Tom Ysebaert, Peter Herman, Herman Hummel, Bart Schaub, Wil Sistermans & Carlo Heip

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Monitoring and modeling of estuarine benthic macrofauna and their relevance to resource management problems. Tom Ysebaert, Peter Herman, Herman Hummel, Bart Schaub, Wil Sistermans & Carlo Heip Netherlands Institute of Ecology (NIOO) [email protected]. - PowerPoint PPT Presentation

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  • Monitoring and modeling of estuarine benthic macrofauna and their relevance to resource management problems

    Tom Ysebaert, Peter Herman, Herman Hummel, Bart Schaub, Wil Sistermans & Carlo HeipNetherlands Institute of Ecology (NIOO)

    [email protected] Colour of Ocean Data - The Palais des Congrs, Brussels, Belgium, 25-27 November 2002

  • OUTLINEIntroduction: estuarine management and the problem of scale

    Benthic monitoring programmesPredictive modelingSpatio-temporal dynamicsTrend calculations

    General conclusions

  • FIELD STUDIES - EXPERIMENTSENVIRONMENTAL PROBLEMSSCALETIDAL FLAT+ multidisciplinary research + detailed process studies+ food web and stable isotope studies + sediment processes

    LINKS monitoring integrative studies time-series data modelingSmallLargeSCHELDE ESTUARY- large-scale dredging operations- habitat loss- water quality- fisheries

    INTRODUCTION

  • Benthic monitoring programmesBenthic organisms: suitable indicators for changes in environmental qualityDutch Delta area (SW Netherlands): long tradition in monitoring of estuarine benthic macrofaunadesigned to detect long-term trends in large parts of different systems (e.g. Grevelingen) Explore relationships between biota and environmental variables to improve prediction and trend calculations

  • SCHELDE ESTUARYLarge data set available (>5000 samples)Different sampling designs (stratified random, fixed stations)Environmental variables (model derived)

  • Predictive modelingLogistic regression: model probability of occurrence of species as a function of environmental variables

    Ysebaert et al. 2002, MEPS

  • Macoma balthica: comparison pred./obs.Observed presencesPredicted presencesYsebaert et al. 2002, MEPS

  • Predictive modeling: conclusionsfor 20 macrobenthic species response surfaces were modeled (Ysebaert et al., MEPS 2002)

    the overall prediction performed very well (>75%).

    % predicted observed vs actually observed: 25%-85%.

    Within-estuary validation: successful

    where patterns of distribution are strongly and directly coupled to physico-chemical processes, our modeling approach is capable of predicting macrobenthic species distributions with a relatively high degree of success

  • Time-averaged approach - no temporal dynamicsExtrapolation to other systems limited - needs incorporation of system-wide characteristics (e.g. SPM content, productivity, wave vs. tide dominance)No prediction of abundance or biomass

    Limitations of the approachAnalysis of spatio-temporal variability of abundance and biomassAnalysis of dependence on environmental factors

  • 11 transects in 3 salinity zones, 2-4 stations per transect15 replicates per stationsampled twice yearly 1994-2000 height, mud content, chl a monitoredFit hierarchical Anova model to observations (variance components)Regression on environmental variables

    Spatio-temporal dynamics

  • R0.41Mud0.37 ***MedianChl aHeight0.53 ***SlopeSalinityFlood0.33 ***Ebb-0.16 MudChl a0.15 Height-0.16 Salinity0.21 *Macoma balthica: spatial and temporal variabilityYsebaert et al., in press, MEPS

  • In general fair proportion of variance explained by station-averaged environmental variablesTemporal variation in environmental variables poor explanatorsTemporal variation synchronized over estuary or region for bivalves (recruitment) but seldom for other speciesLargest proportion of variance usually in unsyn-chronized, station-dependent, temporal variation points to important patchiness and independent development at a scale > replicate scale (1m2), but < transect scale -> biological interactions?Spatio-temporal dynamics: conclusions

  • Application to trend calculationsUse information on the environment in trend calculationsBIOMON Westerschelde: stratified random design

    Approach : define relationships between environment and biota (presence-absence, abundance, biomass)Compare regression models where year is considered the only independent variable with regression models with year and environmental variables as independent variables

  • Trends 1992-2001

    Chart4

    7.06603023857.053215574

    6.58449705525.0113479639

    6.1357792156.1797382047

    5.71764043025.8061064273

    5.32799681084.2661010592

    4.96490647883.701248232

    4.62655989093.9991305371

    4.31127081954.371222843

    4.01746794984.479861118

    3.7436870484.4082393282

    trend [year]

    trend [year+env]

    count

    Heteromastus filiformis

    Sheet1

    hetefilimacobaltbathpilopygoeleghydrulvaaphemarinephcirrneredivearenmaricorovoluceraedul

    trend [year]trend [year+env]predpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-env

    19927.06603023857.0532155743.36009784423.49818265864.05222232523.50499502237.11507843714.90925506725.1524047445.35665438682.99337833462.96815356190.29957435250.28578022071.34972937081.00154005980.13456869070.13791135595.1049584946.25827152552.45207373072.6084427824

    19936.58449705525.01134796393.12671397292.75195667764.10331069934.38630690357.43843838625.39009690144.92445280934.14307009293.13052797962.91696997840.25518267390.26129082641.26307402640.87886691550.13156781450.1252280285.12766489353.16839358142.29315349341.7485409957

    19946.1357792156.17973820473.06706420022.9849478484.21244589954.60407090087.6446190876.7456576955.00137096145.43296221843.42288314192.41083600590.21655846570.21230954441.23550855691.17882376260.12819498450.13877132425.23056224377.5306240922.22622306531.83619622

    19955.71764043025.80610642732.99794022622.49728739464.32061423824.91966068217.86510037047.0713715355.05873954194.67487835353.73146304312.79564844440.18362483930.16975331521.20498334511.07016138070.12549841850.12346786696.98451277748.6608646011.90741590482.3061898959

    19965.32799681084.26610105922.90466506143.34134284194.42141452974.01677424538.11508232357.49482567545.06507440985.83434572284.03773498334.82468247780.15438985270.16789576691.16654611560.96110239510.12507732280.11975071778.17305779987.24854710211.38584950341.12775744

    19974.96490647883.7012482322.8631546863.24857254134.54505305323.77987008428.32567539996.98345284665.17282157016.38663055554.43317380966.06013110990.13081646940.15179612931.14581358170.84546735130.12210072080.11472333589.11914544845.42074794061.2901525661.2585268231

    19984.62655989093.99913053712.74011362713.07395353514.6360502794.07088624118.62533335817.29254612155.10647030865.32370548264.74734169145.4403556930.11100845410.12111793711.09782029460.94328223320.11943838940.10779418337.93875051985.54833945021.12646685221.0615432582

    19994.31127081954.3712228432.67714286072.86957128564.75462593695.11189763178.87502277279.39040437235.16225435985.25109416245.17341054985.14526396010.09405604450.0889249511.07030301960.93399346370.11715518480.11724203218.31344598797.71313108671.06086551781.1874273017

    20004.01746794984.4798611182.46393258182.82265701874.80141260625.44958081619.308928601410.90459177744.8711369965.11936563375.36091856115.37404340790.07995022960.07477021870.99246070881.1348461060.11501913990.128981203510.697991957814.27362896840.74087043530.7820145884

    20013.7436870484.40823932822.66779720411.97695888395.05967833875.13106270769.255807421110.22065920175.54129008224.06629035216.37272583034.54479528940.06778437020.05506056191.05508529860.94369737660.11106622120.118195627113.084355909410.16073130360.79275997960.9817382348

    Sheet1

    trend [year]

    trend [year+env]

    count

    Heteromastus filiformis

    Sheet2

    trend [year]

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    Macoma balthica

    Sheet3

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    Bathyporeia pilosa

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    Pygospio elegans

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    Hydrobia ulvae

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    Aphelochaeta marioni

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    Nephtys cirrosa

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    Nereis diversicolor

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    Arenicola marina

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    Corophium volutator

    trend

    trend env

    count

    Cerastoderma edule

    7.06603023857.053215574

    6.58449705525.0113479639

    6.1357792156.1797382047

    5.71764043025.8061064273

    5.32799681084.2661010592

    4.96490647883.701248232

    4.62655989093.9991305371

    4.31127081954.371222843

    4.01746794984.479861118

    3.7436870484.4082393282

    trend [year]

    trend [year+env]

    count

    Heteromastus filiformis

  • Trends 1992-2001

    Chart6

    3.36009784423.4981826586

    3.12671397292.7519566776

    3.06706420022.984947848

    2.99794022622.4972873946

    2.90466506143.3413428419

    2.8631546863.2485725413

    2.74011362713.0739535351

    2.67714286072.8695712856

    2.46393258182.8226570187

    2.66779720411.9769588839

    trend [year]

    trend [year+env]

    count

    Macoma balthica

    Sheet1

    hetefilimacobaltbathpilopygoeleghydrulvaaphemarinephcirrneredivearenmaricorovoluceraedul

    trend [year]trend [year+env]predpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-envpredpred-env

    19927.06603023857.0532155743.36009784423.49818265864.05222232523.50499502237.11507843714.90925506725.1524047445.35665438682.99337833462.96815356190.29957435250.28578022071.34972937081.00154005980.13456869070.13791135595.1049584946.25827152552.45207373072.6084427824

    19936.58449705525.01134796393.12671397292.75195667764.10331069934.38630690357.43843838625.39009690144.92445280934.14307009293.13052797962.91696997840.25518267390.26129082641.26307402640.87886691550.13156781450.1252280285.12766489353.16839358142.29315349341.7485409957

    19946.1357792156.17973820473.06706420022.9849478484.21244589954.60407090087.6446190876.7456576955.00137096145.43296221843.42288314192.41083600590.21655846570.21230954441.23550855691.17882376260.12819498450.13877132425.23056224377.5306240922.22622306531.83619622

    19955.71764043025.80610642732.99794022622.49728739464.32061423824.91966068217.86510037047.0713715355.05873954194.67487835353.73146304312.79564844440.18362483930.16975331521.20498334511.07016138070.12549841850.12346786696.98451277748.6608646011.90741590482.3061898959

    19965.32799681084.26610105922.90466506143.34134284194.42141452974.01677424538.11508232357.49482567545.06507440985.83434572284.03773498334.82468247780.15438985270.16789576691.16654611560.96110239510.12507732280.11975071778.17305779987.24854710211.38584950341.12775744

    19974.96490647883.7012482322.8631546863.24857254134.54505305323.77987008428.32567539996.98345284665.17282157016.38663055554.43317380966.06013110990.13081646940.15179612931.14581358170.84546735130.12210072080.11472333589.11914544845.42074794061.2901525661.2585268231

    19984.62655989093.99913053712.74011362713.07395353514.6360502794.07088624118.62533335817.29254612155.10647030865.32370548264.74734169145.4403556930.11100845410.12111793711.09782029460.94328223320.11943838940.10779418337.93875051985.54833945021.12646685221.0615432582

    19994.31127081954.3712228432.67714286072.86957128564.75462593695.11189763178.87502277279.39040437235.16225435985.25109416245.17341054985.14526396010.09405604450.0889249511.07030301960.93399346370.11715518480.11724203218.31344598797.71313108671.06086551781.1874273017

    20004.01746794984.4798611182.46393258182.82265701874.80141260625.44958081619.308928601410.90459177744.8711369965.11936563375.36091856115.37404340790.07995022960.07477021870.99246070881.1348461060.11501913990.128981203510.697991957814.27362896840.74087043530.7820145884

    20013.7436870484.40823932822.66779720411.97695888395.05967833875.13106270769.255807421110.22065920175.54129008224.06629035216.37272583034.54479528940.06778437020.05506056191.05508529860.94369737660.11106622120.118195627113.084355909410.16073130360.79275997960.9817382348

    Sheet1

    trend [year]

    trend [year+env]

    count

    Heteromastus filiformis

    Sheet2

    trend [year]

    trend [year+env]

    count

    Macoma balthica

    Sheet3

    trend [year]

    trend [year+env]

    count

    Bathyporeia pilosa

    trend [year]

    trend [year+env]

    count

    Pygospio elegans

    00

    00

    00

    00

    00

    00

    00

    00

    00

    00

    trend

    trend env

    count

    Hydrobia ulvae

    trend [year]

    trend [year+env]

    count

    Aphelochaeta marioni

    trend [year]

    trend [year+env]

    count

    Nephtys cirrosa

    trend [year]

    trend [year+env]

    count

    Nereis diversicolor

    trend [year]

    trend [year+env]

    count

    Arenicola marina

    00

    00

    00

    00

    00

    00

    00

    00

    00

    00

    trend

    trend env

    count

    Corophium volutator

    trend

    trend env

    count

    Cerastoderma edule

    7.06603023857.053215574

    6.58449705525.0113479639

    6.1357792156.1797382047

    5.71764043025.8061064273

    5.32799681084.2661010592

    4.96490647883.701248232

    4.62655989093.9991305371

    4.31127081954.371222843

    4.01746794984.479861118

    3.7436870484.4082393282

    trend [year]

    trend [year+env]

    count

    Heteromastus filiformis

    3.36009784423.4981826586

    3.12671397292.7519566776

    3.06706420022.984947848

    2.99794022622.4972873946

    2.90466506143.3413428419

    2.8631546863.2485725413

    2.74011362713.0739535351

    2.67714286072.8695712856

    2.46393258182.8226570187

    2.66779720411.9769588839

    trend [year]

    trend [year+env]

    count

    Macoma balthica

  • Trends 1992-2001

  • Trend calculations: conclusionsFor some species, regression models with the factor year as independent variable or regression models with the factor year and environmental variables as independent variables showed similar results, but for several species the significant trend disappeared when environmental variables were included

    environmental variables, incorporated into regression models, might improve long-term trend calculations, as they allow to compensate for differences in local environmental variability.

  • GENERAL CONCLUSIONSThe results demonstrate the important role environmental variables play in explaining variability of soft-sediment benthic macrofauna at scales from 100m to complete estuarine systems.

    Predictions of presence-absence data of macrobenthic species successful within the Schelde estuary

    environmental variables, incorporated into regression models, might improve long-term trend calculations, as they allow to compensate for differences in local environmental variability.

  • GENERAL CONCLUSIONSA large proportion of variance is in 10m - 100 m unpredictable patchiness and (biologically induced?) year-to-year variation

    Emphasis of monitoring of impacts should be on long-term (> 3yr) average populations, and should be related to long-term changes in environment

    There is a gap in the monitoring scheme at scales between 1m and ~200 m, which could be important to cover

  • Thank youData obtained in co-operation with RIKZ,the National Institute for Coastal and Marine Management (The Netherlands)