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United States General Accounting Office: 
GAO: 

Testimony: 

Before the Subcommittee on Environment and Hazardous Materials, 
Committee on Energy and Commerce, House of Representatives. 

For Release on Delivery: 
Expected on Thursday: 
April 11, 2002, at 9:30 a.m. 

Drinking Water Infrastructure: 

Information on Estimated Needs and Financial Assistance: 

Statement of David G. Wood: 
Director, Natural Resources and Environment: 

GAO-02-592T: 

Mr. Chairman and Members of the Subcommittee: 

I am pleased to be testifying before you today as you consider the 
infrastructure needs facing the nation’s drinking water systems. As you 
know, the U.S. Environmental Protection Agency (EPA) is required to 
conduct an infrastructure needs assessment every 4 years to estimate 
the future capital investment needs of local drinking water systems. In 
its most recent national survey, EPA estimated that nearly $151 billion 
will be needed over the next 20 years to repair, replace, and upgrade 
the nation’s 55,000 community water systems. The needs assessment 
survey, which EPA uses to estimate infrastructure needs for each state, 
serves as the basis for EPA’s grants to the states under the Drinking 
Water State Revolving Fund (DWSRF) program. This program helps 
communities finance the infrastructure projects needed to comply with 
federal drinking water regulations and protect public health. EPA 
requests annual appropriations to capitalize the states’ revolving loan 
funds and then makes specific allotments to each state. The states, 
which are required to match a portion of the grants, use the funds to 
make low-interest loans to their local water systems; as the loans are 
repaid, the states’ funds are replenished, enabling them to make loans 
to other eligible drinking water projects. For projects located in 
communities that qualify as “disadvantaged,” the states may extend loan 
repayment periods or use a portion of their grants to provide additional
subsidies. 

In addition to EPA, a number of federal agencies provide financial 
assistance for drinking water facilities through a variety of grant and 
loan programs, some of which also may be used for wastewater 
facilities. Further, some states sponsor their own financial assistance 
programs for local drinking water and wastewater facilities. 

My testimony today discusses several issues critical to assessing the 
nation’s drinking water infrastructure needs: (1) the precision of 
EPA’s most recent estimate of drinking water infrastructure needs, (2) 
states’ use of EPA’s drinking water state revolving funds to aid 
disadvantaged communities, and (3) the amounts and types of drinking 
water infrastructure funding EPA, other federal agencies, and the 
states have made available. 

The information provided in this testimony is based on two recently-
issued reports: our January report for this subcommittee and committee 
[Footnote 1] and our November 2001 report on federal and state 
financial assistance for water infrastructure.[Footnote 2] We focused 
on certain aspects of EPA’s methodology in reviewing the agency’s needs 
assessment, specifically the impact of sampling on the estimate’s 
precision. In addition, we surveyed all 50 states to determine how they 
use their drinking water state revolving loan funds to assist 
disadvantaged communities. Finally, we obtained information on federal 
and state drinking water and wastewater infrastructure funding over a 
10-year period (fiscal years 1991 through 2000) by collecting data from 
the nine federal agencies responsible for the majority of the federal 
assistance and, using a detailed questionnaire, surveying the states to 
collect information on state-sponsored programs. Forty-six states 
responded to our funding survey. We converted the annual amounts 
reported by the federal agencies and the states to constant year 2000 
dollars. 

In summary, our work has shown the following: 

* EPA took a number of steps to help ensure that it collected valid 
data to estimate drinking water infrastructure needs, such as 
conducting site visits to selected systems and asking states to review 
supporting documentation. However, EPA and other users of the needs 
assessment cannot tell how closely the estimates reflect actual state-
by-state needs because EPA did not calculate the precision of the 
estimates. EPA set a target level of precision—generally, the agency 
wanted to be 95 percent certain that its estimates were within 10 
percent of the “true” needs. We found indications that the level of 
uncertainty was higher than EPA’s target level of precision, possibly 
by a considerable amount, for reasons associated with some of EPA’s 
sampling methods. Because the results of the survey are used to 
estimate both national and state-level needs, they can influence the 
level of congressional appropriations for the drinking water state 
revolving fund program, and they form the basis for EPA’s allotment of 
these funds to the states. Accordingly, we recommended that EPA 
calculate and report the level of precision actually achieved in its 
recent needs assessment, and determine what implications, if any, its 
findings have on the methodology to be used to conduct future needs 
assessment surveys. EPA concurred that such a calculation would confirm 
whether the survey met its precision targets and stated that it would
revisit the issue in the design of the 2003 survey. 

* Thirty-one states have established programs under their revolving 
loan funds to assist disadvantaged communities, according to the 
results of our 50-state survey. Of the states with programs, 21 
provided about $94 million in special subsidies—mainly loan principal 
forgiveness—and 23 offered extended loan terms. While criteria for 
defining disadvantaged communities vary, states typically use some 
measure of household water rates relative to a community’s median 
household income. In addition, states reported that other factors, such 
as concerns about depleting the fund and the availability of assistance 
from other federal and state sources, influenced their decisions to 
offer assistance to disadvantaged communities under the revolving fund 
program. Because providing additional loan subsidies can affect the 
extent to which states’ revolving loan funds are replenished—and 
therefore potentially the extent to which future federal funds will be 
requested—we attempted to estimate of the number of systems potentially
eligible for such assistance. On the basis of limited information 
provided by the states, we estimate that about 28 percent of the 
nation’s smallest water systems could qualify for additional subsidies. 

* In fiscal years 1991 through 2000, nine federal agencies made 
available about $44.0 billion in grants, loans, and loan guarantees for 
drinking water and wastewater capital improvements. Of this amount, EPA 
provided about $3.7 billion in drinking water state revolving loan fund 
grants and about $16.6 billion under a similar program for wastewater 
facilities. EPA’s assistance, combined with that of three other 
agencies—the Departments of Agriculture, Housing and Urban Development, 
and Commerce—accounted for about 98 percent of the total federal 
assistance. About 11 percent of the federal aid was specifically for
drinking water facilities and another 40 percent was for either 
drinking water or wastewater facilities. Also, according to responses 
to our survey, state governments made a total of about $25 billion in 
state funds available for water infrastructure programs over the 10-
year period, including over $10 billion to match EPA’s capitalization 
grants. State-sponsored grant and loan programs accounted for about 
$9.1 billion of the states’ contributions, including $800 million 
specifically designated for drinking water facilities and $6.3 billion 
that could be used for either drinking water or wastewater facilities 
(and in some cases for other types of infrastructure projects). In 
addition, states reported that they made another $4.4 billion available 
for loans by selling general obligation and revenue bonds, and 
contributed about $1.4 billion from other state sources for purposes 
such as matching non-EPA federal funds and financing state-designated 
specific drinking water or wastewater projects. 

Background: 

Under the 1996 amendments to the Safe Drinking Water Act, EPA is 
required to conduct an infrastructure needs assessment every 4 years to 
estimate the future capital investment needs of water systems eligible 
for assistance through the DWSRF program.[Footnote 3] Of the estimated 
$150.9 billion capital investment needed according to EPA’s most recent
survey, 80 percent ($119.7 billion) is linked to projects involving the 
installation, upgrade, and replacement of the basic infrastructure 
needed to deliver safe drinking water to the public. The remainder of 
the estimated needed investment--$31.2 billion, or about 20 
percent—will go to projects directly associated with existing, 
proposed, or recently issued regulations. 

Water systems vary in size, which is often measured by the number of 
customers they serve. In its most recent survey, EPA obtained 
information from 100 percent of the largest 1,111 community water 
systems (those serving more than 40,000 people) and samples of the 
remaining 7,534 medium systems (those serving from 3,301 to 40,000 
people) and 44,373 small systems (those serving 3,300 or fewer people). 
Small water systems represent over 80 percent of all community water 
systems, but they only account for about 22 percent of the estimated 
infrastructure needs. In contrast, the largest water systems represent 
about 2 percent of the community systems and account for nearly 44 
percent of the needs.[Footnote 4] 

Subsidized loan assistance is an integral part of the DWSRF program in 
that the interest rates that states offer to local water systems must 
be at or below the current market rate.[Footnote 5] In addition, the 
Congress has authorized states to use an amount equal to up to 30 
percent of their DWSRF capitalization grants to provide additional 
subsidies to communities that qualify as “disadvantaged” under state-
defined affordability criteria. States with disadvantaged community 
programs may opt to forgive a portion of the loan principal or issue a 
loan at a negative interest rate. States also have the option of 
extending the loan repayment period from the standard 20 years to up to 
30 years, provided that the repayment period does not exceed the 
expected design life of the project. 

U.S. drinking water and wastewater systems encompass thousands of 
treatment facilities, collection facilities, and related works and well 
over a million miles of pipes and conduits. While the investment, made 
over decades, in these facilities is enormous, even more funds will be 
needed in the future to support efforts to maintain clean and safe 
water. The Water Infrastructure Network—a consortium of industry, 
municipal, and nonprofit associations—recently estimated needs of up to 
$1 trillion over the next 20 years for drinking water and wastewater 
systems combined, when both the capital investment needs and the cost 
of financing are considered. User rates serve as the major source of 
facilities’ financing, but both federal and state government agencies 
offer financial support as well. In the 107th Congress, legislation has 
been introduced in both the House and the Senate that would increase 
the amount of federal assistance available through EPA’s revolving loan 
fund programs. 

EPA Took Steps to Validate Needs Data, But Did Not Calculate the 
Precision of Its Estimates: 

The 1996 amendments to the Safe Drinking Water Act require EPA to use 
the results of its most recent needs assessment survey to allocate the 
amount of each state’s annual DWSRF allotment. EPA allocates the DWSRF 
funds on the basis of each state’s share of the total estimated 
national need, except that each state receives a minimum share of 1 
percent. According to EPA, its periodic surveys are therefore intended 
to provide “statistically precise” estimates of the needed capital 
investments, not just in total for the nation, but within each state. 

EPA took a number of steps to ensure that it collected valid 
information about infrastructure needs at local water systems, and the 
cost of addressing those needs. For example, EPA took the following 
measures: 

* For large and medium-sized systems, EPA used a questionnaire to 
collect information on capital projects needed to protect the public 
health. According to EPA’s report to the Congress,[Footnote 6] the 
agency asked the surveyed water systems to provide detailed information 
on each project including documentation explaining (1) why it is 
needed, (2) the basis for the project (e.g., whether it addressed a 
current or future need), and (3) the project’s estimated cost (or 
enough information on the design capacities so that EPA could use a 
model to estimate the cost.) 

* For the smallest water systems, EPA sent trained water system 
specialists on site visits to collect data after deciding that 
specialists would provide better information than a questionnaire 
because small systems generally have neither the data nor personnel to 
complete a questionnaire of this type. 

In the case of the large and medium-sized systems, EPA obtained 
information from a sufficient number of systems to estimate 
infrastructure needs on a state-by-state basis. (EPA surveyed 100 
percent of the largest water systems—those serving populations of
more than 40,000—and a statistical sample of medium-sized systems, 
which amounted to about one-third of the systems serving populations 
from 3,301 to 40,000.) For these systems, which typically comprise the 
majority of a state’s needs, EPA set a precision target of plus or 
minus 10 percent, at the 95 percent confidence level. This means that
EPA wanted a 95 percent likelihood that its estimate of the needed 
capital investment in a particular state would fall within 10 percent 
of the actual or “true” need for that state. 

For the small systems, the agency’s precision target for the national-
level estimate was similarly set at plus or minus 10 percent at the 95 
percent confidence level. EPA officials explained that the agency did 
not have the resources to send specialists to enough small systems to 
get an accurate picture of small-system needs on a state-level basis.
(Specifically, EPA estimated that it would have to conduct site visits 
at approximately 22,000 small water systems to collect enough data to 
estimate needs on a state-by-state basis.) Instead, EPA selected a 
sample of about 600 small water systems for these site visits. EPA used 
the results of these visits to calculate a national-level estimate of 
small system infrastructure investment needs. EPA then apportioned this 
estimated total among the states on the basis of the number of each 
state’s small systems, categorized by population served and type of 
water source. 

In an effort to assess the precision of EPA’s needs estimates, we 
performed a limited review of EPA’s methodology, focusing on the impact 
of sampling on the estimate’s precision. We concluded that EPA probably 
did not achieve its intended level of precision. More specifically, we 
found indications that the level of uncertainty, or sampling error, 
[Footnote 7] was higher than EPA’s target level of precision, possibly 
by a considerable amount. For example, we found that: 

* The agency’s approach did not account for the fact that it 
extensively used average costs estimated from models when calculating 
its sample size.[Footnote 8] Thus, EPA’s sample sizes were probably too 
small, and it is likely that EPA did not collect data from enough 
systems to achieve its precision target. 

* Even though EPA’s technical experts believed that a simple random 
sample[Footnote 9] would be required to achieve the target level of 
precision for small-system needs, EPA deviated from this sampling 
methodology in two important ways. First, to avoid the travel costs 
associated with visiting about 600 randomly selected systems located 
throughout the country, EPA used statistical sampling to select 100 
geographical areas and then chose six systems within each area. 
Although an acceptable approach, such a statistical sampling technique 
can require a considerably larger sample size than when simple random 
sampling is used to achieve the desired level of precision. EPA did not 
increase its sample size to account for the change in technique. 
Second, based on recommendations from an advisory workgroup,[Footnote 
10] EPA intentionally selected at least one area in each of the 50 
states, Puerto Rico, and the U.S. Virgin Islands. Such geographical 
constraints had the potential of increasing the sampling error, thereby 
reducing the level of precision of EPA’s estimate. 

Although EPA has calculated and reported the actual precision levels 
for other surveys, EPA officials told us that doing so for the most 
recent drinking water needs assessment would not be worthwhile, because 
it would not affect the allocation of DWSRF funds to the states. In 
addition, according to an EPA official responsible for managing the 
periodic needs surveys, EPA has already invested approximately 4 years 
and $3.6 million to implement its most recent assessment and summarize 
the results. The official said that calculating the actual precision of 
the cost estimates would cost at least an additional $30,000 to 
$40,000. Moreover, actually achieving the precision target could cause 
the agency to incur further costs, depending on how many additional 
site visits were needed. 

On the other hand, there are arguments in favor of calculating the 
precision of EPA’s estimates. A number of leading survey research 
associations advocate for the calculation and reporting of the 
precision level to fully inform users of a sample’s limitations. 
[Footnote 11] More importantly, determining the precision level of its 
estimates could help EPA identify any needed changes in its survey 
methodology—for example, larger or differently selected samples 
designed to minimize sampling error—to improve the future surveys 
required by the Safe Drinking Water Act. In commenting on a draft of our
January report, EPA agreed that the calculation of confidence limits 
would confirm whether the survey met its precision targets. EPA also 
stated that it would fully consider our recommendation and that it 
would revisit the issue in the design of the 2003 survey. 

States Have Made Limited Use of the Optional DWSRF Provision to Assist
Disadvantaged Communities: 

Under the 1996 amendments to the Safe Drinking Water Act, the Congress 
authorized states to use an amount equal to up to 30 percent of their 
DWSRF capitalization grants to provide additional subsidies to 
communities that qualify as “disadvantaged.” The subsidies may take the 
form of forgiving a portion of the loan principal or issuing a loan at 
a negative interest rate.[Footnote 12] States have the flexibility to 
develop their own criteria to define a disadvantaged community. States 
with disadvantaged community programs typically use some measure of 
household water rates relative to the community’s median household 
income, allowing the states to assess the impact of capital project 
debt on the community’s water rates and measure the project’s 
affordability. 

According to our state survey: 

* Thirty-one states have adopted a disadvantaged community program and 
offer assistance in the form of loan subsidies or extended loan terms. 
Three more states reported plans to offer such assistance as part of 
their DWSRF programs within the next 3 years. As of December 31, 2000, 
25 of the 31 states had provided assistance to qualified communities. 

* Of the 31 states with a disadvantaged community program, 27 have 
adopted criteria that consider local water rates, often in conjunction 
with a community’s median household income. In total, 21 states use 
median household income as a criterion in determining whether 
communities qualify as disadvantaged.[Footnote 13] 

* Most states that have a disadvantaged community program offer 
principal forgiveness or extended loan terms for capital improvement 
projects. States rarely offer negative interest rate loans to 
disadvantaged communities. (According to state DWSRF officials, they 
find this option difficult to explain to local communities and 
difficult to administer.) 

* Of the 14 states that had provided loan subsidies,[Footnote 14] only 
Maine, which had used 23 percent of its grants for assistance to 
disadvantaged communities, came close to reaching the 30 percent cap. 

In our survey, we asked the states that had not adopted a DWSRF program 
for disadvantaged communities to report the reasons why. Of the 19 
states without disadvantaged community programs: 

* 16 states cited concerns about maintaining the body of the fund or 
the long-term viability of the fund as a major (12) or moderate (4) 
reason for not establishing a disadvantaged community program; 

* 14 states cited the fact that their DWSRF program already offers 
loans at below-market interest rates as a major (9 states) or moderate 
(5 states) reason for not offering additional assistance to 
disadvantaged communities; and; 

* 12 states cited the availability of other federal or state programs 
to address the needs of disadvantaged communities as a major (5 states) 
or moderate (9 states) reason for not providing assistance through the 
DWSRF.[Footnote 15] 

Non-DWSRF financing from other federal and state sources is available 
to help disadvantaged communities, and many states coordinate with 
these sources to help disadvantaged communities secure the funding they 
need. According to the state drinking water officials we interviewed, 
disadvantaged communities often receive a combination of DWSRF and non-
DWSRF funding to finance their drinking water projects. A significant 
amount of funding is available for local drinking water projects from 
other federal agencies and through state-sponsored grant and loan 
programs. In our survey on assistance to disadvantaged communities, 
more than half the states indicated that they provided some type of 
financial assistance for drinking water projects. Six of the 19 states 
without DWSRF-related disadvantaged community programs had state grant 
or loan programs intended specifically to help economically distressed 
communities to finance drinking water improvement projects. 

Because providing additional loan subsidies to disadvantaged 
communities can affect the rate at which states’ revolving funds are 
replenished—and therefore potentially the extent to which future 
federal funds will be requested—we attempted to determine the 
proportion of the nation’s community water systems that might qualify as
“disadvantaged” and thus be eligible to receive special assistance. 
According to EPA officials, the vast majority of systems serving 
disadvantaged communities are likely to be small systems.[Footnote 16] 
Therefore, we used the same statistical sample of small water systems 
that EPA had selected for its infrastructure needs assessment. (A 
statistical sample allows generalizing the results to the universe of 
small systems, thereby obtaining a national estimate.) 

We identified the specific systems included in EPA’s sample—from 5 to 
34 systems in each state—and as part of our survey asked the states to 
determine which of those systems they would consider to be 
disadvantaged. We asked states that were able to apply their own 
criteria to determine whether each system initially qualified as 
disadvantaged or qualified as a result of the additional costs needed 
to improve it. Other states were asked to use GAO surrogate criteria 
(i.e., to qualify as “disadvantaged,” a community’s water rates would 
have to exceed 1.4 percent of its median household income). 

Our effort met with limited success for several reasons. The primary 
reasons were that some states did not have the information necessary to 
readily make a determination about a system’s disadvantaged status or 
they lacked the time and resources to collect the information for us. 
[Footnote 17] In total, we obtained information on a portion of EPA’s 
sample representing 24,334 systems, or nearly 55 percent of the 44,373 
small community water systems in the United States. On the basis of 
EPA’s sample and the states’ determinations, we estimated that 6,925 
systems, or about 28 percent of the 24,334 small systems reflected in 
the results of our survey, qualified as “disadvantaged.”[Footnote 18] 
However, the high non-response rate associated with this analysis left 
us without information on the systems representing the remaining 45 
percent of the universe. As a result, we could not determine whether 
our findings matched the actual percentage of systems that would 
qualify as disadvantaged. Specifically, we had no way of determining 
whether the systems for which we had information were systematically 
different from those systems for which we lacked information in a way 
that would make the estimated percentage of disadvantaged communities 
higher or lower. 

Federal Agencies Made About $44 Billion Available for Drinking Water and
Wastewater Infrastructure, While States Provided About $25 Billion: 

From fiscal years 1991 through 2000, nine federal agencies made about 
$44 billion in financial assistance available for drinking water and 
wastewater infrastructure projects. Of this amount, EPA provided about 
$3.7 billion in drinking water state revolving loan fund grants and 
about $16.6 billion under a similar program for wastewater facilities.
EPA’s assistance, combined with that of three other agencies—the 
Departments of Agriculture, Housing and Urban Development, and 
Commerce—accounted for about 98 percent of the total federal 
assistance. About 11 percent of the federal aid was specifically for 
drinking water facilities and another 40 percent was for either drinking
water or wastewater facilities. Over 82 percent of the total assistance 
was provided in the form of grants; the remainder consisted of loans 
and loan guarantees. Although the programs differed in terms of 
eligibility criteria, allowable uses, and funding priorities, for the 
most part, the financial assistance was available to a broad range of 
entities. We use the term “made available” to encompass several forms 
of federal funding. Because of differences in the programs and in the 
ways that federal agencies account for their financial assistance, the 
information that best reflected the amounts made available for drinking 
water and wastewater facilities came from data on appropriations, 
obligations, or expenditures, depending on the agency and the specific 
program in question. For example, EPA’s data include appropriated 
amounts for the revolving loan fund capitalization grants to the states 
for each year; the states may not have loaned the funds (i.e., actually 
made them available) to local water systems until after the end of the
fiscal year in which they were appropriated. In contrast, the data for 
HUD and Commerce consist of obligated amounts—that is, the amounts of 
funds allocated by the agencies to drinking water and wastewater 
infrastructure projects during the fiscal year. For the loan programs 
of the Small Business Administration and USDA’s Rural Utilities 
Service, the amounts represent the face value of the loans or loan 
guarantees that were available to be made for the fiscal year; however, 
because most of these loans are repaid, the ultimate cost to the 
federal government is significantly less than the face value. 

More specifically: 

* EPA’s financial assistance came primarily in the form of grants to 
the states to capitalize the Drinking Water and Clean Water State 
Revolving Funds. In addition, EPA provided $4.5 billion in grants for 
drinking water and wastewater projects specifically designated in the 
appropriations process. 

* USDA provided local communities $4.5 billion in grants, $7.1 billion 
in loans, and $550 million in loan guarantees. USDA also provided $376 
million in grants for water and wastewater projects specifically 
designated in the appropriations process. 

* HUD provided $4.4 billion in block grants—some directly to large 
communities and others to states for distribution to smaller 
communities—to be used for water and wastewater projects. HUD provided 
another $39.9 million for specific projects designated in the 
appropriations process. 

* Commerce’s Economic Development Administration provided $1.1 billion 
in grants to local communities for water and wastewater infrastructure. 

The remaining federal assistance, which totaled about $1.1 billion over 
the 10 years, was provided by the Appalachian Regional Commission, the 
Federal Emergency Management Agency, the Department of the Interior’s 
Bureau of Reclamation, the Small Business Administration, and the U.S. 
Army Corps of Engineers. 

In addition to the assistance available to disadvantaged communities 
under EPA’s DWSRF program, other federal programs give priority to 
projects in economically distressed areas. For example, to be eligible 
for USDA assistance, facilities generally must serve rural areas with 
populations of 10,000 or less and must be unable to finance their needs 
from their own resources or obtain credit at reasonable rates and terms.
Proposed projects must be located in economically distressed areas to 
obtain funding under Commerce’s program, and projects in severely 
distressed areas are eligible for higher funding levels. 

According to our state funding survey responses, state governments made 
a total of about $25 billion in state funds available for water 
infrastructure programs from fiscal years 1991 through 2000. 
Specifically, the states reported that they collectively: 

* Contributed about $10.1 billion to match EPA’s capitalization grants 
for the drinking water and wastewater state revolving funds. This 
amount consisted of about $3.3 billion from state appropriations or 
other state sources, and about $6.8 billion that the states 
leveraged—that is, raised through the sale of state-issued bonds backed 
by the funds. 

* Made about $9.1 billion in grants and loan commitments under state-
sponsored programs, including $3.4 billion through a variety of grant 
programs and $5.7 billion in loans.[Footnote 19] The states reported 
having a total of 56 state-sponsored grant programs, 29 state-sponsored 
loan programs, and 35 state-sponsored programs that include grants 
and/or loans. Of this funding, $800 million was specifically designated 
for drinking water facilities while $6.3 billion could be used for 
either drinking water or wastewater facilities or for other types of
infrastructure projects. 

* Made another $4.4 billion available for loans by selling general 
obligation and revenue bonds (15 states). 

In addition, the states reported that they contributed about $1.4 
billion from state appropriations, interest earnings, and other state 
sources for purposes, such as matching non-EPA federal funds and 
financing state-designated specific drinking water or wastewater 
projects. 

Mr. Chairman, this concludes my prepared statement. I would be happy to 
respond to any questions that you or other Members of the Subcommittee 
may have at this time. 

Contact and Acknowledgments: 

For further information, please contact David G. Wood at (202) 512-
3841. Individuals making key contributions to this testimony included 
Ellen Crocker, Karen Bracey, Les Mahagan, and Jonathan McMurray. 

[End of section] 

Footnotes: 

[1] U.S. General Accounting Office, Drinking Water: Key Aspects of 
EPA’s Revolving Fund Program Need to Be Strengthened [hyperlink, 
http://www.gao.gov/products/GAO-02-135] (Washington, D.C.: Jan. 24, 
2002). 

[2] U.S. General Accounting Office, Water Infrastructure: Information 
on Federal and State Financial Assistance [hyperlink, 
http://www.gao.gov/products/GAO-02-134] (Washington, D.C.: Nov. 30, 
2001). 

[3] Eligible systems include community water systems and not-for-profit 
noncommunity water systems. Community systems serve at least 25 people 
or 15 connections year-round. Noncommunity systems serve at least 25 
people for more than 60 days but less than year-round. 

[4] For both large and small systems, these percentages are calculated 
excluding the estimated $9.3 billion in needs associated with proposed 
or recently promulgated regulations. 

[5] According to EPA, the weighted average interest rate of DWSRF loans 
in 2001 was 2.4 percent, or about 3 percent lower than the market rates 
reported by the states. 

[6] U.S. Environmental Protection Agency, Drinking Water Infrastructure 
Needs Survey Second Report to Congress EPA 816-R-01-004 (Washington, 
D.C.: February 2001), p. 58. 

[7] Sampling error is a measure of the amount of uncertainty that 
exists about the true cost when costs are estimated from a sample of 
systems rather than from data collected from all systems. 

[8] For example, in its current needs assessment, EPA had to rely on 
modeling—and substituted the average costs generated by the models—for 
67 percent of the capital projects identified in its needs survey, 
including over 80 percent of the projects associated with small water 
systems. Modeling was necessary because project-specific documentation 
was not available in many instances. 

[9] In a simple random sample, each system has an equal chance of being 
included in the sample. 

[10] The workgroup consisted of state, American Indian, Alaskan Native 
Village, Indian Health Service, and EPA representatives. 

[11] The American Association for Public Opinion Research, “in the 
spirit of upgrading current survey practice,” has promulgated a list of 
best practices that includes reporting a measure of each estimate’s
precision along with the estimate, rather than reporting only the 
statistic itself. In addition, the Council of American Survey Research 
Organizations’ code of standards and ethics requires that estimates of 
sampling error be calculated and “available.” 

[12] States may also extend the loan repayment period from the standard 
20 years to up to 30 years, provided that the repayment period does not 
exceed the expected design life of the project. While an extended loan 
term makes financing a project more affordable to a community by 
reducing the amount of monthly payments, it is not considered a loan 
subsidy. 

[13] The state of Utah also reported an income-based criterion, but the 
state uses the median adjusted gross income rather than household 
income. 

[14] Although 21 states offer subsidy assistance in their disadvantaged 
community programs, only 14 states have actually forgiven a portion of 
the loan principal or reduced the loan interest rate below zero 
percent. 

[15] Our responses do not add to 12 because some states cited the 
availability of both federal and state funding as reasons for not using 
their DWSRF to assist disadvantaged communities. 

[16] Among other problems, small water systems often lack the economies 
of scale that make infrastructure projects more affordable at larger 
systems. 

[17] Determining which systems might fall into the disadvantaged 
category because of the high cost of a project, for example, would 
require a case-by-case analysis. 

[18] Another way of looking at this is to compare the number of systems 
estimated to be disadvantaged (6,925) with the total number of small 
systems (44,373). Using this approach, we could conclude that 
“disadvantaged” systems comprised a minimum of about 16 percent of 
small systems. 

[19] Approximately $1.8 billion of the state-sponsored loan programs 
were available for other local projects, such as solid waste disposal 
facilities, in addition to drinking water and wastewater 
infrastructure. 

[End of section] 

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