日本有明海上部的沿筑后川海口梯度的最大浊度在空间和课件_第1页
日本有明海上部的沿筑后川海口梯度的最大浊度在空间和课件_第2页
日本有明海上部的沿筑后川海口梯度的最大浊度在空间和课件_第3页
日本有明海上部的沿筑后川海口梯度的最大浊度在空间和课件_第4页
日本有明海上部的沿筑后川海口梯度的最大浊度在空间和课件_第5页
已阅读5页,还剩71页未读, 继续免费阅读

下载本文档

版权说明:本文档由用户提供并上传,收益归属内容提供方,若内容存在侵权,请进行举报或认领

文档简介

SpatialandseasonalvariationsincopepodcommunitiesrelatedtoturbiditymaximumalongtheChikugoestuarinegradientintheupperAriakeBay,Japan日本有明海上部的沿筑後川海口梯度的最大濁度在空間和季節橈足類群落變異Md.ShahidulIslam

HiroshiUeda

MasaruTanaka報告者:闕禎儀Spatialandseasonalvariation1INTRODUCTIONINTRODUCTION2marinefoodchainsmarinefoodchains3Theestuarineturbiditymaximum(ETM)isaubiquitousfeatureindynamicestuarineecosystemswithsubstantialimpactsoncopepodabundanceanddistribution.RothschildandOsborn,1988

Gasparinietal.,1999

Romanetal.,2001

Winkleretal.,2003Turbidity↑

PlanktonicpredatorsencountermorepreyHydrodynamicconditionsalsoresultinhighabundanceandbiomassofcopepodsinETM.MacKenzieetal.,1994

MacKenzieandKiørboe,2000

Visseretal.,2001

Davidetal.,2005Theestuarineturbiditymaximu4ETMzonesareresidedbycopepodswithlowsalinitytolerance.Romanetal.,2001;Winkleretal.,2003ETMzonesarecharacterizedbylowcopepoddiversitythatisgenerallyuniqueanddifferentfromthatofupstreamfreshwateranddownstreamcommunities.LapriseandDodson,1994;Romanetal.,2001;

Winkleretal.,2003ETMzonesareresidedbycopep5Estuarinecopepodcommunitiesarebelievedtobeannuallystablebutshowstrongseasonalandspatialdynamics.Temperature,salinity,andfoodsupplyareamongthemostimportantfactorsthatinfluencetheobservedspatialandseasonalpatternsindemographicvariationsofcopepods.Winkleretal.,2003Roddieetal.,1984;Hassel,1986Estuarinecopepodcommunities6JapanKyushuJapanKyushu7Romanetal.,2001LapriseandDodson,1994;Winkleretal.,2003Kimmereretal.,1998IrigoienandCastel,1997;Davidetal.,2005→ChesapeakeBay→St.Lawrenceestuary→SanFranciscoBay→GirondeestuaryRomanetal.,2001Lapriseand8MaterIalsAndMethodsMaterIals9DATE:

2004.4~2005.3Fig.1MapoftheAriakeBayandthehikugoRiverestuaryshowingthesamplingstations.DATE:2004.4~2005.3Fig.110EnvironmentalMonitoringSystem

(YSI650MDS,YSIIncorporated,USA)Ⅰ.Temperature(°C)

Ⅱ.Turbidity(nephelometricturbidityunit,NTU)

Ⅲ.Salinity(practicalsalinityunit,PSU)

Ⅳ.chlorophyll-a(chl-a,μgl-1)

Ⅴ.Phaeopigment(PhP,μgl-1)HydrographicdatacollectionEnvironmentalMonitoringSyste11ZooplanktoncollectionObliquetowsPlanktonnet

(45cmmouthdiameterand0.1mmmeshsize)

equippedwithaflowmeter10%seawaterformalinZooplanktoncollectionOblique12ShannoneWienerindex

(H)Two-wayanalysisofvariance

(ANOVA)copepodspecies

diversityspatialandtemporal

differencesShannoneWienerindex

(H)Two-w13ResultsResults14Ⅰ.HydrographicenvironmentFig.2Spatialandtemporalvariationsinthehydrographicalvariablesalongthehikugoestuary;valuesaremean(±SD)andPvaluesindicatetheresultsofANOVA.Ⅰ.HydrographicenvironmentFig15TemperatureSalinityTurbidityChl-aPhPDensityBiomassSalinity0.12-Turbidity-0.22*-0.42**-Chl-a0.50**-0.080.25*-PhP-0.07-0.49**0.68**0.43**-Density0.43**0.080.130.60**0.22*-Biomass0.26*-0.19

0.39**0.69**0.45**

0.82**-H0.45**

0.27*-0.200.04-0.20-0.14-0.16Table1

Pearson’scorrelationcoefficientbetweendifferenthydrographicalvariables,pigmentsandcopepoddensity,diversityandbiomasscollectedoverthespatiotemporalscalesfromtheChikugoestuary(*P<0.05;**P<0.01)TemperatureSalinityTurbidityCh16Fig.3SpatialvariationsinPhP:TPratioalongtheChikugoestuary(valuesaremean±SD);TPistotalpigment(chlorophyll-a+phaeopigment);PvalueindicatestheresultsofANOVA.Fig.3Spatialvariationsin1731.28415.33Oithonadavisae25.52338.96Sinocalanussinensis12.81170.06Paracalanusparvus6.6187.78Cyclopoidaspp.5.9979.61Acartiaomorii5.9078.35Pseudodiapomusinopinus2.6635.27Pseudodiaptomusmarinus2.4332.34Copepodite1.8724.88Acartiaerythraea1.5120.08Acartiapacifica0.759.92Nauplii0.749.79Euterpinaacutifrons0.385.11Centropagesabdominalis0.344.54Hemicyclopsjaponicus0.344.50Unidentified0.314.14Paraclanuscrassirostris0.273.64Sinocalanustenellus0.070.91Centropagestenuiremis0.060.78Calanussinicus0.050.69Trotanusderjugini0.040.54Microsetellasp.0.030.44Labidocerarotunda0.020.21Temoraturbinata0.010.17Eurytemorapacifica0.000.04CentropagesgracilisDensity(number×103m-3)%TatalSpeciesTable2-1

ContributionofeachspeciestotheoveralldensityandbiomassofcopepodscollectedoveraperiodoftwelvemonthsalongtheChikugoestuary;speciesarearrangedinorderofabundanceⅡ.Copepodcommunitystructure,

density,biomassanddiversity31.28415.33Oithonadavisae25.51844.601825.98Sinocalanussinensis12.12496.23Pseudodiapomusinopinus10.66436.30Paracalanusparvus8.62353.03Oithonadavisae7.26297.18Acartiaomorii5.03205.81Cyclopoidaspp.3.09126.42Pseudodiaptomusmarinus2.4399.54Acartiaerythraea1.7772.29Acartiapacifica1.7069.63Centropagesabdominalis1.3454.72Copepodite0.4920.05Sinocalanustenellus0.2510.06Hemicyclopsjaponicus0.156.31Nauplii0.124.89Euterpinaacutifrons0.114.34Unidentified0.093.75Calanussinicus0.072.73Trotanusderjugini0.041.69Microsetellasp.0.041.43Centropagestenuiremis0.031.11Labidocerarotunda0.010.21Temoraturbinata0.000.17EurytemorapacificaBiomass(mgm-3)%TatalSpeciesTable2-2

ContributionofeachspeciestotheoveralldensityandbiomassofcopepodscollectedoveraperiodoftwelvemonthsalongtheChikugoestuary;speciesarearrangedinorderofabundance44.601825.98Sinocalanussinens19Fig.4SpatialandtemporalvariationsinthenumericalcompositionofcopepodfromApril(A)2004toMarch(M)2005alongthespatialgradientinChikugoestuary.Notethatthescaleofthex-axiswhichshowsthesalinitiesaredifferent.Fig.4Spatialandtemporalv20CopepodspeciesSourcesofvariationdfFPCyclopoidasp.TemporalSpatial1165.217.020.0000.000SinocalanussinensisTemporalSpatial1161.9021.760.0550.000NaupliiTemporalSpatial1162.420.820.0130.556AcartiaomoriiTemporalSpatial1165.0817.490.0000.000HemicyclopsjaponicusTemporalSpatial1162.612.300.0080.045OithonadavisaeTemporalSpatial1165.6123.610.0000.000PseudodiapomusinopinusTemporalSpatial1163.3410.000.0010.000PseudodiaptomusmarinusTemporalSpatial1164.898.870.0000.000ParacalanusparvusTemporalSpatial1165.9720.300.0000.000CopepoditeTemporalSpatial1163.980.730.0000.626AcartiaerythraeaTemporalSpatial1168.512.980.0000.012AcartiapacificaTemporalSpatial1169.006.670.0000.000Table3

Two-wayanalysisofvariance(ANOVA)summaryresultsofthespatial(sevensamplingstations)andtemporal(12months)variationsinthedensityofthedominantcopepodspeciesalongtheChikugoestuaryCopepodspeciesSourcesofvari21Fig.5Spatialvariationinthedensityofeachofthedominantcopepodspecies.Mean(±SD)valuesarenaturallogtransformeddensity(numberm-3)datageneratedfrom12monthssamplescollectedfromApril2004toMarch2005alongthespatialgradientintheChikugoRiverestuary.Fig.5Spatialvariationint22Fig.6Temporalvariationinthedensityofeachofthedominantcopepods.Valuesarenaturallogtransformeddensity(numberm-3)collectedfromApril2004toMarch2005alongthespatialgradientintheChikugoRiverestuary.Fig.6Temporalvariationin23SpeciesTemperatureChl-aSinocalanussinensis-0.010.39Oithonadavisae0.440.28Acartiaomorii0.380.68*Cyclopoidaspp.0.460.48Nauplii0.410.16Centropagesabdominalis0.170.01Paracalanusparvus0.470.41Pseudodiapomusinopinus0.62*0.60*Pseudodiaptomusmarinus0.64*0.72**Acartiaerythraea0.69*0.66*Acartiapacifica0.74**0.66*Hemicyclopsjaponicus0.76**0.68*Copepodite0.74**0.54Table4

Relationships(Pearson’scorrelationcoefficient)betweenthemonthlypatternsoftemperatureandchl-aandthemonthlyabundanceofdominantspeciesofcopepods(**P<0.01;

*P<0.05)SpeciesTemperatureChl-aSinocal24SpeciesTemperatureChl-aSinocalanussinensis-0.010.39Oithonadavisae0.440.28Acartiaomorii0.380.68*Cyclopoidaspp.0.460.48Nauplii0.410.16Centropagesabdominalis0.170.01Paracalanusparvus0.470.41Pseudodiapomusinopinus0.62*0.60*Pseudodiaptomusmarinus0.64*0.72**Acartiaerythraea0.69*0.66*Acartiapacifica0.74**0.66*Hemicyclopsjaponicus0.76**0.68*Copepodite0.74**0.54SpeciesTemperatureChl-aSinocal25Fig.7Variationsinthedensityofdominantcopepodswithsalinity;theoligohalinecopepodsS.sinensisandP.inopinusshowedaseawarddecreaseinabundancewhiletheeuryhalinecopepodsP.inopinus,O.davisae,P.parvusandA.omoriishowedseawardincreaseinabundance.Valuesarenaturallogtransformeddensity(numberm-3).SinocalanussinensisPseudodiaptomusmarinusPseudodiapomusinopinusOithonadavisaeParacalanusparvusAcartiaomoriiFig.7Variationsinthedens26Fig.8Spatialandtemporalvariationsinthetotalcopepoddensity,biomassanddiversity;valuesaremean(±SD)andPvaluesindicatetheresultsofANOVA.Fig.8Spatialandtemporalv27DependentvariableDesignsummary(ANOVA)IndependentvariableBetaValuePDensityF=8.72;R2=0.38;P<0.0001Chl-a0.3250.030BiomassF=13.08;R2=0.51;P<0.0001Chl-aNTU0.5490.4270.0000.046DiversityF=4.64;R2=0.24;P<0.0001Chl-a

Salinity0.3310.2930.0460.026SinocalanussinensisF=4.95;R2=0.74;P<0.050Chl-a

PhP3.48-6.360.0210.025OithonadavisaeF=6.54;R2=0.80;P<0.050Chl-a-2.530.035Table5Summaryresultsformultipleregressionontheeffectsofenvironmentalvariablesondensity,biomassanddiversityofallcopepodsandonthedensityofthetwomostdominantspecies(S.sinensisandO.davisae);theR2valuesareadjustedR2Ⅲ.Roleofhydrographicvariables

incopepodabundanceanddiversityDependentDesignsummaryIndepen28Fig.9Patternsofinterrelationshipsamongtemperature(°C),chl-a(μgl-1)andcopepoddensity(numberm-3)duringfourmainseasons.Valuesaremeananderrorbarsarestandarddeviationsofthreesamplesduringeachseason.Pearson’scorrelationcoefficientshowedthatseasonalpatternsintemperature,chl-aanddensityweresignificantlyrelatedtoeachother(valuesorrwere0.917(P<0.05),0.921(P<0.05)and0.997(P<0.01)fortemperaturevschl-a,temperaturevsdensityandchl-avsdensityrespectively.Fig.9Patternsofinterrelat29DIscussIonDIscussIon30TemperatureSalinityNTUNTUnegativecorrelationnegativecorrelation-Chl-apositivelycorrelationpositivelycorrelationPhPnegativecorrelationpositivelycorrelationAreaSalinityDominantSpeciesSeasontheETM

intheupperestuaryoligohaline

(0.5-2.5)S.

sinensisduringautumntospring

(summerislowdensityandwasreplacedby

P.inopinusandCyclopoidaspp.)theETM

inthelowerestuaryeuryhaline

(9.0-25.0)O.davisae

P.parvus

A.omoriithefourseasons

TemperatureSalinityNTUNTUnegat31S.

sinensis

P.inopinus

CyclopoidasppS.sinensis

P.inopinus

Cyclo32O.davisae

P.parvus

A.omoriithethreemostdominantspecies

inthiscommunityPlourdeetal.,2002

Satapoominetal.,2004

Davidetal.,2005O.davisae

P.parvus

A.omorii33Highabundant

(notshowsignificantrelationwithtemperatureandseason)Mediumabundant

(highlysignificantcorrelationwithtemperature,seasonandChl-a)S.sinensis(intheupper)

O.davisae

P.parvus

A.omoriiP.inopinus(intheupper)

A.erythraea

A.pacifica

P.inopinus

H.japonicusHighabundant

(notshowsignif34Bousfieldetal.(1975)Thecopepodsthataretransportedfromtheiroriginalhabitatsaremostlymoribund,non-reproductiveanimals,suggestingthatthetransportedhabitatsmayconstituteanextremeenvironmentforthesespecies.Theedgeeffects,causedbymixingindividualsfromthetwoassemblages,resultinincreasingthespeciesrichness.

Therefore,speciesrichnessmaygiveerroneousimpressionsontheevolutionofcopepodspeciesdiversityalongthespatialgradientinanestuary.LapriseandDodson,1994Bousfieldetal.(1975)Thecop35AreaImportantIntheestuaryasawholeChl-a(ex.O.davisae)InupperestuaryPhP(ex.S.sinensis)AreaImportantIntheestuaryas36Ⅰ.Chl-aandsalinitywerethemostimportantpredictorvariables.Ⅱ.Inthehighersalinityregionshadhigherdiversity.Ⅰ.Chl-aandsalinitywerethe37THANKYOUTHANKYOU38SpatialandseasonalvariationsincopepodcommunitiesrelatedtoturbiditymaximumalongtheChikugoestuarinegradientintheupperAriakeBay,Japan日本有明海上部的沿筑後川海口梯度的最大濁度在空間和季節橈足類群落變異Md.ShahidulIslam

HiroshiUeda

MasaruTanaka報告者:闕禎儀Spatialandseasonalvariation39INTRODUCTIONINTRODUCTION40marinefoodchainsmarinefoodchains41Theestuarineturbiditymaximum(ETM)isaubiquitousfeatureindynamicestuarineecosystemswithsubstantialimpactsoncopepodabundanceanddistribution.RothschildandOsborn,1988

Gasparinietal.,1999

Romanetal.,2001

Winkleretal.,2003Turbidity↑

PlanktonicpredatorsencountermorepreyHydrodynamicconditionsalsoresultinhighabundanceandbiomassofcopepodsinETM.MacKenzieetal.,1994

MacKenzieandKiørboe,2000

Visseretal.,2001

Davidetal.,2005Theestuarineturbiditymaximu42ETMzonesareresidedbycopepodswithlowsalinitytolerance.Romanetal.,2001;Winkleretal.,2003ETMzonesarecharacterizedbylowcopepoddiversitythatisgenerallyuniqueanddifferentfromthatofupstreamfreshwateranddownstreamcommunities.LapriseandDodson,1994;Romanetal.,2001;

Winkleretal.,2003ETMzonesareresidedbycopep43Estuarinecopepodcommunitiesarebelievedtobeannuallystablebutshowstrongseasonalandspatialdynamics.Temperature,salinity,andfoodsupplyareamongthemostimportantfactorsthatinfluencetheobservedspatialandseasonalpatternsindemographicvariationsofcopepods.Winkleretal.,2003Roddieetal.,1984;Hassel,1986Estuarinecopepodcommunities44JapanKyushuJapanKyushu45Romanetal.,2001LapriseandDodson,1994;Winkleretal.,2003Kimmereretal.,1998IrigoienandCastel,1997;Davidetal.,2005→ChesapeakeBay→St.Lawrenceestuary→SanFranciscoBay→GirondeestuaryRomanetal.,2001Lapriseand46MaterIalsAndMethodsMaterIals47DATE:

2004.4~2005.3Fig.1MapoftheAriakeBayandthehikugoRiverestuaryshowingthesamplingstations.DATE:2004.4~2005.3Fig.148EnvironmentalMonitoringSystem

(YSI650MDS,YSIIncorporated,USA)Ⅰ.Temperature(°C)

Ⅱ.Turbidity(nephelometricturbidityunit,NTU)

Ⅲ.Salinity(practicalsalinityunit,PSU)

Ⅳ.chlorophyll-a(chl-a,μgl-1)

Ⅴ.Phaeopigment(PhP,μgl-1)HydrographicdatacollectionEnvironmentalMonitoringSyste49ZooplanktoncollectionObliquetowsPlanktonnet

(45cmmouthdiameterand0.1mmmeshsize)

equippedwithaflowmeter10%seawaterformalinZooplanktoncollectionOblique50ShannoneWienerindex

(H)Two-wayanalysisofvariance

(ANOVA)copepodspecies

diversityspatialandtemporal

differencesShannoneWienerindex

(H)Two-w51ResultsResults52Ⅰ.HydrographicenvironmentFig.2Spatialandtemporalvariationsinthehydrographicalvariablesalongthehikugoestuary;valuesaremean(±SD)andPvaluesindicatetheresultsofANOVA.Ⅰ.HydrographicenvironmentFig53TemperatureSalinityTurbidityChl-aPhPDensityBiomassSalinity0.12-Turbidity-0.22*-0.42**-Chl-a0.50**-0.080.25*-PhP-0.07-0.49**0.68**0.43**-Density0.43**0.080.130.60**0.22*-Biomass0.26*-0.19

0.39**0.69**0.45**

0.82**-H0.45**

0.27*-0.200.04-0.20-0.14-0.16Table1

Pearson’scorrelationcoefficientbetweendifferenthydrographicalvariables,pigmentsandcopepoddensity,diversityandbiomasscollectedoverthespatiotemporalscalesfromtheChikugoestuary(*P<0.05;**P<0.01)TemperatureSalinityTurbidityCh54Fig.3SpatialvariationsinPhP:TPratioalongtheChikugoestuary(valuesaremean±SD);TPistotalpigment(chlorophyll-a+phaeopigment);PvalueindicatestheresultsofANOVA.Fig.3Spatialvariationsin5531.28415.33Oithonadavisae25.52338.96Sinocalanussinensis12.81170.06Paracalanusparvus6.6187.78Cyclopoidaspp.5.9979.61Acartiaomorii5.9078.35Pseudodiapomusinopinus2.6635.27Pseudodiaptomusmarinus2.4332.34Copepodite1.8724.88Acartiaerythraea1.5120.08Acartiapacifica0.759.92Nauplii0.749.79Euterpinaacutifrons0.385.11Centropagesabdominalis0.344.54Hemicyclopsjaponicus0.344.50Unidentified0.314.14Paraclanuscrassirostris0.273.64Sinocalanustenellus0.070.91Centropagestenuiremis0.060.78Calanussinicus0.050.69Trotanusderjugini0.040.54Microsetellasp.0.030.44Labidocerarotunda0.020.21Temoraturbinata0.010.17Eurytemorapacifica0.000.04CentropagesgracilisDensity(number×103m-3)%TatalSpeciesTable2-1

ContributionofeachspeciestotheoveralldensityandbiomassofcopepodscollectedoveraperiodoftwelvemonthsalongtheChikugoestuary;speciesarearrangedinorderofabundanceⅡ.Copepodcommunitystructure,

density,biomassanddiversity31.28415.33Oithonadavisae25.55644.601825.98Sinocalanussinensis12.12496.23Pseudodiapomusinopinus10.66436.30Paracalanusparvus8.62353.03Oithonadavisae7.26297.18Acartiaomorii5.03205.81Cyclopoidaspp.3.09126.42Pseudodiaptomusmarinus2.4399.54Acartiaerythraea1.7772.29Acartiapacifica1.7069.63Centropagesabdominalis1.3454.72Copepodite0.4920.05Sinocalanustenellus0.2510.06Hemicyclopsjaponicus0.156.31Nauplii0.124.89Euterpinaacutifrons0.114.34Unidentified0.093.75Calanussinicus0.072.73Trotanusderjugini0.041.69Microsetellasp.0.041.43Centropagestenuiremis0.031.11Labidocerarotunda0.010.21Temoraturbinata0.000.17EurytemorapacificaBiomass(mgm-3)%TatalSpeciesTable2-2

ContributionofeachspeciestotheoveralldensityandbiomassofcopepodscollectedoveraperiodoftwelvemonthsalongtheChikugoestuary;speciesarearrangedinorderofabundance44.601825.98Sinocalanussinens57Fig.4SpatialandtemporalvariationsinthenumericalcompositionofcopepodfromApril(A)2004toMarch(M)2005alongthespatialgradientinChikugoestuary.Notethatthescaleofthex-axiswhichshowsthesalinitiesaredifferent.Fig.4Spatialandtemporalv58CopepodspeciesSourcesofvariationdfFPCyclopoidasp.TemporalSpatial1165.217.020.0000.000SinocalanussinensisTemporalSpatial1161.9021.760.0550.000NaupliiTemporalSpatial1162.420.820.0130.556AcartiaomoriiTemporalSpatial1165.0817.490.0000.000HemicyclopsjaponicusTemporalSpatial1162.612.300.0080.045OithonadavisaeTemporalSpatial1165.6123.610.0000.000PseudodiapomusinopinusTemporalSpatial1163.3410.000.0010.000PseudodiaptomusmarinusTemporalSpatial1164.898.870.0000.000ParacalanusparvusTemporalSpatial1165.9720.300.0000.000CopepoditeTemporalSpatial1163.980.730.0000.626AcartiaerythraeaTemporalSpatial1168.512.980.0000.012AcartiapacificaTemporalSpatial1169.006.670.0000.000Table3

Two-wayanalysisofvariance(ANOVA)summaryresultsofthespatial(sevensamplingstations)andtemporal(12months)variationsinthedensityofthedominantcopepodspeciesalongtheChikugoestuaryCopepodspeciesSourcesofvari59Fig.5Spatialvariationinthedensityofeachofthedominantcopepodspecies.Mean(±SD)valuesarenaturallogtransformeddensity(numberm-3)datageneratedfrom12monthssamplescollectedfromApril2004toMarch2005alongthespatialgradientintheChikugoRiverestuary.Fig.5Spatialvariationint60Fig.6Temporalvariationinthedensityofeachofthedominantcopepods.Valuesarenaturallogtransformeddensity(numberm-3)collectedfromApril2004toMarch2005alongthespatialgradientintheChikugoRiverestuary.Fig.6Temporalvariationin61SpeciesTemperatureChl-aSinocalanussinensis-0.010.39Oithonadavisae0.440.28Acartiaomorii0.380.68*Cyclopoidaspp.0.460.48Nauplii0.410.16Centropagesabdominalis0.170.01Paracalanusparvus0.470.41Pseudodiapomusinopinus0.62*0.60*Pseudodiaptomusmarinus0.64*0.72**Acartiaerythraea0.69*0.66*Acartiapacifica0.74**0.66*Hemicyclopsjaponicus0.76**0.68*Copepodite0.74**0.54Table4

Relationships(Pearson’scorrelationcoefficient)betweenthemonthlypatternsoftemperatureandchl-aandthemonthlyabundanceofdominantspeciesofcopepods(**P<0.01;

*P<0.05)SpeciesTemperatureChl-aSinocal62SpeciesTemperatureChl-aSinocalanussinensis-0.010.39Oithonadavisae0.440.28Acartiaomorii0.380.68*Cyclopoidaspp.0.460.48Nauplii0.410.16Centropagesabdominalis0.170.01Paracalanusparvus0.470.41Pseudodiapomusinopinus0.62*0.60*Pseudodiaptomusmarinus0.64*0.72**Acartiaerythraea0.69*0.66*Acartiapacifica0.74**0.66*Hemicyclopsjaponicus0.76**0.68*Copepodite0.74**0.54SpeciesTemperatureChl-aSinocal63Fig.7Variationsinthedensityofdominantcopepodswithsalinity;theoligohalinecopepodsS.sinensisandP.inopinusshowedaseawarddecreaseinabundancewhiletheeuryhalinecopepodsP.inopinus,O.davisae,P.parvusandA.omoriishowedseawardincreaseinabundance.Valuesarenaturallogtransformeddensity(numberm-3).SinocalanussinensisPseudodiaptomusmarinusPseudodiapomusinopinusOithonadavisaeParacalanusparvusAcartiaomoriiFig.7Variationsinthedens64Fig.8Spatialandtemporalvariationsinthetotalcopepoddensity,biomassanddiversity;valuesaremean(±SD)andPvaluesindicatetheresultsofANOVA.Fig.8Spatialandtemporalv65DependentvariableDesignsummary(ANOVA)IndependentvariableBetaValuePDensityF=8.72;R2=0.38;P<0.0001Chl-a0.3250.030BiomassF=13.08;R2=0.51;P<0.0001Chl-aNTU0.5490.4270.0000.046DiversityF=4.64;R2=0.24;P<0.0001Chl-a

Salinity0.3310.2930.0460.026SinocalanussinensisF=4.95;R2=0.74;P<0.050Chl-a

PhP3.48-6.360.0210.025OithonadavisaeF=6.54;R2=0.80;P<0.050Chl-a-2.530.035Table5Summaryresultsformultipleregressionontheeffectsofenvironmentalvariablesondensity,biomassanddiversityofallcopepodsandonthedensityofthetwomostdominantspecies(S.sinensisandO.davisae);theR2valuesareadjustedR2Ⅲ.Roleofhydrographicvariables

incopepodabundanceanddiversityDependentDesignsu

温馨提示

  • 1. 本站所有资源如无特殊说明,都需要本地电脑安装OFFICE2007和PDF阅读器。图纸软件为CAD,CAXA,PROE,UG,SolidWorks等.压缩文件请下载最新的WinRAR软件解压。
  • 2. 本站的文档不包含任何第三方提供的附件图纸等,如果需要附件,请联系上传者。文件的所有权益归上传用户所有。
  • 3. 本站RAR压缩包中若带图纸,网页内容里面会有图纸预览,若没有图纸预览就没有图纸。
  • 4. 未经权益所有人同意不得将文件中的内容挪作商业或盈利用途。
  • 5. 人人文库网仅提供信息存储空间,仅对用户上传内容的表现方式做保护处理,对用户上传分享的文档内容本身不做任何修改或编辑,并不能对任何下载内容负责。
  • 6. 下载文件中如有侵权或不适当内容,请与我们联系,我们立即纠正。
  • 7. 本站不保证下载资源的准确性、安全性和完整性, 同时也不承担用户因使用这些下载资源对自己和他人造成任何形式的伤害或损失。

评论

0/150

提交评论