development of individual-based models in shorebirds

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DEVELOPMENT OF INDIVIDUAL-BASED MODELS IN SHOREBIRDS

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  • DEVELOPMENT OF INDIVIDUAL-BASED MODELS IN SHOREBIRDS

  • High Water MarkLow Water MarkWASH1972-75Intertidal mudflats and sandflatsProposed fresh-water reservoir

  • HOW WE THOUGHT ABOUT THE ISSUEDecreasing area Increasing densityIncreasing competitionPercentage starving over winter

  • EMPIRICAL APPROACH?Increasing densityPercentage starving over winterXX X X X X X X XX??(i) It would be technically very difficult 0 0 0 0 0 00 0 0

  • Increasing densityPercentage starving over winterHabitat of above average quality is lostHabitat of average quality is lost..and (ii) the function would probably change after habitat loss

  • THE QUESTION: HOW TO DESCRIBE THE DENSITY-DEPENDENT STARVATION FUNCTION - NOT ONLY AS IT IS AT PRESENT BUT HOW IT WOULD BE IF THE FEEDING ENVIRONMENT WAS CHANGED BY:Habitat loss Disturbance ShellfishingSea-level rise Mitigation measuresetc etc

  • EVENTUAL ANSWER: develop and test individual-based models using oystercatchers eating mussels on the Exe estuary

  • MUSSELSLOCAL ISSUE: WOULD HARVESTING MUSSELS AFFECT THE BIRDS?

  • NO EFFECT EFFECTIncreasing harvest/Decreasing food supply Percentage starving

    Before After

  • DEVELOPMENT OF THE MODEL1976-1996Field work on interference and exploitation competition between oystercatchers for mussels

  • HOW THE MODEL WORKSMORE DETAILS AT:http://www.dorset.ceh.ac.uk/shorebirds/

  • Each bird decides each tide where, when and on what prey species it is best to feedhttp://www.dorset.ceh.ac.uk/shorebirds/

  • Each of the three displaced birds will choose the next best place in which to feedPRINCIPLE: birds in model use optimality decision rules (= fitness maximising) to decide how to respond to a change in their feeding environment just as real birds do

  • Calibration period for overwinter mortality of adult mussel-feeding oystercatchers on the Exe

    Sept 1976 Mar 1980

  • MORE NATURAL HISTORY WAS NEEDED: eg. feeding in fields over high tide

  • Predicted (retrospective) and observed increase in mortality 1980 - 1999Calibration period:

  • CONCLUSION

    Winter mortality was density-dependent and the model postdicted it quite well

  • NO LONGER SO!Applying the model to species other than Oystercatchers: some say that they take too long to parameteriseThe models can usually be built, tested and applied within the time typically taken to conduct an EIA: i.e. 1 3 years

  • Bird energetics Prey energy content Functional responses Interference functions Food supply, exposure time, weather Human activities eg. fisheryObtained for the site being modelledBuilt into model allometric functionsMODELS CAN NOW BE BUILT AND TESTED VERY QUICKLY AS MOST PARAMETERS ARE IN THE LITERATURE:

  • Applications to other species: whatwe need to know

    Bird energetics Prey energy content Functional response Interference function Food supply, exposure time and weatherAPPLICATION TO OTHER SPECIES - 1

  • Functional responses of oystercatchers eating musselsA

    Chart2

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    Data

    Fit

    Biomass density of mussels > 30mm long(gAFDM/sq m)

    Intake rate (mgAFDM/s)

    Sheet1

    vh=2 dh=1 st=0Site AFDM IR (mgAFDM/s)Days since August 1stMussels >30mm per sq.mSite biomass >30mm (gAFDM30mm (gAFDM/sqm)c6c7fitsc6c7residsc2c5fitsc2c5residsc2c4fitsc2c4residsFMFitBiomc2c5fitFitNumberc2c4fit

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    Sheet1

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    Data

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    Biomass density of mussels > 30mm long(gAFDM/sq m)

    Intake rate (mgAFDM/s)

    Sheet2

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    (b)

    Data

    Fit

    Biomass density of mussels > 30mm long(gAFDM/sq m)

    Intake rate (mgAFDM/s)

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    (c)

    Data

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    Biomass density of mussels > 30mm long(gAFDM/sq m)

    Intake rate (mgAFDM/s)

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    (a)

    Data

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    Numerical density of mussels > 30mm long(no./sq m)

    Intake rate (mgAFDM/s)

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    (b)

    Data

    Fit

    Numerical density of mussels > 30mm long(no./sq m)

    Intake rate (mgAFDM/s)

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    (c)

    Data

    Fit

    Numerical density of mussels > 30mm long(no./sq m)

    Intake rate (mgAFDM/s)

  • Predicting the asymptote of the functional response in shorebirds from 486 spot estimates of intake rate

    Intake rate (i.e. asymptote) depends on:

    Body mass of bird Mass of prey

    R2 = 75.5% (log transformed data)

  • Curlew sandpiperKnotRedshankGrey ploverCurlewOystercatcherTEST OF PREDICTIONS FOR ASYMPTOTEy = x

  • Test of predictions for asymptotes

    Observed asymptotes

    Predicted asymptote (mgAFDM/s)

  • Applications to other species: whatwe need to know

    Bird energetics Prey energy content Functional response Interference function Food supply, exposure time and weatherAPPLICATION TO OTHER SPECIES - 2

  • Interference function for stabbing oystercatchers: intake rate (mgAFDM/s) against density of birds

  • Prey sizeBird sizeHandling timeRunning speedPredicting interference parameters from Stillmans state-dependent behavioural model Interference function

  • Test of Stillmans behaviour-based model: cockle-eating oystercatchers on the baie de Somme

  • Predicted and observed interference functions in cereal-feeding cranes. Predictions from Stillmans model. Data: L. M. Bautista, J. C. Alonso & J. Alonso.

  • Applications to other species: whatwe need to know

    Bird energetics Prey energy content Functional response Interference function Food supply, exposure time and weather Human activitiesAPPLICATION TO OTHER SPECIES and SYSTEMS What do we need to measure?

  • RECENT DEVELOPMENTS Risk of being killed by predators: trade-off between foraging and safety

    Multi-species models:up to 9 species in one estuary

    Multi-site models:several estuaries across several countries

  • SOME EXAMPLES OF RECENT APPLICATIONS IN SHOREBIRDSOystercatchersShellfishing, disturbance 8 estuaries 4 countries

    Other shorebirds: Disturbance, habitat loss,12 speciesbait-digging, Spartina 10 estuariesencroachment, hunting 4 countriessea-level rise, monitoringestuary quality, mitigation

    WildfowlHunting, farming, wind4 speciesfarms >25 estuaries 4 countriesBlue - examples used here

  • 1. OYSTERCATCHERS and SHELLFISHINGHow much shellfish should we leave after shellfish harvesting to ensure that the birds fitness is not reduced?

  • EXE: oystercatchers eating musselsPrey biomass/bird left over after shellfish harvesting

    Mortality Fail to reach target body mass

    %%With disturbanceNo disturbanceRange 1976-19990 55 110 165 kg/bird0 55 110 165 kg/bird

  • CRITICAL THRESHOLD or ECOLOGICAL FOOD REQUIREMENT (food/bird)Critical threshold = 61kgAFDM/birdPercentage starvingEXE ESTUARY

  • Ecological requirement Multiples of (threshold)kgAFDM/bird Exe Mussel 61 9.13 7.74

    Bangor Mussel 50 9.62 6.42 Burry Cockle 44 9.27 5.58

    Wash Cockle 20 7.93 2.52

    Somme Cockle 33 6.56 5.03

    * Taking into account wastage of shellfish flesh (stolen from the birds; winter loss of flesh from the shellfish themselves) Critical threshold or Ecological requirement (E) Physiological requirement (P)kgAFDM/bird kgAFDM/bird * E/P

  • Because of interference and individual variation in efficiency, just leaving enough shellfish for oystercatchers after harvesting is not enough to ensure they survive in good condition - as Dutch experience confirmsCONCLUSION: ecological requirements are 3-8 times larger than physiological requirements

  • 2.DISTURBANCE: people and raptors

  • SOMME : DISTURBANCE IN OYSTERCATCHERSACTUAL AMOUNT:1994-951996-971997-981997-98 including raptors

    DISTURBANCES PER HOURPERCENTAGE STARVINGSevere winterMild winter

  • POLICY ADVICE:

    IN SEVERE WINTERS, DO NOT ALLOW OYSTERCATCHERS TO BE DISTURBEDBUTIN MILD WINTERS, THEY CAN BE DISTURBED but only up to about ONE disturbance/hour - including raptors

  • 3.SPREAD OF THE GRASS Spartina ON TO UPSHORE MUDFLATS

  • SOMME: Spartina spreads downshore at 20-40m per year into the feeding areas of dunlin

    High Water mark

  • 0ha 100ha 200ha 0 years 5 years 10 yearsDunlin with Spartina spreading at 40m/yearMortality over winter %POLICY ADVICE: get rid of it!

  • 4.HABITAT LOSS and MITIGATION for it

  • English ChannelR. SeinePORT (105 ha of mudflats)MITIGATION: Convert reed beds into 50 or 100 ha of mudflatsHigh Water MarkPORT DEVELOPMENT: SEINE ESTUARY

  • 5%

    0%Mortality %Before PortAfter Port50ha mitigation 100ha mitigationFailing to reach 75% body mass %15%0%DUNLIN in SEINE ESTUARY: Port development and proposed mitigationScenarioScenario

  • POLICY ADVICE:

    The mitigation is needed but should be 100ha if it is to fully effective

  • TESTS of model predictions:

    Distribution and prey choiceImpact on food supplyHours feeding per daylight tide4Mortality of oystercatchers

    CONFIDENCE IN MODEL PREDICTIONS?

  • Percentage of birds1. DISTRIBUTION and PREY CHOICE: proportion of birds eating cockles or mussels in the Burry InletObserved = Predicted =

  • 2. IMPACT ON FOOD: Mussel consumption by oystercatchers on the ExeObservedPredictedPercentExclosure Survey

    Chart3

    12.1

    12.1

    11.4

    Deadbirds

    BirdBirdName$AgeClFeedMethFightAbPropDomPatTypeIFIRBirdAliveIntDay1FESTI

    103+S3113.020.13021109.331000.08354350-0.2668136238

    132S2117.650.1765152.451300.058772565-0.2052213001

    143+S3131.590.3159189.19140-0.015806585-0.1230982019

    163+S3132.340.3234182.76160-0.0198191250.0411479945

    252S2139.340.3934177.32250-0.0572691450.1232710927

    293+S3114.530.14531122.522900.0754645

    362S210.850.0085184.883600.1486525

    423+S3115.120.1512197.114200.072308

    522S216.470.06471101.255200.1185855

    553+S310.240.0024186.245500.151916

    563+S319.630.09631100.085600.1016795

    573+S310.90.009183.25700.148385

    593+S312.650.0265187.955900.1390225

    623+S3124.120.2412180.296200.024158

    701S1134.580.3458185.42700-0.031803

    773+S3124.250.24251105.457700.0234625

    783+S3132.960.3296195.41780-0.023136

    793+S317.620.07621129.37900.112433

    802S2111.530.11531100.478000.0915145

    923+S3143.340.4334178.92920-0.078669

    942S2143.830.4383172.77940-0.0812905

    953+S3145.330.4533186.64950-0.0893155

    1042S2137.70.377173.411040-0.048495

    1073+S319.040.09041103.410700.104836

    1253+S313.880.0388190.3412500.132442

    1272S2122.240.22241105.1812700.034216

    1283+S314.170.0417189.5712800.1308905

    1343+S318.160.0816195.9113400.109544

    1403+S3113.120.13121108.0214000.083008

    1443+S3138.120.3812168.121440-0.050742

    1473+S3143.920.4392190.951470-0.081772

    1503+S315.560.0556193.7115000.123454

    1523+S313.020.0302172.0515200.137043

    1633+S319.370.09371104.9316300.1030705

    1703+S3129.360.2936189.571700-0.003876

    1733+S31530.53176.011730-0.13035

    1792S2115.340.15341117.7817900.071131

    1883+S3114.130.14131102.2518800.0776045

    1893+S3120.110.20111105.318900.0456115

    1963+S313.620.0362197.8119600.133833

    1993+S3141.540.4154183.171990-0.069039

    2103+S3114.150.14151106.9821000.0774975

    2193+S3130.170.3017181.662190-0.0082095

    2343+S3146.210.4621172.862340-0.0940235

    2411S111.760.01761106.7824100.143784

    2423+S3140.150.4015159.262420-0.0616025

    2453+S319.480.0948183.7224500.102482

    2463+S3121.070.21071100.9124600.0404755

    2511S1122.330.2233110525100.0337345

    2603+S3114.80.1481101.0126000.07402

    2653+S311.380.01381103.9226500.145817

    2692S2119.920.1992183.0726900.046628

    2813+S3113.380.1338194.9228100.081617

    2901S1124.330.2433189.6529000.0230345

    2943+S3129.690.2969176.952940-0.0056415

    2992S2136.420.3642189.472990-0.041647

    3003+S3110.80.1081112.9630000.09542

    3103+S3115.650.1565172.0731000.0694725

    3173+S3124.280.2428188.2231700.023302

    3183+S315.860.05861136.4431800.121849

    3303+S3114.150.14151107.8333000.0774975

    3512S2111.430.1143194.5935100.0920495

    3552S2131.780.3178173.683550-0.016823

    3883+S3110.770.10771104.0138800.0955805

    3932S2143.060.4306181.813930-0.077171

    3983+S3130.170.30171113.783980-0.0082095

    4093+S3135.480.3548189.124090-0.036618

    4133+S3111.40.1141105.2441300.09221

    4223+S3119.960.1996192.5842200.046414

    4293+S313.860.0386190.3642900.132549

    4303+S316.740.06741116.8243000.117141

    4352S2129.280.2928180.84350-0.003448

    4373+S317.890.0789192.0743700.1109885

    4503+S3131.110.3111192.254500-0.0132385

    4623+S3137.530.3753190.164620-0.0475855

    4663+S3121.720.2172197.3346600.036998

    4693+S3156.120.5612165.154690-0.147042

    4873+S3125.890.25891104.3648700.0146885

    4892S2124.390.2439164.148900.0227135

    4923+S3120.880.20881101.949200.041492

    4941S1110.650.1065189.9649400.0962225

    4973+S3139.760.3976180.134970-0.059516

    5003+S319.230.0923181.8650000.1038195

    13+S3171.520.7152199.2511-0.229432

    62S2136.930.36931109.2161-0.0443755

    83+S3161.650.6165183.1881-0.1766275

    122S2166.170.6617194.49121-0.2008095

    193+S3129.630.29631120.65191-0.0053205

    202S2156.810.56811114.96201-0.1507335

    213+S3176.420.76421122.28211-0.255647

    223+S3150.90.5091117.62221-0.119115

    243+S3145.610.45611115.16241-0.0908135

    303+S3170.960.7096190.9301-0.226436

    323+S3160.420.6042195.5321-0.170047

    343+S3124.870.24871126.173410.0201455

    353+S3188.850.88851109.98351-0.3221475

    373+S3192.750.92751107.15371-0.3430125

    433+S3146.580.46581123.31431-0.096003

    453+S3176.070.76071116.32451-0.2537745

    493+S3184.480.84481102.03491-0.298768

    513+S3132.960.32961100.92511-0.023136

    613+S3164.670.64671101.92611-0.1927845

    643+S3196.960.96961134.31641-0.365536

    652S215.150.0515196.046510.1256475

    663+S3168.760.6876181.19661-0.214666

    713+S3174.590.74591100.08711-0.2458565

    723+S3124.190.24191119.387210.0237835

    863+S3192.010.92011114.86861-0.3390535

    883+S3194.380.94381106.11881-0.351733

    913+S3197.20.9721106.78911-0.36682

    1033+S3144.640.44641106.761031-0.085624

    1053+S3155.520.5552192.451051-0.143832

    1082S2157.30.5731121.931081-0.153355

    1093+S3177.290.77291106.111091-0.2603015

    1103+S3164.490.64491110.71101-0.1918215

    1133+S3195.580.9558177.161131-0.358153

    1143+S3178.440.7844195.921141-0.266454

    1193+S3172.280.72281105.91191-0.233498

    1203+S3162.850.62851103.011201-0.1830475

    1223+S3144.80.448178.731221-0.08648

    1243+S3146.890.4689180.81241-0.0976615

    1303+S3187.410.8741187.931301-0.3144435

    1313+S3193.580.9358177.291311-0.347453

    1323+S3178.450.7845179.81321-0.2665075

    1353+S3139.760.3976170.31351-0.059516

    1383+S3135.820.35821102.191381-0.038437

    1393+S3125.730.25731127.0713910.0155445

    1453+S3123.880.23881138.3414510.025442

    1573+S3157.980.57981117.281571-0.156993

    1663+S3167.510.6751187.231661-0.2079785

    1683+S3187.460.8746175.291681-0.314711

    1693+S3168.220.68221113.151691-0.211777

    1713+S31990.991101.671711-0.37645

    1783+S3138.230.38231101.531781-0.0513305

    1803+S3135.120.35121114.811801-0.034692

    1823+S3177.450.7745196.591821-0.2611575

    1832S2143.950.4395191.211831-0.0819325

    1863+S3160.520.6052192.851861-0.170582

    1953+S3177.620.77621115.341951-0.262067

    1973+S3162.030.62031113.971971-0.1786605

    2013+S31780.78185.892011-0.2641

    2073+S3131.740.31741119.962071-0.016609

    2143+S3182.980.8298192.732141-0.290743

    2163+S3175.450.75451110.152161-0.2504575

    2183+S3199.940.9994186.252181-0.381479

    2203+S3135.040.35041108.172201-0.034264

    2242S2144.750.4475179.482241-0.0862125

    2273+S3123.020.23021122.422710.030043

    2333+S3187.590.8759198.922331-0.3154065

    2353+S3164.110.64111112.362351-0.1897885

    2383+S3166.990.66991108.412381-0.2051965

    2393+S3182.40.8241119.982391-0.28764

    2433+S3125.160.25161118.1924310.018594

    2443+S3176.770.7677198.282441-0.2575195

    2473+S3194.410.94411106.432471-0.3518935

    2543+S3191.060.91061105.952541-0.333971

    2573+S3196.460.96461131.912571-0.362861

    2593+S3195.30.9531107.842591-0.356655

    2613+S3152.060.5206175.062611-0.125321

    2623+S3177.580.77581114.172621-0.261853

    2661S1151.530.5153196.442661-0.1224855

    2673+S3142.860.4286196.762671-0.076101

    2733+S3178.790.7879198.22731-0.2683265

    2743+S3187.030.87031115.762741-0.3124105

    2793+S3167.10.6711109.152791-0.205785

    2833+S3170.420.7042199.052831-0.223547

    2843+S3182.010.82011105.272841-0.2855535

    2871S1134.760.34761121.072871-0.032766

    3022S2151.820.51821106.693021-0.124037

    3033+S3178.350.7835195.223031-0.2659725

    3043+S3188.250.8825187.183041-0.3189375

    3063+S3150.60.506194.763061-0.11751

    3113+S3189.810.89811114.453111-0.3272835

    3193+S3171.440.7144199.553191-0.229004

    3203+S3134.110.34111100.73201-0.0292885

    3253+S3175.080.7508187.263251-0.248478

    3293+S3184.170.8417172.453291-0.2971095

    3353+S3166.80.6681118.473351-0.20418

    3423+S31950.95187.853421-0.35505

    3453+S3179.010.7901195.823451-0.2695035

    3463+S317.510.0751199.6834610.1130215

    3473+S3156.710.56711111.273471-0.1501985

    3493+S3151.840.51841110.973491-0.124144

    3523+S3157.940.5794188.73521-0.156779

    3533+S3166.940.6694180.263531-0.204929

    3603+S3167.440.67441103.63601-0.207604

    3622S2156.970.5697186.723621-0.1515895

    3652S2120.040.20041111.2236510.045986

    3673+S3186.010.86011125.533671-0.3069535

    3743+S3152.610.52611120.483741-0.1282635

    3783+S3144.630.4463190.513781-0.0855705

    3791S1146.470.46471125.33791-0.0954145

    3833+S3155.890.5589189.743831-0.1458115

    3913+S3193.20.9321103.553911-0.34542

    3923+S3135.990.35991117.963921-0.0393465

    4013+S3151.390.51391108.34011-0.1217365

    4023+S3174.410.7441193.244021-0.2448935

    4063+S3112.420.1242198.840610.086753

    4103+S3132.440.32441115.144101-0.020354

    4113+S3136.70.3671116.494111-0.043145

    4143+S3153.990.5399193.694141-0.1356465

    4153+S3186.720.8672187.394151-0.310752

    4173+S3152.470.5247195.594171-0.1275145

    4233+S3191.430.91431115.484231-0.3359505

    4243+S3133.520.33521103.634241-0.026132

    4273+S3186.880.8688175.424271-0.311608

    4323+S3198.270.9827177.854321-0.3725445

    4363+S3163.430.6343195.514361-0.1861505

    4383+S3123.350.23351119.9643810.0282775

    4393+S3162.530.62531116.554391-0.1813355

    4403+S3184.520.8452188.254401-0.298982

    4443+S3164.750.64751118.924441-0.1932125

    4453+S3158.440.5844196.614451-0.159454

    4553+S3168.040.6804194.614551-0.210814

    4573+S3168.570.68571103.454571-0.2136495

    4603+S3141.90.4191112.464601-0.070965

    4682S2133.410.33411120.754681-0.0255435

    4713+S3190.350.9035197.964711-0.3301725

    4743+S3193.350.93351109.774741-0.3462225

    4763+S3174.260.7426175.624761-0.244091

    4793+S3133.480.33481102.44791-0.025918

    4803+S3168.410.68411109.594801-0.2127935

    4813+S3196.530.9653198.84811-0.3632355

    4883+S3142.480.4248196.754881-0.074068

    4933+S3154.360.5436168.164931-0.137626

    Deadbirds

    0.083543-0.229432-0.2668136238

    0.0587725-0.0443755-0.2052213001

    -0.0158065-0.1766275-0.1230982019

    -0.019819-0.20080950.0411479945

    -0.057269-0.00532050.1232710927

    0.0754645-0.1507335

    0.1486525-0.255647

    0.072308-0.119115

    0.1185855-0.0908135

    0.151916-0.226436

    0.1016795-0.170047

    0.1483850.0201455

    0.1390225-0.3221475

    0.024158-0.3430125

    -0.031803-0.096003

    0.0234625-0.2537745

    -0.023136-0.298768

    0.112433-0.023136

    0.0915145-0.1927845

    -0.078669-0.365536

    -0.08129050.1256475

    -0.0893155-0.214666

    -0.048495-0.2458565

    0.1048360.0237835

    0.132442-0.3390535

    0.034216-0.351733

    0.1308905-0.36682

    0.109544-0.085624

    0.083008-0.143832

    -0.050742-0.153355

    -0.081772-0.2603015

    0.123454-0.1918215

    0.137043-0.358153

    0.1030705-0.266454

    -0.003876-0.233498

    -0.13035-0.1830475

    0.071131-0.08648

    0.0776045-0.0976615

    0.0456115-0.3144435

    0.133833-0.347453

    -0.069039-0.2665075

    0.0774975-0.059516

    -0.0082095-0.038437

    -0.09402350.0155445

    0.1437840.025442

    -0.0616025-0.156993

    0.102482-0.2079785

    0.0404755-0.314711

    0.0337345-0.211777

    0.07402-0.37645

    0.145817-0.0513305

    0.046628-0.034692

    0.081617-0.2611575

    0.0230345-0.0819325

    -0.0056415-0.170582

    -0.041647-0.262067

    0.09542-0.1786605

    0.0694725-0.2641

    0.023302-0.016609

    0.121849-0.290743

    0.0774975-0.2504575

    0.0920495-0.381479

    -0.016823-0.034264

    0.0955805-0.0862125

    -0.0771710.030043

    -0.0082095-0.3154065

    -0.036618-0.1897885

    0.09221-0.2051965

    0.046414-0.28764

    0.1325490.018594

    0.117141-0.2575195

    -0.003448-0.3518935

    0.1109885-0.333971

    -0.0132385-0.362861

    -0.0475855-0.356655

    0.036998-0.125321

    -0.147042-0.261853

    0.0146885-0.1224855

    0.0227135-0.076101

    0.041492-0.2683265

    0.0962225-0.3124105

    -0.059516-0.205785

    0.1038195-0.223547

    -0.2855535

    -0.032766

    -0.124037

    -0.2659725

    -0.3189375

    -0.11751

    -0.3272835

    -0.229004

    -0.0292885

    -0.248478

    -0.2971095

    -0.20418

    -0.35505

    -0.2695035

    0.1130215

    -0.1501985

    -0.124144

    -0.156779

    -0.204929

    -0.207604

    -0.1515895

    0.045986

    -0.3069535

    -0.1282635

    -0.0855705

    -0.0954145

    -0.1458115

    -0.34542

    -0.0393465

    -0.1217365

    -0.2448935

    0.086753

    -0.020354

    -0.043145

    -0.1356465

    -0.310752

    -0.1275145

    -0.3359505

    -0.026132

    -0.311608

    -0.3725445

    -0.1861505

    0.0282775

    -0.1813355

    -0.298982

    -0.1932125

    -0.159454

    -0.210814

    -0.2136495

    -0.070965

    -0.0255435

    -0.3301725

    -0.3462225

    -0.244091

    -0.025918

    -0.2127935

    -0.3632355

    -0.074068

    -0.137626

    Dead

    Alive

    Discriminant

    Feeding Efficiency (%)

    STI at the start of the winter

    MusselsLost

    Exclosures12.1

    Estuary-wide12.1

    Model prediction11.4

    MusselsLost

    0

    0

    0

    Percent

    Percent of mussels lost over the winter

    DisturbanceCosts

    NoDist%dead

    500499.33333333330.1333333333

    1000995.66666666670.4333333333

    15001459.66666666672.6888888889

    20001882.66666666675.8666666667

    3500301014

    5000385023

    75004693.333333333337.4222222222

    100005153.333333333348.4666666667

    &R&14&D

    DisturbanceCosts

    00.13333333330.41.066666666711.0666666667

    01.22.33333333337.320.6666666667

    04.46.9113.8230.5333333333

    07.911.320.8554.3766666667

    015.236666666723.6240.096666666763.6666666667

    027.733333333337.653.066666666775.3766666667

    041.4753.066666666765.1180.0333333333

    053.163.566666666772.80

    No Disturbance

    10% without costs

    10% with costs

    50% without costs

    50% with costs

    Initial number of birds

    Percent mortality

    Costs of disturbance

    NoDepletion

    0.13333333330.13333333330.13333333330.20.06666666670.40.41

    1.13333333330.43333333331.03333333330.93333333331.43333333332.33333333333.97

    4.62.68888888894.37666666673.97666666673.75666666676.9112.58

    7.98333333335.86666666677.48333333337.257.516666666711.318.8266666667

    17.33333333331415.813333333317.523333333315.8123.6240.0566666667

    29.33333333332326.266666666725.266666666724.837.660.05

    45.333333333337.422222222242.356666666741.641.823333333353.066666666786.8

    55.848.466666666753.352.566666666751.033333333363.566666666798.9766666667

    Big

    NoDist

    BigNC

    Best10

    Worst10

    Small

    SmallNC

    Initial number of birds

    Percent mortality

    10% of area disturbed or lost

    0.66666666670.13333333330.80.66666666670.83.26666666671.0666666667

    5.63333333330.43333333333.75.93333333335.611.06666666677.3

    12.66666666672.68888888899.513333333312.5810.846666666720.666666666713.82

    18.93333333335.866666666714.7518.883333333316.083333333330.533333333320.85

    36.28333333331429.6238.7633.426666666754.376666666740.0966666667

    49.62340.450.733333333343.463.666666666753.0666666667

    62.843333333337.422222222257.3866.933333333360.6275.376666666765.11

    69.733333333348.466666666766.375.066666666775.433333333380.033333333372.8

    Big

    NoDist

    BigNC

    Best50

    Worst50

    Small

    SmallNC

    Initial number of birds

    Percent mortality

    50% of area disturbed or lost

    FileExtAgeFM% in fieldsProportion of time feedingMean mass loss% MortalityInitial NFinal NULDepULNoDep

    00a001AllAll4.410.5410.010.250049900.0666666667

    00b001AllAll15.230.6420.860.310009970.83333333330.8333333333

    00c001AllAll23.20.7223.021.07150014842.88888888892.2444444444

    00d001AllAll32.160.7847.442.4200019526.16666666675.3833333333

    0.00E+00AllAll58.150.8815.186.573500327015.714285714313.9047619048

    00f001AllAll69.090.90817.0911.65000442026.733333333322.8666666667

    00g001AllAll78.460.95823.217.077500622046.088888888939.6888888889

    00h001AllAll82.240.97243.0623.510000765061.066666666750.8333333333

    00i001AllAll82.890.97657.7130.72125008660

    00j001AllAll84.550.98173.8237.93150009310

    00k001AllAll85.640.982108.0260.35200007930

    00l001AllAll88.550.992140.5486.43300004070

    500499.6666666667

    991.6666666667991.6666666667

    1456.66666666671466.3333333333

    1876.66666666671892.3333333333

    29503013.3333333333

    3663.33333333333856.6666666667

    4043.33333333334523.3333333333

    3893.33333333334916.6666666667

    000

    000

    000

    000

    000

    000

    000

    000

    0

    0

    0

    0

    No decline

    Depletion

    No Depletion

    Number of oystercatchers in September

    Percent starving by March

    500

    991.6666666667

    1456.6666666667

    1876.6666666667

    2950

    3663.3333333333

    4043.3333333333

    3893.3333333333

    Initial N

  • 3. HOURS FEEDING: oystercatcher (open symbols), little stint, sanderling, dunlin, curlew. Exe estuary, Burry Inlet, Bangor flats, Seine estuary; Cadiz bay.

  • 4. MORTALITY (from autumn to spring) % (se) % (se) N* Predicted ObservedWash*: shellfish abundant 4 0 1.4 (0.3) Wash*: shellfish scarce 3 15.9(4.9) 16.8 (6.4)Exe: low bird density 3 2.3(0.4) 1.7 (0.3)Exe: high bird density 3 3.8(0.1) 3.5 (1.0)Burry Inlet: cockles and mussels: 1 0 ?Bangor mussel beds: 1 0 ?

    * Number of years* Assuming upshore intake rates same as on Exe

  • Basic principles upon which the models are built

    1 Well-established behavioural decision rules so that animals in the model are likely to respond to environmental changes as real ones would

    2 Include some natural history details because these adaptations can be critical to bird survival

    3Calibration may be needed - because we don't know every parameter value precisely

    4 Validation of mortality predictions otherwise predictions should not be believed

  • http://www.dorset.ceh.ac.uk/shorebirds/FIND OUT MORE ON:Co-workers:Richard Stillman Richard Caldow Sarah Durell Andy West

  • EVEN A SMALL DECREASE IN MORTALITY COULD BE VERY IMPORTANT!!

  • Equilibrium population size..population size is very sensitive to mortality rate, irrespective of the density-dependence on the breeding groundsWeak density dependence in summer Oystercatcher rangeStrong density dependence in summer

    Chart1

    161.96473.868

    56.34295.504

    29.5128.314

    18.2360.596

    0.5960.102

    0.1020.07

    0.07

    bT = 0.3

    bT = 0.7

    Adult annual mortality (%)

    Sheet1

    Adult mortality (%)Stable Population Size

    bT = 0.3bT = 0.7

    214338641619601433.864161.96

    447386856342473.86856.342

    6955042951095.50429.51

    8283141823628.31418.236

    105965960.5960.596

    121021020.1020.102

    1470700.070.07

    1624240.0240.024

    Sheet1

    00

    00

    00

    00

    00

    00

    0

    bT = 0.3

    bT = 0.7

    Adult mortality (%)

    Equilibrium Population Size (000s)

    Sheet2

    Sheet3

  • The model had to be able to predict FITNESSMortality rate over the winterBUT ALSO2Fat reserves in springPRINCIPLE: If the FITNESS of the birds in the non-breeding season is maintained, the quality of the estuary for the birds is being maintained