Wetlandscommonly referred to as marshes, bogs, or swampsprovide
public benefits such as habitat for plants and animals, flood abatement,
water quality protection, and recreational and educational opportunities.
Activities that alter wetlands are regulated under various federal, state,
and local laws, but the Department of Natural Resources (DNR) is the
primary state agency responsible for their protection and management.
Because many wetlands are located on private lands, concerns have been
raised about the extent to which Wisconsin’s regulatory program
balances the public’s interest in protecting wetlands with the rights of
property owners. In addition, some legislators have questioned the
consistency, predictability, and timeliness of DNR’s wetland permitting
decisions and have asked how wetland regulations in Wisconsin compare
to those in other states. To address these concerns, and at the direction of
the Joint Legislative Audit Committee, we:
reviewed DNR revenues, expenditures, and staffing levels from
fiscal year (FY) 2001-02 through FY 2005-06;
analyzed permit approval rates and the timeliness of permitting
decisions from January 2001 through June 2006;
analyzed compliance monitoring and enforcement differences
among DNR regions;
evaluated Wisconsin’s wetland compensatory mitigation program,
which was created by 1999 Wisconsin Act 147; and
reviewed wetland regulatory programs in surrounding states,
including Minnesota.
Staffing and Finances
Under the federal Clean Water Act,
most activities that involve grading,
filling, removing, or disturbing
the soil in a wetlandsuch as
residential construction, road
building, and pond creationrequire approval from both DNR
and the Army Corps of Engineers.
DNR is also authorized under
2001 Wisconsin Act 6 to regulate
activities in small, isolated
wetlands that are not subject to
federal permitting requirements.
DNR regulates Wisconsin wetlands
as part of a larger waterway permitting
program. In FY 2005-06, an
estimated 19.3 full-time equivalent
(FTE) staff performed wetland
permitting, enforcement, mapping,
policy coordination, and other
regulatory activities. Expenditures
for these activities were estimated
at $1.75 million.
DNR charges $500 for most state
wetland permits, regardless of
project size, the nature of the
disturbance, or the extent of its
effects on wetlands. However,
wetland permit fees do not cover
all program costs. In FY 2005-06,
general purpose revenue (GPR)
funded 45.5 percent of program
expenditures.
Wetland Permits
States differ in the manner and
extent to which they regulate
wetlands. For example, local governments
are responsible for
wetland permitting in Minnesota,
and the State of Michigan has
assumed federal wetland permitting
authority. Generally, both DNR
and the Corps approve permits in
Wisconsin, but only if wetlands
cannot be avoided and if projects
will not have significant adverse
environmental effects.
Wisconsin and several other
midwestern states regulate at least
some activities in wetlands that are
not subject to federal jurisdiction.
Indiana, Michigan, and Minnesota
exempt activities that result in
only small wetland disturbances,
but Wisconsin does not.
From January 2001 through
June 2006, DNR approved 3,582
wetland permits, or 82.6 percent
of the permit requests it received.
The three most frequently approved
activities were pond creation
(659 permits), utility projects
(555 permits), and residential construction
(501 permits). Approval
rates ranged from 74.0 percent
in DNR’s Northern Region to
88.0 percent in the South Central
Region. Approved permits disturbed
an estimated 867.7 wetland
acres.
The Natural Resources Board has
directed that wetland permits be
issued in a simple, straightforward,
and predictable manner. However,
the process is complicated and
requires frequent communication
with applicants. Existing laws give
DNR flexibility, but this flexibility
can be confusing and frustrating for
applicants.
Permit requests were generally
approved or rejected within
statutorily prescribed time frames
and, overall, median processing
time declined significantly from
2001 to 2005. However, 282 permit
decisions took longer than one year.
Compliance and Enforcement
Verifying compliance with permit
requirements is an important component
of a regulatory program.
From January 2005 through September
2006, regional staff reported
conducting only 27 inspections of
completed projects for which permits
had been issued. Violations were
found at six of these project sites.
DNR also identified 325 violationsincluding
disturbing wetlands
without a permit or not following
wetland permit requirementsin
response to complaints from the
public or other government officials.
More than half of these violations
occurred in the Northern Region,
where in 10 of 18 counties, more
than 20 percent of the land area is
classified as wetland.
According to DNR, most violations
are resolved voluntarily. During our
audit period, DNR issued 229 after-the-fact
permits and 69 notices of
violation for non-permitted
activities. However, regional staff
lack clear guidelines for resolving
violations, and our report includes
recommendations to ensure
consistent enforcement practices.
Compensating for
Wetland Losses
Compensatory mitigation is the
process of restoring, enhancing,
or creating wetlands to replace
those lost through permitted
projects. Wisconsin implemented
a voluntary program in 2002.
Applicants are typically required
to restore 1.5 wetland acres for each
acre lost, but the manner in which
that is done varies.
Some applicants create or restore
wetlands on site, while others
purchase credits from wetland
mitigation banks that provide a
market-based system for restoring
or creating wetlands in advance of
permitted losses. As of June 30, 2006,
six wetland mitigation banks in
Wisconsin had been approved.
Compensatory mitigation was
included in only 1.8 percent
of permits approved by DNR during
our audit period. They provided
compensation for a total of
41.1 wetland acres disturbed by
52 projects. Most projects were
located in the Southeast Region.
The use of compensatory mitigation
in DNR permits is limited by:
geographic restrictions;
additional costs to applicants
for long-term monitoring
and maintenance; and
state policies that discourage
the use of wetland mitigation
banks.
In contrast, compensatory mitigation
is mandatory, and therefore
more widely used, in Department
of Transportation projects, as well
as under federal wetland permits
and those issued by other states.
Wetland mitigation banks offer
administrative, economic, and
ecological advantages, although
some believe that increasing their
use would reduce wetland quality
and protection.
Wetland Mapping
Consistent, accurate, and up-to-date
wetland maps are important for
measuring program effectiveness,
making informed program
decisions, and prioritizing limited
resources. As required by law, DNR
has mapped wetlands larger than
five acres. However, existing maps
are outdated and not readily
available to the public, and they lack
sufficient detail to help landowners
locate wetlands on their property.
Recommendations
Our report includes recommendations for DNR to:
improve its tracking of wetland
losses and the timeliness of
permit processing,
(pp. 31 and
42);
develop general permits for
activities that have minimal
effects on wetlands
(p. 38);
increase efforts to monitor
compliance and ensure
consistent enforcement
practices
(pp. 50 and
51);
improve its coordination with
federal agencies
(p. 53 and
62); and
report to the Joint Legislative
Audit Committee by
December 31, 2007, on:
its efforts to ensure that
regional staff document
consistency in reaching
decisions, and to provide
permit applicants with
additional guidance
(p. 37);
the advantages and disadvantages of increasing the use of wetland mitigation banks
(p. 69);
options for establishing permit fees that better reflect staff and resource costs
(p. 84);
the feasibility of assuming responsibility for administering the federal wetland permit program, as allowed
by the Clean Water Act
(p. 86); and
a strategy for updating wetland maps and increasing their availability to the public
(p. 91);