Jwtj. Lemmens et al., FILTERING CAPACITY OF SEAGRASS MEADOWS AND OTHER HABITATS OF COCKBURNSOUND, WESTERN-AUSTRALIA, Marine ecology. Progress series, 143(1-3), 1996, pp. 187-200
Macro-suspension-feeders (predominantly ascidians, sponges, bivalves)
and epifaunal suspension-feeders (hydroids, spirorbids, bryozoans, bar
nacles, amphipods) in Posidonia meadows of Cockburn Sound, Western Aus
tralia, demonstrate a clear spatial distribution. Although this may be
due to a number of environmental variables, this compares well with s
patial patterns in phytoplankton levels, which are relatively high in
Cockburn Sound (0.94 to 2.66 g chlorophyll a l(-1)) and are generally
highest at the southeastern boundary. Macro-suspension-feeder biomass
was high in Posidonia meadows (28.6 to 41.3 g AFDW m(-2) at the southe
astern boundary, 9.6 to 15.4 g AFDW m(-2) at other sites) and generall
y lower in bare sediment (0.2 to 9.3 g AFDW m(-2)), although on bare s
ediment of the Southern Flats (a site in the southwest) the introduced
polychaete Sabella spallanzanii reaches considerable biomass (458.9 g
AFDW m(-2)). Heterozostera (1.2 g AFDW m(-2)) and Amphibolis meadows
(2.3 g AFDW m(-2)) were found at only 1 site each, but appear to suppo
rt a low biomass of macro-suspension-feeders. Epifaunal suspension-fee
ders on Posidonia leaves (hydroids, bryozoans, spirorbids, barnacles,
corophiid amphipods) reached a substantial biomass (2.3 x 10(6) feedin
g units m(-2) at the southeastern site; 0.6 to 0.7 x 10(6) units m(-2)
at other sites; 'feeding units' refers to individual polyps, zooids,
etc.). Amphibolis leaves supported similar numbers of epifaunal suspen
sion-feeders (0.7 x 10(6) units m(-2)) but Heterozostera supported far
lower numbers (80 x 10(3) units m(-2)). Initial estimates indicate th
at the suspension feeding assemblages associated with Posidonia and Am
phibolis meadows in Cockburn Sound are potentially able to filter the
overlying water column daily, and may partially control local densitie
s of suspended organic matter. Filtration rates in unvegetated and Het
erozostera habitats are orders of magnitude lower, so benthic inverteb
rate control of suspended particles in these habitats is unlikely. How
ever, habitats dominated by the introduced polychaete S. spallanzanii,
which has colonised large areas in Cockburn Sound where seagrass mead
ows have disappeared, have a filtering capacity of at least the same o
rder of magnitude as that of the seagrass meadows they have replaced.