RESISTANCE TO DIFFERENT GASOLINE AND OTHER PETROLEUM-HYDROCARBON DERIVATES IN Cnesterodon decemmaculatus (PISCES, CYPRINODONTIFORMS)
Keywords:
petroleum-hydrocarbons, gasoline, ecotoxicology, bioassay, Cyprinodontiforms, Cnesterodon decemmaculatusAbstract
Following the “maximum critical” (MC) technique, the resistance to different gasoline and petroleum-hydrocarbon derivates in Cnesterodon decemmaculatus was studied. Additional bioassays were carried out in Poecilia reticulata and Jenynsia lineata. The average values (MC) obtained in C. decemmaculatus in decreasing order (standard deviation in brackets) were: Super gasoline 98 octane: 1.1 (0.32); Super gasoline 95 octane: 1.3 (0.26); Common gasoline 85 octane: 2.3 (1.33); Fuel-jet 100-130 octane: 4.1 (0.58); Aerokerosene JetA-1: >7 and Diesel oil: >7 cc/l. Using common gasoline , the differences between the MC in C. decemmaculatus, P. reticulata and J. lineata were not significant (F= 2.088; p>0.05), a general mean MC value of 2.8 cc/l (0.43) could be considered. MC values of C. decemmaculatus, with common gasoline at different water salinity (S range: 0.005 to 36.45 gr/l), were significativaly correlated with salinity (r=0.836; p<0.05). Also regression analysis was significative (p<0.05; n= 10; R2= 69.85%), the relationship between variables was: MC= exp(0.850+S.-0.027). These data are useful on an environmental impact assessment, to generate comparative data with other bioindicator cyprinodontids and to apply in monitoring programs.
Downloads
References
BECKER C.D. & GENOWAY R.G. 1979. Evaluation of the critical thermal maximum for determining thermal tolerance of freshwater fish. Env. Biol. Fish 4(3):245-246.
BUCHER E.H., BONETTO A.A., BOYLE T., CANEVARI P., CASTRO G., HUSZAR P. y STONE T. 1993. Hidrovía. Un exámen ambiental inicial de la vía fluvial Paraguay-Paraná. Humedales para las Américas, Manomet, Massachussetts, USA y Bs. As., Argentina: 74 pp.
CASSARA C., GOMEZ S.E., GIUSTO A., FERRIZ R.A. y ASIKIAN V. 1999. Resistencia a diversos tóxicos y anestésicos en Poecilia reticulata Peters, 1859. Bioikos, 13 (1/2):29-39.
COPPOLA A. 1994. Contaminación acuática por hidrocarburos. Anales de la Sociedad Científica Argentina, 224(2): 35-42.
DAS P.K.M.N. & KONAR S.K. 1988. Acute toxicity of petroleum products, crude oil and oil refinery effluent on plankton, benthic invertebrates and fish. Environ. Ecol. 6(4): 885-891.
DE LA TORRE F.R., DEMICHELIS S.O., FERRARI L. & SALIBIAN A. 1997. Toxicity of Reconquista river water: bioassays with juvenile Cnesterodon decemmaculatus. Bull. Environ. Contam. Toxicol., 58:558- 565.
DE LA TORRE F.R., FERRARI L. & SALIBIAN A. 2002. Freshwater pollution biomarker: response of brain acetyl- cholinesterase activity in two fish species. Comp.Biochem. Physiol., 131 C (3): 271-280.
GARCIA M.E, DEMICHELIS S.O, DE LA TORRE F.R. & FERRARI L. 1998. Freshwater toxicity to Cnesterodon sp: biossays with water from the Reconquista River. Verh. Internat. Verein. Limnol., 26:1216-1218.
GIUSTO A., GOMEZ S.E., CASSARA C. y FERRIZ R.A. 1998. Resistencia a la temperatura y salinidad en Poecilia reticulata Peters, 1859. Bioikos, 12(2):45-52.
GOMEZ S.E. 1996. Resistenza alla temperatura e salinitá in pesci della Provincia di Buenos Aires (Argentina), con implicazioni zoogeografiche. En: Atti Congressuali, IV Convegno Nazionale Associazione Italiana Icttiologi Acque Dolci, Trento, Italia (1991):171:192.
GOMEZ S.E. y TORESANI N.I. 1998. Las Pampas. En: Los Humedales de la Argentina. (Cap. 3:97-113) Canevari P., D. Blanco, E. Bucher, G. Castro y Y. Davison (eds.), Wetlands International, Publ. 46, Buenos Aires, 208 pp.
HEATH, A.G. 1995. Water pollution and fish physiology. Second edition. Lewis Publishers, Florida, 359 pp.
JONES J.R.E. 1964. Fish and river pollution. Butterworth Inc., Washington. 203 pp.
JOHNSTON R. 1977. What north sea oil might cost fisheries. Rapp. P. -v. Réun. Cons. Int. Explor. Mer.,171: 212-223.
LOCKHART W.L., METNER D.A., MURRAY D.A.J. & MUIR D.C.G. 1987. Hydrocarbons and complaints about fish quality in the Mackenzie River, Northwest Territories, Canada. Water Pollution Research Journal of Canada, 22(4):616-628.
MACKIE P.R., McGILL A.S. & HARDY R. 1972. Diesel oil contamination of brown trout (Salmo trutta). Environmental Pollution, 3(1):9-16.
PALADINO F.V., SPOTILA J.R., SCHUBAUER J.P. & KOWALSKI K.T. 1980. The critical thermal maximum: a technique used to elucidate physiological stress and adaptation in fishes. Rev. Can. Biol. 39:115-122.
RAVINDRAN K. 1988. Effect of petroleum hydrocarbon toluene on some oxidoreductase systems of freshwater fisk Tilapia mossambica. Environ. Ecol. 6(3): 705-708.
RINGUELET R.A. 1967. Contaminación o polución del ambiente acuático con referencia especial a la que afecta el área Platense. Agro. 9(15):5-33.
RINGUELET R.A. 1971. La polución o contaminación de origen industrial del Delta Bonaerense. Trab. Téc. Dir.de Recursos Pesqueros Pcia. de Buenos Aires (M.A.A),1: 1-41.
RINGUELET R.A., ARAMBURU R.H. y ALONSO DE ARAMBURU A. 1967. Los peces Argentinos de agua dulce. CIC, La Plata, 622 pp.
VILLAR C.A., GOMEZ S.E & BENTOS C.A. 2000. Lethal concentration of Cooper in the neotropical fish Cnesterodon decemmaculatus (Pisces, Cyprinodontiformes). Bull. Environ. Contam. Toxicol., 65(4):465-469.