Numerous anthropogenic chemicals of environmental concern-including some ph
enoxy acid herbicides, organophosphorus insecticides, polychlorinated biphe
nyls, phthalates, freon substitutes and some DDT derivatives-are chiral. Th
eir potential biological effects, such as toxicity, mutagenicity, carcinoge
nicity, and endocrine disrupter activity, are generally enantiomer-selectiv
e, and different enantiomers are preferentially degraded (transformed) by m
icro-organisms in various environments(1-8). Here we use field and laborato
ry experiments to demonstrate that environmental changes in soils can alter
these preferences, and to suggest that the preferences shift owing to diff
erent groups of related microbial genotypes being activated by different en
vironmental changes. In Brazilian soils, almost all pasture samples prefere
ntially transformed the non-herbicidal enantiomer of dichlorprop ((RS)-2-(2
,4-dichlorophenoxy)propionic acid), while most forest samples either transf
ormed the herbicidal enantiomer more readily or as rapidly as the non-herbi
cidal enantiomer. Organic nutrient enrichments shifted enantioselectivity f
or methyl dichlorprop ((RS)-methyl 2-(2,4-dichlorophenoxy)propionic acid) s
trongly towards preferentially removing the non-herbicidal enantiomer in so
ils from Brazil and North America, potentially increasing phytotoxicity of
its residues relative to that of the racemate. Assessments of the risks che
mical pollutants pose to public health and the environment need to take int
o account the chiral selectivity of microbial transformation processes and
their alteration by environmental changes, especially for pesticides as up
to 25 per cent are chiral(9).