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Ohio Water Science Center |
U.S. Geological Survey, Open-File Report 2006–1385
By S. Alex. Covert, Stephanie P. Kula, and Laura A. Simonson
National Gap Analysis Program
The goal of the GAP Analysis Program is to keep common species common by identifying those species and habitats that are not yet adequately represented in the existing matrix of conservation lands. The Gap Analysis Program (GAP) is sponsored by the Biological Resources Discipline of the U.S. Geological Survey (USGS). The Ohio Aquatic GAP (OH-GAP) is a pilot project that is applying the GAP concept to aquatic—specifically, riverine—data. The mission of GAP is to provide regional assessments of the conservation status of native animal species and to facilitate the application of this information to land-management activities. OH-GAP accomplished this through
Gap analysis is a coarse-scale assessment of aquatic
biodiversity and conservation; the goal is to identify gaps in the conservation
of native aquatic species. It is not a substitute for biological field studies
and monitoring programs. Gap analysis was conducted for the continuously flowing
streams in Ohio. Lakes, reservoirs, wetlands, and the Lake Erie islands were not
included in this analysis. The streams in Ohio are in the Lake Erie and Ohio
River watersheds and pass through six of the level III ecoregions defined by
Omernik: the Eastern Corn Belt Plains, Southern Michigan/Northern Indiana
Drift Plains, Huron/Erie Lake Plain, Erie Drift Plains, Interior Plateau, and
the Western Allegheny Plateau.
To characterize the aquatic habitats available to Ohio fish,
crayfish, and bivalves, a classification system needed to be developed and
mapped. The process of classification includes delineation of areas of
relative homogeneity and labeling these areas using categories defined by the
classification system. The variables were linked to the 1:100,000-scale streams
of the National Hydrography Dataset of the USGS. Through
discussions with Ohio aquatic experts, OH-GAP identified eight separate enduring
physical features which, when combined, form the physical habitat type:
Potential distribution models were developed for 130 fish, 70
bivalve, and 17 native crayfish species. These models are based on 5,686 fish,
4,469 crayfish, and 2,899 freshwater bivalve (mussels and clams) sampling
locations, the variables describing the physical habitat types, and variables
indicating the major drainage basins and Omernik’s Level III ecoregion. All potential species distributions are displayed and
analyzed at the 14-digit hydrologic unit (14-HUs), or subwatershed, level.
Mainland Ohio contains 1,749 14-HUs. All statistics and conclusions, as well as
spatial data, are discussed and presented in terms of these units.
The Ohio Aquatic Gap Analysis Project compiled a map of
public and private conservation lands and OH-GAP classified the lands into four
status categories (status 1 through status 4) by the degree of protection
offered based on management practices. A status of 1 denotes the highest, most
permanent level of maintenance, and status 4 represents the lowest level of
biodiversity management, or unknown status. The results of this mapping show
that only about 3.7 percent of the state’s land (4.3 percent if lakes and
reservoirs are also included) is protected for conservation, either publicly or
privately. Of this total, state agencies control about 52 percent, and Federal
agencies control about 29 percent.
Conservation areas that presently protect a portion of Ohio’s
aquatic biodiversity were identified through the analysis of the distributions
of species and conservation lands on a 14-HU scale. In addition, based on
measures of predicted species richness and taxa richness, 75 (out of 504) 14-HUs
in the Lake Erie Basin and 67 (out of 1,291) 14-HUs in the Ohio River Basin were
identified for their conservation potential. Results show that 22 fish species and 2 bivalve species had
predicted distributions exclusive of conservation lands classified as status 1
or status 2. Nine of these fish species are considered rare, threatened, or
endangered in the state. Status 1 and status 2 lands are generally considered by
GAP to offer adequate protection.
The primary factor used by OH-GAP for
identifying potential high-priority conservation areas was species richness.
Because of the known gradient of species diversity, the Lake Erie and Ohio River
Basins were analyzed separately for all taxa. Fifteen percent (75 of 504) of the
14-HUs in the Lake Erie Basin were identified by OH-GAP as high potential
priorities for conservation. Thirty-seven of them already have some conservation
lands located within them. In the Ohio River Basin, 57 of 1,291 14-HUs (4.5
percent) were identified by OH-GAP as potential high-priority conservation areas
for conservation using species richness. Of the 57 14-HUs identified as
potential high-priority conservation areas, 56 percent already have conservation
lands. In both the Lake Erie and Ohio River Basins, a larger, though
not significant, percentage of 14-HUs with existing conservation land were
identified by OH-GAP for their potential for high species richness. It is beyond
the scope of this report to assess whether high-quality habitats were
deliberately protected or whether conservation of habitat has allowed species to
thrive. Because only enduring physical characteristics were used in the models,
it is likely that these habitats were deliberately protected, and this gap
analysis provides further evidence of the habitat quality.
Data Use and Availability
The primary products of the Ohio Aquatic GAP project are
geospatial data for land stewardship, stream-habitat
types, and predicted distribution models for native fish, crayfish, and
bivalves. Associated OH-GAP geospatial data include mapped locations of fish, crayfish, and bivalves.
These data are available from the USGS along with this report.
Executive Summary............................................................................................................................................................... |
1 |
1. Introduction..................................................................................................................................................................... | 5 |
2. Stream Classification and Mapping........................................................................................................................................ | 10 |
3. Predicted Animal Species Distributions and Species Richness...................................................................................................... | 19 |
4. Land Stewardship............................................................................................................................................................... | 49 |
5. Analysis Based on Stewardship and Management Status............................................................................................................ | 64 |
6. Analysis Based on Aquatic Biodiversity.................................................................................................................................... | 80 |
7. Product Use and Availability.................................................................................................................................................. | 118 |
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Executive Summary (48.3 KB) - 4 pages
Main Body [includes Executive Summary] (4.04 MB) - 137 pages
Appendix A - Ohio Stream Classification Codes (69 KB) - 3 pages
Appendix B - Maps of Ecological Drainage Unit (EDU), Major Watersheds, and Level III Ecoregions (202 KB) - 3 pages
Appendix C - Stream physical habitat types (3.98 MB) - 120 pages
Appendix D - Bivalve specimen collectors for the data obtained from the Ohio State University Museum of Biological Diversity (256 KB) - 22 pages
Appendix E - A dichotomous key for categorization of land units, based on biodiversity management, for land-stewardship map (33.1 KB) - 1 page
Appendix F - The dichotomous key for categorization of land units, based on biodiversity management, for land-stewardship map, in flowchart format (30.3 KB) - 1 page
Appendix G - Ohio land stewardship areas in GAP conservation status category 1 and 2 (209 KB) - 11 pages
Appendix H - Stakeholders and consulted experts (28.2 KB) - 1 page
Appendix I - Data and report reviewers (31.4 KB) - 2 pages
Maps of Predicted Fish Distributions (20.5 MB) - 130 pages
Maps of Predicted Crayfish Distributions (2.67 MB) - 17 pages
Maps of Predicted Freshwater Bivalve Distributions (10.8 MB) - 70 pages
Fish Species List 32.6 KB) - 2 pages
Crayfish Species List (18.5 KB) - 1 page
Freshwater Bivalve Species List (26.7 KB) - 2 pages
Downloadable Data | Size zipped | Size unzipped | Contents |
Analysis | 1.10 MB | 3.84 MB | README |
Ancillary | 9.12 MB | 13.4 MB | README |
Habitat | 9.77 MB | 35.2 MB | README |
Modelling | 1.10 GB | 3.23 GB | README |
Stewardship | 4.22 MB | 11.0 MB | README |
Suggested Citation:
Covert, S.A., Kula, S.P., and Simonson, L.A., 2007,
Ohio Aquatic Gap Analysis: An Assessment of the Biodiversity and
Conservation Status of Native Aquatic Animal Species: U.S. Geological
Survey Open-File Report 2006–1385, 509 p.
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