Biomonitors can be used to establish geographical and/or temporal vari
ations in the bioavailabilities of heavy metals in the marine environm
ent, offering time-integrated measures of those portions of the total
ambient metal load that are of direct ecotoxicological relevance. Heav
y metal biomonitors need to conform to certain required characteristic
s, not least being metal accumulators, Use of a suite of biomonitors a
llows recognition of the presence and relative magnitude of different
metal sources, For example, a macrophytic alga responds essentially to
dissolved metal sources only, a suspension feeder like a mussel respo
nds to metal sources in dissolved and suspended phases, and a deposit
feeder responds to metal available in the sediment. Examples are given
of suitable heavy metal biomonitors in the coastal waters of Europe,
New Zealand, Hong Kong and China, It is not valid to compare absolute
accumulated metal concentrations in biomonitors interspecifically, alt
hough interspecific comparisions of rank orders do allow cross correla
tions of relative bioavailabilities of heavy metals to different biomo
nitors at the same sites. There is a need to identify widespread cosmo
politan biomonitors to allow intraspecific comparisons of bioavailabil
ities between geographical areas. Such cosmopolitan biomonitors may in
clude the alga Ulva lactuca, mussels of the genera Mytilus and Perna,
the oysters Ostrea and Crassostrea, barnacles Like Balanus amphitrite
and Tetraclita squamosa, and the talitrid amphipod Platorchestia plate
nsis, A major caveat in the use of such cosmopolitan biomonitors remai
ns the need for reliable, specific taxonomic identification.