title: Examining the effects of metal mining mixtures on fathead minnow (Pimephales promelas) using field-based multi-trophic artificial streams.
abstract: This study illustrates the use of a mesocosm approach for assessing the independent effects of three treated metal mine effluents (MME) discharging into a common receiving environment and regulated under the same regulation. A field-based, multi-trophic artificial stream study was conducted in August 2008 to assess the effects of three metal mining effluents on fathead minnow (Pimephales promelas) in a 21-day reproduction bioassay. The nature of the approach allowed for assessment of both dietary and waterborne exposure pathways. Elements (e.g. Se, Co, Cl, Cu, Fe) were analyzed in several media (water, sediments) and tissues (biofilm, Chironomus dilutus, female fathead minnow (FHM) body, ovary, liver, gills). Significant increases in metal and micronutrient concentrations were observed in the water and biofilm tissues in all MME treatments [20% surface water effluent (SWE), 30% mine water effluent (MWE), and 45% process water effluent (PWE)], compared to reference. However, copper was the only element to significantly increase in the sediments when exposed to PWE. Co and Ni increased significantly in C. dilutus tissues in SWE (1.4- and 1.5-fold, respectively), Cu and Se also increased in chironomid tissues in PWE (5.2- and 3.3-fold, respectively); however, no significant increases in metals or micronutrients occurred in chironomid tissues when exposed to MWE compared to reference. There were no significant increases in metal concentrations in female FHM tissues (body, liver, gonads, gills) in any of the treatments suggesting that metals were either not bioavailable, lost from the females via the eggs, or naturally regulated through homeostatic mechanisms. Cumulative number of eggs per female per day increased significantly (∼127%) after exposure to SWE and decreased significantly (∼33%) after exposure to PWE when compared to reference. Mean total number of days to hatch was reduced in PWE compared to reference. This study shows the importance of isolating treatment streams in cumulative discharge environments to assess aquatic effects due to the different nature of the effluents.
authors.affiliation: Toxicology Centre, University of Saskatchewan, 44 Campus Drive, Saskatoon, Sask., Canada S7N 5B3. lisa.ramilo@usask.ca
authors.forename: Lisa D
authors.initials: LD
authors.lastname: Rozon-Ramilo
authors.forename: Monique G
authors.initials: MG
authors.lastname: Dubé
authors.forename: Carrie J
authors.initials: CJ
authors.lastname: Rickwood
authors.forename: Som
authors.initials: S
authors.lastname: Niyogi
mesh_terms: D000818:Animals; D001681:Biological Assay; D002683:Chironomidae / Q000254:growth & development / Q000378:metabolism; D003300:Copper / Q000633:toxicity; D003530:Cyprinidae / Q000502:physiology*; D004784:Environmental Monitoring; D005260:Female; D008670:Metals / Q000032:analysis / Q000633:toxicity*; D008906:Mining; D009532:Nickel / Q000633:toxicity; D012098:Reproduction / Q000187:drug effects; D045483:Rivers / Q000737:chemistry; D014874:Water Pollutants, Chemical / Q000032:analysis / Q000633:toxicity*
chemical_list: D008670:Metals; D014874:Water Pollutants, Chemical; D003300:Copper; D009532:Nickel