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Allen RL. 1983. Feeding behaviour of Asterias rubens (1..I on soli hottom bivalves, a stud) in selective predation. J. exp. mar. BioL Ecol. 70:79-90. Ankai S. I'WO. Growlh and production of Macoma huliliicu (L.) in a northern Baltic sofl bottom, Ophelia Suppl. I: 31-48. •\noiiyiiius 1962. Mean monthly tcmperalurc and salinity of ihe sur face layer of the North Sea and adjacent waders from 1905 IO 1954. Conseil pom I'evploraiion de la mer service hydro- graphique. Charlottenlund Slot Ansell A.D. 1962. Observations on burrowing in the Veneridac (Eu- lamellibranchia). Biol. Hull mar. biol. Woods Hole 123 721 530. Ansell A.D. A: A 1'revallion l%7. Sludies on Tellina tenuis Da Costa I. Seasonal growth ami biochemical cycle. J. exp. mar. Biol. Ecol. 1:220-235 Ashkena/ie -S. & U.N. Safriel 1979. Time-energy budget oi the Semipalmaled Sandpiper Calidris pusilla ai Barrow. Alaska Ecology 60:783-799. Bachelet G. 1979. Dynamiqiicdc la macrofaunahentiqueet pnxluc lion des l.ainellibranclies de I'esiuairc dc la Gironde. Thesis University Pierre el Mane Curie, Pans Baehelel Cl. 1980 Growth and rccruumenl of Ihe tellinid bivalve Macoma balthica al the southern limit of its geographical dis tribution. Uie Gironde estuary (S . Mai Biol. 59: 105- 117. Bachelet G. I9KI. Application de I'equation de Von Bertalanffy Ilia croissaoce du bivalve Scrobicularia plana. Cah. Biol. Mar 22 291-311. Baggcrman B 1953. Spatfall and transport of Cardium edule L. Arch. Neerl. Zool 10: 315-342. Baird R.H. 1966. Factors affecting the growth and condition of Mus sels {Mytilus edulis Li. Rah. Invest Land. (See Hi 25: 1-33. Baird D. & H. Milne 1981. Energy Bow in the Yih.in estuary. Aberdeenshire. Scotland Esiuar. (sil Shelf Sci. 13: 455- 472. Barnard CJ. 1980. Equilibrium Hock si/e ami factors affecting arrival and departure in feeding house sparrows. Anim. Behav 28:503-511. Barnes R.S.K. 1986. Daily activity rhythms in the intertidal . rjodlVw/rof-ia «/«•
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WADERS AND THEIR ESTUARINE FOOD SUP
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plia^ohi. WADERS AND THEIR ESTUARI
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Waders and their estuarine food sup
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WADERS AND THEIR ESTUARINE FOOD SUP
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figuren: Dick Visser omslagfoto: Ja
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15 Versatility of male curlews (Num
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That science is making progress, ma
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INTRODUCTION The remnants of brushw
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When hcnlhic bivalves extend llien
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the burrow depths and on the fracti
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INTRODUCTION Ms,i invest 409 of (he
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able lo sw itch 10 oiher prey which
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Long-term, broadly-based research c
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Chapter 1 SEASONAL VARIATION IN BOD
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SEASONAL VARIATION IN BODY WEIGHT O
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Tahle 1 Weight loss ('•- ± SE) m
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i 60 50 40 30 20 10 0 • INFESTED
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240- SEASONAL VARIATION IN BODY WEI
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20 10 0 -10 -20h 2 3 4 5 6 7 8 9 se
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a E 400 - S. plana 35 mm 320 240 16
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Chapter 2 HOW THE FOOD SUPPLY HARVE
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FOOD SUPPLY HARVESTABLE BY WADERS H
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Methods The study sites were situat
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less than that of bivalves, partly
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I Fig. 3). Peak condition was reach
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total biomass since most of those t
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on the basis of the preceding and t
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However, for obvious reasons, we ma
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prey. A decrease in the prey densit
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Tahle 2. The intake rate ol < lyste
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* ' % -. . ; a X - . - * • ^ •
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(Zwarts & Wanink 1989). In quiet we
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general law relating handling time
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nearly twice as much time (0.79 s).
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4 5 6 7 8 9 size class of Corophium
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and annually. Second, the lower siz
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Prey switching Waders feeding on ti
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autumn and spring, and the contrary
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where they switch to surface-living
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Chapter 3 BURYING DEPTH OF THE BENT
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DEPTH AND SIPHON CROPPING IN SCROBI
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I DEPTH AND SIPHON CROPPING IN SCRO
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DEPTH AND SIPHON CROPPING IN SCROBI
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Table 3. Three-Way analysis Of vari
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Chapter 4 SIPHON SIZE AND BURYING D
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15 20 size (mm) Fig. 3. Cerasioderm
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10 size (mm) SIPHON SIZE AND DEPTH
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o, 7 01 5 | * CL 5- SIPHON SIZE AND
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4 Q) Si •a a. 16- 20- A predator:
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prey risk for an animal al a depth
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Table 6. Size al which there is a m
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* ' 1 /-/ "».-^*«C
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face and so expose themselves to a
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surface in die containers was varie
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50 OOF 310.00 I 5.00 ^ 1.00 3=" 0.5
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Tahle 1. Macoma and Scrobicularia.
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siphon would not have to reach the
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known siphon weight and burying dep
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ACCESSIBLE PREY ARE OFTEN IN POOR C
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1 2 3 4 burying depth (cm) Kin. I.
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I—1 • • : : : : ! - ! -|-r 0
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Chapter 7 DOES AN OPTIMALLY FORAGIN
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OPTIMAL FORAGING AND THE FUNCTIONAL
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100 200 300 prey density (n-m-2) Fi
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Table I. Results of five one way an
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Table 2. Results of eight iwo-wav a
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prey density II III Fig. 12. Freque
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PREY SIZE SELECTION AND INTAKE RATE
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Predicted 'passive size selection'
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lig. 2. Larger Mussels are less ava
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Fig. 5. Scrobicularia plana. Size c
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and maiiv are too thick-shelled to
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The measurements of handling time i
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1 2 3 4 5 6 7 probing depth (cm PRE
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valves may vary by a factor of two
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optimal foraging model, the minimum
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their gut is full? Do they reduce t
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PREY PROFITABILITY AND INTAKE RATE
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catchers to take only certain prey
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licult error of estimate arose if p
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Counts of feeding and non-feeding b
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20 30 40 50 shell length (mm) PREY
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Nereis Arenicola tipuia earthwo'm M
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take rate. We might therefore expec
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prey species, using parallel slopes
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5.0 4.0 1-3.0 a & • % * • * •
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time during the feeding period. As
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winter. Similarly, handling time in
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5.0 - f-4.0 S 3.0 in I 20 a 2 a | 1
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situation arrived in the western pa
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• ' • 14 PREY PROFITABILITY AND
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Notes lo appendix: PREY PROFITABILI
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Chapter 10 WHY OYSTERCATCHERS HAEMA
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2 4 6 8 10 time on feeding area (h)
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80- 60- o 80 60- 40- 20- INTAKE RAT
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est of bod\ behind: an estimated 22
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INTAKE RATE AND PROCESSING RATE IN
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Wanink 1993). The energy content of
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(7) Age All studies dealt with adul
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irds over long periods. As an examp
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Discussion There is no difference i
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comparison between the weight of ih
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. 1', L ! •
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Introduction PREDICTING SEASONAL AN
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PREDICTING SEASONAL AND ANNUAL FLUC
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1000 r 1 II" 1 - r^Jan'80 PREDICTIN
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IOO BO 60 40 20 0 PREDICTING SEASON
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WHY KNOT TAKE MEDIUM-SIZED MACOMA W
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in Zwarts & Esselink 1989). The len
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shell length (mm) FIR. 3. Peringia.
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fused, specimens larger than this w
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50 100- s s I — f = S. plana, n=2
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area is twice as large as the touch
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10 15 lower size threshold (mm) Fig
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lime (Hughes 1979). This would furt
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WHY KNOT TAKE MEDIUM-SIZED MACOMA T
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Chapter 13 ANNUAL AND SEASONAL VARI
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VARIATION IN FOOD SUPPLY OF KNOT AN
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Two sites (N and M in Fig. 2) were
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20 30 VARIATION IN FOOD SUPPLY OF K
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20 l i r'l ' i •o j^y^T n ^ ' " ^
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July ' Aug ' Sept Fig. 9. Proportio
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available. There must, however, be
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Chapter 14 SEASONAL TREND IN BURROW
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BURROWING AND FEEDING IN NEREIS SEA
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Table 2. Results of a 2-way analysi
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June 1981 June 1982 is * N.MUD •
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8 10 I 12 JZ 5. -g 1*» •e o i 16
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6 - n=!080 5 • g 4 CP > i 3 CO CD
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1985) and Curlew (/wails ,v, Lsseli
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Chapter 15 VERSATILITY OF MALE CURL
Page 314 and 315: Smid! 1951. Muus 1967, Wolff 1973,
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Page 318 and 319: Na oi both Nrieck Fig. 7. Numenius
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Page 322 and 323: too (Fig. 11 A). Indeed, the averag
Page 324 and 325: VERSATILITY OF CURLEWS FEEDING ON N
Page 326 and 327: total time spent al the surface. Th
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Page 331 and 332: PREY DEPLETION BY OYSTERCATCHER AND
Page 333 and 334: the rule: the observed lower limit
Page 335 and 336: to locate the clams after they had
Page 337 and 338: Curlew, by bury ing some hundreds o
Page 339 and 340: PREY DEPLETION BY OYSTERCATCHER AND
Page 341 and 342: SAMENVATTING 345
Page 343 and 344: Voorgeschiedenis In 1960 verscheen
Page 345 and 346: maken. Als gebied A een grotere voe
Page 347 and 348: omdat ze nog vrijwel niets wegen. l
Page 349 and 350: kunnen opzuigen. of diep leven en z
Page 351 and 352: van de uitgerekte sifo over het wad
Page 353 and 354: het toen niet gemakkelijk hebben ge
Page 355 and 356: doende nonnetjes van 10 tot 15 mm l
Page 357 and 358: aangevoerde voedsel en de wulp past
Page 359 and 360: zijn dan twee jaar en wulpen geen s
Page 361 and 362: was dan ook dank/ij de inzet van al
Page 363: REFERENCES 367
Page 367 and 368: BreyT. 1989. Der Einfluss physikali
Page 369 and 370: latie tol chironoiiiiilen en de wai
Page 371 and 372: huch der Vogel Milteleuropas, Band
Page 373 and 374: llolmann II. & H. Huerschelmann 196
Page 375 and 376: l-cndrem D.W. 1984. Flocking, feedi
Page 377 and 378: Pekkarinen M. 1984. Regeneration of
Page 379 and 380: lion of Mussels Mytilus edulis hy O
Page 381 and 382: lulal Dal esiuanes: a comparison of
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