IDOWU, Rachel Toyisi et al.15Burkina Faso. Pages 29 – 55. In:Hydrobiological aspects <strong>of</strong> fisheries insmall reservoirs in the sahel region.Technical centre for Agricultural andRural Cooperation, Wageningen,Netherlands.BANKOLE, N. O., SULE, O. D., OKWUNDU, E. C.and AMADI M. (1994). Preliminaryinvestigation on the frame and catchassessment survey <strong>of</strong> Alau reservoir,Annual Report <strong>of</strong> NIFFRI 28 p.BOYD, C .E. (1979). Water quality in warmwater ponds. Craft Master Print. Inc.Auburn Alabama 353 pp.CALAMARI, D. and CHIAUDARI, G. (1984).Problems and methods in definingwater quality criteria <strong>of</strong> micro pollutantsin aquatic ecosystems. Pages 302 –320. In: Proceedings <strong>of</strong> the thirdconference <strong>of</strong> prevention by substancesderived <strong>from</strong> wastes, Rome.CBDA (1986). A resettlement plan for the Alaureservoir dam and Jere bowl scheme.Report submitted to Chad BasinDevelopment Authority. AskoningNigerian Limited, 59 pp.DEJOUX, C. (1988). La pollution des eauxcontinental africines. Experienceacquice situation actuelle etperspectives. Trav. Doc .inst. fr. Rech.Sci. Dev. Coop., 213: 513.DENINGER, R. A. (1981). A water quality indexfor rivers and lakes. WaterInternational, 5(3): 16 - 21.FORSTNER V. and WITTMAN G. T. (1981).Metal pollution in the aquaticenvironment. 2 nd Edition. Berlin.Spriner. 486 pp.GESAMP (Joint Group <strong>of</strong> Experts on thescientific Aspect <strong>of</strong> Marine pollution)(1988). Review <strong>of</strong> potentially harmfulsubstances. Rep. Stup. GESAMP, 28: 17p.GODBERG. E.D. (1976). The health o f theocean. Paris, UNESCO 172 p.KAKULU, S. E. and OSIBANJO, O. (1987).Comparison <strong>of</strong> digestion methods fortrace metal determination in fish.International Journal EnvironmentalStudies, 13: 247 - 251.KAKULU, S. E. and OSIBANJO, O. (1992):Pollution studies <strong>of</strong> Nigeria rivers: Tracelevels <strong>of</strong> surface water in the NigerDelta area. International JournalEnvironmental Studies, 41: 287 - 292.MACKERETH, F. J. and HERON, J. J. F. (1978).Water analysis. Some revised methodsfor limnologist. Fresh water BiologicalAssociation scientific publication, 36:112p.MOMBESHORA, C. O., OSIBANJO, O. and AJAYI,S. O. (1987). Pollution studies onNigeria rivers. The on sit <strong>of</strong> leadpollution <strong>of</strong> surface water in Ibadan.Environment International, 9: 81 - 84.NRIAGU, J. O. (1989). Trace metals in lakes.International conference on tracemetals in lakes. Hamilton, OntarioScience.ODIETE W. O. (1999). Environmental physiology<strong>of</strong> animals and pollution. DiversifiedPublisher Limited, Lagos. 261 pp.ODUNZE, F. C., AMOJOBI, R. and NTAKIGM, R.T. (1995). Preliminary fisheries survey<strong>of</strong> Alau reservoir Maiduguri. Paperpresented a t the workshop onsustenance management andconservation <strong>of</strong> fisheries and otheraquatic resources <strong>of</strong> lake Chad and thesahel zone <strong>of</strong> Nigeria. Held on the 16 th–17 th January. 10 pp.OKOYE. B. C. O., AFOLABI, O. A. and AJAO, E.A. (1991). Heavy metals in the Lagoslagoon sediments. International Journal<strong>of</strong> Environmental Studies, 37: 35 - 41.OLSEN R. D. (1975): The phytoplankton ecology<strong>of</strong> a desert lake. PhD Dissertation.Arizona State University, Arizona. 321pp.OLSEN, R. D. and SOMMERFIELD, M. R. (1977).The physical, chemical limnology <strong>of</strong> adesert reservoir. Hydrobiologia, 53(2):117 – 129.PHILLIPS, D. J. H. (1991). Selected traceelements and the use <strong>of</strong> biomonitors insubtropical and tropical aquaticecosystems. Review o f EnvironmentalContamination and Toxicology, 120:105 - 129.SOLOMON, W. and FORSTNER, U. (1984).Metals in the hydrocycle. Berlin,Springer. 349 pp.UNIFE (1986). Determination <strong>of</strong> <strong>org</strong>anochlorinepesticides and some heavy metals inKainji lake ecosystems. Final Reportsubmitted to Kainji lake ResearchInstitute. Institute <strong>of</strong> Ecology,University <strong>of</strong> Ife. Ile Ife. 167 pp.
Animal Research International (2004) 1(1): 16 - 22 16EFFECTS OF TEMPERATURE AND pH ON THE OXYGEN CONSUMPTIONRATE OF Sudanonautes (Convexonautes aubryi) floweri(DE MAN) (CRUSTACEA: DECAPODA)INYANG, Nicholas Mathias and NWANKWO, Enyinnaya LewechiDepartment <strong>of</strong> <strong>Zoo</strong>logy, University <strong>of</strong> Nigeria, Nsukka. Enugu State, Nigeria.Corresponding author: INYANG, Nicholas Mathias, Department <strong>of</strong> <strong>Zoo</strong>logy, University <strong>of</strong> Nigeria,Nsukka. Enugu State, Nigeria.ABSTRACTThe oxygen consumption rate <strong>of</strong> a freshwater sub-terrestrial crab, Sudanonautes floweriin relation to different temperatures and pH was investigated. The average temperatureand pH o f the crab’s peaty stream habitat were 29.50 C and 7.5 respectively. The lethaltemperatures at pH 7.0 recorded for the species were 14.5 0 C and 34.5 0 C respectively. Theoxygen consumption rate (Q) within the temperature range <strong>of</strong> 21 0 C – 31 0 C increasedwith temperature but decreased in the zones <strong>of</strong> temperature stress (≤ 16 0 C and ≥ 31 0 C).There was no significant difference (P>0.05) between <strong>weight</strong> specific oxygenconsumption (QW -1 ) <strong>of</strong> the male and female crabs. The oxygen consumption rate waspositively correlated with the body <strong>weight</strong> <strong>of</strong> the crabs (r = 1.0); but was inverselyrelated to the unit <strong>weight</strong> <strong>of</strong> the crab per hour (r = -0.95). The average oxygenconsumption <strong>of</strong> the animal at 30 0 C and pH 7.0 was 53.1 µg O 2 g -1 h -1 .Key words: Temperature, pH, Oxygen consumption, Sudanonautes floweriINTRODUCTIONFactors affecting the metabolic rate <strong>of</strong>invertebrates can be either endogenous (bodysize, respiratory surfaces, activity, nutritionalstatus and state <strong>of</strong> reproductive cycle (Newell etal., 1979) or exogenous (temperature, salinity,hydrogen ion concentration (pH), photoperiodand oxygen concentration among others).These factors affect the life pattern andactivities <strong>of</strong> animals in a particular ecosystem.Temperature is a measure <strong>of</strong> “hotness” and“coldness” in an animal’s body. It is usually afunction <strong>of</strong> the rate <strong>of</strong> molecular agitation whichis controlled to a large extent by the rate <strong>of</strong>physico-chemical reactions in the body <strong>of</strong> theanimal (Hardy, 1979). Since crabs arepoikilotherms, it is expected that temperaturewill grossly affect their metabolic rates. Thoughmetabolic rate <strong>of</strong> an animal tends to increasewith increasing temperature, Aldrich (1975)noted that because <strong>of</strong> the complex interactions<strong>of</strong> environmental, demographic andphysiological factors it may not be surprising tonotice individual variability <strong>of</strong> oxygenconsumption rates in some crustaceans. Lagleret al. (1977) stated that there is similarity <strong>of</strong>effects <strong>of</strong> oxygen carrying capacity <strong>of</strong> the bloodby carbon (IV) oxide (CO 2 ) tension and pH.Thus, respiratory rate is generally expected toincrease with increasing hydrogen ionconcentration.Bell et al. (1970) defines metabolism asthe total chemical changes occurring in the cellor in the body. Metabolic rate in an animal canbe quantified <strong>from</strong> the rate <strong>of</strong> foodconsumption, energy released as heat or theamount <strong>of</strong> oxygen consumed in its oxidationprocesses to obtain energy. Of these threemethods, the third is more widely used becauseit is easy and technically accurate. Thus,metabolic rate conventionally means orrepresents the rate <strong>of</strong> oxygen consumption.Information on the metabolic rates <strong>of</strong>animals is <strong>of</strong> basic importance in defining theenergy budget <strong>of</strong> animals. Such information isuseful for the establishment <strong>of</strong> aquaculturefacilities and for the evaluation <strong>of</strong> theaquaculture perspectives <strong>of</strong> the species involved(Buesa, 1979).The <strong>relationship</strong> between oxygenconsumption (Q) and the unit body <strong>weight</strong>oxygen requirement (QW -1 ) is a welldocumented phenomenon in the animalkingdom and is most evident in animalsweighing <strong>from</strong> one gram (1 g) to 1000 grams (1kg). Though metabolism in poikilothermsgenerally varies with the environmentaltemperature, it is also influenced by size (Bell etal., 1970). So for strict quantitative purposes
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