Ke. Havens et al., Complex interactions between autotrophs in shallow marine and freshwater ecosystems: implications for community responses to nutrient stress, ENVIR POLLU, 113(1), 2001, pp. 95-107
The relative biomass of autotrophs (vascular plants, macroalgae, microphyto
benthos, phytoplankton) in shallow aquatic ecosystems is thought to be cont
rolled by nutrient inputs and underwater irradiance. Widely accepted concep
tual models indicate that this is the case both in marine and freshwater sy
stems. In this paper we examine four case studies and test whether these mo
dels generally apply. We also identify other complex interactions among the
autotrophs that may influence ecosystem response to cultural eutrophicatio
n, The marine case studies focus on macroalgae and its interactions with se
diments and vascular plants. The freshwater case studies focus on interacti
ons between phytoplankton, epiphyton, and benthic microalgae. In Waquoit Ba
y, MA (estuary), controlled experiments documented that blooms of macroalga
e were responsible for the loss of eelgrass beds at nutrient-enriched locat
ions. Macroalgae covered eelgrass and reduced irradiance to the extent that
the plants could not maintain net growth. In Hog Island Bay, VA (estuary),
a dense lawn of macroalgae covered the bottom sediments. There was reduced
sediment-water nitrogen exchange when the algae were actively growing and
high nitrogen release during algal senescence. In Lakes Brobo (West Africa)
and Okechobee (FL), there were dramatic seasonal changes in the biomass an
d phosphorus content of planktonic versus attached algae, and these changes
were coupled with changes in water level and abiotic turbidity. Deeper wat
er and/or greater turbidity favored dominance by phytoplankton. In Lake Bro
bo there also was evidence that phytoplankton growth was stimulated followi
ng a die-off of vascular plants. The ease studies from Waquoit Bay and Lake
Okeechobee support conceptual models of succession from vascular plants to
benthic algae to phytoplankton along gradients of increasing nutrients and
decreasing underwater irradiance. The case studies from Hog Island Bay and
Lake Brobo illustrate additional effects (modified sediment-water nutrient
fluxes, allelopathy or nutrient release during plant senescence) that coul
d Flay a role in ecosystem response to nutrient stress. (C) 2001 Elsevier S
cience Ltd. All rights reserved.