Great Lakes Initiative
EPA and States Have Made Progress, but Much Remains to Be Done If Water Quality Goals Are to Be Achieved Gao ID: GAO-08-312T January 23, 2008Millions of people in the United States and Canada depend on the Great Lakes for drinking water, recreation, and economic livelihood. During the 1970s, it became apparent that pollutants discharged into the Great Lakes Basin from point sources, such as industrial and municipal facilities, or from nonpoint sources, such as air emissions from power plants, were harming the Great Lakes. Some of these pollutants, known as bioaccumulative chemicals of concern (BCC), pose risks to fish and other species as well as to the humans and wildlife that consume them. In 1995, the Environmental Protection Agency (EPA) issued the Great Lakes Initiative (GLI). The GLI established water quality criteria to be used by states to establish pollutant discharge limits for some BCCs and other pollutants that are discharged by point sources. The GLI also allows states to include flexible permit implementation procedures (flexibilities) that allow facilities' discharges to exceed GLI criteria. This testimony is based on GAO's July 2005 report, Great Lakes Initiative: EPA Needs to Better Ensure the Complete and Consistent Implementation of Water Quality Standards (GAO-05-829) and updated information from EPA and the Great Lakes states. This statement addresses (1) the status of EPA's efforts to develop and approve methods to measure pollutants at the GLI water quality criteria levels, (2) the use of permit flexibilities, and (3) EPA's actions to implement GAO's 2005 recommendations.
As GAO reported in 2005, developing the sensitive analytical methods needed to measure pollutants at the GLI water quality criteria level is a significant challenge to achieving GLI's goals. Of the nine BCCs for which criteria have been established, only two--mercury and lindane--have EPA-approved methods that will measure below those criteria levels. Measurement methods for the other BCCs are either not yet approved or cannot reliably measure to GLI criteria. Without such measurement, it is difficult for states to determine whether a facility is exceeding the criteria and if discharge limits are required in the facility's permit. As methods become available, states are able to include enforceable discharge limits in facilities' permits. For example, since EPA approved a more sensitive method for mercury in 1999, the number of permits with mercury limits has increased from 185 in May 2005 to 292 in November 2007. EPA and state officials expect this trend to continue. Similar increases may occur as more sensitive analytical methods are developed and approved for other BCCs. Flexibilities included in permits allow facilities' discharges to exceed GLI water quality criteria. For example, one type of flexibility--variances--will allow facilities to exceed the GLI criteria for a pollutant specified in their permits. Moreover, the GLI allows the repeated use of some of these permit flexibilities, and does not set a time frame for facilities to meet the GLI water quality criteria. As a result, EPA and state officials do not know when the GLI criteria will be met. In the 2005 report, GAO made a number of recommendations to EPA to help ensure full and consistent implementation of the GLI and to improve measures for monitoring progress toward achieving GLI's goals. EPA has taken some actions to implement the recommendations. For example, EPA has begun to review the efforts and progress made by one category of facilities--municipal wastewater treatment plants--to reduce their mercury discharges into the basin. However, until EPA gathers more information on the implementation of GLI and the impact it has had on reducing pollutant discharges from point sources, as we recommended, it will not be able to fully assess progress toward GLI goals.
GAO-08-312T, Great Lakes Initiative: EPA and States Have Made Progress, but Much Remains to Be Done If Water Quality Goals Are to Be Achieved
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Testimony:
Before the Subcommittee on Water Resources and Environment, Committee
on Transportation and Infrastructure, House of Representatives:
United States Government Accountability Office:
GAO:
For Release on Delivery Expected at 10:00 a.m. EST:
Wednesday, January 23, 2008:
Great Lakes Initiative:
EPA and States Have Made Progress, but Much Remains to Be Done If Water
Quality Goals Are to Be Achieved:
Statement of David Maurer:
Acting Director, Natural Resources and Environment:
Great Lakes Initiatives:
GAO-08-312T:
GAO Highlights:
Highlights of GAO-08-312T, a testimony before the Subcommittee on Water
Resources and Environment, Committee on Transportation and
Infrastructure, House of Representatives.
Why GAO Did This Study:
Millions of people in the United States and Canada depend on the Great
Lakes for drinking water, recreation, and economic livelihood. During
the 1970s, it became apparent that pollutants discharged into the Great
Lakes Basin from point sources, such as industrial and municipal
facilities, or from nonpoint sources, such as air emissions from power
plants, were harming the Great Lakes. Some of these pollutants, known
as bioaccumulative chemicals of concern (BCC), pose risks to fish and
other species as well as to the humans and wildlife that consume them.
In 1995, the Environmental Protection Agency (EPA) issued the Great
Lakes Initiative (GLI). The GLI established water quality criteria to
be used by states to establish pollutant discharge limits for some BCCs
and other pollutants that are discharged by point sources. The GLI also
allows states to include flexible permit implementation procedures
(flexibilities) that allow facilities‘ discharges to exceed GLI
criteria.
This testimony is based on GAO‘s July 2005 report, Great Lakes
Initiative: EPA Needs to Better Ensure the Complete and Consistent
Implementation of Water Quality Standards (GAO-05-829) and updated
information from EPA and the Great Lakes states. This statement
addresses (1) the status of EPA‘s efforts to develop and approve
methods to measure pollutants at the GLI water quality criteria levels,
(2) the use of permit flexibilities, and (3) EPA‘s actions to implement
GAO‘s 2005 recommendations.
What GAO Found:
As GAO reported in 2005, developing the sensitive analytical methods
needed to measure pollutants at the GLI water quality criteria level is
a significant challenge to achieving GLI‘s goals. Of the nine BCCs for
which criteria have been established, only two”mercury and lindane”have
EPA-approved methods that will measure below those criteria levels.
Measurement methods for the other BCCs are either not yet approved or
cannot reliably measure to GLI criteria. Without such measurement, it
is difficult for states to determine whether a facility is exceeding
the criteria and if discharge limits are required in the facility‘s
permit. As methods become available, states are able to include
enforceable discharge limits in facilities‘ permits. For example, since
EPA approved a more sensitive method for mercury in 1999, the number of
permits with mercury limits has increased from 185 in May 2005 to 292
in November 2007. EPA and state officials expect this trend to
continue. Similar increases may occur as more sensitive analytical
methods are developed and approved for other BCCs.
Flexibilities included in permits allow facilities‘ discharges to
exceed GLI water quality criteria. For example, one type of
flexibility”variances”will allow facilities to exceed the GLI criteria
for a pollutant specified in their permits. Moreover, the GLI allows
the repeated use of some of these permit flexibilities, and does not
set a time frame for facilities to meet the GLI water quality criteria.
As a result, EPA and state officials do not know when the GLI criteria
will be met.
In the 2005 report, GAO made a number of recommendations to EPA to help
ensure full and consistent implementation of the GLI and to improve
measures for monitoring progress toward achieving GLI‘s goals. EPA has
taken some actions to implement the recommendations. For example, EPA
has begun to review the efforts and progress made by one category of
facilities”municipal wastewater treatment plants”to reduce their
mercury discharges into the basin. However, until EPA gathers more
information on the implementation of GLI and the impact it has had on
reducing pollutant discharges from point sources, as we recommended, it
will not be able to fully assess progress toward GLI goals.
Figure 1: Area Comprising the Great Lakes Basin:
This figure is a map of the area comprising the Great Lakes Basin.
[See PDF for image]
Source: GAO (MapArt).
[End of figure]
To view the full product, including the scope and methodology, click on
[hyperlink, http://www.GAO-08-312T]. For more information, contact
David Maurer at (202) 512-3841 or maurerd@gao.gov.
[End of section]
Madam Chairwoman and Members of the Subcommittee:
I am pleased to be here today to discuss our work on the Great Lakes
Initiative (GLI), and its impact on water quality in the Great Lakes
Basin.[Footnote 1] As you know, millions of people in the United States
and Canada depend on the Great Lakes--the largest system of freshwater
in the world--as a source of drinking water, recreation, and economic
livelihood. During the 1970s, it became apparent that pollutants
discharged into the basin from point sources, such as industrial and
municipal facilities, or from nonpoint sources, such as air emissions
from power plants and agricultural runoff, were harming the Great
Lakes. Because less than 1 percent of the Great Lakes' water recycles
or turns over each year, on average, many of these pollutants stay in
place, settling in sediments or bio-accumulating in fish and other
aquatic species. As a result, some of these pollutants, such as mercury
and dioxin, known as bioaccumulative chemicals of concern (BCC), pose
risks to those species as well as to the humans and wildlife that
consume them.
In 1990, following a series of binational agreements aimed at improving
environmental conditions in the Great Lakes Basin, the Congress passed
the Great Lakes Critical Programs Act. This act, which amended the
Clean Water Act, required the Environmental Protection Agency (EPA) to
publish water quality guidance on minimum water quality standards and
antidegradation policies for protecting existing water quality. In
response, in 1995, EPA published the Final Water Quality Guidance for
the Great Lakes System, otherwise known as the GLI, to control over 100
toxic pollutants and protect aquatic life, wildlife, and human health.
Through the GLI, EPA established stringent water quality criteria--
numeric values to be used by states to set pollutant discharge limits
for point sources--for 9 BCCs and 20 other pollutants found in the
basin. In addition, the GLI established methodologies that the states
are to use in developing criteria for the remaining pollutants. Meeting
the criteria established by GLI requires sensitive analytical methods
that allow measurement of pollutant concentrations at or below the
level established by GLI water quality criteria. These methods allow
states to determine if a facility is exceeding the criteria and if a
discharge limit is required in the facility's permit as well as to
assess the facility's compliance. The Great Lakes Critical Programs Act
required that the eight Great Lakes states--Illinois, Indiana,
Michigan, Minnesota, New York, Ohio, Pennsylvania, and Wisconsin--adopt
provisions consistent with GLI into their environmental regulations and
point source permit programs within 2 years of issuance of GLI
guidance.
As you requested, my testimony today focuses on (1) the status of EPA's
efforts to develop and approve methods needed to measure pollutants at
the GLI water quality criteria level, (2) the use of permit
flexibilities, and (3) the actions EPA has taken to implement the
recommendations we made in our 2005 report on the GLI to better ensure
full and consistent implementation of GLI and monitor progress in
meeting GLI goals.[Footnote 2] My testimony is based on the 2005 report
and additional information we have obtained from EPA and the Great
Lakes states. Our testimony primarily focuses on the nine BCCs for
which EPA has developed GLI water quality criteria. Most of these BCCs
are responsible for fish consumption advisories in the Great Lakes.
We conducted this performance audit from October 2007 through January
18, 2008 in accordance with generally accepted government auditing
standards. Those standards require that we plan and perform the audit
to obtain sufficient, appropriate evidence to provide a reasonable
basis for our findings and conclusions based on our audit objectives.
We believe that the evidence obtained provides a reasonable basis for
our findings and conclusions based on our audit objectives. We
determined that the data provided were sufficiently reliable for
purposes of this testimony.
In summary:
* As we reported in 2005, developing the sensitive analytical methods
needed to determine whether GLI water quality criteria are being met is
a significant challenge to fully achieving GLI's goals. At the time of
our report, a method that allowed measurement of the pollutant at or
below the GLI criteria had been developed and approved for only two of
the nine BCCs--mercury and lindane. Mercury and lindane remain the only
BCCs for which an approved method is available that measures pollutant
concentrations below the GLI criterion. Once EPA approves an analytical
method, Great Lakes states are able to issue point source permits that
require facilities to use that method unless an alternative procedure
has been approved by the EPA region. Methods have been developed for
the remaining seven BCCs, but these methods either have not yet been
approved or only allow for measurement above the GLI criteria. For
example, because chlordane has a water quality criterion of 0.25
nanograms per liter but can only be measured down to a level of 14
nanograms per liter, it cannot always be determined if the pollutant is
exceeding the criterion. When methods are developed that can measure
pollutant concentrations at or below the level established by GLI water
quality criteria, a more pervasive problem of high pollutant levels in
the Great Lakes Basin waterbodies than previously recognized may be
revealed and could result in additional permits with discharge limits.
For example, the number of permits with mercury limits increased from
185 in May 2005 to 292 in November 2007. EPA officials attribute this
increase to the development of a more sensitive method for mercury in
1999 and EPA and state officials expect this trend to continue. Similar
increases may occur as more sensitive analytical methods are developed
and approved for other BCCs.
* Although permits may include BCC discharge limits, the GLI authorizes
states to use flexibilities that allow facilities' discharges to exceed
GLI water quality criteria. For example, one type of flexibility--
variances--will allow facilities to exceed the GLI criteria for a
particular pollutant specified in their permits. Furthermore, the GLI
allows the repeated use of some of these flexibilities and does not set
a time frame for facilities to meet the GLI water quality criteria. As
a result, EPA and state officials could not tell us when the use of
these flexibilities will be discontinued or when the GLI criteria will
be met.
* EPA has taken some actions to implement the recommendations we made
in our 2005 report to help ensure the full and consistent
implementation of the GLI and to improve measures for monitoring
progress toward achieving GLI's goals. First, EPA implemented our
recommendation to fully develop the GLI Clearinghouse and make it
available to the Great Lakes states. Second, as we recommended, EPA is
beginning to gather and track information to assess the progress of GLI
implementation although the information collected is limited to
municipal wastewater treatment plants. Third, to ensure the equitable
and timely implementation of GLI among all the Great Lakes states, EPA
has increased its efforts to resolve disagreements with the state of
Wisconsin on the adoption and implementation of GLI provisions.
Finally, although EPA disagreed with our recommendation to issue a
permitting strategy for mercury to ensure a more consistent approach
for controlling mercury by the states, it has continued to support
state implementation efforts by assessing which approaches are most
effective in reducing mercury discharges by point sources.
Progress Made in Developing Analytical Methods Will Ultimately Result
in More Permits with BCC Discharge Limits:
The ability to accurately and reliably measure pollutant concentrations
is vital to successfully implementing GLI water quality criteria.
Without this ability, it is difficult for states to determine if a
facility's discharge is exceeding GLI water quality criteria and if a
discharge limits are required. For example, because chlordane has a
water quality criterion of 0.25 nanograms per liter but can only be
measured down to a level of 14 nanograms per liter, it cannot always be
determined if the pollutant is exceeding the criterion. As we reported
in 2005, developing the analytical methods needed to measure pollutants
at the GLI water quality criteria level is a significant challenge to
fully achieving GLI goals. Although methods have been developed for the
nine BCCs for which GLI water quality criteria have been established,
EPA has only approved the methods to measure mercury and lindane below
GLI's stringent criteria levels. Analytical methods for the other BCCs
either have not received EPA approval or cannot be used to reliably
measure to GLI criteria levels. Once EPA approves an analytical method,
Great Lakes states are able to issue point source permits that require
facilities to use that method unless the EPA region has approved an
alternative procedure. According to EPA officials, specific time frames
for developing and approving methods that measure to GLI criteria have
not yet been established. EPA officials explained that developing EPA-
approved methods can be a time-consuming and costly process. Table 1
shows the status of the methods for the nine BCCs.
Table 1: Status of BCC Analytical Methods:
BCC: Chlordane;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
BCC: Dieldrin;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
BCC: DDT;
Status of method to measure GLI water quality criteria: Measures at the
GLI criterion but not yet approved by EPA[A].
BCC: Hexachlorobenzene;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
BCC: Lindane;
Status of method to measure GLI water quality criteria: Measures below
the GLI criterion and approved by EPA.
BCC: Mercury;
Status of method to measure GLI water quality criteria: Measures below
the GLI criterion and approved by EPA.
BCC: PCBs;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
BCC: 2,3,7,8-TCDD;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
BCC: Toxaphene;
Status of method to measure GLI water quality criteria: Measures above
the GLI criterion.
Source: GAO analysis of EPA information.
[A] An analytical method exists for DDT; however, this method does not
measure this pollutant at the GLI criterion level. A more sensitive
method has been developed but it is in draft and EPA has not yet
approved it.
[End of table]
As we reported in 2005, if pollutant concentrations can be measured at
or below the level established by GLI water quality criteria,
enforceable permit limits can be established on the basis of these
criteria. The Great Lakes states' experience with mercury illustrates
the impact of sufficiently sensitive measurement methods on identifying
pollutant discharges from point sources. Methods for measuring mercury
at low levels were generally not available until EPA issued a new
analytical method in 1999 to measure mercury concentrations below the
GLI water quality criterion of 1.3 nanograms per liter of water. This
more sensitive method disclosed a more pervasive problem of high
mercury levels in the Great Lakes Basin than previously recognized and
showed, for the first time, that many facilities had mercury levels in
their discharges that were exceeding water quality criteria. Since this
method was approved, the number of permits with discharge limits for
mercury rose from 185 in May 2005 to 292 in November 2007. Moreover,
EPA and state officials are expecting this trend to continue. As EPA
officials explained, it may take up to two permit cycles--permits are
generally issued for 5-year periods---to collect the monitoring data
needed to support the inclusion of discharge limits in permits. EPA
officials are expecting a similar rise in permits with discharge limits
for polychlorinated biphenyls (PCBs) when detection methods are
approved.
Permit Flexibilities Allowing Discharges in Excess of GLI Water Quality
Standards Delay Achievement of GLI Goals:
Permit flexibilities often allow facilities' discharges to exceed GLI
water quality criteria. These flexibilities can take several forms,
including the following:
* Variance. Allows dischargers to exceed the GLI discharge limit for a
particular pollutant specified in their permit.
* Compliance schedule. Allows dischargers a grace period of up to 5
years in complying with a permitted discharge limit.
* Pollutant Minimization Program (PMP). Sets forth a series of actions
by the discharger to improve water quality when the pollutant
concentration cannot be measured down to the water quality criterion. A
PMP is often used in conjunction with a variance.
* Mixing Zone. Allows dischargers to use the areas around a facility's
discharge pipe where pollutants are mixed with cleaner receiving waters
to dilute pollutant concentrations. Within the mixing zone,
concentrations of pollutants are generally allowed to exceed water
quality criteria as long as standards are met at the boundary of the
mixing zone. This flexibility expires in November 2010 with some
limited exceptions.
These flexibilities are generally only available to permit holders that
operated before March 23, 1997, and are in effect for 5 years or the
length of the permit.[Footnote 3] GLI allows states to grant such
permit flexibilities under certain circumstances, such as when the
imposition of water quality standards would result in substantial and
widespread economic and social impacts. Table 2 shows the number and
type of BCC permit flexibilities being used as of November 2007 in the
Great Lakes Basin for mercury, PCBs, and dioxin, as well as BCC
discharge limits contained in permits.
Table 2: Number and Type of BCC Permit Flexibilities Used and BCC
Discharge Limits in Great Lakes Basin Permits:
Mercury: Variance;
IL: 0;
IN: 2;
MI: 136;
MN: 0;
NY: 0;
OH: 15;
PA: 0;
WI: 2;
Total as of: Nov. 2007: 155.
Mercury: PMP;
IL: 0;
IN: 2[A];
MI: 136[A];
MN: 3[B];
NY: [C];
OH: 25[D];
PA: 0;
WI: 31[E];
Total as of: Nov. 2007: 197.
Mercury: Compliance Schedule;
IL: 0;
IN: 12;
MI: 0;
MN: 3;
NY: [C];
OH: 48;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 63.
Mercury: Mixing Zone;
IL: 0;
IN: 0;
MI: 0;
MN: 0;
NY: [C];
OH: 20;
PA: 0;
WI: f;
Total as of: Nov. 2007: 20.
Mercury: Mercury discharge limits contained in permits;
IL: 0;
IN: 16;
MI: 136;
MN: 4;
NY: 49;
OH: 83;
PA: 0;
WI: 4;
Total as of: Nov. 2007: 292.
PCBs: Variance;
IL: 0;
IN: 0;
MI: 0;
MN: 0;
NY: 0;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 0.
PCBs: PMP;
IL: 0;
IN: 0;
MI: 0;
MN: 1;
NY: c;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 1.
PCBs: Compliance Schedule;
IL: 0;
IN: 0;
MI: 0;
MN: 1;
NY: c;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 1.
PCBs: Mixing Zone;
IL: 0;
IN: 0;
MI: 0;
MN: 0;
NY: c;
OH: 1;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 1.
PCBs: PCB discharge limits contained in permits;
IL: 0;
IN: 2;
MI: 7;
MN: 1;
NY: 39;
OH: 1;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 50.
2,3,7,8-TCDD; Dioxin: Variance;
IL: 0;
IN: 0;
MI: 0;
MN: 0;
NY: 0;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 0.
2,3,7,8-TCDD; Dioxin: PMP;
IL: 0;
IN: 0;
MI: 0;
MN: 1;
NY: c;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 1.
2,3,7,8-TCDD; Dioxin: Compliance Schedule;
IL: 0;
IN: 0;
MI: 0;
MN: 1;
NY: c;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 1.
2,3,7,8-TCDD; Dioxin: Mixing Zone;
IL: 0;
IN: 0;
MI: 0;
MN: 0;
NY: c;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 0.
2,3,7,8-TCDD; Dioxin: Dioxin discharge limits contained in permits;
IL: 0;
IN: 0;
MI: 2;
MN: 1;
NY: 0;
OH: 0;
PA: 0;
WI: 0;
Total as of: Nov. 2007: 3.
2,3,7,8-TCDD; Dioxin: Total Flexibilities Used[A];
IL: 0;
IN: 16;
MI: 272;
MN: 10;
NY: c;
OH: 109;
PA: 0;
WI: 33;
Total as of: Nov. 2007: 440.
BCC discharge limits for mercury, PCBs, and dioxin contained in
permits;
IL: 0;
IN: 18;
MI: 145;
MN: 6;
NY: 88;
OH: 84;
PA: 0;
WI: 4;
Total as of: Nov. 2007: 345.
Source: GAO analysis of state permit data.
[A] These PMPs are used as a condition of a variance in a permit.
[B] These PMPs are associated with compliance schedules.
[C] Currently, no variances have been granted by the New York State
Department of Environmental Conservation (NYSDEC). However, the
department was unable to determine the number of permitted facilities
that had other flexibilities, and the number of flexibilities used.
According to NYSDEC, 51 facilities could use these permit
flexibilities.
[D] These 25 PMPs are used as both a condition of a variance (15) and
associated with compliance schedules (10).
[E] Two of these PMPs are used as a condition of a variance in a
permit. In general, Wisconsin officials are using PMPs in lieu of
discharge limits to address mercury.
[F] Wisconsin officials were unable to provide data on the number
mixing zones used for mercury.
[End of table]
According to EPA and state officials, in many cases, facilities cannot
meet GLI water quality criteria for a number of reasons, such as
technology limitations, and the flexibilities are intended to give the
facility time to make progress toward meeting the GLI criteria. With
the exception of compliance schedules, the GLI allows for the repeated
use of these permit flexibilities.[Footnote 4] As a result, EPA and
state officials could not tell us when the GLI criteria will be met.
EPA Has Taken Some Actions to Ensure Consistent Implementation of the
GLI as Recommended in Our 2005 Report:
In our 2005 report, we described several factors that were undermining
EPA's ability to ensure progress toward achieving consistent
implementation of GLI water quality standards. To help ensure full and
consistent implementation of the GLI and to improve measures for
monitoring progress toward achieving GLI's goals, we made a number of
recommendations to the EPA Administrator. EPA has taken some actions to
implement the recommendations contained in our 2005 report, as the
following indicates:
* Ensure the GLI Clearinghouse is fully developed. We noted that EPA's
delayed development of the GLI Clearinghouse--a database intended to
assist the states in developing consistent water quality criteria for
toxic pollutants--was preventing the states from using this resource.
To assist Great Lakes states in developing water quality criteria for
GLI pollutants, we recommended that EPA ensure that the GLI
Clearinghouse was fully developed, maintained, and made available to
Great Lakes states. EPA launched the GLI Clearinghouse on its Web site
in May 2006 and in February 2007, EPA Region 5 provided clearinghouse
training to states. The clearinghouse currently contains criteria or
toxicity information for 395 chemicals. EPA officials told us that the
clearinghouse is now available to the states so they can independently
calculate water quality criteria for GLI pollutants. EPA officials told
us that some states, including Ohio, Wisconsin, and Illinois, plan on
updating their water quality standards in the near future and believe
that the clearinghouse will benefit them as well as other states as
they update their standards.
* Gather and track information to assess the progress of GLI
implementation. In 2005, we reported that EPA's efforts to assess
progress in implementing the GLI and its impact on reducing point
source discharges have been hampered by lack of information on these
discharges. To improve EPA's ability to measure progress, we
recommended that EPA gather and track information on dischargers'
efforts to reduce pollutant loadings in the basin. EPA has begun to
review the efforts and progress made by one category of facilities--
municipal wastewater treatment facilities--to reduce their mercury
discharges into the basin. However, until EPA develops additional
sources of information, it will not have the information needed to
adequately assess progress toward meeting GLI goals.
* Increase efforts to resolve disagreements with Wisconsin. Although we
found that the states had largely completed adoption of GLI standards,
EPA had not resolved long-standing issues with Wisconsin regarding
adoption and implementation of GLI provisions. To ensure the equitable
and timely implementation of GLI by all the Great Lakes states, we
recommended that that the EPA Administrator direct EPA Region 5, which
is responsible for Wisconsin, to increase efforts to resolve
disagreements with the state over inconsistencies between the state's
and the GLI's provisions. Wisconsin officials believe the GLI
provisions are not explicitly supported by Wisconsin law. Subsequently,
EPA and Wisconsin officials have held discussions on this matter, and
neither Wisconsin nor EPA officials believe that these disagreements
are significantly affecting GLI implementation. However, they have been
unable to completely resolve these issues. We found that similar issues
have also surfaced with New York.
* Issue a permitting strategy for mercury. Because we found that Great
Lakes' states had developed inconsistent approaches for meeting the GLI
mercury criterion, including differences in the use of variances, we
recommended that EPA issue a permitting strategy to ensure a more
consistent approach. EPA disagreed with this recommendation, asserting
that a permitting strategy would not improve consistency. Instead, the
agency continued to support state implementation efforts by developing
guidance for PMPs, evaluating and determining compliance, and assessing
what approaches are most effective in reducing mercury discharges by
point sources. One such effort is EPA Region 5's review of mercury PMP
language in state-issued permits for wastewater treatment facilities.
This review resulted in recommendations to the states in May 2007 to
improve the enforceability and effectiveness of PMP provisions.
However, additional efforts will be needed to ensure consistency at
other types of facilities, such as industrial sites, across the Great
Lakes states.
In closing, Madam Chairwoman and Members of the Subcommittee, although
progress has been made with mercury detection and increased knowledge
of wastewater treatment facilities' pollutant discharges to the Great
Lakes, information is still lacking on the full extent of the problem
that BCCs pose in the Great Lakes. As methods are developed to
determine whether facilities' discharges for other BCCs meet GLI
criteria and EPA approves them, and as more permits include discharge
limits, more information will be available on pollutant discharges in
the basin. Even with these advances, however, extensive use of permit
flexibilities could continue to undercut reductions in pollution levels
and the ultimate achievement of GLI's goals.
This concludes my prepared statement. I would be happy to respond to
any questions that you or Members of the Subcommittee may have at this
time.
GAO Contacts:
Contact points for our Offices of Congressional Relations and Public
Affairs may be found on the last page of this statement. For further
information about this testimony, please contact David Maurer at (202)
512-3841 or maurerd@gao.gov. Key contributors to this testimony were
Greg Carroll, Katheryn Summers Hubbell, Sherry L. McDonald, and Carol
Herrnstadt Shulman. Other contributors included Jeanette Soares and
Michele Fejfar.
[End of section]
Footnotes:
[1] The Great Lakes Basin includes the five Great Lakes--Superior,
Michigan, Huron, Ontario, and Erie--and a large land area that extends
beyond the lakes, including their watersheds, tributaries and
connecting channels.
[2] GAO, Great Lakes Initiative: EPA Needs to Better Ensure the
Complete and Consistent Implementation of Water Quality Standards, GAO-
05-829 (Washington, D.C.: July 27, 2005).
[3] Mixing zones are available for facilities that were discharging the
pollutant or facilities that were under construction on the date that
the GLI took effect in that state.
[4] The GLI does not provide a sunset date for permit flexibilities
other than mixing zones, which are set to expire in 2010 with limited
exceptions. Individual compliance schedules cannot be used for more
than the 5-year period they establish; however, after the schedules
expire, facilities may use other permit flexibilities such as variances.
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