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2010264339-343JournalofEcologyandRuralEnvironment122331SylvanaLi451.2100422.2003363.2100264.202505.21004280∶2080%20%2。。COD、TP、TN、NH3-NNO-2-N21、0.12、2.06、0.340、0.021mg·L-125、0.15、2.56、0.706、0.113mg·L-1BOD5、PO43--P、NO-3-Na。12.5%11.2%TPTN13.5%5.1%。80∶20。X-651X82A1673-4831201004-0339-05ComparisonBetweenAmericanEcologicalAquacultureandTraditionalPolycultureinEnvironmentalImpact.LI-ANGBin1ZHANGJian2ZHOUEn-hua2ZHANGYong-jiang3CHENHuan-gen3ZHUYi-ling1SylvanaLI4MIAOXu-bo51.NanjingInstituteofEnvironmentalSciencesMinistryofEnvironmentalProtectionNanjing210042China2.AmericanSoybeanAssociationShanghai200336China3.JiangsuProvincialFisheryTechnologyExtensionStationNanjing210026China4.ForeignAgriculturalServiceUnitedStatesDepartmentofAgricultureWashingtonDC20250USA5.EastChinaEnvironmentalSupervisionCentreMinistryofEnvironmentalProtectionNanjing210042ChinaAbstractAnaquacultureexperimentwascarriedoutinYangzhongJiangsuProvincewithgrasscarpastheprincipalfishtocompareecologicalaquaculturewithtraditionalpolycultureinimpactonwaterqualityandsediments.Itwasfoundthattheformerwasobviouslysuperiortothelatterinyieldandeconomicprofit.Theannualmeanvaluesofsomeofthewa-terqualityindexessuchasCODTPTNNH3-NandNO2--Nweremeasuredtobe210.122.060.340and0.021mg·L-1forthepondsofUS80∶20ecologicalaquacultureand250.152.560.706and0.113mg·L-1forthepondsoftraditionalpolyculture.Obviouslytheformerwasbetterthanthelatterrespectively.NosignificantdifferenceswerefoundincontentsofBOD5PO43--PNO3--Nandchlorophyll-a.Thebottomsedimentwas12.5%thinnerinthepondsoftheUS80∶20ecologicalpolyculturethaninthepondsofthetraditionalpolyculture11.2%higherinorganicmattercontentbut13.5%and5.1%lowerinTPandTN.Themechanismofgenerationofthepollutantshasbeenanalyzed.Keywordsecologicalaquacultureenvironmentalimpactpondwaterqualitysediment2006DFA915602008ZX07103-005-42009-11-13200470%12-3。、、、。COD、BOD、TN、TP、NH3-N4。。、5。。。61·340·26。11.16160m50m0.8hm2。。20084—11。。6。F1。1~380∶20680%20%。32/3。200841hm270g5250、100g1500。6510kg·hm-2。4~6。1hm270g2250、750g1500、1001500、1001500、1000300。1hm28790kg、5625kg、1125kg。、。4—111~329h4~6196h。。1.8m、1.5m。2.0m·s-111.3~32.5℃8266mm1423h。1.2、5、9—11146—82。900—1100。50cm3。。7。DOJPBJ-608。1~34~6。411110~5cm。5。、TP、TN8-10。1111010~12。1.32。。Tamhane'sT20.05。SPSS16.0。22.1111250g1020g2P<0.05。5880kg·hm-21358kg·hm-27238kg·hm-23582kg·hm-2、3449kg·hm-27031kg·hm-2。。11.183.35。。2.220415·hm-258.7%8220·hm-226.2%。2.32.3.1CODBOD5、COD5BOD51。1CODCOD、4·341·。、COD11、21、25mg·L-1。COD。1CODBOD5ρFig.1VariationofCODandBOD5intheponds1BOD5。、BOD51.9、4.7、5.8mg·L-1。BOD5。BODCOD2。。2.3.2TPPO43--P、TPPO43--P2。2TPPO43--P、。、TP0.06、0.12、0.15mg·L-1PO43--P0.02mg·L-1。TP3PO43--P。2TPPO43--PρFig.2VariationoftotalphosphorusandPO43--PinthepondsTPPO43--P、。TP。PO43--PPO43--PPO43--P。2.3.3TNTNNH3-N、·342·26NO-2-NNO-3-N3。3TN。、TN1.78、2.06、2.56mg·L-1。。NH3-N。、NH3-N0.220、0.340、0.706mg·L-1。TN。NO-3-N。、NO-3-N0.96、0.11、0.14mg·L-1。NO-2-N。、NO-2-N0.031、0.021、0.113mg·L-1。NH3-NNO-2-N11。NH3-N。NO-2-N、。NH3-NNH3-NNO-2-NNO-3-N。NH3-NNO-2-N。NO-3-NNH3-N1213。NH3-NNO-2-NDO0.5~3.0mg·L-1。3TN、NH3-N、NO-3-NNO-2-NρFig.3VariationoftotalnitrogenNH3-NNO-3-NandNO-2-Nintheponds2.3.4a、a4。4a、PO43--PPO43--P。、a0.040、0.092、0.095mg·L-1。4·343·4aρFig.4Variationofchlorophyll-aintheponds2.41。1Table1Thicknessofsedimentsandtheirnutrientcontentsoftheaquacultureponds/cm/g·kg-1TPTN2822.91.540.2803220.61.780.295112.5%11.2%TPTN13.5%5.1%。。380∶20。COD、TP、TN、NH3-NNO-2-N21、0.12、2.06、0.340、0.021mg·L-125、0.15、2.56、0.706、0.113mg·L-112.5%11.2%TPTN13.5%5.1%、。1.J.2006211-13.2.J.200441-5.3.J.200726319-332.4.J.2007131161-67.5.J.200936267-72.6M.C..80∶20J.2007591-93.7《》.M.4.200224-671.8《》.M.3.1989464-464.9GB9837—88S.10GB7173—87S.11.J.2004941-43.12.J.2004435103-106.13.J.200924171-77.1973—。E-mailliangbin.cn@gmail.com
本文标题:美国生态水产养殖模式与常规混养模式的环境效应比较
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