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International
Symposium
Wetlands 2006
Applying Scientific, Legal, and Management
Tools for the
Great Lakes and Beyond
August 28-31, 2006
Grand Traverse Resort,
Near Traverse City, Michigan
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Abstracts
(PDF)
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Sponsorship/Cooperating
Parties
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Exhibit/Poster
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Registration
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Hotel/Travel
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ABSTRACTS
Continued (4 of 7)
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1, Page
2, Page
3, Page
5, Page
6, Page
7)
Please note, more abstracts will be added. Not all speakers have
submitted abstracts. Abstracts are listed in alphabetical order
by the name of the speaker.
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Abstracts on
this page by: (updated
7-31-06)
Upland
Habitat Restoration for the Eastern Massasauga Rattlesnake
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Authors/Presenter*:
Bruce Kingsbury* and Joe Sage
Indiana-Purdue University
Fort Wayne, IN 46805
(260) 481-5755
kingsbur@ipfw.edu
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Eastern Massasauga (Sistrurus c. catenatus) is a Candidate
for listing as federally Threatened, and is imperiled throughout
its Midwestern range. Unlike most rattlesnakes, this diminutive
species is affiliated with wetlands. However, it is not aquatic,
and in fact often makes extensive use of upland areas. Consequently,
while the proper management of saturated and inundated emergent
systems is critical for massasauga conservation, management of
uplands adjacent to these areas is also important. Given that
the uplands used are open canopy habitats, maintenance and restoration
of early seral stages is required. Furthermore, we must have confidence
that snakes will occupy managed habitat. Using radio telemetry,
we have been studying the spatial ecology of massasaugas at sites
undergoing restoration and management. Our findings indicate that
successional inhibition and grassland/savanna restoration can
succeed in attracting use by snakes. Massasaugas will also find,
use, and persist in habitat refugia. Islands of habitat left in
construction areas thus serve as sources for recolonization by
plants and animals into restored habitat and as safe zones for
larger animals such as massasaugas that move in and out of them.
Paved roads appear to present significant barriers to massasaugas,
while paths and gravel roads with limited traffic do not. Gravid
females may be attracted to areas of active management if the
managed area provides a better microclimate for gestation. This
means that any added mortality from human activity may differentially
impact gravid females, potentially affecting the reproductive
output of the population as a whole. |
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Observations
on the Hibernation Ecology of the Eastern Massasauga Rattlesnake
in Southern Michigan
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Authors/Presenter*:
Joe Sage and Bruce Kingsbury*
Department of Biology
Indiana-Purdue University
Fort Wayne, IN 46805
(260) 481-5755
kingsbur@ipfw.edu
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| The
once locally abundant Eastern Massasauga (Sistrurus c. catenatus)
is in decline throughout its range, and is a Candidate for listing
as federally Threatened. If we are to successfully manage for
the species, we must better understand all of its life history
needs, yet the specific requirements for hibernation are poorly
understood. Snakes monitored via telemetry at two sites in southeast
Michigan behaved similarly to snakes previously monitored in Indiana,
ranging widely over the landscape during the active season, but
constraining hibernation to relatively small areas. This pattern
reinforces the concern that suitable hibernacula are limited,
and we need to know why. We monitored the behavior of snakes as
they overwintered, and evaluated water quality in test wells in
and around hibernacula. As is the case for several other Great
Lakes reptiles and amphibians, massasaugas generally hibernate
in association with wetlands, and often use crayfish burrows to
gain entry into saturated ground. Water table depth was an important
factor in hibernacula selection. All snakes chose areas in which
the water table was relatively close to the surface, but wetland
areas where the surface was inundated were never used. Thus, it
is most appropriate to think of them as often hibernating adjacent
to jurisdictional wetlands rather than in them. We also report
on other findings regarding the behavior of hibernating snakes,
burrow co-habitants, and environmental attributes of the burrows,
such as temperature and water chemistry. |
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Development
of Wetland Invertebrate Index of Biotic Integrity in Ohio
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Author/Presenter:
Marty
Knapp
Ohio Environmental Protection Agency
Ecological Assessment Section
4675 Homer Ohio Lane
Groveport, Ohio 43125
Marty.Knapp@epa.state.oh.us
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ABSTACT Invertebrates collected in 24-hr activity traps placed
in shallow water areas (6-12 inches) around the perimeter of wetlands
are characteristic of the overall assessment of the habitat, soils,
and water quality of the wetland. Establishing invertebrate criteria
for wetlands has often focused on relative abundance (% based)
methods. Tolerant and sensitive index metrics were developed based
on individual densities at the generic and specific taxonomic
level from 228 records collected in May and June from 1996 to
2004. This density based approach will be compared to more frequently
used relative abundance (% based) methods.
Mitigation banks studied in 2004 exhibited drastic changes in
invertebrate assemblages from those found in high quality natural
systems. Tolerant macroinvertebrate taxa of beetles, corixids,
and snails were present in high densities at the bank sites. Taxonomy
to the generic and specific levels of oligochaetes, cladocerans,
and ostracods has added refinement to measurable ecological differences.
Two opportunistic species of ostracods, Cypridopsis vidua
and Cypria maculata, were numerically abundant at many
of the bank sites in comparison to densities of more sensitive
ostracod species collected at high quality natural sites.
Additionally, a less intense level of wetland assessment using
macroinvertebrates that can be identified in the field was developed
for training demonstrations. The wetland assessment is in a format
similar to macroinvertebrate stream quality assessments used for
educational purposes. The wetland assessment sheets are geared
toward indicator taxa greater than 3 mm and include photos of
the more common types. The scoring system can differentiate a
poor community from others, but due to the lesser taxonomic effort,
may not be able to differentiate between fair and good communities
as efficiently. Laminated copies will be available. |
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Anthropogenic
Pressures of Nal Sarovar Bird Sanctuary, Gujarat, India
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Authors/Presenter*:
Nirmal Kumar, J. I.*
Head, P.G. Department of Environmental Sciences
Institute of Science & Technology for Advanced Studies & Research
(ISTAR)
Vallabh Vidyanagar - 388 120
Gujarat, India
nvpas2003@yahoo.com
Hiren Soni, and Rita N. Kumar
Head, Department of Biological Sciences & Environmental Sciences
N.V. Patel College of Pure & Applied Sciences
Vallabh Vidyanagar - 388 120
Gujarat, India
istares2005@yahoo.com)
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| The
Nal Sarovar Bird Sanctuary (NSBS) is an important Protected Area
(PA) and one of the proposed Ramsar sites of Gujarat State; encompassing
an area of 120 sq. km. It is situated along the western border
of Ahmedabad district and southern border of Surendranagar district.
The area lies between 220 78' N to 220 96' N latitude and 710
92' E to 720 64' E longitude. The Sanctuary supports floral as
well as faunal elements with rich diversity. The entire area experiences
three seasons. Winter being the coldest with minimum of 70C temperature,
while the hottest summer with 450C and monsoon experiences 600
mm average rainfall. Geologically, the basaltic rocks of the area
belonging to Deccan trap interspersed with igneous and metamorphic
rocks of Cretaceous sandstones. In the present study, 8 villages
were selected to investigate various anthropogenic interventions.
Besides human (n=47,550) and livestock population (n=20,387) of
these villages, collection of fuelwood, generation of income through
fishing, boating, horse-riding and poaching of waterfowls by local
people were identified as the major threats of anthropogenic pressures.
The local inhabitants reside within and outside the PA zone are
partly or fully dependent upon the water reserve for their livelihood.
The paper mainly focuses on human generated threats like plant
removal for fodder and fuelwood, fishing, boating, horse-riding
and hunting and poaching of waterfowl within sanctuary area. Among
the studied parameters, human and cattle population, fishing,
boating, horse-riding and poaching go parallel to each other.
The anthropogenic influence was found maximum in Ranagadh village,
followed by Shiyal, Nani Kathechi, Kayla and Shahpur villages.
However, such pressures were low in Durgi, Vekaria and Meni villages.
The quantification of each pressure and salient findings are discussed
in the paper. |
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Success
of Corps-Required Wetland Mitigation in New England
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Author/Presenter:
Ruth M. Ladd, PWS
U.S. Army Corps of Engineers - New England District
Regulatory Division
696 Virginia Road
Concord, MA 01742-2751
(978) 318-8818
ruth.m.ladd@usace.army.mil
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Key
words: Wetland mitigation, New England, assessment
In June 2001, the National Academy of Sciences' National Research
Council issued a report on the effectiveness of mitigation in
the Corps of Engineers Regulatory Program which identified a variety
of weaknesses in the mitigation aspects of the Corps' program.
Prior to release of that report, the Environmental Resources Section
in the New England District's Regulatory Division was tasked with
developing a study to analyze the effectiveness of compensatory
mitigation projects in New England.
The study was designed to determine the effectiveness of compensatory
mitigation (creation and restoration only) for permitted impacts
in New England, and to provide a basis for making programmatic
improvements as warranted. Mitigation success was assessed in
two ways: comparison to permit requirements and a determination
if the mitigation functions as a natural wetland system and compensates
for the lost functions.
A stratified random selection of 60 mitigation sites was studied.
Each site was visited and a variety of data collected. An early
finding was that there were not always adequate records and data
management. The study results further indicate that insufficient
compensatory mitigation has been required to fully offset project
impacts. Several causes of degradation of mitigation site functions
were observed.
Recommendations include improved data management and the need
to concentrate on identifying and replacing the functions proposed
to be impacted to the extent possible. |
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Cut
& Git: Waters/Wetlands Restoration In The Third Forest Of The
Pacific Northwest
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Authors/Presenter*:
Lyndon C. Lee Ph.D.*, Peggy L. Fiedler, Ph.D., and Kevin L.
Fetherston, Ph.D.
Ecosystem Science & Restoration Services
ENTRIX, Inc.
Seattle, WA
(206) 239-0276; Fax: (206) 269-0098
llee@entrix.com
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| In
the Pacific Northwest Region (PNW) of the western United States,
restoration of forested waters of the U.S., including wetlands
(waters/wetlands) relies on syntheses and applications of science
and practical knowledge both old and new. Since the 1850's, the
strength of the forest products economy and a focus on resource
extraction and (lately) sustained yield management has made market-driven
conservation a priority for forest managers. Although waters/wetlands
ecosystems have always been "inconvenient" in the context of silvicultural
plans and practices, their productivity, resilience, and potential
to degrade rapidly and impact adjacent forestry operations has
compelled modern-day foresters to pay close attention to operations
in waters/wetlands. In addition to the forest industry, the importance
of fish and shellfish economies combined with rapidly expanding
human populations, resource degradation, and habitat fragmentation
has required a rethinking of management approaches for forested
waters/wetlands. Today, our endangered anadromous fishes, threatened
shellfish resources, and soaring populations compel us to integrate
and link waters/wetlands restoration efforts across traditional
boundaries of land, ownership, politics, and discipline. This
isn't easy, especially as factions that require or hope for restoration
of forested waters/wetlands are also consumers of forest products
and land resources. Therefore, in the post-modern PNW, the practice
of ecosystem restoration thrives in a curious tension among old
silviculture and new forestry, art and science applied, and resource
extraction versus burgeoning commitments to resource conservation. |
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Ecological
Restoration on the Detroit River
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Author/Presenter:
Chris Lehr
Nativescape LLC
10380 Clinton Road
Manchester, MI 48158
(517) 456-9696; Fax: (517) 456-7245
info@nativescape.net
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About
97 percent of the natural coastal wetland habitats along the Detroit
River have been lost to development and "hard" engineering to
stabilize shorelines. The river shoreline is almost entirely artificial
having been lined with steel sheet piling, broken rock and concrete
rubble. Increasing urbanization has had a negative impact on the
environment. With the Detroit River Remedial Action Plan (RAP)
identifying "loss of fish and wildlife habitat" as one of the
nine impaired beneficial uses of these waters, restoring and preserving
wetland habitats must be a priority for all shoreline projects
in the area. Therefore, there is an urgent need to protect existing
coastal wetlands, rehabilitate degraded ones and remediate the
lost wetlands along the Detroit River.
In all of Nativescape's projects on the Detroit River "soft engineering"
was used to establish natural shorelines, reduce erosion, achieve
shoreline stability and safety, while enhancing habitats and improving
aesthetics. Specializing in ecological restoration Nativescape
uses the latest information in local native plant community types.
Native habitat types enhance
biodiversity (biological variety); these habitats will not compete
with existing remnant native habitats in the surrounding area.
The processes used can be utilized for degraded shorelines along
the coastal Great Lakes, streams, rivers and inland lakes.
Nativescape LLC takes a scientific approach using proven BMP's
in native ecosystem restoration, soil-bioengineering and natural
landscaping to ecologically rehabilitate the shoreline. A natural
storm water management approach will provide a buffer from storm
water run off, create an infiltration zone, and restore a more
natural shoreline along a very industrialized river corridor.
All these projects create a number of ecosystems that will benefit
aquatic and terrestrial wildlife: wetlands that provide spawning
and fingerling habitat, shoreline shade for cover and water cooling
and an upland buffer to provide water quality protection. |
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Using
Remote Sensing and Landscape Ecology to Assess the Condition
of Great Lakes Wetlands
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Author/Presenter:
Ric Lopez, Ph.D.
Ecologist
U.S. Environmental Protection Agency
National Exposure Research Laboratory
Environmental Sciences Division
Landscape Ecology Branch
944 East Harmon Avenue, Mail Code CSB 201-K
Las Vegas, NV 89119
(702) 798-2394; Fax: (702) 798-2208
lopez.ricardo@epa.gov
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| Geospatial
modeling approaches are being used to locate and assess the condition
of natural resources (particularly wetland ecosystems) in the
Great Lakes Basin. These assessments involve measuring landscape
characteristics at multiple scales, primarily focusing on surface
water quality, hydrologic connectivity, and biological diversity.
Wetland ecosystems in the Great Lakes present special challenges
to landscape ecologists because they are a transitional ecosystem,
containing a mixture of aquatic and upland biophysical characteristics.
Although the response of ecosystems to landscape conditions has
been generally postulated and tested for decades at a fine-scale,
broad-scale applications are lacking, particularly for wetlands.
Hyperspectral and multispectral remote sensing techniques are
both being used to address these challenges in order to increase
capabilities for protecting and restoring wetlands. These techniques
are leading to a forecasting method for understanding the influence
of landscape structure and pattern on wetland ecosystems, and
the Great Lakes Basin as a whole. Results from wetland detection
and mapping; opportunistic plant species detection and mapping;
and the broad-scale assessment of landscape condition will be
presented. |
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Temporal
Dynamics in Wetland Habitats and the Implementation of Management
Strategies
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Author/Presenter:
Mark R. Luttenton
Biology Department and Annis Water Resources Institute
Grand Valley State University
Allendale, MI 49401
luttentm@gvsu.edu
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| Wetland
assessments in Great Lakes Areas of Concern are a snapshot that
provide information on current habitat conditions. Often assessments
identify environmental factors structuring the habitat at that
point in time and AOC habitat management plans are conceived to
remedy these factors. However, aquatic plant communities and environmental
conditions are temporally dynamic and initial assessments may
capture habitat conditions that are transient. Because management
plans often take years to implement, habitat conditions at the
time of implementation may have transitioned to alternate habitat
conditions. Assessments of the SAV in the aquatic bed portion
of the White Lake and Muskegon Lake wetland complexes conducted
ten years apart identify changes in macrophyte community composition
and total biomass. Environmental factors such as the introduction
of exotic species during or after an initial assessment and groundwater
nutrient load appear to be important in community changes and
should influence management considerations. Consequently, assessment
and management should be closely linked and consideration given
to temporal dynamics of aquatic macrophyte communities prior to
and during implementation of management strategies. |
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Using
Condition to Assess Function: A Condition-Based Approach to
Mitigation Performance
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Authors/Presenter*:
John J. Mack* and Mick Micacchion
Wetland Ecology Group
Division of Surface Water
Ohio Environmental Protection Agency
4675 Homer-Ohio Lane
Groveport, OH 43125
john.mack@epa.state.oh.us, mick.micacchion@epa.state.oh.us.
and
M. Siobhan Fennessy
Department of Biology
Kenyon College
Gambier, OH
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A condition-based approach to assessing "functional" replacement
for wetland mitigation has been developed using a reference wetland
data set of natural wetlands that includes data from the major
hydrogeomorphic (HGM) and plant community classes that span a
gradient of human disturbance. From this data set multiple wetland
program tools were developed 1) multimetric biological indices
(IBIs) and hydrological and biogeochemical indicators; 2) a rapid
(condition-based) wetland assessment tool (Ohio Rapid Assessment
Method for Wetlands); and 3) a wetland classification scheme based
on landscape position and dominant vegetation. Ensuring functional
replacement occurs in a several step process. First, as part of
permit application, the HGM class and dominant plant community
of the impacted wetland(s) are determined which accounts for the
ecosystem processes (functions) and ecological services (values)
of different wetland types without the necessity of developing
a comprehensive list of those functions and values. Second, the
condition of the impacted wetland is assessed with the rapid condition
tool (ORAM v. 5.0) or a wetland IBI providing a measure of wetland
quality. Third, the size of the wetland to be impacted is determined
and appropriate mitigation ratios are applied. Fourth, any residual
moderate to high functions or values the impacted wetland(s) may
still be providing, despite moderate to severe degradation, are
evaluated using a checklist with a narrative discussion. Finally,
requirements for mitigation are specified in the permit. If there
is 1) replacement by size of the impacted wetland, 2) replacement
of the type of wetland impacted, 3) and replacement of the quality
of the impacted wetland as measured by quantitative, condition-based
ecological performance targets, then there is strong assurance
that functional replacement is occurring. Fundamentally, the above
approach is strongly data-driven and it follows that meaningful
and adequate mitigation monitoring is necessary to determine whether
the mitigation wetland has "succeeded" or "failed." Case studies
of the application of this approach to mitigation banks and individual
mitigations are presented. |
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An
Ecological Assessment of Ohio Mitigation Banks
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Authors/Presenter*:
John J. Mack* and Mick Micacchion
Ohio Environmental Protection Agency
Division of Surface Water
Wetland Ecology Group
4675 Homer Ohio Lane
Groveport, OH 43125
john.mack@epa.state.oh.us
mick.micacchion@epa.state.oh.us.
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| Mitigation
banks are often considered to have multiple advantages over individual
mitigations including improved economies of scale; consolidation
of economic, planning, and scientific resources; greater likelihood
of success, etc. There are few assessments of multiple banks to
determine whether these advantages are in fact producing a more
successful or more consistently successful mitigation wetland.
And no attention has been paid to the main risk of mitigation
bank: failure of large banks represents a substantial net loss
of wetland acreage or function whereas failure of individual small
mitigations usually represents a nominal loss. Of the bank area
assessed (nearly 400 ha), approximately 25% was not "wetland"
but was primarily shallow unvegetated pond; of the remaining "wetland"
acreage, approximately 25% was "poor" quality, 58% was "fair"
quality, and 18% was "good" quality when vegetation data from
mitigation banks was compared to ecoregionally calibrated scores
from natural reference wetlands. Only one bank had areas where
forest regeneration is occurring and no bank had restored common
Ohio shrub swamp communities, e.g. buttonbush or alder swamps.
Based on the data collected here, successful banks were defined
as maximizing areas defined as "wetland," minimizing areas of
open water, having hydroperiods which mimic hydroperiods of natural
wetlands, maximizing cover of perennial native hydrophytes, minimizing
cover of invasive plant species, and have mean VIBI scores of
40-60 (fair to good). Based on these criteria, of the 12 banks
assessed in Ohio, 3 were mostly successful, 5 were successful
in some areas but failed in other areas, and 4 were mostly failed.
Unfortunately, this is not the proportion of success and failure
that was at least implicitly promised in the Federal Bank Guidance.
The economies of scale and consolidation of resources was to provide
a consistently higher quality "product" of wetland restoration
than was achievable by individual restorations. This "promise",
although clearly achievable, has not been consistently attained
in practice. But the basic practical fact remains, that a workable
regulatory compensatory mitigation program needs a mitigation
banking system that is successful acre for acre and also ecologically.
What is needed is a re-appreciation that this is not easy work,
that the "devil" is in the details at all levels (theory, planning,
design, and management), and that "nature" does know "best" (or
at least is our best referent for "success"). |
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Updating
and Tracking Wetlands in the Great Lakes
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Author/Presenter:
Robb Macleod
GIS Manager
Great Lakes/Atlantic Regional Office
Ducks Unlimited
331 Metty Drive, Suite 4
Ann Arbor, MI 48103
(734) 623-2000
rmacleod@ducks.org
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| Using
data that is both temporally and spatially relevant when developing
waterfowl habitat models and planning wetland restoration and
protection activities is extremely important. The U.S. Fish and
Wildlife Service's National Wetlands Inventory (NWI) has been
used for many modeling and planning activities due to its areal
extent and spatial relevance. However, much of this inventory
is between 15 and 20 years old and some of the data for the Great
Lakes is still in hardcopy format. As part of a pilot project
to test methodology for updating NWI throughout the Great Lakes,
Ducks Unlimited (DU) has updated the NWI for the southern portion
of Michigan's Lower Peninsula by identifying both losses and gains
of wetlands. The update was accomplished by viewing the NWI data
over spring 1998 series color infrared (CIR) digital orthophotos
to determine the status of the wetlands. Drained wetlands were
given a modifier as to the drainage type (agriculture, developed,
recreation, or other). This project identified 42,876 acres of
drained wetlands and 12,665 acres of new wetlands in the project
area. DU has embarked upon an ambitious project to update and
track the wetland changes in the Great Lakes states of Wisconsin,
Illinois, Indiana, Michigan, and Ohio. This presentation will
discuss the procedures and attribute system for updating and tracking
the wetland changes over multiple time periods. |
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Great
Lakes HEN: A Science-based Application for Guiding Habitat Restoration
for Breeding Waterfowl
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Authors/Presenter*:
Robb Macleod*, Tina Yerkes, John Coluccy, and Rob Paige
Ducks Unlimited
331 Metty Drive, Suite 4
Ann Arbor, MI 48103
(734) 623-2000
rmacleod@ducks.org
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| Wetlands
and adjacent uplands play a critical role in breeding waterfowl
habitat in the Great Lakes. Until now, very little was known about
where and how much of this habitat existed or needed to be created
in order to reach the Upper Mississippi River / Great Lakes Joint
Venture goals. Ducks Unlimited (DU) has completed an ambitious
five-year research and planning project that provides natural
resource managers with information for managing breeding waterfowl
populations in the Great Lakes. In combining a predicted breeding
mallard map and specific habitat information on nest success and
duckling survival from the research, DU was able to create Great
Lakes HEN, or Habitat Evaluation Network. Great Lakes HEN utilizes
the latest in GIS and Internet technology to provide the breeding
waterfowl habitat information and planning tools at a local level
for conservation resource managers. HEN identifies areas that
are important for breeding waterfowl and describes what type of
conservation is needed (protection or restoration) and how much
in order to reach the goals. Great Lakes HEN also allows the user
to view other data layers, such as: aerial photos, soils, potential
wetland restoration areas, topographic maps, and land cover. Basic
GIS analysis tools like calculating the area of a polygon, querying
attributes, and zooming to a specific location are also included
in HEN. |
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