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Gulf of Maine Library Collection
Identification of Important Habitats in
the Lower Casco Bay (Maine) Watershed
Chapter 4. Eelgrass, Cordgrass
Habitats
GENERAL: Eelgrass (Zostera marina) and smooth
cordgrass (Spartina alterniflora) are highly ranked species on
the Gulf of Maine Council's Species List for Identifying Regionally Significant
Habitats. Both are of major ecological importance as structure for marine
and estuarine vertebrates and invertebrates, and as primary producers
of organic matter for coastal food chains. In the current context their
habitats are appraised in purely horticultural terms, their suitability
for growth of these plants; other aspects are considered in the analyses
for fish and wildlife species which share their "community". Accordingly,
the greatest observed density of plant growth is regarded as indicating
the highest value habitat for that species.
SOURCES OF BIOLOGICAL AND SPATIAL DATA: The analysis
relies on National Wetland Inventory (NWI) maps for cordgrass and maps
of eelgrass created by Seth Barker, Maine Department of Marine Resources
(DMR). Eelgrass beds had been identified from true color 1:12,000 aerial
photos, field verified, and digitized from mylar overlays produced from
the photos. Areal coverage of eelgrass (crown densities) were estimated
and assigned to four classes: 0-10%, 10-40%, 40-70%, and 70-100%.
MAPPING OF HABITATS: The cordgrass coverage (CORDGRS4)
was created by selecting all areas from NWI digital maps designated estuarine
intertidal emergent and converting them to grid cell format. Corrections
to the NWI information were made as noted in Chapter 2. We also found
that most of the tidal marshes had pronounced zonation. In marshes having
freshwater tributaries the lowest band was smooth cordgrass, the next
higher a band of saltmeadow hay (Spartina patens), and the highest
was cattail. When such areas of mixed vegetation were dominated by S.
alterniflora, we included the entire NWI polygon in our coverage.
In lieu of information on vigor or biomass, as indicating relative habitat
quality, all areas of cordgrass were assigned an "intermediate" score
of 4 (out of a possible 8, before adjustments for species rank, habitat
abundance, etc.). We did not establish a sensitivity or buffer zone for
this coverage.
The DMR eelgrass coverage was converted to grid cell format (CASEELG6).
Cells having eelgrass were scored 2 to 8 for habitat quality, corresponding
to the density classes originally assigned by Seth Barker.
Figure 4, eelgrass
Figure 5, cordgrass
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