Populations of microcrustaceans were studied for 24 months in two New
Jersey high salt marsh impoundments, and in three separate 14 month st
udies of high salt marsh pools in northeastern Massachusetts. In Massa
chusetts high marsh pools, dominants were all harpacticoids: Amphiascu
s pallidus, Cletocamptus deitersi, Harpacticus chelifer, Mesochra lill
jeborgii, Metis jousseaumei, and Nitokra lacustris. The cyclopoids Apo
cyclops spartinus, Halicyclops sp. and the calanoid Eurytemora affinis
were also numerically important. While there was extensive overlap, d
ominants varied to some extent from year to year and among the three s
tudies. The New Jersey saline impoundment fauna showed extreme dominan
ce (low equitability) in the first summer, somewhat less in the second
and much less in the third. Total microcrustacean densities also decl
ined each year. Variation in Apocyclops spartinus densities was the ma
jor factor, as this species comprised in three consecutive summers, 95
, 85 and 51% of the total zooplankton at one station. Diversity as spe
cies richness was highest in a New Jersey freshwater impoundment which
compared well with South Carolina salt marsh values. Impoundment dive
rsity which was very low, and comparable with that found in a New Jers
ey Spartina patens marsh, increased each year becoming progressively m
ore like that found in the Massachusetts pools. Vegetation changed sig
nificantly in the New Jersey impoundments over the three years. Sparti
na patens died-off in the first summer, while S. alterniflora graduall
y declined each year. A visit to the site twenty years later showed al
l emergent vegetation to be gone. These successional zooplankton and v
egetation changes, together with the possible consequences of interrup
ted marsh-bay exchanges should be considered before undertaking any co
astal mosquito control involving permanent flooding.