Sensitivity of Atlantic salmon (Salmo salar) to dietary endosulfan as assessed by haematology, blood biochemistry, and growth parameters.

The presence of the organochlorine pesticide endosulfan in the water column confers a significant direct risk to the biota therein, yet relatively little is known regarding the toxic impact of dietborne endosulfan to aquatic organisms. Pre-smolt Atlantic salmon (Salmo salar) were fed at levels of technical endosulfan equal to the European Union regulatory limit (5 microg kg(-1)) and at levels 10 and 100 times greater, for a total of 49 days with haematology (e.g. erythrocyte count, haemoglobin, haematocrit, white blood cell composition), blood biochemistry (e.g. serum aminotransferase, plasma ions) and growth parameters (e.g. condition factor) recorded at days 0, 14, 35, and 49. Toxicological assessment of the individual alpha and beta-isomers that comprise technical endosulfan was also attempted. No mortality was observed in any group during the experiment. In the groups exposed to the control, 5, and 50 microg kg(-1) technical endosulfan feeds no significant alterations in any measured parameters were determined at any time point. No differences were observed between the technical mixture and the individual alpha and beta-isomer treatment groups. Condition factor was significantly reduced in fish exposed to 500 microg kg(-1) at day 49, while haematocrit, haemoglobin and mean corpuscular haemoglobin were significantly elevated after 35 days of exposure to the same dietary level, but returned to control levels by day 49. The present study shows that with regards to acute toxicity, Atlantic salmon are able to tolerate dietary technical endosulfan levels up to 500 microg kg(-1).

Treatment of creosote-contaminated groundwater in a peat/sand permeable barrier--a column study.

A column study was conducted to determine if a permeable barrier can be used to treat creosote-contaminated groundwater based on sorption and biodegradation, and to determine which processes remove the various creosote compounds. Creosote-contaminated water (sterile and non-sterile) was applied to sterile and non-sterile saturated columns with peat (20 vol.%) and sand (80 vol.%) for 2 months. Temperature was 9 degrees C, inlet oxygen concentration 9-10mg/l and average residence time was two days. The peat/sand barrier material removed 94-100% polycyclic aromatic hydrocarbons (PAHs), 93-98% nitrogen/sulfur/oxygen (NSO)-containing heterocyclic aromatic compounds, and 44-97% total phenols. The peat/sand material efficiently sorbed PAHs (>2 rings) and three-ring NSO-compounds, and also sorbed significant amounts of two-ring NSO-compounds and naphthalene. Naphthalene and NSO-compounds not sorbed were biological degraded. Phenol and cresols were efficiently removed by microbial degradation. The barrier material was somewhat less efficient removing dimethylphenols (DMPs) and trimethylphenols (TMPs), where DMPs were hardly sorbed and TMPs were hardly degraded. The results imply that a peat/sand barrier can treat creosote-contaminated groundwater. Modifications might be needed for enhanced removal of DMPs and TMPs, and oxygen supply might be necessary in aquifers with low oxygen content.