Full ecoregional plan - Conservation Gateway
Full ecoregional plan - Conservation Gateway Full ecoregional plan - Conservation Gateway
Connectivity GoalsConnectivity of aquatic ecological systems is based on the absence of physical barriers tomigration or water flow. Connectivity is of critical importance for viable regional andintermediate-scale fish and community targets and for maintaining processes dependent on watervolume and flooding. The regional scale connectivity goal was to provide at least one “focusnetwork” of connected aquatic ecological systems from headwaters to large river mouth for eachsize 3 river type where a regional wide-ranging species was present. A secondary intermediatescale connectivity goal was to provide the best pattern of connectivity for intermediate-scalepotadromous fish, intermediate scale communities, and processes. The goal for theseintermediate scale targets was to provide at least one connected suite of headwaters to mediumsized river. Again, here the focus was on functional connections at the mouth of a size 2 riverand some functional connections from the size 2 to its size 1 tributaries.Assessing ViabilityViability refers to the ability of a species to persist for many generations or an AquaticEcological System to persist over some specified time period. In aquatic ecosystems, viability isoften evaluated in the literature by a related term “biotic integrity”. Biotic integrity is defined asthe ability of a community to support and maintain a balanced, integrated, adaptive communityof organisms having species compositions, diversity, and functional organization comparable tothat of a natural habitat of the region. 19A myriad of anthropogenic factors contribute to lower viability and biologic integrity of aquaticsystems. Dams and other hydrologic alteration, water quality degradation from land use change,and introduced species all have well documented negative impacts on the structure andfunctioning of aquatic ecosystems. Dams alter the structure and ecosystem functioning by 1)creating barriers to upstream and downstream migration, 2) setting up a series of changesupstream and downstream from the impoundment including changes in flow, temperature, waterclarity; and 3) severing terrestrial/aquatic linkages critical for maintaining the riparian andfloodplain communities. The spread of human settlement has intensified agriculture, roadbuilding, timber harvest, draining of wetlands, removal of riparian vegetation, and released manyharmful chemicals into the environment. This land use alteration has led aquatic habitats tobecome fragmented and degraded through increased sedimentation, flow and temperature regimealteration, eutrophication, and chemical contamination. Introduced nonindigenous species havealso had negative impacts as they compete with indigenous species for food and habitat, reducenative populations by predation, transmit diseases or parasites, hybridize, and alter habitat.Introductions and expansions of nonindigenous species are causing an increasing threat toaquatic systems and are usually extremely difficult if not impossible to undo.Quality AssessmentAssessing the viability and condition of the coarse scale watershed system targets presented aunique challenge. In the Northeast U.S., State level Index of Biotic Integrity ranks and datasetsonly exist in Pennsylvania and Maryland, and even these focus only on wadeable rivers.Although some water quality and biomonitoring data existed in various states, this informationwas not readily available or in a standardized comparable format across states. Viabilitythresholds for condition variables related to the biological functioning of aquatic ecosystems19 Moyle and Randal 1998REVISED 7/2003AQUA-9
have also not been extensively researched and developed, with the exception of impervioussurface thresholds. There was also limited time and funding to compile and analyze existinginstream sample data and its relation to the intactness and functioning of aquatic ecosystems.Given these challenges, a two phase approach was taken. First, available spatial data was used toperform a GIS condition screening analysis to rank all watersheds and individual streamsegments according to landscape factors that previous research has shown are correlated withbiological integrity of aquatic communities. 20 Second, this preliminary assessment was refinedand expanded during a series of expert interviews conducted with scientists and resourcemanagers across the planning region. Experts were asked to comment on the TNC aquaticclassification, identify threats and local conditions that were not modeled in the GIS screening,and highlight location of best examples of high-quality aquatic sites in the ecoregion.The GIS screening analysis was used as a surrogate, but standardized, method of evaluatingcurrent condition of the aquatic ecosystems. It used landscape variables such as percentdeveloped land, road density, density of road/stream crossings, percent agriculture, dam density,dam storage capacity, drinking water supply density, and point source density. These variableswere divided into three generally non-correlated impact categories 1) Land cover and RoadImpact to represent changes in permeable surfaces and other threats from roads, urbanization, oragriculture; 2) Dam and Drinking Water Supply Impacts to represent changes in hydrologicregime and migration barriers from dams; and 3) Point Source Impact to represent potential pointsource chemical alteration threats.Ordinations were run on a subset of variables in the Land cover and Road Impact, Dam andDrinking Water Supply Impact, and Point Source Impact categories to develop a rank for eachsize 2 watershed in each impact category. The ordination ranks were used to highlight the mostintact watershed examples within each watershed system type. Three variables, percentdeveloped land, percent agriculture land, and total road density per watershed area, were alsoused to develop a simplified overall “landscape context” rank for each size 2 watershed. SeeTable 3 for the landscape context component rank criteria. The overall Landscape Contextwatershed rank was determined by worst individual component category score. 21Table 3: Watershed Landscape Context RankingLandscape Context RankingsRank %Developed % Agriculture Road Density(mi.rd./sq.mi. watershed1 15%At the aquatic expert interviews, experts at the state level were engaged for information on localconditions that could not be modeled in a GIS such as stocking, channelization, introduced20 Fitzhugh 200021 For more information on the reach and watershed level condition variables and statistical ranking analysis, seeOlivero 2003.REVISED 7/2003AQUA-10
- Page 29 and 30: and distribution pattern for each e
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- Page 37 and 38: systems. Conversely, high elevation
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- Page 41 and 42: Results for Terrestrial Communities
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- Page 65 and 66: MATRIX SITE:NAME:STATE/S:SIZE:Total
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Connectivity GoalsConnectivity of aquatic ecological systems is based on the absence of physical barriers tomigration or water flow. Connectivity is of critical importance for viable regional andintermediate-scale fish and community targets and for maintaining processes dependent on watervolume and flooding. The regional scale connectivity goal was to provide at least one “focusnetwork” of connected aquatic ecological systems from headwaters to large river mouth for eachsize 3 river type where a regional wide-ranging species was present. A secondary intermediatescale connectivity goal was to provide the best pattern of connectivity for intermediate-scalepotadromous fish, intermediate scale communities, and processes. The goal for theseintermediate scale targets was to provide at least one connected suite of headwaters to mediumsized river. Again, here the focus was on functional connections at the mouth of a size 2 riverand some functional connections from the size 2 to its size 1 tributaries.Assessing ViabilityViability refers to the ability of a species to persist for many generations or an AquaticEcological System to persist over some specified time period. In aquatic ecosystems, viability isoften evaluated in the literature by a related term “biotic integrity”. Biotic integrity is defined asthe ability of a community to support and maintain a balanced, integrated, adaptive communityof organisms having species compositions, diversity, and functional organization comparable tothat of a natural habitat of the region. 19A myriad of anthropogenic factors contribute to lower viability and biologic integrity of aquaticsystems. Dams and other hydrologic alteration, water quality degradation from land use change,and introduced species all have well documented negative impacts on the structure andfunctioning of aquatic ecosystems. Dams alter the structure and ecosystem functioning by 1)creating barriers to upstream and downstream migration, 2) setting up a series of changesupstream and downstream from the impoundment including changes in flow, temperature, waterclarity; and 3) severing terrestrial/aquatic linkages critical for maintaining the riparian andfloodplain communities. The spread of human settlement has intensified agriculture, roadbuilding, timber harvest, draining of wetlands, removal of riparian vegetation, and released manyharmful chemicals into the environment. This land use alteration has led aquatic habitats tobecome fragmented and degraded through increased sedimentation, flow and temperature regimealteration, eutrophication, and chemical contamination. Introduced nonindigenous species havealso had negative impacts as they compete with indigenous species for food and habitat, reducenative populations by predation, transmit diseases or parasites, hybridize, and alter habitat.Introductions and expansions of nonindigenous species are causing an increasing threat toaquatic systems and are usually extremely difficult if not impossible to undo.Quality AssessmentAssessing the viability and condition of the coarse scale watershed system targets presented aunique challenge. In the Northeast U.S., State level Index of Biotic Integrity ranks and datasetsonly exist in Pennsylvania and Maryland, and even these focus only on wadeable rivers.Although some water quality and biomonitoring data existed in various states, this informationwas not readily available or in a standardized comparable format across states. Viabilitythresholds for condition variables related to the biological functioning of aquatic ecosystems19 Moyle and Randal 1998REVISED 7/2003AQUA-9