The,mechanisms of arsine (AsH3) toxicity are not completely understood. Stu
dies were undertaken to determine AsH3, and arsenite [As(lll)] toxicity in
a renal tubular epithelial cell line to model kidney dysfunction caused by
AsH3, exposure. The hypothesis was that As(III) is the toxic metabolite res
ponsible for the renal toxicity of AsH3,. There was a concentration- and ti
me-dependent toxic response after As(III) incubation. As(III) produced sign
ificant LDH leakage as early as 1 h and intracellular potassium loss at 5 h
. AsH3, produced no changer in these parameters. AsH3, affected neither pot
assium nor LDH levels over 24 h and up to I mM AsH3, concentration. In this
system, As(III) induced LDH leakage before K+ loss. Oxidative stress-like
toxicity effects were also studied by determining levels of glutathione (GS
H), glutathione disulfide (GSSG), and heat-shock protein 32 (Hsp32) levels.
GSH levels were not markedly affect ed by any arsenical over a 6-h period
or UP to 100 mu M concentration of the arsenical. However, 100 CIM AsH3, si
gnificantly increased GSSG levels as early as 30 min and reached a maximum
at 2.5 h. Incubation with 10 mu M AsH3, was sufficient to significantly inc
rease GSSG levels. As(lll) had no marked effect on GSSC. Both arsenicals (5
0 mu M) produced a slight increase (about threefold) in Hsp32 levels after
4-h incubation. These results showed that unchanged Ast-l, produced oxidati
ve stress-like toxic effects without producing cell death. However, similar
As(III) concentrations induced the stress response and were toxic to the c
ells. These data indicated that AsH3, is not directly toxic to LLC-PK1 cell
s.