In general, the biological activation of nephrocarcinogenic chlorinated hyd
rocarbons proceeds via conjugation with glutathione. It has mostly been ass
umed that the main site of initial conjugation is the liver, followed by a
mandatory transfer of intermediates to the kidney. It was therefore of inte
rest to study the enzyme activities of subgroups of glutathione transferase
s (GSTs) in renal cancers and the surrounding normal renal tissues of the s
ame individuals (n = 21). For genotyping the individuals with respect to kn
own polymorphic GST isozymes the following substrates with differential spe
cificity were used: 1-chloro-2,4-dinitrobenzene for overall GST activity (e
xcept GST theta); 7-chloro-4-nitrobenzo-2-oxa-1,3-diazole for GST alpha; 1,
2-dichloro-4-nitro-benzene for GST mu; ethacrynic acid and 4-vinylpyridine
for GST pi; and methyl chloride for GST theta. In general, the normal tissu
es were able to metabolize the test substrates. A general decrease in indiv
idual GST enzyme activities was apparent in the course of cancerization, an
d in some (exceptional) cases individual activities, expressed in the norma
l renal tissue, were lost in the tumour tissue. The GST enzyme activities i
n tumours were independent of tumour stage, or the age and gender of the pa
tients. There was little influence of known polymorphisms of GSTM1, GSTM3 a
nd GSTP1 upon the activities towards the test substrates, whereas the influ
ence of GSTT1 polymorphism on the activity towards methyl chloride was stra
ightforward. In general, the present findings support the concept that the
initial GST-dependent bioactivation step of nephrocarcinogenic chlorinated
hydrocarbons may take place in the kidney itself. This should be a consider
ation in toxicokinetic modelling.