Jt. Morris et A. Jensen, THE CARBON BALANCE OF GRAZED AND NONGRAZED SPARTINA-ANGLICA SALT-MARSHES AT SKALLINGEN, DENMARK, Journal of Ecology, 86(2), 1998, pp. 229-242
1 Canopy-level CO2 exchange and biomass were measured monthly for 9 co
nsecutive months during 1990 on grazed and non-grazed portions of a Da
nish salt marsh dominated by Spartina anglica. The empirical measureme
nts were used to calibrate a model of canopy photosynthesis and soil r
espiration that was subsequently integrated to provide estimates of an
nual net ecosystem production (NEP). 2 Standing total and green biomas
s on the non-grazed site reached maxima during September of 1.9 +/- 0.
2 and 1.1 +/- 0.2 kg m(-2) (+/- 1 SD, n = 3), respectively. Correspond
ing maxima (0.8 +/- 0.1 and 0.5 +/- 0.05 kg m(-2)), were achieved duri
ng July at the grazed site. 3 Sediment organic matter as a percentage
of dry weight was 31.6% and 5% at the non-grazed and grazed sites, res
pectively. Accounting for the higher sediment bulk density at the graz
ed site meant that concentrations of organic carbon were 0.027 and 0.0
21 g cm(-3) at non-grazed and grazed sites, respectively. Thus, the fr
action of NEP removed by grazing animals significantly reduced the acc
umulation of sediment organic matter. 4 Estimate of NEP varied between
17 and 38 mol m(-2) year(-1) of carbon at the grazed site and between
5 and 38 mol m(-2) year(-1) at the non-grazed site, depending on assu
mptions about canopy geometry. Soil respiration, 36 mol m(-2) year(-1)
, did not differ between sites. Canopy respiration was less (21 mol m(
-2) year(-1)) at the grazed site than at the non-grazed site (28 mol m
(-2) year(-1)), and accounted for 22-29% and 28-41% of gross photosynt
hesis at grazed and non-grazed sites, respectively. The decrease in ca
nopy respiration compensated the grazed canopy for losses to herbivore
s. 5 A canopy photosynthesis model was used to calculate a theoretical
envelope of canopy biomass, termed the production window, inside of w
hich NEP is positive and outside of which NEP is negative. The product
ion window is bisected by the optimum canopy biomass, which is the the
oretical biomass at which NEP is maximized. The seasonality of NEP is
determined by the trajectory of actual canopy biomass through the prod
uction window. It was shown that canopy biomass on the grazed site was
close to the theoretical optimum biomass late in the season, while th
e non-grazed canopy biomass was supraoptimal.