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MONITORING SALT MARSH VEGETATION AND NEKTON AT GATEWAY NATIONAL RECREATION AREA'S SANDY HOOK UNIT
2010 Summary Report
Natural Resource Data Series NPS/NCBN/NRDS—2011/132
Erika L. Patenaude
Penelope S. Pooler
National Park Service
Northeast Coastal and Barrier Network
University of Rhode Island
1 Greenhouse Rd
Kingston, RI 02881
January 2011
U.S. Department of the Interior
National Park Service
Natural Resource Program Center
Fort Collins, Colorado
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Executive Summary
The Northeast Coastal and Barrier Network (NCBN) is one of 32 networks of parks created by
the National Park Service (NPS) Inventory and Monitoring Program (I&M Program). The I&M
Program has two components, 1) to collect baseline ecological inventory datasets and 2) to
implement Vital Signs monitoring, a long-term ecological monitoring program, in each of the 32
networks. The Northeast Coastal and Barrier Network consists of eight parks linked by
geography and shared ecological characteristics along the Northeastern Atlantic Coast. As part of
the I&M Program, each network has developed detailed protocols for monitoring a select number
of Vital Signs, or ecological indicators. Because the majority of parks in the NCBN are coastal
parks, salt marsh monitoring was chosen as a high priority and protocols were developed for
collecting long-term data on salt marsh vegetation and nekton (James-Pirri and Roman In
Review-a,b). The objective of monitoring vegetation and nekton is to identify long-term trends in
community structure, and to provide resource managers with a better understanding of the
current status and condition of the salt marsh resources they manage.
This report summarizes the first year of vegetation and nekton data collected at Gateway
National Recreation Area’s Sandy Hook Unit (GATE-SHU) in 2010. The salt marsh at GATESHU
is not very extensive, and therefore a complete sample of all salt marsh habitat was conducted. The marsh was delineated into three monitoring sites ranging from approximately 6.5
to 15 ha in size. Monitoring data will be collected at these sites biennially.
Fifty vegetation plots were sampled at each of the three marsh sites in August of 2010. The
percent cover of each vegetation species and non-vegetation cover type within each 1 m2 plot
was visually estimated using a revised Braun-Blanquet method (Kent and Coker 1992). Twentyeight
vegetation species and five non-vegetation cover types were recorded during sampling in
2010. Non-vegetation cover types recorded included wrack & litter, bare ground, rock, water,
and trash. Spartina alterniflora (salt marsh cordgrass) was by far the most abundant and
frequently observed species.
A total of 18 nekton stations were sampled at two marsh sites. The third site was not suitable for
nekton sampling. Nekton in marsh pools (Site 3) and large tidal creeks (Site 1) were sampled
with a 1m2 aluminum throw trap (Kushlan 1981, Sogard & Able 1991, Raposa and Roman
2001). A total of 12 species of nekton were recorded at GATE-SHU in 2010, including eight fish
species, two crab species, and two shrimp species. Examination of percent catch data indicates
that two species account for approximately 95% of all nekton captured. The most prevalent
species, Fundulus heteroclitus (common mummichog), accounts for approximately 59% of all
nekton recorded at GATE-SHU in 2010. The second most common species, Menidia menidia (Atlantic silverside), accounts for approximately 25% of all nekton recorded and was much more
abundant in June than in August. Palaemonetes pugio (daggerblade grass shrimp) accounts for
approximately 11% of all nekton recorded and was more abundant in August. Substantial
differences in abundances and species composition between the two sampling visits are to be
expected and reinforce our decision to sample nekton twice during the summer.
Open the report (1.12 MB)
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