Translator Disclaimer
1 March 2010 Phenology, Stopover Dynamics and Population Size of Migrating Black-Tailed Godwits Limosa Limosa Limosa in Portuguese Rice Plantations
Pedro M. Lourenço, Rosemarie Kentie, Julia Schroeder, José A. Alves, Niko M. Groen, Jos C.E.W. Hooijmeijer, Theunis Piersma
Author Affiliations +

Between 2005/06 and 2008/09 we studied Black-tailed Godwits Limosa I. limosa staging in the rice fields surrounding the Tejo and Sado estuaries, Portugal. Godwits were counted weekly and flocks were scanned for colour-ringed individuals. We analysed phenology, dynamics of the stopover, and estimated the size of the Portuguese staging population as well as the total western limosa population, Godwits started arriving in January. Numbers peaked in the second half of February, after which they quickly departed from the area. Comparison with previous records suggested that numbers have decreased since the early 1990s, and that godwits currently peak later than some 15 years ago. Individual staging durations averaged 22.6 days in 2007 and 25.3 days in 2009, and increased towards the end of the staging period. We estimated that a total 59 200 birds used the area in 2007 and 53 100 in 2009. Using estimates for the proportion of colour-ringed birds in the flocks, we estimated the population size of the western part of the L. l. limosa population at 133 151–140 722 birds. This is higher than previous estimates based on inventories of the breeding population, but accounts for the non-breeding segment of the population. Thus, we estimate that 38–44% of the NW European Black-tailed Godwit population stage in Portugal. It is argued that processes in Iberia are not likely to have contributed to the population decline as the area for rice cultivation has increased. Nevertheless, as godwits staging in Iberia are totally dependent on human-made habitats, changes in rice farming practices could have great impact on the total population size.

Staging episodes are considered critical in the annual life cycle of migratory birds (Piersma & Baker 2000, Chernetsov 2006, Buehler & Piersma 2008) and can have consequences on survival and breeding success (Newton 2006). Important aspects of the staging period are timing and duration, and knowledge of the turnover rate of individuals is crucial to understanding the importance of staging sites for the conservation of migratory species (Chernetsov 2006). Despite this, stopover ecology remained one of the least studied aspects of avian migration (Lindström 1995).

Continental Black-tailed Godwits Limosa limosa limosa mostly breed in the agricultural grasslands of northern Europe. Their breeding range extends from the UK and The Netherlands in the west to near Russia in the east (Thorup 2006, Gill et al. 2007). The western part of the population is believed to be relatively isolated (Höglund et al. 2008), both during the breeding season (breeding mostly in The Netherlands, but also in Germany, Belgium, France, Denmark, Sweden, Norway and the UK) and in winter (when using coastal sites in West Africa). This sub-population has undergone serious population declines over the last decades, probably by as much as 50% since the 1980s (Piersma 1986, SOVON 1987, SOVON 2002, Teunissen & Soldaat 2005). Much of this decline has been associated with agricultural intensification in the breeding areas (Beintema et al. 1995, Schekkerman & Müskens 2000, Schekkerman et al. 2008).

A significant portion of this sub-population stages on the rice fields of the Iberian Peninsula during northward migration (Kuijper et al. 2006, Lourenço & Piersma 2008a), where they forage on rice kernels to accumulate energy for the subsequent flights (Lourenço & Piersma 2008b). Although these areas seem important to the godwits, little is known about when and in which numbers they occur in these areas. In this study we capitalized on the large number of Black-tailed Godwits colour-ringed at Dutch breeding sites in recent years (e.g. van den Brink et al. 2008), which mix with birds from other breeding areas, allowing for a robust estimation of size of the source population (White 1996, Gunnarsson et al. 2005).

In order to better understand the staging processes of the declining population of continental Black-tailed Godwit and to substantiate the importance of the rice fields in central Portugal (surrounding the estuaries of the Tejo and Sado rivers, see Lourenço et al. in press) we aimed to collect the following information. (1) Describe the current phenology in comparison with the situation in the early 1990s, (2) estimate staging duration of individual godwits and the total number of godwits using this staging area, and (3) estimate the size of the western L. l. limosa population.



Field work took place in the winters 2005/06 through 2008/09. The main rice field areas around the Tejo (38°57′N, 8°54′W) and Sado (38°24′N, 8°38′W) river estuaries were surveyed for godwit presence in each winter during the period that Black-tailed Godwits migrate through the area (Kuijper et al. 2006), from early December to mid-March. For information on the study area see Lourenço & Piersma (2008b). Each site was visited at least three times per week, and weekly counts were made for the total area. The observed phenology was compared with data for 1991/92 and 1992/93 (R. Rufino, unpubl. data) to check for possible changes in the timing of stopover.

Staging duration

Since 2004, continental Black-tailed Godwits received individual combinations of four colour rings and one leg-flag at breeding sites in The Netherlands (van den Brink et al. 2008). Icelandic Black-tailed Godwits were colour-ringed in different parts of their range since the 1990s (Gunnarsson et al. 2005). In Portugal, flocks were checked for the presence of colour-marked individuals. We found 16 (2005/06), 66 (2006/07), 71 (2007/08) and 127 (2008/09) different Dutch individuals. However, only in 2006/07 and 2008/09 we achieved a stable resighting effort throughout the study period. Therefore, to estimate staging duration we used only the data sets from these years.

To analyse the mark—recapture data, we used the program MARK (Cooch & White 2006). Week was the temporal unit as daily resighting rates were too low. Model selection was based on Akaike's information criterion corrected for small sample size (AICc). All models used the logit link function. We assessed goodness-of-fit for the most general model in each set by the bootstrapping method included in MARK. We calculated the deviances from 100 simulations of data that are not over-dispersed. We accepted a general model if its deviance ranked over 90 of the 100 rank-ordered simulated deviances. We also tested for overdispersion: the median ĉ was 0.95 for 2006/07 and 0.92 for 2008/09, which indicates a slight underdispersion of the data. In MARK we constructed two types of models, the first to estimate the ‘survival’ phi parameter (for emigration = 1-phi) and the second to estimate the ‘seniority’ gamma parameter (for immigration = 1—gamma). The first parameter predicts the chance that an individual present just after time t will still be present just before time t+1, while the second parameter predicts the chance that an individual present just before time t was already present just after time t-1 (Pradel 1996).

To calculate the stopover duration, we used the most parsimonious models to estimate phi and gamma and applied these in software SODA (Schaub et al. 2001), which provided a stopover duration estimate (± SD) for each week. In the first winter we had eight staging duration estimates. In the second winter, when resightings of colour ringed birds started two weeks earlier, we had 10.

Number of Black-tailed Godwits staging in Portugal and size of source population

We used gamma to estimate how many birds arrived at the site just before time t as the number of birds counted each week (t) multiplied by 1—gamma calculated for that week. Also, by adding all new birds from each week we obtain an estimate of the total number of birds staging in the sites. Total numbers of birds were corrected for the numbers of the Icelandic subspecies L. l. islandica that also occurred in the same rice fields (Gunnarsson et al. 2005). Based on the proportion of ringed birds of each subspecies in each week, only 5–8% were L. l. Mandica (Alves et al., unpubl. data).

Past ring recoveries have shown that the limosa Black-tailed Godwits visiting Iberia come exclusively from north-western Europe (Haverschmidt 1963, Beintema & Drost 1986). During our field work we observed birds from four different breeding areas: two from The Netherlands, one from Germany and one from the UK. This indicates that there is mixing of birds from different breeding areas at the staging sites. We therefore assumed that birds seen in Iberia are a random sample of birds from the western population, and used the density of ringed birds in our samples to estimate population size.

To estimate the density of ringed birds (number of colour-ringed birds on total number), we sampled 81 (in 2007), 67 (in 2008) and 76 (in 2009) godwit flocks, considering a different flock per site and per sampling day. In each flock, we checked all visible legs, starting at one end of the flock and counting until either the end of the flock or until the flock flew up. We checked an average of 691 (SE 49) birds per flock. Only birds ringed within the University of Groningen ringing scheme (van den Brink et al. 2008) were considered to be ringed, as only for these birds we had a reliable estimate of how many were alive in each winter (see below).

Furthermore, we used data on the density of ringed birds collected following the same methodology in the Extremadura rice fields located along the Guadiana river near Mérida, Spain (38°58′N, 5°59′W) (Sánchez-Guzmán et al. 2007). In total 75 (2007), 111 (2008) and 200 (2009) godwit flocks were sampled, with an average of 151 (SE 11) birds per flock.

To estimate the number of ringed birds alive (University of Groningen ringing scheme only) at the time of the observations in each year, we used the best available annual survival estimates for the ringed population, 0.91 for adults and 0.53 for first calendar year birds (R. Kentie, unpubl. data). This may slightly underestimate the number of ringed birds alive, as birds had been ringed in the breeding areas in May and the observations were made in January and February, so not a full year had passed. Since the godwits had already undergone a southbound migration, a summer and autumn in Africa and a large part of the northbound migratory flight, the remaining mortality until the following breeding season is likely to be low. All samples of the density of ringed birds, separated by year and country were input in program NOREMARK (White 1996, Gunnarsson et al. 2005) in which we used JHE closed population model estimation to calculate population estimates with 95% confidence intervals.


Phenological pattern

Over the four studied winters we found a similar phenology in the Tejo and Sado rice fields. Although some birds were already present in December, godwits mostly started to arrive in early January, reaching peak numbers in the second half of February. The birds left the area in the beginning of March (Fig. 1). In 2006, the pattern was somewhat different, with two separate peaks. The dip was probably caused by missing birds that had gone to a location that was not yet counted. Data available for 1992 and 1993 suggests that the migration peak occurred on average three weeks earlier than what was found in 2006–09. Peak numbers were similar among the four recent years (mean 44 185 birds, SD 2768), while in the 1990s there was much more variation. The current peak numbers were 46% lower than the maximum peak in the 1990s (Fig. 1).

Stopover dynamics

The most parsimonious emigration models were those that estimated a constant phi during the first weeks, and a varying phi in the final weeks (Table 1). In 2007 the top-ranking models estimated a constant resighting probability during the stopover period, averaged at 29% (SE 6). In 2009 the top-raking models estimated a temporal resighting probability, which averaged 28% (SE 3).

Figure 1.

Total counts of Black-tailed Godwits in Portuguese rice fields in 2006–09. For comparison, data are given for two winters in the 1990s (1992 and 1993).


The top-ranking seniority models estimated a fully temporal gamma. In 2007, there was equal support for models that estimated a constant resighting probability and a temporal resighting probability (Table 2). Model averaging provided an estimate of 35% (SE 2) for the resighting probability over the stopover period. In 2009 the top-ranking model estimated a fully temporal resighting probability, which averaged 32% (SE 3).

In both years the staging duration seemed to vary with time, becoming longer closer to the end (Fig. 2). Staging duration was similar in the two years, averaging 22.6 days (SD 7.2 days) in 2007 and 25.3 days (SD 3.6) in 2009.

Table 1.

Modelling ‘survival’ probabilities (to estimate emigration rate) of Black-tailed Godwit in Portugal in 2007 and 2009. Phi = survival probability, p = resighting probability, weight = Akaike weight, NP = number of parameters, t = temporal variation (by week), c = constant. Notations like 5c+2t mean that the parameter is constant in the first five periods and varies in the last two. Models with lowest AICc are the most parsimonious. Other candidate models were less parsimonious and are not shown here.


Table 2.

Modelling ‘seniority’ probabilities (to estimate immigration rate) of Black-tailed Godwit in Portugal in 2007 and 2009. Gamma = seniority probability, p = resighting probability, Weight = Akaike weight, NP = number of parameters, t = temporal variation (by week), c = constant. Models with lowest AICc are the most parsimonious. Other candidate models were less parsimonious and are not shown here.


Figure 2.

Average staging duration ± SE for individual Black-tailed Godwits present in the study area in each week.


Number of Black-tailed Godwits staging in Portugal and a new population estimate

During the first three weeks in 2007 Black-tailed Godwits arrived at a constant rate of about 10 000 birds/week, after which the rate of new arrivals dropped to almost zero by the end of February (Fig. 3). In 2009 godwits arrived in three distinct peaks, one in January and two in February (Fig. 3). We estimated the total number of birds migrating through the area at 59 200 ± 2900 for 2007 and at 53 100 ± 4600 for 2009.

From 2007 to 2009 the density of ringed birds in the flocks increased, and the variation between samples decreased. These trends corresponded with an increasing number of birds ringed in the Dutch breeding population. Based on the density of ringed birds and number of ringed birds alive in the population, the population estimates ranged from 133 151 to 140 722 birds (Table 3).

Table 3.

Population estimates for the western population of L. l. limosa. Given is the number of ringed birds estimated to be alive each winter (ringed population, based on ringing scheme of the University of Groningen), the number of flocks sampled, the total number of birds checked and the population estimates with their 95% confidence intervals (C.I.).


Figure 3.

Comparison between the total numbers of Black-tailed Godwits counted and estimated new arrivals in each week of the staging periods in 2007 and 2009.


We thus conclude that 38–44% of the western population of Limosa l. limosa used the rice fields in Portugal during the period of our study.


We estimated that the total number of birds migrating through the Portuguese rice fields was roughly 25% higher than the peak counts. This clearly underlines the importance of taking into account the turn-over of birds at staging sites to correctly assess the importance of the sites (e.g. Frederiksen et al. 2001, Schaub et al. 2001). That 38–44% of the western L. l. limosa's use Portugal during northward migration confirms the importance of Portuguese rice fields for this near-threatened population (Kuijper et al. 2006; Lourenço et al. in press). Despite this, most of the fields are outside local protected areas and no management measures are currently enforced to assure that the favourable staging conditions will remain in the future.

If we exclude the first week of February in 2006, when we probably missed some birds in a rice plantation not yet surveyed at that time, the pattern of occurrence of godwits was basically the same in all years. Numbers peaked at 44 000–45 000 birds in the second half of February, after which the sites were quickly abandoned by the godwits on their way towards their breeding areas. In a nearby stopover area in the Spanish Extremadura, the migratory peak is not quite as constant, ranging between the first and third week of February and being on average earlier than in Portugal (Masero et al. 2007).

Peak counts in the 1990s seemed to occur on average three weeks earlier than during our study, but there was large variation between the two years for which data is available. At that time counts were not performed every week, so the data might not be comparable in terms of timing. If we assume the trend towards a later stopover in Iberia is true, this is in accordance with the apparently larger reduction in the numbers stopping over in France than in Iberia (Lourenço & Piersma 2008a). If birds remain longer in Iberia they are likely to overfly France altogether in order to arrive timely at their breeding sites. Indeed, arrival dates of first birds at breeding sites in The Netherlands start in the beginning of March (J.C.E.W. Hooijmeijer et al., unpubl. data), shortly after departure from Portugal.

The maximum count in the early 1990s reached nearly 82 000 birds, which indicates that peak numbers have been reduced by 46%. If the turn-over rate in the 1990s was similar to the present value, and the number of birds passing through the area was 25% more than the average of the two peak counts, then the decline would be similarly around 40%. This figure is close to the decline witnessed in the breeding areas (50% since the early 1980s, Piersma 1986, SOVON 1987, SOVON 2002, Teunissen & Soldaat 2005). Although there are no reliable data on overall population changes in Spain in the last decades (Kuijper et al. 2006), numbers have probably declined in the Coto Doñana area, a traditional staging site. In the Extremadura rice fields numbers have increased as this is a novel staging area that has only become available for godwits following the vast irrigation projects in the 1980s (Sánchez-Guzmán et al. 2007, Lourenço & Piersma 2008a).

On average, Black-tailed Godwits remained in the area for 22–25 days, although the latest birds seemed to stay longer than early arriving birds. This means that there is a larger turn-over of birds in the beginning of the season, with birds arriving and departing. In February, the turn-over is reduced, the arrivals lead to a build up of birds, culminating in the peak counts, while departures seem to be delayed until most birds depart almost simultaneously in the beginning of March. Such an increase in staging time towards the end of the staging period, coupled with a synchronized group departure might suggest that the birds delay departure to await favourable conditions on the breeding grounds. Maybe leaving too early would imply a risk of facing bad weather and frozen soils that make food unavailable on the breeding areas. Also, staying in Iberia longer instead of making further stopovers in France might be the safest option, as the hunting pressure is much higher in France (Gill et al. 2007).

At the Extremadura staging areas in Spain, average staging duration was estimated at 21.7 days in 2007 (J.A. Masero et al., unpubl. data). This is similar to what we observed in Portugal and suggests that turnover rates are similar at both Iberian staging areas.

The lower number of godwits seen in France during migration in recent years (Lourenço & Piersma 2008a) could be explained by the relatively low turn-over in Iberia. The reason for this change in France could be an increase in the available foraging habitat in Iberia, where the hunting pressure is lower. Recent work has shown that the Iberian rice fields provide a very profitable foraging habitat for godwits (Masero et al. 2007, Lourenço & Piersma 2008b). However, in Portugal the extent of rice plantations decreased by at least 25% in the last three decades. Over the same period the area used for rice cultivation in Spain increased by 35%. Overall this resulted in a 28% increase of the rice cultivated area in Iberia (FAOSTAT 2008). Even if not all rice fields are usable by godwits, due to the specific habitat requirements (Lourenço & Piersma 2008b), the available high-quality habitat in Iberia seems to have increased. This increase in available habitat suggests that stopover processes in Iberia are not contributing to the ongoing population decline. However, the population is now almost exclusively dependent on man-made habitats, making it very sensitive to any future changes in the extent of rice cultivation or in rice farming practices, which can easily fluctuate according to the profitability of planting rice and the economic incentives that rice planters receive from the EU (GPPAA 2006).

The total European population of limosa Blacktailed Godwits was estimated at 86 500–120 000 breeding pairs in 2000 (Thorup 2006), and the western segment of this population, migrating through Iberia, would have amounted 53 200–59 600 pairs or c. 110 000 individuals (Thorup 2006). Our estimate of 135 000–140 000 is slightly larger, but includes adults that for some reason skip a breeding season, which can be a substantial proportion in some years and at some breeding sites (P.M. Lourenço et al., unpubl. data) and also some second calendar year birds that venture north. Covering only three years, and considering the uncertainty associated with the estimates, these data do not establish a current rate of population decline. However, a repetition of this study in the next 5 to 10 years could provide robust estimates of population trends.


We want to thank all the observers who reported sightings of colour-marked birds in Portugal and Spain, namely F. Mandema, J.A. Masero and his team, N. Cidraes-Vieira, P. Potts and several members of the Farlington Ringing Group. R. Rufino provided us with the count data from the 1990s and J.A. Masero provided information on staging duration of black-tailed godwits staging in the Spanish Extremadura. The University of Extremadura generously provided housing and access permission for us in the several visits we made to their field sites to search for our ringed birds. T.G. Gunnarsson and K. Kraaijeveld provided many useful comments to this manuscript. PML was supported by grant SFRH/BD/21528/2005 of the Portuguese Science and Technology Foundation, JAA was supported by a grant from the Calouste Gulbenkian Foundation and TP received a start-up grant from the University of Groningen. BirdLife-Netherlands enabled some of us to travel south to meet up with the godwits through the Global Flyway Network.



A.J. Beintema & N. Drost 1986. Migration of the black-tailed godwit. Gerfaut 76: 37–62. Google Scholar


A.J. Beintema , O. Moedt & D. Ellinger 1995. Ecologische Atlas van de Nederlandse Weidevogels. Schuyt & Co BV, Haarlem. Google Scholar


D.M. Buehler & T. Piersma 2008. Travelling on a budget: predictions and ecological evidence for bottlenecks in the annual cycle of long-distance migrants. Phil. Trans. R. Soc. B 363: 247–266. Google Scholar


N. Chernetsov 2006. Habitat selection by nocturnal passerine migrants en route: mechanisms and results. J. Ornithol. 147: 185–191. Google Scholar


E. Cooch & G. White 2006. Program MARK: a gentle introduction. 5th edition. (accessed Aug 2007). Google Scholar


FAOSTAT. 2008. FAO World agricultural production statistics. FAO Statistics Division. (accessed Dec 2008). Google Scholar


M. Frederiksen , A.D. Fox , J. Madsen & K. Colhoun 2001. Estimating the total number of birds using a staging site. J. Wildl. Manage. 62: 282–289. Google Scholar


J.A. Gill , R.H.W Langston , J.A. Alves , P.W. Atkinson , P. Bocher , N.C. Vieira , N.J. Crockford , G. Gelinaud , N. Groen , T.G. Gunnarsson , B. Hayhow , J. Hooijmeijer , R. Kentie , D. Kleijn , P.M. Lourenco , J.A. Masero , F. Meunier , P.M. Potts , M. Roodbergen , H. Schekkerman , J. Schroeder , E. Wymenga & T. Piersma 2007. Contrasting trends in two black-tailed godwit populations: a review of causes and recommendations. Wader Study Group Bull. 114: 43–50. Google Scholar


GPPAA. 2006. Envolvente Sócio-Económica 2005 ao Sector Agrícola Português. Ministério da Agricultura, do Desenvolvimento Rural e das Pescas, Lisboa. Google Scholar


T.G. Gunnarsson , J.A. Gill , P.M. Potts , P.W. Atkinson , R.E. Croger , G. Gélinaud , A. Gardarsson & W.J. Sutherland 2005. Estimating population size in black-tailed godwits Limosa limosa islandica by colour-marking. Bird Study 52: 153–158. Google Scholar


F. Haverschmidt 1963. The Black-tailed Godwit. E.J. Brill, Leiden. Google Scholar


J. Höglund , T. Johansson , A. Beintema & H. Schekkerman 2008. Phylogeography of the black-tailed godwit Limosa limosa: substructuring revealed by mtDNA control region sequences. J. Ornithol. 150: 44–53. Google Scholar


D.P.J. Kuijper , E. Wymenga , J. van der Kamp & D. Tanger 2006. Wintering areas and spring migration of the black-tailed godwit. Bottlenecks and protection along the migration route. A&W Rapport no. 820. Altenburg & Wymenga ecologisch onderzoek, Veenwouden. Google Scholar


Å. Lindström 1995. Stopover ecology of migrating birds: some unsolved questions. Israel J. Zool. 41: 407–416. Google Scholar


P.M. Lourenço , N. Groen , J.C.E.W. Hooijmeijer & T. Piersma in press. The rice fields around the estuaries of the Tejo and Sado are a critical stopover area for the globally near-threatened black-tailed godwit Limosa l. limosa: Site description, international importance and conservation proposals. Airo. Google Scholar


P.M. Lourenço & T. Piersma 2008a. Changes in the non-breeding distribution of continental black-tailed godwits Limosa limosa limosa over 50 years: a synthesis of surveys. Wader Study Group Bull. 115: 91–97. Google Scholar


P.M. Lourenço & T. Piersma 2008b. Stopover ecology of blacktailed godwits Limosa limosa limosa in Portuguese rice fields: a guide on where to feed in winter. Bird Study 55: 194–202. Google Scholar


J.A. Masero , F. Santiago-Quesada , J.M. Sánchez-Guzmán , N. Albano , J.M. Abad-Gómez , A. Villegas , C. Corbacho & E. Costillo 2007. Key issues influencing non-breeding season processes of black-tailed godwit Limosa l. limosa: springstaging ecology of black-tailed godwit at East Atlantic Flyway's rice fields. Wader Study Group Bull. 114: 14. Google Scholar


I. Newton 2006. Can conditions experienced during migration limit the population levels of birds? J. Ornithol. 147: 146–166. Google Scholar


T. Piersma 1986. Breeding waders in Europe: a review of population size estimates and a bibliography of information sources. Wader Study Group Bull. 48, Suppl.: 1–116. Google Scholar


T. Piersma & A.J. Baker 2000. Life history characteristics and the conservation of migratory shorebirds. In: L.M. Gosling & W.J. Sutherland (eds) Behaviour and Conservation, Vol. 2. Cambridge University Press, Cambridge, pp. 105–124. Google Scholar


R. Pradel 1996. Utilization of capture-mark-recapture for the study of recruitment and population growth rate. Biometrics 52: 703–709. Google Scholar


J.M. Sánchez-Guzmán , M. Morán , J.A. Masero , C. Corbacho , E. Costillo , A. Villegas & F. Santiago-Quesada 2007. Identifying new buffer areas for conserving waterbirds in the Mediterranean basin: the importance of the rice fields in Extremadura, Spain. Biodivers. Conserv. 16: 3333–3344. Google Scholar


M. Schaub , R. Pradel , L. Jenni & J.D. Lebreton 2001. Migrating animals stop over longer than usually thought: an improved capture-recapture analysis. Ecology 82: 852–859. Google Scholar


H. Schekkerman & G.J.D.M. Müskens 2000. Do black-tailed godwits Limosa limosa breeding in agricultural grasslands produce suficient young for a stable population? Limosa 73: 121–134. Google Scholar


H. Schekkerman W.A. Teunissen & E. Oosterveld 2008. The effect of ‘mosaic management’ on the demography of black-tailed godwit Limosa limosa on farmland. J. Appl. Ecol. 45: 1067–1075. Google Scholar


SOVON 1987. Atlas van de Nederlandse Vogels. SOVON, Beek-Ubbergen. Google Scholar


SOVON 2002. Atlas van de Nederlandse Broedvogels 1998–2000. Nederlandse Fauna 5. Nationaal Natuurhistorisch Museum Naturalis, KNNV Uitgeverij & European Invertebrate Survey-Nederland, Leiden. Google Scholar


W.A. Teunissen & L.L. Soldaat 2005. Indexen en trends van een aantal weidevogelsoorten uit het Weidevogelmeetnet. Periode 1990–2004. Weidevogelindexen 1990–2004, SOVON-informatie 2005/13. SOVON Vogelonderzoek Nederland. Google Scholar


O. Thorup (comp.). 2006. Breeding waders in Europe 2000. International Wader Studies 14. International Wader Study Group, U.K. Google Scholar


V. van den Brink , J. Schroeder , C. Both , P.M. Lourenço , J.C.E.W Hooijmeijer & T. Piersma 2008. Space use by blacktailed godwits Limosa limosa limosa during settlement at a previous or a new nest location. Bird Study 55: 188–193. Google Scholar


G.C. White 1996. NOREMARK: population estimation from mark-resighting surveys. Wildlife Soc. B. 24: 50–52. Google Scholar



De westelijke populatie van de Grutto Limosa limosa, die voornamelijk in Nederland broedt, neemt sterk in aantal af. Een belangrijk deel van deze populatie verzamelt zich in de loop van de winter op de rijstvelden van het Iberisch schiereiland. Bij dit onderzoek werden tellingen en observaties van gekleurringde vogels in Portugal gebruikt om een beter inzicht te krijgen in de timing van deze doortrek en het aantal vogels dat van deze gebieden gebruikmaakt. Bovendien is aan de hand van de dichtheid aan gekleurringde vogels een schatting van de totale grootte van de West-Europese populatie gemaakt. De eerste Grutto's komen in januari in Portugal aan. Daarna lopen de aantallen op tot ze een piek in de tweede helft van februari bereiken. Daarna nemen de aantallen weer snel af. Een vergelijking van gegevens uit 1992 en 1993 met die uit recente jaren geeft aan dat de piek tegenwoordig twee weken later wordt bereikt dan destijds. Mogelijk stelt dit de vogels in staat rechtstreeks naar de broedgebieden door te vliegen, zonder in Frankrijk te hoeven stoppen, waar de jachtdruk hoger is dan op het Iberisch schiereiland. Uit de analyse van de observaties aan gekleurringde vogels blijkt dat de vogels gemiddeld zo'n 23–25 dagen in het gebied verblijven. De lengte van het verblijf lijkt echter op te lopen naar het einde van de doortrekperiode. Het totaal aantal Grutto's dat de Portugese rijstvelden aandoet, werd geschat op 53.000–59.000 vogels, een afname van zo'n 40% ten opzichte van de jaren 1990. De totale West-Europese populatie werd geschat op 133.000–141.000 vogels, wat zou betekenen dat 38–44% van de populatie de rijstvelden van Portugal aandoet.


Pedro M. Lourenço, Rosemarie Kentie, Julia Schroeder, José A. Alves, Niko M. Groen, Jos C.E.W. Hooijmeijer, and Theunis Piersma "Phenology, Stopover Dynamics and Population Size of Migrating Black-Tailed Godwits Limosa Limosa Limosa in Portuguese Rice Plantations," Ardea 98(1), 35-42, (1 March 2010).
Received: 2 September 2009; Accepted: 1 November 2009; Published: 1 March 2010

Back to Top