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Effects of nitrogen loading and salt marsh habitate on gross primary production and chlorophyll a in estuaries of Waquoit Bay.

Nixon (1) showed, using comparative data from different systems, that increased nitrogen load to shallow coastal estuaries increased production of phytoplankton. Furthermore, it has been well established that the growth of coastal producers is nitrogen limited (2). In Waquoit Bay, we have a complex of separate estuaries that are subject to different nitrogen loading rates (3). This variation in loading rate provides the opportunity to test, in one system, whether increased nitrogen loads result in increased production.

The range of nitrogen loading to the estuaries extended from a high rate of 8.1 X [10.sup.3] kg N [y.sup.-1] in Childs River to approximately 0.051 kg N [y.sup.-1] in Sage Lot Pond. Because phytoplankton growth in shallow estuaries is nitrogen limited (2), increased loading rates are likely to affect activity and abundance of these primary producers.

Salt marsh habitats are active sites of denitrification and nutrient uptake (2). A strip of salt marsh located between the watershed and the estuary could, therefore, intercept incoming nitrogen and significantly reduce estuarine nitrogen loading. The estuaries of Waquoit Bay are surrounded by different areas of salt marsh. We could, consequently, also evaluate the effects of salt marsh on interception of nitrogen by comparing phytoplankton abundance and activity in estuaries with different extents of fringing salt marsh.

In this paper we ask, first, whether there is a relationship between nitrogen loading rate and phytoplankton abundance and productivity; and second, whether the presence of a salt marsh fringe decreases the nitrogen loading rate and, accordingly, lowers phytoplankton abundance and productivity.

We measured gross primary production (GPP) and chlorophyll a concentration at two stations in each of five estuaries of Waquoit Bay (Childs River, Quashnet River, Jehu Pond, Hamblin Pond, and Sage Lot Pond). We used standard light/dark bottle technique with 5-h in situ incubation period, and the Winkler titration method to determine primary production of the estuaries. Chlorophyll a concentration was measured by the Lorenzen method (4). The nitrogen loading rate was calibrated based on total dissolved nitrogen (DIN) at shore edge, rate of water recharge, and total area of the estuary.

GPP and chlorophyll a increased significantly with higher nitrogen loads (Fig. 1, top panels). For the regression of phytoplankton and loading, P [is less than] 0.003 for both GPP and Chl a. In Childs River, for example, the average chlorophyll a concentration and GPP levels were about three times as high as those in Sage Lot Pond.

Both GPP rates and chlorophyll a concentration decreased in estuaries with larger areas of fringing salt marsh (Fig. 1, middle panels). The cause of this decrease is not well established. The salt marshes could be physically removing phytoplankton from the flooding estuarine water during high tide and, thus, lowering GPP and chlorophyll a. Because tidal ranges reach, at most, 0.5 m in Waquoit Bay, and coverage of vegetation occurs only during a few days of spring tides each month, this mechanism does not seem convincing. More likely, denitrification and storage of watershed-derived nitrogen in salt marshes could be responsible for a sufficient reduction of nitrogen supplies to lower phytoplankton production. Similar results were obtained when we compared GPP or chlorophyll a in relation to the percent of the periphery of each estuary that is composed of salt marsh fringes (Fig. 1, bottom panels).

We therefore conclude that the increase in producer activity due to nitrogen loading from watersheds may be mediated by the extent of salt marsh interposed between land and estuary. Further, salt marshes can decrease the nutrient supply to the estuaries and limit phytoplankton production and chlorophyll a levels.

This work was supported by the WBMLER Research Experience for Undergraduates Grant and by a grant from NOAA Coastal Ocean Studies Program.

Literature Cited

(1.) Nixon, S. 1988. Limnol. Oceanog. 33:1005-1025.

(2.) Howarth, R. W. 1992. Ann. Rev. Ecol. Syst. 19:89-110.

(3.) Valiela, I., et al. 1992. Estuaries 15:443-457.

(4.) Lorenzen, C. J. 1979. Limnol. Oceanog. 24:1117-1120.
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Author:Callaway, David W.; Valiela, Ivan; Foreman, Kenneth; Soucy, Lori A.
Publication:The Biological Bulletin
Date:Oct 1, 1995
Words:665
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