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Exposure of fish to water of impaired quality has been shown to disrupt the function of the hypothalamo-pituitary-interrenal (HPI) axis and alter the interpretation of data from field studies due to the varying effects of handling and delayed sampling on exposed and reference animals. In the present study, juvenile whitefish, Coregonus lavaretus, were exposed for 6 weeks to diluted (4-8%) untreated and biologically treated bleached kraft mill effluent (BKME) and their response to acute handling was investigated. Liver microsomal EROD activity and glycogen phosphorylase (GPase) activity, in addition to gill Na+-K+-ATPase activity, and blood hemoglobin and hematocrit levels were increased in whitefish exposed for 6 weeks to untreated BKME, whereas those exposed to treated BKME exhibited increased blood hemoglobin and red blood cell K+ concentrations. Both handling procedures, exposure to a shallow water (10 cm, 5 min) and to an air challenge (10 s air/10 s water/30 s air/10 s water/10 s air), resulted in acute physiological stress, as recorded after 5-, 60-, and 120-min recovery periods. Following air exposure, the levels of plasma cortisol, blood glucose, hemoglobin, and hematocrit as well as the liver GPase activity were increased, and liver glycogen concentration decreased in control fish. These responses were attenuated in fish exposed to untreated or treated BKME. Plasma estradiol and testosterone levels were not affected by the BKME exposures or by the air challenge. Handling also resulted in attenuated EROD induction in fish exposed to untreated BKME. According to the present findings, the sensitivity of some widely used cellular and physiological variables may be improved by time-dependent standardization when interpreting data obtained following delayed sampling.

A study was conducted to determine the influence of decontamination on winter flounder living downstream from a pulp and paper mill. The fish and controls were held 8-26 weeks under contaminant-free conditions in aquaria supplied with ambient sea water. Groups of flounder, for comparison, were also sampled near the paper mill at the time of or following autopsy. No differences were apparent in length/organ-weight relationships between depurated and control groups after 26 weeks at 0-6 degrees C, but condition factor, gonadal and hepatosomatic indices, coincident with elevated levels of detoxifying enzymes, differed from field-derived samples. Pathological changes, including hemosiderin deposits in the liver and spleen, decreased, whereas pericholangitis and clear cell foci were apparent in the depurated fish and in the field samples. In two additional groups decontaminated for 8-16 weeks at 6-16 degrees C, there was no evidence of pericholangitis, but hemosiderin deposits persisted and an increase of fibrosis and clear cell foci occurred in contrast to the field group. These results suggest that some tissue repair in the liver transpired primarily during summer while other lesions, such as preneoplastic clear cell foci, which were probably induced prior to depuration, increased, but hemosiderin concentration remained unchanged. The latter observation is consistent with previous studies that suggest that hemosiderin concentration is not seasonally but age influenced.

To determine whether a 7- to 10-d embryo toxicity/teratogenicity test with the inland silverside fish, Menidia beryllina, is a sensitive indicator for evaluation of bleached kraft mill effluents, we compared this test with the Microtox(R) 15-min acute toxicity test and the Ceriodaphnia dubia 7-d chronic toxicity test. Water samples used in each test were collected from three areas in a bleached kraft pulp and paper mill using a 100% chlorine dioxide bleaching process: 1) river water prior to use in the mill; 2) the combined acid/base waste stream from the pulping process prior to biological treatment in the aerated stabilization basin (ASB); and 3) the effluent from the ASB with a retention time of approximately 11 d. Relative toxicity determined by the three tests for each water sampling location was compared. All three toxicity tests were predictive indicators of toxicity; however, the C. dubia and M. beryllina tests were the more similar and sensitive indicators of toxicity. Process water (ASB influent) prior to biological treatment in the ASB was toxic at all concentrations using the Microtox(R) and C. dubia tests. The fish embryo test showed no toxicity at 1% concentrations, slight toxicity at 10%, and acute toxicity at the 100% ASB influent concentration. Tests with biologically-treated ASB effluent indicated a substantial reduction in observed toxicity to Microtox(R) bacteria, C. dubia, and M. beryllina. No toxic responses were observed in any test at a 1% ASB effluent concentration which was the approximate effluent concentration in the receiving river following mixing. No relationship was found among any toxicological response and effluent levels of adsorbable organic halides, polychlorinated phenolic compounds, 2,3,7,8-tetrachlorodibenzo-p-dioxin, 2,3,7,8-tetrachlorodibenzofuran, total suspended solids, color, chemical oxygen demand, or total organic carbon.