult because many 
stakeholders do not perceive a strong connection between most of these 
funding options and wastewater infrastructure use. 

Excise Taxes on Products That May Contribute to the Wastewater Stream: 

The proportion of stakeholders supporting excise taxes on the five 
product groups ranged from over a half to about a third. Specifically, 
over half of stakeholders responding to our questionnaire supported 
excise taxes on fertilizers and pesticides and flushable products, and 
about half supported excise taxes on beverages and pharmaceuticals. In 
contrast, only about a third of stakeholders supported an excise tax on 
water appliances and plumbing fixtures. More importantly, we identified 
some stakeholders who had not yet taken a position on any of the five 
excise tax options--they neither supported nor opposed these options or 
did not know or had no opinion on these options--making it unclear what 
their level of support would be if excise taxes on these product groups 
were proposed. Specifically, half of stakeholders responding to our 
questionnaire had not yet taken a position on taxing water appliances 
and plumbing fixtures, while about a third of stakeholders did not have 
a position on taxing beverages or pharmaceuticals. Table 3 shows the 
level of stakeholders' support for excise taxes on each of the five 
product groups that we identified. 

Table 3: Stakeholder Support for Excise Taxes (Number of stakeholders): 

Product group: Beverages; 
Strongly support or support: 10; 
Neither support nor oppose: 6; 
Strongly oppose or oppose: 2; 
Don't know/no opinion: 1; 
Included multiple responses: 1; 
Total responses: 20. 

Product group: Fertilizers and pesticides; 
Strongly support or support: 11; 
Neither support nor oppose: 4; 
Strongly oppose or oppose: 3; 
Don't know/no opinion: 0; 
Included multiple responses: 1; 
Total responses: 19. 

Product group: Flushable products; 
Strongly support or support: 12; 
Neither support nor oppose: 4; 
Strongly oppose or oppose: 2; 
Don't know/no opinion: 0; 
Included multiple responses: 1; 
Total responses: 19. 

Product group: Pharmaceuticals; 
Strongly support or support: 9; 
Neither support nor oppose: 5; 
Strongly oppose or oppose: 4; 
Don't know/no opinion: 1; 
Included multiple responses: 0; 
Total responses: 19. 

Product group: Water appliances and plumbing fixtures; 
Strongly support or support: 7; 
Neither support nor oppose: 8; 
Strongly oppose or oppose: 3; 
Don't know/no opinion: 2; 
Included multiple responses: 0; 
Total responses: 20. 

Source: GAO analysis of stakeholder responses. 

Note: Not all stakeholders responded to each question, so the total 
number of responses can vary. In addition, 1 stakeholder provided 
multiple responses. 

[End of table] 

Obtaining stakeholder support for some of these excise taxes may be 
difficult because stakeholders did not always see a strong connection 
between these products and wastewater infrastructure use. For example, 
about half of stakeholders did not see a strong connection between 
pharmaceuticals and water appliances and plumbing fixtures and 
wastewater infrastructure use. On the other hand, stakeholders saw a 
strong connection between fertilizers and pesticides and flushable 
products and wastewater infrastructure use. Taxing these two product 
groups to fund a clean water trust fund also garnered the greatest 
level of stakeholder support. Table 4 shows stakeholders' views on the 
extent of the connection between wastewater infrastructure use and the 
five product groups. 

Table 4: Stakeholder Views on the Extent of the Connection between 
Wastewater Infrastructure Use and Product Groups (Number of 
stakeholders): 

Product group: Beverages; 
Great extent or very great extent: 8; 
Moderate extent: 4; 
Little or no extent: 3; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18. 

Product group: Fertilizers and pesticides; 
Great extent or very great extent: 12; 
Moderate extent: 2; 
Little or no extent: 1; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18. 

Product group: Flushable products; 
Great extent or very great extent: 12; 
Moderate extent: 3; 
Little or no extent: 0; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18. 

Product group: Pharmaceuticals; 
Great extent or very great extent: 6; 
Moderate extent: 7; 
Little or no extent: 2; 
Don't know/no opinion: 3; 
Included multiple responses: 0; 
Total responses: 18. 

Product group: Water appliances and plumbing fixtures; 
Great extent or very great extent: 5; 
Moderate extent: 7; 
Little or no extent: 3; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18. 

Source: GAO analysis of stakeholder responses. 

Note: Not all stakeholders responded to each question, so the total 
number of responses can vary. In addition, 1 stakeholder provided 
multiple responses. 

[End of table] 

In addition, industry groups were consistently opposed to a tax on 
their specific product groups to support a clean water trust fund. In 
their view, their products did not contribute significantly to the 
deterioration of wastewater infrastructure and therefore should not be 
taxed. Stakeholder and industry reasons for their support or opposition 
to these excise taxes, along with the views of wastewater utility 
operators, are summarized in table 5. 

Table 5: Stakeholder and Industry Reasons for Support or Opposition to 
Excise Taxes on Specific Product Groups Along with Views of Utility 
Operators: 

Excise Tax: Beverages; 
Reasons for stakeholder support[A]: 
* The process for manufacturing relies heavily on clean water as an 
input; 
* Production and consumption of beverages generates waste; 
* Purchases are discretionary; 
Reasons for stakeholder opposition[A]: 
* These products do not pose much of a burden to wastewater systems; 
* Unfair to single out one industry for taxation; 
* Producers already pay taxes and other fees for wastewater services; 
Views of utility operators: 
* Bottles can enter the wastewater stream and need to be removed and 
disposed of; 
Reasons for industry opposition[B]: 
* Amount of water that beverage companies use is small; 
* Companies already pay for the water they consume; 
* Federal excise tax is already levied on alcoholic beverages and there 
are state and local taxes on beverages; 
* These companies already pay corporate and state income taxes. 

Excise Tax: Fertilizers and pesticides; 
Reasons for stakeholder support[A]: 
* These products contribute to nonpoint source pollution; 
Reasons for stakeholder opposition[A]: 
* This would be an unfair tax on a product that does not impact 
wastewater infrastructure; 
* Unfair to single out one industry for taxation; 
* Producers already pay taxes and other fees for wastewater services; 
Views of utility operators: 
* These are nonpoint source pollutants that affect surface waters and 
do not necessarily go through wastewater treatment plants; 
Reasons for industry opposition[B]: 
* It was unlikely that fertilizers and pesticides applied on 
agricultural land would enter a municipality's wastewater 
infrastructure system and it would not be fair to tax these products in 
order to fund this infrastructure; 
* EPA already charges a fee to register pesticides, and several states 
charge fees on fertilizers and pesticides. 

Excise Tax: Flushable products; 
Reasons for stakeholder support[A]: 
* These products contribute to the wastewater burden faced by utility 
operators and must be removed during the treatment process; 
Reasons for stakeholder opposition[A]: 
* The additional cost of treating these products is trivial during the 
wastewater treatment process; 
* Producers already pay taxes and other fees for wastewater services; 
* These products include necessities; 
Views of utility operators: 
* Certain products in this group can pose a burden to wastewater 
treatment plants, while others do not; 
Reasons for industry opposition[B]: 
* While some of these products could enter the wastewater stream, not 
enough research had been done to determine the impact these products 
have had on wastewater infrastructure; 
* Levying a similar tax on all of these products would not be fair. 

Excise Tax: Pharmaceuticals; 
Reasons for stakeholder support[A]: 
* Impact the quality of the nation's waters; 
* Investment was already being made in drinking water infrastructure to 
help remove these contaminants and similar investment may be needed in 
wastewater infrastructure in the future; 
Reasons for stakeholder opposition[A]: 
* Pharmaceuticals are an essential product that is already expensive 
for consumers; 
* Unfair to single out one industry for taxation; 
* Producers already pay taxes and other fees for wastewater services; 
Views of utility operators: 
* Removal of pharmaceuticals during wastewater treatment is not 
currently required and if a tax were levied on pharmaceuticals to fund 
wastewater infrastructure, the public could expect that pharmaceuticals 
would be removed by wastewater treatment plants; 
Reasons for industry opposition[B]: 
* Could increase cost for consumers; 
* Federal fees are in place for the registration of some prescription 
drugs, and state sales taxes are in place for over-the-counter 
pharmaceuticals; 
* A tax focused on one industry is not broad based. 

Excise Tax: Water appliances and plumbing fixtures; 
Reasons for stakeholder support[A]: 
* These appliances and fixtures can introduce flushable products into 
the wastewater stream; 
Reasons for stakeholder opposition[A]: 
* Unfair to single out one industry for taxation; 
* Producers already pay taxes and other fees for wastewater services; 
Views of utility operators: 
* Food scraps have to be removed during the wastewater treatment 
process which is generally introduced into the waste stream by 
dishwashers and garbage disposals; 
* Higher efficiency appliances can release stronger effluents which 
require additional treatment; 
Reasons for industry opposition[B]: 
* Would be a disincentive for consumers to buy newer, more efficient 
appliances that conserved water and helped to lower the burden on 
wastewater infrastructure. 

Source: GAO analysis of stakeholder views. 

[A] The views presented in these columns are from stakeholders that 
responded to our questionnaire. They are national groups that represent 
wastewater and drinking water industries, state and local governments, 
engineers, and environmental groups. 

[B] The views presented in this column are from industry groups we 
interviewed that represented the manufacturers of some of the products 
that were identified as potential funding options. 

[End of table] 

Additional Tax on Corporate Income: 

About a third of stakeholders responding to our questionnaire (6 of 19) 
opposed or strongly opposed this option. Another 7 stakeholders had not 
taken a position on this funding option, making it unclear what their 
level of support would be. Furthermore, of the eight funding options, 
stakeholders saw the least connection between this funding option and 
wastewater infrastructure use, with nearly two-thirds of stakeholders 
(11 of 18) responding that there was little or no connection. In fact, 
stakeholders' inability to see the connection was one of the reasons 
they cited for their opposition to this funding option. Other reasons 
that stakeholders provided for opposing this option were the current 
economic crisis and that corporations already pay taxes and fees to 
local systems for wastewater treatment services. Among the reasons that 
stakeholders gave for supporting this option were that the nation, and 
all industrial sectors, benefit from clean water, and this tax would be 
spread across a number of different polluting industries. 

Water Use Tax: 

Stakeholder opposition to this funding option was the strongest of the 
eight funding options we identified. Over half of stakeholders (11 of 
21) that responded to our questionnaire opposed a water use tax to fund 
a clean water trust fund. Some of these opponents said that such a tax 
would infringe on the ability of local utilities to raise rates for 
their own needs. Drinking water industry officials said that many 
communities have adopted comprehensive asset management plans and 
raised their water rates to pay for infrastructure needs, and it would 
be unfair to tax all communities and then distribute money to those 
communities that have not managed their systems well. In addition, 
stakeholders we interviewed said that redistribution of tax revenue 
would be a concern with this option if communities contributed more to 
the trust fund than they received back in funding.[Footnote 34] They 
also told us that a water use tax could disproportionately affect low- 
income households because these households pay a larger portion of 
their income for their water bills. On the other hand, 5 stakeholders 
supported this funding option and some said that rates are still 
relatively low in many parts of the country and local ratepayers should 
pay for the costs of the infrastructure they use. 

Industrial Discharge Tax: 

Over a third of stakeholders (7 of 19) supported or strongly supported 
an industrial discharge tax, while another 7 stakeholders neither 
supported nor opposed this option. The most common reasons that 
stakeholders gave for supporting this option was that industries should 
pay for the pollution they discharge. Among the reasons that 
stakeholders provided for opposing this option was that industrial 
facilities already pay for wastewater services. 

Agency Comments: 

We provided a draft of this report to EPA and IRS for review and 
comment. Neither agency provided written comments to us. EPA provided 
technical comments, which we have incorporated as appropriate. 

As agreed with your offices, unless you publicly announce the contents 
of this report earlier, we plan no further distribution until 30 days 
from the report date. At that time, we will send copies to the 
Administrator of EPA, the Commissioner of IRS, and interested 
congressional committees. In addition, the report will be available at 
no charge on GAO's Web site at [hyperlink, http://www.gao.gov]. 

If you or your staffs have any questions regarding this report, please 
contact me at (202) 512-3841 or mittala@gao.gov. Contact points for our 
Offices of Congressional Relations and Public Affairs may be found on 
the last page of this report. Key contributors to this report are 
listed in appendix V. 

Signed by: 

Anu Mittal:
Director, Natural Resources and Environment: 

[End of section] 

Appendix I: Scope and Methodology: 

To determine stakeholders' views on the issues that need to be 
addressed in designing and establishing a clean water trust fund, we 
reviewed past legislative proposals and wastewater industry position 
papers on establishing a clean water trust fund. In addition, we 
interviewed over 50 different stakeholders with knowledge of a variety 
of wastewater infrastructure issues, including individuals and groups 
from the wastewater industry; industry associations; and federal, 
state, and local government; and obtained their views on establishing 
and designing a clean water trust fund. During this process, we 
identified other relevant stakeholders to speak to by asking 
interviewees to identify other knowledgeable stakeholders in this area 
that we should contact, a process known as the "snowball" approach. 

Based on the information obtained through these interviews and our 
review of reports, we developed and sent a questionnaire to 28 national 
organizations with expertise in one or more of the following areas: 
financing of wastewater projects, constructing and maintaining 
wastewater infrastructure, local and state wastewater infrastructure 
needs, and environmental protection. Prior to sending out this 
questionnaire, we pretested the questionnaire with stakeholders and 
made changes based on their input. This questionnaire asked for their 
views on how a clean water trust fund should be administered, the types 
of activities it should fund, and how funding should be distributed. We 
received responses from 22 of these stakeholders. Of the 6 stakeholders 
that did not respond, 4 of these told us they could not come to a 
consensus on behalf of their organization. For a list of the groups 
that responded to the questionnaire, see appendix III. We also reviewed 
information on the Clean Water State Revolving Fund (CWSRF) program and 
interviewed federal and state officials responsible for implementing 
this program to gain an understanding for how this program might 
interact with a clean water trust fund. 

We also visited three states--Arizona, Maryland, and Wisconsin--and the 
District of Columbia where we interviewed state and local officials 
about their wastewater infrastructure needs and how a clean water trust 
fund could be designed to meet these needs. We selected these states 
because they were geographically dispersed, had different wastewater 
infrastructure needs, and used various approaches to finance wastewater 
projects. On these visits, we toured wastewater facilities in large and 
small cities and spoke with local and state officials about how they 
were financing wastewater projects. 

To identify and describe potential options for funding a clean water 
trust fund that could generate $10 billion annually, we reviewed past 
legislative proposals and position papers from wastewater industry 
groups that discussed specific funding options for such a fund. We also 
reviewed reports on how existing federal trust funds that support 
environmental and infrastructure projects are funded and conducted 
Internet searches to identify funding options that some states were 
using to finance wastewater projects. Finally, we interviewed 
stakeholders with knowledge of wastewater infrastructure issues, 
including those from the wastewater industry and federal, state, and 
local government to identify other options that could be used to 
generate revenue for a clean water trust fund. 

To estimate the revenue that these options could potentially generate, 
we used the most recent government data available to estimate the value 
of products or activities that could be subject to a federal tax--the 
tax base--and applied a range of tax rates to these bases, which were 
based on current or past taxation policies. 

* For the five excise taxes we identified, we used the U.S. Census 
Bureau (Census) data from the 2006 Annual Survey of Manufactures, which 
provides data on the value of products manufactured domestically by 
different industrial codes, known as North American Industry 
Classification System (NAICS) codes.[Footnote 35] We identified 
specific NAICS codes for the five groups of products that could be 
subject to an excise tax. For three of our excise taxes--beverages, 
fertilizers and pesticides, and pharmaceuticals--these products are 
captured in a discrete set of NAICS codes according to Census 
officials. For the two other product groups--flushable products, and 
water appliances and plumbing fixtures--we examined prior reports to 
examine how these products were defined, analyzed these NAICS codes 
along with their descriptions, and worked with Census officials to 
ensure our list of NAICS codes was reasonable. To this value of 
products produced domestically, we added the value of products imported 
and subtracted the value of products that were exported to determine 
the tax base for these product groups.[Footnote 36] We made this 
calculation because according to Internal Revenue Service (IRS) 
officials, federal excise taxes are generally levied on imports but not 
on exports. We then converted the values of these tax bases to 2009 
constant dollars. Certain limitations exist with regard to our use of 
these data to estimate potential revenue from the funding options. 
Specifically, our use of NAICS codes for these groups of products may 
include a wider range of products than would be part of actual excise 
taxes on these products. In addition, due to data limitations, there 
are certain products that are not captured in our tax bases. For 
example, toilet paper is not included in our tax base for flushable 
products because this product is grouped under a NAICS code with other 
sanitary paper products that most likely would not impact wastewater 
infrastructure, such as disposable diapers. To determine the 
reliability of these data, we reviewed documentation from Census, 
interviewed relevant officials, and conducted some basic logic testing 
of the data, and we determined the data were sufficiently reliable for 
our purposes. For our estimate of a per container charge on bottled and 
canned beverages, we used Container Recycling Institute data on the 
number of packaged beverages sold in the United States in 2006. 
[Footnote 37] To determine the reliability of these data, we spoke with 
officials familiar with these data and reviewed relevant documentation 
on the data. We determined the data were sufficiently reliable for our 
purposes. 

* For our estimate of the corporate income tax, we used data from the 
IRS 2006 Statistics of Income and identified the value of taxable 
income that corporations had in this year. The amount of income subject 
to tax at the corporate level includes taxable income less certain 
deductions such as a corporation's net operating loss or other special 
deductions. To determine the reliability of these data, we reviewed 
documentation from IRS and interviewed relevant officials. We 
determined the data were sufficiently reliable for our purposes. 

* For our estimate of the water use tax, we used 1995 and 2000 data 
from the United States Geological Survey (USGS) on estimates of water 
delivered by public and private suppliers to domestic, commercial, and 
industrial users.[Footnote 38] After consulting with USGS officials, we 
estimated the use for residential, commercial, and industrial uses for 
2000 based on information available in 1995. Specifically, we used the 
2000 estimate for total public supply water deliveries and the 1995 
estimate of the proportion of total water deliveries to domestic, 
commercial, and industrial users in 1995 because the 2000 USGS report 
included information on total water deliveries but did not include 
information on types of users.[Footnote 39] To determine the 
reliability of these data, we interviewed USGS officials and reviewed 
relevant documentation on the data. We determined the data were 
sufficiently reliable for our purposes. For our estimate of a flat 
charge on household wastewater bills, we used Environmental Protection 
Agency (EPA) data on the population served by publicly owned treatment 
works to estimate the number of households that receive wastewater 
services.[Footnote 40] To determine the reliability of these data, we 
spoke with EPA officials and reviewed relevant documentation on the 
data. We determined the data were sufficiently reliable for our 
purposes. 

* For our estimate of an industrial discharge tax, we examined data 
from the National Pollutant Discharge Elimination System (NPDES) permit 
system and the 2006 Toxics Release Inventory (TRI). For the NPDES 
permit system, we determined there were not reliable national data on 
the total number of NPDES permits issued. For the TRI, we determined 
that these data were based on self-reported information from only 
certain facilities that discharged above a certain level. Moreover, 
these reports can be based on estimates rather than actual 
measurements. The TRI also does not contain data on discharges of 
conventional pollutants. Due to these data limitations, we determined 
that these data were not sufficiently reliable to make an estimate of 
the revenue that could be generated from a tax on industrial discharge. 

After identifying the taxable bases for these different funding 
options, we applied various tax rates to these bases based in part on 
existing or past taxation policies. Our review of existing federal 
excise taxes found that most excise taxes levied as a percentage of 
sales range from 3 percent to 12 percent so we applied the rates of 1 
percent, 3 percent, 5 percent, and 10 percent to our tax bases. For the 
tax on corporate income, we used 0.1 percent because a 0.12 percent on 
corporate income had been used to fund Superfund. For the water use 
tax, we used existing and proposed water taxes as the basis for the tax 
rates we applied. For all of the funding options, we also calculated 
the tax rate that would be needed to generate $10 billion annually. 

The revenue estimates presented in our report are not official revenue 
estimates as would be prepared by the Joint Committee on Taxation, and 
they are subject to various limitations. For example, we did not model 
consumer or market responses to these funding options, the potential 
extent of noncompliance, or estimate the cost of implementing and 
enforcing these options. As a result, our revenue estimates may be 
higher than actual receipts that would be generated from these funding 
options. Ultimately, the amount of revenue that any of these options 
would generate would depend heavily on the number of products that 
would be taxed, the tax rate used, and the compliance with the tax. 

To identify the challenges associated with implementing these different 
funding options, we interviewed federal and state officials who might 
be involved in collecting and enforcing these taxes. At the federal 
level, we spoke with IRS officials who collect and enforce excise taxes 
and corporate income taxes. For the water use tax, we also spoke with 
representatives of wastewater and drinking water utilities to learn 
about how they collect fees from the users of their systems and how a 
federal tax on water might make use of these systems. We also spoke 
with officials who were involved in taxing some of these products 
already. At the federal level, we spoke with officials in the Alcohol 
and Tobacco Tax Trade Bureau regarding the federal excise tax on 
alcoholic beverages, and we also spoke with EPA officials about the 
fees the agency levies on pesticides. On our state visits, we spoke 
with officials who had experience with implementing some of these 
funding options as well. 

To identify stakeholders' views of these funding options, we examined 
position papers that discussed these funding options. We also used our 
questionnaire to gauge stakeholder support for these options and to 
learn about their views on the connection between these options and 
wastewater infrastructure use. In addition, we spoke with industry 
groups that represented some of the products that could be targeted by 
excise taxes for their views. In particular, we spoke with groups 
representing many of the manufacturers in the following industries: 
beverages, fertilizers and pesticides, flushable products, 
pharmaceuticals, and water appliances and plumbing fixtures. 

We conducted our work from June 2008 to May 2009 in accordance with all 
sections of GAO's quality assurance framework that are relevant to our 
objectives. The framework requires that we plan and perform the 
engagement to obtain sufficient and appropriate evidence to meet our 
stated objectives and to discuss any limitations in our work. We 
believe that the information and data obtained, and the analysis 
conducted, provide a reasonable basis for any findings and conclusions. 

[End of section] 

Appendix II: Summary of Stakeholder Responses to Questionnaire: 

This appendix provides information on stakeholders' responses to our 
questionnaire about their views on the issues that need to be addressed 
in designing and establishing a trust fund as well as their views on 
the potential funding options that could be used for this fund. A list 
of stakeholders that responded to the questionnaire is presented in 
Appendix III. 

Table 6: Stakeholder Views on Administration: 

Which entity or entities should administer a clean water trust fund? 

EPA only; 
Number of Stakeholders: 0. 

EPA partnership with the states (like the current CWSRF); 
Number of Stakeholders: 15. 

Independent, non-governmental board of trustees; 
Number of Stakeholders: 0. 

Other; 
Number of Stakeholders: 4. 

Don't know/no opinion; 
Number of Stakeholders: 1. 

Total responses; 
Number of Stakeholders: 20. 

No response; 
Number of Stakeholders: 2. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 7: Stakeholder Views on Use of a Trust Fund: 

In your opinion, how, if at all, should a clean water trust fund be 
used? 

A trust fund should be used only to fund the existing CWSRF;
Number of Stakeholders: 7. 

A trust fund should not be used to fund the existing CWSRF but rather a 
separate and distinct program to support wastewater infrastructure; 
Number of Stakeholders: 3. 

A trust fund should be used partially to fund the existing CWSRF along 
with a separate and distinct program to support wastewater 
infrastructure; 
Number of Stakeholders: 5. 

A trust fund should not be created for the purpose of funding 
wastewater infrastructure; 
Number of Stakeholders: 3. 

Other; 
Number of Stakeholders: 2. 

Don't know/no opinion;
Number of Stakeholders: 0. 

Total responses; 
Number of Stakeholders: 20. 

No response; 
Number of Stakeholders: 2. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 8: Stakeholder Views on Funding Distribution: 

How should funding from a clean water trust fund be distributed to 
support wastewater projects? 

Loans only (like the current CWSRF); 
Number of Stakeholders: 3. 

Grants only; 
Number of Stakeholders: 2. 

Combination of loans and grants; 
Number of Stakeholders: 13. 

Other; 
Number of Stakeholders: 3. 

Don't know/no opinion; 
Number of Stakeholders: 0. 

Total responses; 
Number of Stakeholders: 21. 

No response; 
Number of Stakeholders: 1. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 9: Stakeholder Views on What Activities Should be Eligible for 
Funds: 

In your opinion, what wastewater infrastructure activities should be 
eligible for funding from a clean water trust fund? 

Routine operations and maintenance: 
Yes: 2; 
No: 17; 
Don't know/no opinion: 1; 
Indicated both Yes and No: 1; 
Total responses: 21; 
No response: 1. 

Planning and design of wastewater projects: 
Yes: 18; 
No: 2; 
Don't know/no opinion: 0; 
Indicated both Yes and No: 1; 
Total responses: 21; 
No response: 1. 

Ratepayer assistance to low-income households: 
Yes: 10; 
No: 9; 
Don't know/no opinion: 1; 
Indicated both Yes and No: 0; 
Total responses: 20; 
No response: 2. 

Capital costs: 
Yes: 19; 
No: 1; 
Don't know/no opinion: 0; 
Indicated both Yes and No: 1; 
Total responses: 21; 
No response: 1. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 10: Stakeholder Views on Eligible Capital Costs: 

If, in your opinion, capital costs should be eligible for funding from 
a clean water trust fund, which of the following activities should be 
included as capital costs? 

Replacement or rehabilitation of wastewater collection systems or 
treatment facilities (beyond normal maintenance); 
Number of Stakeholders: 20. 

Expansion of wastewater collection systems or treatment facilities for 
existing needs; 
Number of Stakeholders: 18. 

Expansion of wastewater collection systems or treatment facilities for 
population growth; 
Number of Stakeholders: 10. 

Construction of new wastewater treatment facilities; 
Number of Stakeholders: 17. 

Secondary wastewater treatment; 
Number of Stakeholders: 17. 

Advanced wastewater treatment; 
Number of Stakeholders: 18. 

Combined sewer overflow correction or elimination; 
Number of Stakeholders: 19. 

Infiltration/inflow correction; 
Number of Stakeholders: 18. 

Other; 
Number of Stakeholders: 8. 

Don't know/no opinion; 
Number of Stakeholders: 0. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 11: Stakeholder Views on Eligibility for Funds: 

What factors should be considered in determining what entities should 
be eligible for receiving funding from a clean water trust fund? 

Wastewater infrastructure needs; 
Number of Stakeholders: 15. 

Priority of environmental problem to be addressed; 
Number of Stakeholders: 12. 

Priority of waters or watersheds involved; 
Number of Stakeholders: 11. 

Population; 
Number of Stakeholders: 4. 

Median household income; 
Number of Stakeholders: 9. 

Other (please specify); 
Number of Stakeholders: 9. 

Don't know/no opinion; 
Number of Stakeholders: 0. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 12: Stakeholder Support for Funding Options: 

Do you support or oppose the following funding options? 

Beverages (beverages manufactured for consumption including soft 
drinks, bottled water, ice, beer, wine, and liquor but excluding fruit 
and vegetable juices and concentrates): 
Strongly support: 8; 
Support: 2; 
Neither support nor oppose: 6; 
Oppose: 0; 
Strongly oppose: 2; 
Don't know/no opinion: 1; 
Included multiple responses: 1; 
Total responses: 20; 
No response: 2. 

Fertilizers and pesticides: 
Strongly support: 7; 
Support: 4; 
Neither support nor oppose: 4; 
Oppose: 1; 
Strongly oppose: 1; 
Don't know/no opinion: 0; 
Included multiple responses: 1; 
Total responses: 18; 
No response: 4. 

Flushable products (including products introduced directly into 
wastewater, such as soaps, detergents, toilet paper, and cooking oils): 
Strongly support: 7; 
Support: 5; 
Neither support nor oppose: 4; 
Oppose: 0; 
Strongly oppose: 2; 
Don't know/no opinion: 0; 
Included multiple responses: 1; 
Total responses: 19; 
No response: 3. 

Pharmaceuticals: 
Strongly support: 3; 
Support: 6; 
Neither support nor oppose: 5; 
Oppose: 2; 
Strongly oppose: 2; 
Don't know/no opinion: 1; 
Included multiple responses: 0; 
Total responses: 19; 
No response: 3. 

Water appliances and plumbing fixtures (including fixtures and 
appliances that introduce flow into the wastewater system, such as 
washing machines, dishwashers, and showerheads): 
Strongly support: 2; 
Support: 5; 
Neither support nor oppose: 8; 
Oppose: 0; 
Strongly oppose: 3; 
Don't know/no opinion: 2; 
Included multiple responses: 0; 
Total responses: 20; 
No response: 2. 

Additional tax on corporate income (tax on the incomes of corporations 
in addition to any existing corporate income tax): 
Strongly support: 4; 
Support: 1; 
Neither support nor oppose: 7; 
Oppose: 3; 
Strongly oppose: 3; 
Don't know/no opinion: 1; 
Included multiple responses: 0; 
Total responses: 19; 
No response: 3. 

Water use tax (water consumption by local utility users): 
Strongly support: 3; 
Support: 2; 
Neither support nor oppose: 3; 
Oppose: 4; 
Strongly oppose: 7; 
Don't know/no opinion: 1; 
Included multiple responses: 1; 
Total responses: 21; 
No response: 1. 

Industrial discharge tax (tax on industrial pollutants released into 
water and/or fee on permits allowing these releases): 
Strongly support: 4; 
Support: 3; 
Neither support nor oppose: 7; 
Oppose: 1; 
Strongly oppose: 2; 
Don't know/no opinion: 1; 
Included multiple responses: 1; 
Total responses: 19; 
No response: 3. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

Table 13: Stakeholder Views on Funding Options: 

In considering funding options for a clean water trust fund, to what 
extent is there a connection between wastewater infrastructure use and 
the following products or activities? 

Beverages (beverages manufactured for consumption including soft 
drinks, bottled water, ice, beer, wine, and liquor but excluding fruit 
and vegetable juices and concentrates): 
Little or no extent: 3; 
Moderate extent: 4; 
Great extent: 3; 
Very great extent: 5; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18; 
No response: 4. 

Fertilizers and pesticides: 
Little or no extent: 1; 
Moderate extent: 2; 
Great extent: 5; 
Very great extent: 7; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18; 
No response: 4. 

Flushable products (including products introduced directly into 
wastewater, such as soaps, detergents, toilet paper, and cooking oils): 
Little or no extent: 0; 
Moderate extent: 3; 
Great extent: 4; 
Very great extent: 8; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18; 
No response: 4. 

Pharmaceuticals: 
Little or no extent: 2; 
Moderate extent: 7; 
Great extent: 2; 
Very great extent: 4; 
Don't know/no opinion: 3; 
Included multiple responses: 0; 
Total responses: 18; 
No response: 4. 

Water appliances and fixtures (including fixtures and appliances that 
introduce flow into the wastewater system, such as washing machines, 
dishwashers, and showerheads): 
Little or no extent: 3; 
Moderate extent: 7; 
Great extent: 3; 
Very great extent: 2; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 18; 
No response: 4. 

Additional tax on corporate income (tax on the incomes of corporations 
in addition to any existing corporate income tax): 
Little or no extent: 11; 
Moderate extent: 0; 
Great extent: 2; 
Very great extent: 2; 
Don't know/no opinion: 3; 
Included multiple responses: 0; 
Total responses: 18; 
No response: 4. 

Water use tax (water consumption by local utility users): 
Little or no extent: 1; 
Moderate extent: 6; 
Great extent: 1; 
Very great extent: 4; 
Don't know/no opinion: 2; 
Included multiple responses: 1; 
Total responses: 15; 
No response: 7. 

Industrial discharge tax (tax on industrial pollutants released into 
water and/or fee on permits allowing these releases): 
Little or no extent: 3; 
Moderate extent: 2; 
Great extent: 6; 
Very great extent: 5; 
Don't know/no opinion: 2; 
Included multiple responses: 0; 
Total responses: 18; 
No response: 4. 

Source: GAO analysis of stakeholder responses. 

[End of table] 

[End of section] 

Appendix III: Stakeholders Responding to Questionnaire on a National 
Clean Water Trust Fund: 

The following stakeholders responded to our questionnaire regarding the 
issues that need to be addressed in designing and establishing a 
national clean water trust fund as well as potential funding options 
that could be used for this fund. 

American Council of Engineering Companies American Public Works 
Association: 

American Rivers: 

American Society of Civil Engineers: 

American Water Works Association: 

Associated General Contractors of America: 

Association of Metropolitan Water Agencies: 

Clean Water Action: 

Clean Water Construction Coalition: 

Council of Infrastructure Financing Authorities: 

Environmental Financial Advisory Board: 

Food & Water Watch: 

National Association of Clean Water Agencies: 

National Association of Counties: 

National Association of Water Companies: 

National Governors Association: 

National League of Cities: 

Natural Resources Defense Council: 

National Rural Water Association: 

National Utility Contractors Association: 

Water and Wastewater Equipment Manufacturers Association: 

Water Environment Federation: 

[End of section] 

Appendix IV: Estimated Tax Bases for Excise Tax Funding Options: 

To estimate the tax base for products that may contribute to the 
wastewater stream, we added the value of products manufactured 
domestically and the value of products imported and subtracted the 
value of products exported. This appendix provides information on (1) 
the specific industrial classification codes we used to define product 
groups, (2) the value of products manufactured from the U.S. Census 
Bureau's (Census) 2006 Annual Survey of Manufactures, and (3) the value 
of imports and exports from Census' Foreign Trade Division that we used 
to develop the tax bases for the five product groups discussed in this 
report. 

Table 14: Estimated Tax Bases for Excise Tax Funding Options: 

Industry code: Beverages: 312111--Soft Drink Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing soft drinks and artificially carbonated waters; 
Value of products manufactured[A] ($1,000): $33,390,638; 
Value of products imported ($1,000): $1,444,530; 
Value of products exported ($1,000): $330,652; 
Estimated: tax base: ($1,000): $34,504,516. 

Industry code: Beverages: 312112--Bottled Water Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
purifying and bottling water (including naturally carbonated); 
Value of products manufactured[A] ($1,000): $5,726,380; 
Value of products imported ($1,000): $276,634; 
Value of products exported ($1,000): $58,418; 
Estimated: tax base: ($1,000): $5,944,596. 

Industry code: Beverages: 312113 -Ice Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing ice; 
Value of products manufactured[A] ($1,000): $541,298; 
Value of products imported ($1,000): $21,631; 
Value of products exported ($1,000): $43,303; 
Estimated: tax base: ($1,000): $519,626. 

Industry code: Beverages: 312120--Breweries; 
Description of U.S. industry: Establishments primarily engaged in 
brewing beer, ale, malt liquors, and nonalcoholic beer; 
Value of products manufactured[A] ($1,000): $21,490,482; 
Value of products imported ($1,000): $3,595,158; 
Value of products exported ($1,000): $382,596; 
Estimated: tax base: ($1,000): $24,703,044. 

Industry code: Beverages: 312130--Wineries; 
Description of U.S. industry: Establishments primarily engaged in one 
or more of the following: (1) growing grapes and manufacturing wine and 
brandies; (2) manufacturing wine and brandies from grapes and other 
fruits grown elsewhere; and (3) blending wines and brandies; 
Value of products manufactured[A] ($1,000): $11,258,241; 
Value of products imported ($1,000): $4,870,764; 
Value of products exported ($1,000): $899,739; 
Estimated: tax base: ($1,000): $15,229,266. 

Industry code: Beverages: 312140--Distilleries; 
Description of U.S. industry: Establishments primarily engaged in one 
or more of the following: (1) distilling potable liquors (except 
brandies); (2) distilling and blending liquors; and (3) blending and 
mixing liquors and other ingredients; 
Value of products manufactured[A] ($1,000): $5,647,946; 
Value of products imported ($1,000): $3,826,417; 
Value of products exported ($1,000): $941,313; 
Estimated: tax base: ($1,000): $8,533,050. 

Industry code: Beverages: Total in 2006 dollars; 
Value of products manufactured[A] ($1,000): $78,054,985; 
Value of products imported ($1,000): $14,035,134; 
Value of products exported ($1,000): $2,656,021; 
Estimated: tax base: ($1,000): $89,434,098. 

Industry code: Beverages: Total in 2009 dollars; 
Estimated: tax base: ($1,000): $95,551,292. 

Industry code: Fertilizers and Pesticides: 325311--Nitrogenous 
Fertilizer Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in one 
or more of the following: (1) manufacturing nitrogenous fertilizer 
materials and mixing ingredients into fertilizers; (2) manufacturing 
fertilizers from sewage or animal waste; and (3) manufacturing 
nitrogenous materials and mixing them into fertilizers; 
Value of products manufactured[A] ($1,000): $4,623,263; 
Value of products imported ($1,000): $4,090,027; 
Value of products exported ($1,000): $3,202,041; 
Estimated: tax base: ($1,000): $5,511,249. 

Industry code: Fertilizers and Pesticides: 325312--Phosphatic 
Fertilizer Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in one 
of the following: (1) manufacturing phosphatic fertilizer materials or 
(2) manufacturing phosphatic materials and mixing them into 
fertilizers; 
Value of products manufactured[A] ($1,000): $4,923,271; 
Value of products imported ($1,000): $1,581,435; 
Value of products exported ($1,000): $100,860; 
Estimated: tax base: ($1,000): $6,403,846. 

Industry code: Fertilizers and Pesticides: 325320--Pesticide and Other 
Agricultural Chemical Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in the 
formulation and preparation of agricultural and household pest control 
chemicals (except fertilizers); 
Value of products manufactured[A] ($1,000): $13,977,846; 
Value of products imported ($1,000): $632,346; 
Value of products exported ($1,000): $2,107,493; 
Estimated: tax base: ($1,000): $12,502,699. 

Industry code: Fertilizers and Pesticides: Total in 2006 dollars; 
Value of products manufactured[A] ($1,000): $23,524,380; 
Value of products imported ($1,000): $6,303,808; 
Value of products exported ($1,000): $5,410,394; 
Estimated: tax base: ($1,000): $24,417,794. 

Industry code: Fertilizers and Pesticides: Total in 2009 dollars; 
Estimated: tax base: ($1,000): $26,087,944. 

Industry code: Flushable products: 325611--Soap and Other Detergent 
Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing and packaging soaps and other detergents, such as laundry 
detergents, dishwashing detergents, toothpaste gels and tooth powders, 
and natural glycerin; 
Value of products manufactured[A] ($1,000): $19,329,678; 
Value of products imported ($1,000): $1,240,295; 
Value of products exported ($1,000): $2,116,075; 
Estimated: tax base: ($1,000): $18,453,898. 

Industry code: Flushable products: 325620--Toilet Preparation 
Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
preparing, blending, compounding, and packaging toilet preparations, 
such as perfumes, shaving preparations, hair preparations, face creams, 
lotions (including sunscreens), and other cosmetic preparations; 
Value of products manufactured[A] ($1,000): $32,212,490; 
Value of products imported ($1,000): $4,273,115; 
Value of products exported ($1,000): $5,146,411; 
Estimated: tax base: ($1,000): $31,339,194. 

Industry code: Flushable products: 311225--Fats and Oils Refining and 
Blending; 
Description of U.S. industry: Establishments primarily engaged in one 
or more of the following: (1) manufacturing shortening and margarine 
from purchased fats and oils; (2) refining and/or blending vegetable, 
oilseed, and tree nut oils from purchased oils; and (3) blending 
purchased animal fats with purchased vegetable fats; 
Value of products manufactured[A] ($1,000): $9,622,999; 
Value of products imported ($1,000): $145,283; 
Value of products exported ($1,000): $369,123; 
Estimated: tax base: ($1,000): $9,399,159. 

Industry code: Flushable products: Total in 2006 dollars; 
Value of products manufactured[A] ($1,000): $61,165,167; 
Value of products imported ($1,000): $5,658,693; 
Value of products exported ($1,000): $7,631,610; 
Estimated: tax base: ($1,000): $59,192,251. 

Industry code: Flushable products: Total in 2009 dollars; 
Estimated: tax base: ($1,000): $63,240,936. 

Industry code: Pharmaceuticals: 325412--Pharmaceutical Preparation 
Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing in-vivo diagnostic substances and pharmaceutical 
preparations (except biological) intended for internal and external 
consumption in dose forms, such as ampoules, tablets, capsules, vials, 
ointments, powders, solutions, and suspensions; 
Value of products manufactured[A] ($1,000): $128,015,626; 
Value of products imported ($1,000): $38,054,220; 
Value of products exported ($1,000): $19,992,646; 
Estimated: tax base: ($1,000): $146,077,200. 

Industry code: Pharmaceuticals: Total in 2006 dollars; 
Value of products manufactured[A] ($1,000): $128,015,626; 
Value of products imported ($1,000): $38,054,220; 
Value of products exported ($1,000): $19,992,646; 
Estimated: tax base: ($1,000): $146,077,200. 

Industry code: Pharmaceuticals: Total in 2009 dollars; 
Estimated: tax base: ($1,000): $156,068,719. 

Industry code: Water Appliances and Plumbing Fixtures: 333312--
Commercial Laundry, Drycleaning, and Pressing Machine Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing commercial and industrial laundry and drycleaning 
equipment and pressing machines; 
Value of products manufactured[A] ($1,000): $621,459; 
Value of products imported ($1,000): [B]; 
Value of products exported ($1,000): [B]; 
Estimated: tax base: ($1,000): $621,459. 

Industry code: Water Appliances and Plumbing Fixtures: 335224 --
Household Laundry Equipment Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing household-type laundry equipment; 
Value of products manufactured[A] ($1,000): $5,087,524; 
Value of products imported ($1,000): $1,708,490; 
Value of products exported ($1,000): $964,516; 
Estimated: tax base: ($1,000): $5,831,498. 

Industry code: Water Appliances and Plumbing Fixtures: 335228--Other 
Major Household Appliance Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing electric and nonelectric major household-type appliances 
(except cooking equipment, refrigerators, upright and chest freezers, 
and household-type laundry equipment). Illustrative examples of these 
appliances include dishwashers, garbage disposals, and hot water 
heaters; 
Value of products manufactured[A] ($1,000): $3,944,090; 
Value of products imported ($1,000): $1,379,618; 
Value of products exported ($1,000): $746,113; 
Estimated: tax base: ($1,000): $4,577,595. 

Industry code: Water Appliances and Plumbing Fixtures: 327111 --
Vitreous China Plumbing Fixture and China and Earthenware Bathroom 
Accessories Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing vitreous china plumbing fixtures and china and 
earthenware bathroom accessories, such as faucet handles, towel bars, 
and soap dishes; 
Value of products manufactured[A] ($1,000): $728,507; 
Value of products imported ($1,000): $855,586; 
Value of products exported ($1,000): $125,778; 
Estimated: tax base: ($1,000): $1,458,315. 

Industry code: Water Appliances and Plumbing Fixtures: 332998 --
Enameled Iron and Metal Sanitary Ware Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing enameled iron and metal sanitary ware; 
Value of products manufactured[A] ($1,000): $1,438,325; 
Value of products imported ($1,000): $488,088; 
Value of products exported ($1,000): $91,995; 
Estimated: tax base: ($1,000): $1,834,418. 

Industry code: Water Appliances and Plumbing Fixtures: 326191 --
Plastics Plumbing Fixture Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing plastics or fiberglass plumbing fixtures, such as plastic 
or fiberglass bathtubs, hot tubs, portable toilets, and shower stalls; 
Value of products manufactured[A] ($1,000): $4,527,048; 
Value of products imported ($1,000): $158,960; 
Value of products exported ($1,000): $68,068; 
Estimated: tax base: ($1,000): $4,617,940. 

Industry code: Water Appliances and Plumbing Fixtures: 332913 --
Plumbing Fixture Fitting and Trim Manufacturing; 
Description of U.S. industry: Establishments primarily engaged in 
manufacturing metal and plastics plumbing fixture fittings and trim, 
such as faucets, flush valves, and shower heads; 
Value of products manufactured[A] ($1,000): $3,821,468; 
Value of products imported ($1,000): $1,341,991; 
Value of products exported ($1,000): $221,516; 
Estimated: tax base: ($1,000): $4,941,943. 

Industry code: Water Appliances and Plumbing Fixtures: Total in 2006 
dollars; 
Value of products manufactured[A] ($1,000): $20,168,421; 
Value of products exported ($1,000): $5,932,733; 
Value of products exported ($1,000): $2,217,986; 
Estimated: tax base: ($1,000): $23,883,168. 

Industry code: Water Appliances and Plumbing Fixtures: Total in 2009 
dollars; 
Estimated: tax base: ($1,000): $25,516,750. 

Source: GAO analysis of Census data from the 2006 Annual Survey of 
Manufactures and Foreign Trade Division. 

[A] This column represents the "Value of Product Shipments," which 
Census defines as the value of products produced domestically. 

[B] Import and export data for NAICS code 333312 are reflected in NAICS 
code 335224. 

[End of table] 

[End of section] 

Appendix V: GAO Contact and Staff Acknowledgments: 

GAO Contact: 

Anu K. Mittal, (202) 512-3841, or mittala@gao.gov: 

Staff Acknowledgments: 

In addition to the individual named above, Sherry L. McDonald, 
Assistant Director; Janice Ceperich; Nancy Crothers; Cindy Gilbert; and 
Scott Heacock made significant contributions to this report. Also 
contributing to this report were George Bogart, Richard Eiserman, Carol 
Henn, Sarah Reyneveld, Anne Stevens, Jack Warner, and James Wozny. 

[End of section] 

Footnotes: 

[1] EPA, The Clean Water and Drinking Water Infrastructure Gap Analysis 
(Washington, D.C., September 2002). In the report, EPA noted that this 
gap is not inevitable and could be addressed in part if wastewater 
utilities raised the rates they charge consumers. EPA estimates a 
potential gap for drinking water infrastructure as well. 

[2] The Federal Water Pollution Control Act Amendments of 1972, Pub. L. 
No. 92-500, § 2, 86 Stat. 816 (commonly referred to as the Clean Water 
Act). 

[3] Pub. L. 111-5, Div. A, Tit. VII, 123 Stat. 115, 169. 

[4] An excise tax is a tax levied on the manufacture, sale, or 
consumption of various commodities. 

[5] Wastewater treatment generally involves two steps, called primary 
and secondary treatment. During primary treatment, solid materials such 
as sand and grit are removed from wastewater. Secondary treatment 
usually involves using bacteria to remove organic material from 
wastewater. Under the Clean Water Act, municipal wastewater treatment 
plants are required to provide secondary treatment for wastewater. In 
addition, over 30 percent of wastewater treatment plants also provide 
advanced treatment for wastewater, which can purify wastewater to even 
greater levels. 

[6] Fiscal year 2006 includes data for each individual government's 
fiscal year that ended between July 1, 2005, and June 30, 2006. 

[7] American Society of Civil Engineers, 2009 Report Card for America's 
Infrastructure (Reston, Va., Mar. 25, 2009). 

[8] EPA, The Clean Water and Drinking Water Infrastructure Gap Analysis 
(Washington, D.C., September 2002). 

[9] CBO, Future Investment in Drinking Water and Wastewater 
Infrastructure (Washington, D.C., November 2002). 

[10] Many of these options were discussed by stakeholders at an EPA 
forum. See EPA, Closing the Gap: Innovative Solutions for America's 
Water Infrastructure Forum (Washington, D.C., Jan. 31, 2003). 

[11] Our past work has found that many utilities were not routinely 
charging the full cost for the wastewater services they provided. See 
GAO, Water Infrastructure: Information on Financing, Capital Planning, 
and Privatization, [hyperlink, http://www.gao.gov/products/GAO-02-764] 
(Washington, D.C.: Aug. 16, 2002). In addition, we have found that the 
practice of systematically identifying and planning for wastewater 
infrastructure improvements, known as asset management, could help 
these wastewater utilities better address their infrastructure needs. 
See GAO, Water Infrastructure: Comprehensive Asset Management Has 
Potential to Help Utilities Better Identify Needs and Plan Future 
Investments, [hyperlink, http://www.gao.gov/products/GAO-04-461] 
(Washington, D.C.: Mar. 19, 2004). 

[12] Environmental Financial Advisory Board, Relative Benefits of 
Direct and Leveraged Loans in State Revolving Loan Fund (SRF) Programs 
(Aug. 28, 2008). 

[13] In the 110th Congress, three bills were introduced to create such 
a bank or entity: National Infrastructure Bank Act of 2007 (S. 1926 and 
H.R. 3401); the National Infrastructure Development Act of 2007 (H.R. 
3896); and the Build America Bonds Act of 2007 (S. 2021). 

[14] Our previous work has found that public-private partnerships can 
entail potential costs and tradeoffs and should be reviewed to 
determine whether they are appropriate in specific circumstances and, 
if so, how best to implement them. See GAO, Highway Public-Private 
Partnerships: More Rigorous Up-front Analysis Could Better Secure 
Potential Benefits and Protect the Public Interest, [hyperlink, 
http://www.gao.gov/products/GAO-08-44] (Washington, D.C.: Feb. 8, 
2008). 

[15] H.R. 6194, which was introduced in the 110th Congress, The 
Sustainable Water Infrastructure Development Act of 2008, proposed 
lifting the caps on private activity bonds for water and wastewater 
projects. 

[16] In addition, some stakeholders we interviewed raised the issue of 
how a clean water trust fund would be funded. We discuss potential 
revenue sources for a clean water trust fund in the next section of 
this report. 

[17] Twenty-two stakeholders responded to our questionnaire; however, 
because not all stakeholders responded to each question, the total 
number of responses can vary for each question. 

[18] See GAO, Clean Water: How States Allocate Revolving Loan Funds and 
Measure Their Benefits, [hyperlink, 
http://www.gao.gov/products/GAO-06-579] (Washington, D.C.: June 5, 
2006). 

[19] [hyperlink, http://www.gao.gov/products/GAO-02-764] and 
[hyperlink, http://www.gao.gov/products/GAO-04-461]. 

[20] A 1996 study by EPA provided information on using some of these 
products to provide funding for wastewater infrastructure. It noted 
that "Currently, little empirical data exist by which to document the 
volume and toxicity of most potential fee targets. This limitation, 
which research might address over time, results in a significant 
selection bias when products are selected for their link to water 
pollution." EPA, Alternative Funding Study: Water Quality Fees and Debt 
Financing Issues (June 1996). 

[21] If any of the products in these product groups were excluded or 
exempted from an excise tax, the tax base would decline and higher tax 
rates would be needed to raise similar amounts of money. For example, 
if the excise tax on beverages did not include alcoholic beverages, the 
tax base for this product group would decline by over 50 percent to 
about $44 billion, and the tax rate required to raise $10 billion would 
increase to about 25 percent. 

[22] Container Recycling Institute, Wasting and Recycling Trends: 
Conclusions from CRI's 2008 Beverage Market Data Analysis (Glastonbury, 
Conn., December 2008). 

[23] The Superfund program, which Congress established in 1980 to 
address the threats that hazardous waste sites pose to human health and 
the environment, was funded partly by an environmental tax on 
corporations that was imposed in 1986 and expired in 1995. The proceeds 
of this tax went to the Hazardous Substance Superfund Trust Fund and it 
was the fund's largest single source of revenue. The tax raised $612 
million in fiscal year 1995. 

[24] USGS Circular 1268, Estimated Use of Water in the United States in 
2000 (Reston, Va., 2004) and USGS Circular 1200, Estimated Use of Water 
in the United States in 1995 (Denver, Colo., 1998). 

[25] This $30 charge, known as the Bay Restoration fee, helps to 
provide funding to upgrade wastewater treatment plants and septic 
systems in Maryland. In addition to households, commercial and 
industrial customers also are charged this fee. 

[26] A flat charge also could be applied to industrial and commercial 
users, but data are not available on the number of these system users. 

[27] Under the Emergency Planning and Community Right to Know Act 
(EPCRA) of 1986, certain facilities must submit an annual report to EPA 
for each TRI chemical that they manufacture, process, or otherwise use 
in excess of certain thresholds. Pub. L. No. 99-499, § 313, 100 Stat. 
1728, 1741. 

[28] In order to provide the information EPCRA requires, the owner or 
operator of a facility may use readily available data (including 
monitoring data) collected pursuant to other provisions of law, or, 
where such data are not readily available, reasonable estimates of the 
amounts involved. 

[29] In particular, the CEIT was levied on corporations' modified 
alternative minimum taxable income over $2 million. 

[30] Also, to the extent that collection of such a tax on behalf of the 
federal government constitutes local government administration of a 
federal regulatory program, there may be constitutional issues 
associated with this option. We express no view as to how these issues 
may best be avoided. 

[31] NPDES permits generally allow a point source to discharge 
specified pollutants into federal regulated water under specific limits 
and conditions. These permits are issued by EPA or a state agency 
authorized to implement the NPDES program. Currently, 46 states are 
authorized to administer the NPDES program. 

[32] The five conventional pollutants are biological oxygen demand, pH, 
oils and greases, total suspended solids, and fecal coliform bacteria. 

[33] We sent out questionnaires to 28 stakeholders and received 22 
responses. However, not all stakeholders responded to each question, so 
the total number of responses can vary for each question. 

[34] Under the Highway Trust Fund, the users of highways from some 
states contribute more to the fund than they receive in return, also 
known as "donor states." Meanwhile, "donee states" are those that 
receive more from the trust fund than they contribute. See 
Congressional Research Service, Federal-Aid Highway Program: "Donor- 
Donee" State Issues (Washington, D.C., June 10, 2005). 

[35] NAICS was developed as the standard for use by federal statistical 
agencies in classifying business establishments for the collection, 
analysis, and publication of statistical data related to the business 
economy of the United States. NAICS was developed under the auspices of 
the Office of Management and Budget and adopted in 1997 to replace the 
Standard Industrial Classification system. 

[36] The value of products that were imported or exported came from the 
Foreign Trade Division of Census. 

[37] Container Recycling Institute, Wasting and Recycling Trends: 
Conclusions from CRI's 2008 Beverage Market Data Analysis (Glastonbury, 
Conn., 2008). 

[38] These data are available in USGS Circular 1268, Estimated Use of 
Water in the United States in 2000 (Reston, Va., 2004) and USGS 
Circular 1200, Estimated Use of Water in the United States in 1995 
(Denver, Colo., 1998). 

[39] We excluded estimates for water delivered for thermoelectric power 
and public uses or losses because these uses typically do not impact 
the wastewater stream and generally public use water is not billed by 
the public supplier. 

[40] These data are available in EPA's Clean Watersheds Needs Survey 
2004 (January 2008). 

[End of section] 

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