Hormesis is a widespread phenomenon across many taxa and chemicals, and, at
the single species level, issues regarding the application of hormesis to
human health and ecological risk assessment are similar. For example, convi
ncing the public of a 'beneficial' effect of environmental chemicals may be
problematic, and the design and analysis of laboratory studies may require
modifications to detect hormesis. However, interpreting the significance o
f hormesis for even a single species in an ecological risk assessment can b
e complicated by considerations of competition with other species, predatio
n effects, etc. Ecological risk assessments involve more than a single spec
ies; they may involve communities of hundreds or thousands of species as we
ll as a range of ecological processes. Applying hermetic adjustments to thr
eshold effect levels for chemicals derived from sensitivity distributions f
or a large number of species is impractical. For ecological risks, chemical
stressors are frequently of lessor concern than physical stressors such as
habitat alteration or biological stressors such as introduced species, but
the relevance of hormesis to non-chemical stressors is unclear. Although e
cological theories such as the intermediate disturbance hypothesis offer so
me intriguing similarities between chemical hormesis and hermetic-like resp
onses resulting from physical disturbances, mechanistic explanations are la
cking. Further exploration of the relevance of hormesis to ecological risk
assessment is desirable. Aspects deserving additional attention include dev
eloping a better understanding of the hermetic effects of chemical mixtures
, the relevance of hormesis to physical and biological stressors and the de
velopment of criteria for determining when hormesis is likely to be relevan
t to ecological risk assessments.