TOMALES BAY METABOLISM - C-N-P STOICHIOMETRY AND ECOSYSTEM HETEROTROPHY AT THE LAND SEA INTERFACE

被引:120
作者
SMITH, SV
HOLLIBAUGH, JT
DOLLAR, SJ
VINK, S
机构
[1] SAN FRANCISCO STATE UNIV,TIBURON CTR,TIBURON,CA 94920
[2] UNIV HAWAII MANOA,HAWAII INST MARINE BIOL,HONOLULU,HI 96822
基金
美国国家科学基金会;
关键词
CARBON; NITROGEN; PHOSPHORUS; NET METABOLISM; BUDGETS; CYCLING; ESTUARIES; CALIFORNIA COAST;
D O I
10.1016/0272-7714(91)90055-G
中图分类号
Q17 [水生生物学];
学科分类号
071004 ;
摘要
Bays and estuaries receive inputs from the adjacent land and exchange materials with the coastal ocean. Net system metabolism records the role of such land-sea interface ecosystems in altering the chemical state of essential plant nutrients. Water and salt budgets have been constructed for Tomales Bay, California, in order to estimate water advective and mixing exchange rates between the bay and coastal ocean over 2 years. Net non-conservative fluxes of dissolved P, N and C were calculated. The bay is a net source for dissolved P, C and total alkalinity, and is a net sink for dissolved fixed N. Stoichiometric analysis can be used to interpret the non-conservative nutrient fluxes. The dissolved P source is interpreted to be the result of net oxidation of approximately 10 mmol organic C m-2 day-1. CO2 released by this oxidation largely escapes to the atmosphere. This net respiration is about 12% of the total system respiration. Most dissolved inorganic N liberated during the oxidation is not exported hydrographically; rather, the bay is a net sink of dissolved fixed N. This N is assumed to be lost from the water via denitrification (3·2 mmol m-2 day-1). Sulphate reduction (5·1 mmol m-2 day-1) is also an important component of respiration in this system. Denitrification is a minor component of gross C metabolism, but is the major sink of N in this system. The organic matter driving this net heterotrophy may be of either terrestrial or marine origin. © 1991.
引用
收藏
页码:223 / 257
页数:35
相关论文
共 49 条
[1]  
[Anonymous], 1934, J JOHNSTONE MEMORIAL
[3]   CARBONATE ALKALINITY IN PORE WATERS OF ANOXIC MARINE SEDIMENTS [J].
BERNER, RA ;
SCOTT, MR ;
THOMLINSON, C .
LIMNOLOGY AND OCEANOGRAPHY, 1970, 15 (04) :544-+
[4]  
BERNER RA, 1989, PALAEOGEOGR PALAEOCL, V75, P97, DOI DOI 10.1016/0031-0182(89)90186-7
[5]   ALKALINITY CHANGES GENERATED BY PHYTOPLANKTON GROWTH [J].
BREWER, PG ;
GOLDMAN, JC .
LIMNOLOGY AND OCEANOGRAPHY, 1976, 21 (01) :108-117
[6]  
Bunt J.S., 1975, PRIMARY PRODUCTIVITY, V14, DOI [DOI 10.1007/978-3-642-80913-2_8, 10.1007/978-3-642-80913-2_8]
[8]  
DOLLAR SJ, 1991, UNPUB MARINE ECOLOGY
[9]   PHYTOPLANKTON PRODUCTION AND SEASONAL BIOMASS VARIATION OF SEAGRASS, RUPPIA-MARITIMA L, IN A TROPICAL MEXICAN LAGOON WITH AN EPHEMERAL INLET [J].
FLORESVERDUGO, FJ ;
DAY, JW ;
MEE, L ;
BRISENODUENAS, R .
ESTUARIES, 1988, 11 (01) :51-56
[10]   THE CHEMICAL CONTROL OF SOLUBLE PHOSPHORUS IN THE AMAZON ESTUARY [J].
FOX, LE ;
SAGER, SL ;
WOFSY, SC .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1986, 50 (05) :783-794