沉水植物床固定化微生物技术在水源地修复中的应用研究

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33120121ENVIRONMENTALSCIENCEVol.33No.1Jan.2012-*210093-.、、5.4×102~2.7×1033.9×105~9.1×1053~24μg·m2·h-119%~74%24%~81%120d.-X173X172A0250-3301201201-0083-052011-01-302011-05-06BK20100562008ZX07101-0122008ZX07101-0041987~E-maileniac17968@126.com*E-mailzhkuili@nju.edu.cnAppliedStudyoftheSubmergedMacrophytesBed-ImmobilizedBacteriainDrinkingWaterRestorationCHENQi-chunLIZheng-kuiWANGYi-chaoWUKaiFANNian-wenStateKeyLaboratoryofPollutantControlandResourcesReuseSchoolofEnvironmentNanjingUniversityNanjing210093ChinaAbstractTheeffectofsubmergedmacrophytesbed-immobilizedbacteriatechnologywhichappliedindrinkingwaterrestorationwasstudied.AmmonifyingbacterianitrobacterianitrosobacteriaanddenitrifyingbacteriawhichisolatedfromTaihuLabewasimmobilizedtotheporouscarriescombinedwiththesubmergedmacrophytesbedtechnologyweappliedthenewequipmentinwaterrestorationofgonghubaythisequipmenthasgoodabilitytoresiststormthedenitrifyingbacterianumberincreasedfrom5.4×102-2.7×103to3.9×105-9.1×105N2Ofluxofexperimentalplotwas3-24μg·m2·h-1it'smorethanthecontrastgroupobviouslyTNconcentrationreduced19%-74%whileNO-3concentrationreduced24%-81%aftertheequipmentrunningaperiodoftimeTheexperimentaldataof120daysshowedthatthistechnologyissuitablefordrinkingwaterrestorationasitcancontroleutrophication.Keywordseutrophicationdrinkingwatersubmergedmacrophytesbed-immobilizedbacteriarestorationdenitrificationVV..、1~5678~10.、、.11.11-、、.DOI:10.13227/j.hjkx.2012.01.027332010TN1.18~3.44mg·L-1、NH+40~0.58mg·L-1、NO-30.36~0.67mg·L-1、NO-20.0023~0.055mg·L-1、、、、.1Fig.1Sketchmapofdemonstrationproject1.21.2.1、、、、、-β-、-78℃1×104Gy60Co-γ5mm28℃24h3.、、200mL28℃24h、48h、、.1.2.21m×1m×1m、、2cm20m、16m、4m202.2Fig.2Schematicofthesubmergedmacrophytes-bed1.310m×6m642、、、、、、、.1.44ABCD、、.1.51.5.1N-1--、pHpHDO.1.5.2N2O40cm、50cm12V.N2O0900481-19001112130830~1200N2ON2OFF=ρ×VA×ΔcΔt×273273+TFN2ONμg·m2·h-1ρN2O1.25kg/m3Vm3Am2ΔcN2OΔthT14.1.5.315~17.1.6ORIGIN7.5SPSS13.0.22.120107~11、、、、、N2O、DOpH.19%~74%、36%~100%、24%~81%、27%~100%3~6+11.r=-0.771P<0.053Fig.3DynamicchangesofTNconcentrationintheexperimentdistrict4Fig.4DynamicchangesofNH+4concentrationintheexperimentdistrict5Fig.5DynamicchangesofNO-3concentrationintheexperimentdistrict+、、pHpH58336Fig.6DynamicchangesofNO-2concentrationintheexperimentdistrictr=0.819P<0.05.2.2pHpH、、CO2pH18pH+9.67.7pHFig.7DynamicchangesofpHvalueintheexperimentdistrict2.3DO729>>+>7298.8DOFig.8DynamicchangesofDOconcentrationintheexperimentdistrict2.4N2O5.4×102~2.7×103+3.9×105~9.1×1052~3SPSSr=0.975P<0.01-1.95μg·m2·h-111.44μg·m2·h-13~24μg·m2·h-1+9r=-0.78P<0.05pH10.+-681-9Fig.9N2Ofluxintheexperimentdistrict10Fig.10Dynamicchangesofwatertemperatureintheexperimentdistrict-.31120d+.2、2~3.3N2O.4.1.J.20082982154-2159.2.Acinetobactersp.YY-5J.2009155692-697.3.-J.200930123614-3618.4./N2OJ.20093072105-2111.5Risgaard-PetersenNMeyerRLRersbechNP.Denitrificationandanaerobicammoniumoxidationinsediments-effectsofmicrophytobenthosandNO-3J.AquaticMicrobialEcology200540167-76.6.J.2008294890-895.7LauridsenTLJensenJPJeppesenEetal.ResponseofsubmergedmacrophytesinDanishlakestonutrientloadingreductionsandbiomanipulationJ.Hydrobiologia20035061-3641-649.8.、J.200516112199-2203.9.J.2009216782-788.10.N、PN2OJ.200727104333-4341.11DongYSZhangSQiYCetal.FluxesofCO2N2OandCH4fromatypicaltemperategrasslandinInnerMongoliaanditsdailyvariationJ.ChineseScienceBulletin200045171590-1594.12BremnerJMRobbinsSGBlackmerAM.SeasonalvariabilityinemissionofnitrousoxidefromsoilJ.GeophysicalResearchLetter198079641-644.13.N2OJ.200223626-30.14.N2OJ.200324133-39.15.M.1985.16.M.1996.17.M.1993.18.J.2007262798-800.78

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