K. Schirmer et al., Use of fish gill cells in culture to evaluate the cytotoxicity and photocytotoxicity of intact and photomodified creosote, ENV TOX CH, 18(6), 1999, pp. 1277-1288
The influence of ultraviolet (UV) irradiation on creosote toxicity was inve
stigated with the rainbow trout (Oncorhynchus mykiss) gill cell line, RTgil
l-W1, and two indicator dyes, alamar Blue(TM) and 5-carboxyfluorescein diac
etate acetoxymethyl ester. These monitor redox potential and membrane integ
rity, respectively. After solubilization and chemical analysis, creosote wa
s presented to cells in the dark to measure cytotoxicity or concurrently wi
th UV irradiation to evaluate photocytotoxicity. Additionally, creosote was
photomodified by 2 h of UV irradiation before presentation to cells in the
dark or together with UV. Cytotoxicity was detected only at high nominal c
reosote concentrations, but photocytoxicity occurred at creosote concentrat
ions 35-fold lower. All the aromatic hydrocarbons in creosote appeared to c
ontribute to cytotoxicity, but photocytotoxicity was due only to the fluora
nthene, pyrene, anthracene, and benzo[a]anthracene in the mixture. Photomod
ified creosote was much more cytotoxic than intact creosote and this differ
ence was most pronounced in the alamar Blue assay. Likely, this was due to
photomodification products that impaired the mitochondrial electron transpo
rt chain. Photomodified creosote was slightly less photocytotoxic than inta
ct creosote. Overall these results indicate that UV irradiation potentially
enhances the toxicity of creosote to fish in several different but signifi
cant ways.