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Full ecoregional plan - Conservation Gateway

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occurring in the ecoregion were automatically considered primary targets in the<strong>ecoregional</strong> <strong>plan</strong>. In Northeastern <strong>plan</strong>s the number of systems under consideration is afunction of the diversity of varying environmental conditions in the ecoregion and theidiosyncrasies of the system taxonomy. Across all <strong>plan</strong>s the numbers of ecosystems rangefrom 60 to 250 per ecoregion, certainly a manageable set compared to the number ofspecies.Ecosystems and communitiesA source of confusion is the use of the terms: ecosystem, ecological system, community,and natural community. As used in the Northeast these terms are interchangeable with nohard definitions separating their meanings. All the terms refer to a repeatable andrecognizable organization of biodiversity, with a typical species composition, structure,environmental setting and set of sustaining processes.A difference of emphasis is implied in the choice of terms. The term ecosystememphasizes a feature’s structure, environmental setting and sustaining processes,accepting a more generalized species composition. The term community puts moreemphasis on a feature’s specific species composition. In many Northeastern states theterm natural community refers to an inventory unit most similar in concept to anecosystem, since these units are recognized as much by a landscape and environmentalsetting as by a specific composition. Many ecologists conceive of ecosystems as mosaicsof one to several communities that occur together under the same environmentalconditions and controlling processes. These are only conventions, however, and the termsdo not imply a spatial hierarchy, which we discuss below.Our understanding of the ecosystem and community concepts depends on how well wegrasp the dynamics of natural systems and the spatial patterning that develops withinthem. For example, a wetland ecosystem may be composed of relatively distinctvegetation communities with their spatial configuration corresponding to water depth.Understanding the cause of the spatial zonation may add insight into the internaldynamics of the system. However, there is ample evidence that in many systems thedistinctiveness and stability of vegetation communities within the ecosystem is moreapparent than real. In spite of individual preferences for “lumping vs. splitting,”ecologists agree that we should strive to conserve the ecosystem (or, if one prefers, themosaic of communities) as a holistic unit.The term ecosystem also has a variable relationship to the term habitat. Again, thedifference is primarily one of perspective. A freshwater marsh ecosystem is “habitat” formany marsh-breeding species. Moreover, as discussed later in this section, if a specificmarsh ecosystem does not provide habitat for multiple breeding populations of marshbreeding species, then in our analysis it will fail to meet the viability criteria for thatecosystem. Finally, the term habitat is most often defined relative to the needs of aparticular species and may include multiple ecosystem types for breeding, foraging anddispersal.Ecosystems and scaleThe term ecosystem, as used here, does not imply any particular scale of feature. Rather,it focuses on the distinctiveness of the biota, setting and processes that define the system.Floodplain forests, freshwater marshes, peat-forming bogs, fire-adapted forests on coarseREVISED 7/2003COMM-2

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