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Keywords:

  • breeding success;
  • demography;
  • interspecific analysis;
  • latitude;
  • North Atlantic Oscillation;
  • sea surface temperature

Abstract

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

For an understanding of the effect of climate change on animal population dynamics, it is crucial to be able to identify which climatologic parameters affect which demographic rate, and what the underlying mechanistic links are. An important reason for why the interactions between demography and climate still are poorly understood is that the effects of climate vary both geographically and taxonomically. Here, we analyse interspecifically how different climate variables affect the breeding success of North Atlantic seabird species along latitudinal and longitudinal gradients. By approaching the problem comparatively, we are able to generalize across populations and species. We find a strong interactive effect of climate and latitude on breeding success. Of the climatic variables considered, local sea surface temperatures during the breeding season tend to be more relevant than the North Atlantic Oscillation (NAO). However, the effect of NAO on breeding success shows a clear geographic pattern, changing in sign from positive in the south to negative in the north. If this interaction is taken account of, the model explains more variation than any model with sea surface temperature. This superiority of the NAO index is due to its ability to capture effects of more than one season in a single parameter. Mechanistically, however, several lines of evidence suggest that sea surface temperature is the biologically most relevant explanatory variable.


Introduction

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

Climate can have profound effects on the demography and population dynamics of marine top predators. Whereas mass mortality and breeding failure of South Pacific seabirds in El Niño years is a recurrent and comparatively well understood phenomenon (Barber & Chavez, 1983; Schreiber & Schreiber, 1984; Duffy, 1990; Schreiber, 2002), the interaction between climate and top predators in oceanic regions that are not governed by the El Niño-Southern Oscillation, are far more subtle.

In the North Atlantic Ocean it has been shown that many life history and other characteristics of seabirds correlate well with the North Atlantic Oscillation (NAO) index (Reid et al., 1999; Durant et al., 2004; Grosbois & Thompson, 2005; Sandvik et al., 2005; Sandvik & Erikstad, 2008). The NAO is defined as sea level pressure anomalies over the North Atlantic Ocean (Walker, 1924; Hurrell et al., 2003). As such, the NAO can hardly be said to be the direct cause of any biological phenomenon. The widespread statistical associations of biological parameters with the NAO can, thus, be viewed both as a strength and as a call for more research (Hallett et al., 2004; Stenseth & Mysterud, 2005): on the one hand, the NAO index is a useful proxy which seems to integrate information on a temporal and spatial scale that is biologically relevant for many species. On the other hand, it is often still an open question what this biologically relevant information is, because local weather repeatedly performs more poorly as an explanatory variable of ecological processes. In some well-studied terrestrial, freshwater and marine systems, it has been possible to reveal the underlying causal pathways and to disentangle the interactions of climate with geography, topography or food-web structure (e.g. Post & Stenseth, 1999; Hjermann et al., 2004). In other cases, one still knows little more than that NAO and biological characteristics of study species covary. However, knowledge of the underlying mechanisms is crucial for an understanding of the effects global warming will have on the population dynamics of biological species.

In seabirds, the climatic parameter relevant for demography has been hypothesized, and in some study systems substantiated, to be sea surface temperature (SST; Peck et al., 2004; Harris et al., 2005; Sandvik et al., 2005), which is strongly correlated with NAO. However, both the exact magnitude and even the sign of the NAO–SST correlation vary geographically throughout the North Atlantic (Hurrell et al., 2003; cf. Fig. 1). This poses a severe obstacle to understanding the relationships between climate and demography, because the climatic responsiveness of animal demographic parameters likewise can vary considerably across different geographical areas (Mysterud et al., 2000; Sæther et al., 2003, 2004; Harris et al., 2005; Sandvik & Erikstad, 2008). The study of climatic responsiveness in seabird demography is complicated by two further factors. First, seabirds are pelagic organisms spreading over vast oceanic regions where they are extremely difficult to study. This causes difficulties in choosing the appropriate scale at which environmental covariates should be considered. Second, the main effect of SSTs has been shown to be indirect [i.e. to be mediated through the food chain via prey abundance and/or prey availability rather than being the result of weather conditions on seabirds themselves (Weimerskirch et al., 2003; Abraham & Sydeman, 2004; Durant et al., 2004; Sandvik et al., 2005)]. This may introduce time lags into the interaction between climate and demography that can be difficult to identify.

image

Figure 1.  A map of the North Atlantic showing the locations of the study colonies (black diamonds). The colour patterns visualize the local correlation between NAO and the local SST eight months earlier.

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In this study, we investigate whether SST or NAO is better able to capture the effect of climate on seabird breeding success. We also search for geographical patterns in the covariation between seabird breeding success and NAO and/or SST. Those questions are necessary for a better causal and mechanistic understanding of the link between climate and demography. We approach these problems by analysing an interspecific dataset, utilizing available time series on temporal variation in breeding success in the North Atlantic. Addressing the issue comparatively, makes the study nomothetic rather than merely descriptive (i.e. it generalizes across species). The results demonstrate that the climatic response in seabird demography is indeed geographically patterned, among other things because it changes its sign with latitude.

Materials and methods

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

We surveyed the literature for studies reporting breeding success of seabirds in the North Atlantic for at least four consecutive years. ‘Seabird’ was defined as any species belonging to the Alcinae (auks), Larinae (gulls), Procellariidae (petrels and fulmars), Sterninae (terns) or Sulidae (gannets). Breeding success was defined as the proportion of eggs laid that survived until fledging of the chicks. The estimates of breeding success were logit-transformed and standardized. The final data set contained 33 studies on 13 species, differing in length between 4 and 29 years (see Appendix, Table A1). The locations of the colonies are shown in Fig. 1.

Two sorts of analyses were performed. Initially data were analysed using linear mixed effects models. In these analyses, the transformed time series of breeding success were the dependent variables; NAO indices and SSTs at different time lags, latitude, longitude, body mass, clutch size, time series length and a binary variable ‘America vs. Europe’ were considered as fixed effects; whereas colony, cluster of colonies (cf. Table A1), species, higher taxon (as delineated in the first paragraph of ‘Materials and methods’), and/or year were treated as potential random effects. The main aim of these analyses was to identify the climatic time lags that were most relevant.

The interrelationships between breeding success, climate and geography at those time lags were then analysed in greater detail using derived variable analyses. This method entailed estimating for each breeding colony the slope of breeding success against environmental variables (NAO and SSTs) in univariate linear models. Because both the dependent and the explanatory variable were standardized, the slopes were equivalent to correlation coefficients (r). These slopes were then treated as dependent variables and, after z-transformation (Sokal & Rohlf, 1995, p. 757), analysed further using linear models, weighting each slope by the length of the underlying time series. The explanatory variables considered were latitude, longitude, body mass, clutch size, time series length, higher taxon and the local correlation between NAO and SST. The latter variable was defined as the product–moment correlation between winter (December–March) NAO and the local summer (April–July) SST around each breeding colony. The time interval chosen for estimating local NAO–SST correlation was the 30-year-period 1965–1994, because all studies overlapped with this time frame. The time lags considered for those correlations were −1 to +1 [i.e. correlations between NAO and SSTs of the preceding summer (SST leading 8 months), of the same summer (NAO leading by 4 months), and of the following summer (NAO leading by 16 months)].

Model simplification was guided by Akaike's Information Criterion corrected for small sample sizes (AICC). As standard models make a number of implicit statistical assumptions, which may or may not be fulfilled (such as absence of spatial autocorrelation and of density dependence, homogeneous variances, etc.), we run several variations of the final set of preferred models in order to test their robustness. Those variations are listed in Appendix A (Table A2) and discussed in the text only to the degree they differ from the standard models.

The NAO was represented by the principal component-based extended winter (December–March) NAO index (Hurrell, 2005) lagged by zero to two years (i.e. 4, 16 and 28 months before the respective breeding season). Sea surface temperatures (ERSST, Smith & Reynolds, 2006) were averaged for areas of a 250 km radius around each breeding colony for the breeding season (April–July) and the preceding winter (December–March) lagged by 0–2 years. All time series were standardized for each colony. Mean body masses and clutch sizes of each species were taken from Schreiber & Burger (2002).

All analyses were performed in the R environment (R development core team, 2005). Estimates are given as mean±standard error.

Results

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

Linear mixed effects modelling

Linear mixed effects models with colony as random effect were used to analyse the factors affecting breeding success. Higher taxa, species, clusters of colonies, and year increased the models' AICC, and could be dropped as random effects. Among the explanatory variables (fixed effects), longitude, continent (i.e. America vs. Europe), body mass, clutch size, time series length and year did not explain the variation in breeding success. The only time lags at which climatic variables were retained in any model, was at lag 1 for NAO and at time lag 0 for summer SST (Table 1). A model containing these two variables, although not significant, shows that the slopes of breeding success on SST are almost five times larger than the slopes of breeding success on NAO (Table 1). The sign of the effects indicates that breeding success increases with increasing water temperature during the current breading season, and decreases with increasing NAO index during the winter 1 year earlier. In contrast, the effects of winter SSTs are insignificant. Several models with only main effects are considerably better supported than the null model (negative ΔAICC in Table 1). However, in none of these are the effects statistically significant. If allowing for interactions, on the other hand, both the main climate affect and the interaction with latitude turn out to be significant – highly so in the case of NAO (Table 1). The models explain up to 4.9% of the variance in breeding success.

Table 1.   Effects of different climatic variables on the breeding success of North Atlantic seabirds
Model/parameterEstimate ± SEF/tpdfr2ΔAICC
  1. Statistics provided are for the linear mixed effects models as such (boldface: F statistic, significance level, degrees of freedom, variance explained, and Akaike's Information criterion corrected for small sample size) and for their fixed effects (parameter estimate, Student's t, significance level). Localities of the breeding populations were treated as random factors. The environmental variables considered are North Atlantic Oscillation (NAO) index and sea surface temperatures (SST); subscripts indicate the season (S=summer, W=winter) and the time lag (i.e. the number of years the climatic variables predate the relevant breeding seasons). ΔAICC values are expressed as the difference between the AICC of a model and the AICC of the constant model (i.e., without covariates), where low values indicate better models.

SST 1.960.151, 2890.01−6.14
 SSTS, 0+0.10 ± 0.071.450.15289  
NAO 0.360.801, 2890.00−4.61
 NAOW, 10.02 ± 0.07−0.250.80289  
NAO+SST 1.220.302, 2880.01−6.40
 NAOW, 10.02 ± 0.07−0.300.76288  
 SSTS, 0+0.11 ± 0.071.510.13288  
SST including winter 0.970.382, 2880.01−2.20
 SSTS, 0+0.11 ± 0.071.620.106288  
 SSTW, 1+0.03 ± 0.060.540.59288  
NAO × latitude 5.440.00123, 2870.05−12.09
 NAOW, 1+1.16 ± 0.333.530.00049288  
 Latitude0.00 ± 0.000.001.032  
 NAOW, 1× latitude0.02 ± 0.013.680.00028288  
SST × latitude 2.650.0493, 2870.02−6.57
 SSTS, 0+0.90 ± 0.382.360.019288  
 Latitude0.00 ± 0.000.001.032  
 SSTS, 0× latitude0.02 ± 0.012.120.035288  

Derived variables analyses

The mean slopes of breeding success against winter NAO (lagged 1 year) and against summer SSTs (unlagged) are +0.041±0.111 and +0.044±0.110, respectively, when derived from the same bivariate model. The mean-squared slopes (which are equivalent to coefficients of determination, r2) are 0.38±0.14 and 0.38±0.09. If using univariate models (i.e. if not controlling the effect of the other explanatory variable), the mean (squared) slopes are 0.000±0.094 (0.20±0.04) against NAO and +0.110±0.083 (0.22±0.04) against SST. Linear models were used to analyse the variation in the latter slopes. Latitude alone explains 26% of this variation (Table 2, Fig. 2). The respective model is well supported. If an independent class variable that denotes higher taxon (with the levels Alcinae, Larinae, Procellariidae, Sterninae and Sulidae), and its interaction with latitude, is included in the analysis, the proportion of the variance explained is doubled (Fig. 2). However, whereas the taxon and interaction effects are marginally significant (anova, F8, 23=2.34, P=0.053), the high number of parameters leads to its rejection according to AICC (Table 2).

Table 2.   Factors affecting the slopes of seabird breeding success against winter NAO 16 months earlier
Model/parameterEstimate ± SEF/tpdfr2ΔAICC
  1. Statistics provided are for the linear models as such (boldface) and for the model parameters. See Table 1 for further explanations.

Latitude 10.950.00241, 310.26−7.56
 Intercept+1.27 ± 0.403.170.0034   
 Latitude−0.03 ± 0.013.310.0024   
Latitude × taxon 3.720.00529, 230.59+0.52
 Intercept−15.13 ± 5.142.950.0073   
 Latitude+0.26 ± 0.092.930.0075   
 Larinae+10.67 ± 6.451.650.11   
 Procellariidae+16.27 ± 5.163.150.0045   
 Sterninae+17.62 ± 5.223.370.0026   
 Sulidae+27.01 ± 8.703.110.0050   
 Latitude × Larinae−0.19 ± 0.111.690.10   
 Latitude × Procellariidae−0.29 ± 0.093.160.0044   
 Latitude × Sterninae−0.32 ± 0.093.430.0023   
 Latitude × Sulidae−0.48 ± 0.153.100.0051   
Local correlation with SST 15.280.000471, 310.33−10.80
 Intercept+0.76 ± 0.213.540.0013   
 SST correlation−2.13 ± 0.553.910.00047   
image

Figure 2.  Effect of latitude and winter NAO on breeding success 16 months later in different seabird taxa. Overall, the slope of breeding success against NAO decreases towards the north. However, there are pronounced differences between taxa. The slopes (y axis) are equivalent to z-transformed correlation coefficients. Legend: bold solid line, all taxa; green A, auks; turquois G, gulls; red P, petrels (incl. fulmar); black S, sulids (gannet); dark blue T, terns.

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When introducing the local correlation between winter NAO and the preceding summer SSTs (i.e. lag+1 year) as an additional explanatory variable, it turned out that a model with only that variable achieves the lowest (i.e. best) AICC (Table 2, Fig. 3). All local NAO–SST correlations are positive (Figs 1 and 2). None of the other explanatory variables considered (longitude, body mass, clutch size, time series length) are relevant (all P>0.50). Neither do the other time lags of the local correlation improve the model (lag 0, ΔAICC=−6.99; lag−1 year, ΔAICC=+1.09). The difference between taxa is negligible (ΔAICC=+3.89; anova, F8, 23=0.32, P=0.95; cf. Fig. 3).

image

Figure 3.  The combined effect of NAO and SST on breeding success in different seabird taxa. The stronger the local correlation between NAO and SST, the more negative is the slope of the regression of breeding success on NAO. Taxonomic differences are weak to absent. The slopes (y axis) are equivalent to z-transformed correlation coefficients. Legend: bold solid line, all taxa; green A, auks; turquois G, gulls; red P, petrels (incl. fulmar); black S, sulids (gannet); dark blue T, terns.

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The results are very robust to changes in the analysis methods (Appendix A, Table A2). Under all modifications, the model with local NAO–SST correlation achieves the lowest AICC. The latter models (all F>5.5, all P<0.03), and the ones with latitude as explanatory variable (all F>3.5, all P<0.08), are at least marginally significantly supported (Table A1). The interactive model (latitude × taxon) is significant in half of the cases (all F>1.7, all P<0.18), even though its support as measured by AICC or likelihood ratio tests is much poorer than for the other two models.

The variance in slopes of breeding success on SST of the previous summer is only poorly explained by the variables considered (Table 3). The best model according to the AICC contained latitude, the local correlation between SST and NAO, and the interaction between these two variables (Table 3). However, all models contain nonsignificant factors, and none of them would have been preferred over the constant model (with no covariates) according to an anova.

Table 3.   Factors affecting the slopes of seabird breeding success against unlagged summer SST
Model/parameterEstimate ± SEF/tpdfr2ΔAICC
  1. Statistics provided are for the linear models as such (boldface) and for the model parameters. See Table 1 for further explanations.

Latitude 3.080.0891, 310.09−0.70
 Intercept+1.04 ± 0.531.960.059   
 Latitude0.02 ± 0.011.760.089   
Local correlation with NAO 0.070.791, 310.00+2.35
 Intercept+0.20 ± 0.310.650.52   
 NAO correlation0.21 ± 0.790.260.79   
Longitude 3.640.0661, 310.11−1.24
 Intercept0.02 ± 0.110.210.83   
 Longitude0.01 ± 0.001.910.066   
Latitude and local correlation with NAO (additive) 3.650.0382, 300.20−2.16
 Intercept1.48 ± 0.552.670.012   
 Latitude0.04 ± 0.022.690.012   
 NAO correlation2.40 ± 1.211.980.057   
Latitude and local correlation with NAO (multiplicative) 3.860.0193, 290.29−3.26
 Intercept1.76 ± 1.780.990.33   
 Latitude0.02 ± 0.040.610.54   
 NAO correlation16.07 ± 7.272.210.035   
 Latitude × NAO correlation0.27 ± 0.141.910.067   

Discussion

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

In an interspecific analysis of 33 time series from 13 species of North Atlantic seabirds, we demonstrate that the effect of NAO on breeding success shows a strong geographic pattern. When only considering main effects, SST accounts for a considerably larger amount of variance in breeding success among colonies than NAO (Table 1). However, a far better model can be obtained by including latitude and the interaction between latitude and NAO. This shows that the effect of NAO on breeding success becomes increasingly negative towards the north (Fig. 2), a conclusion that mirrors earlier findings in hole-nesting birds (Sæther et al., 2003). If geography is ignored, the positive correlations between breeding success and NAO in the southern colonies on the one hand, and the negative correlations in the northern colonies on the other hand, effectively cancel each other out. This can be seen by comparing the mean slopes (0.00±0.09) with the mean squared slopes (+0.20±0.04, equivalent to an r2). Only in the interaction with latitude, the effect of NAO becomes apparent (Fig. 2). Such a latitudinal pattern is not found for the effect of SST on breeding success (Table 1).

Analyses of the slopes of breeding success against the two major explanatory variables, NAO and SST, confirmed those findings. 26% of the variation in the slopes of breeding success on NAO could be accounted for by latitude alone (Table 2). The proportion was doubled when differences between five higher taxa of seabirds (auks, gulls, terns, petrels, and gannets) were included into the model (Fig. 2). The latter model was poorly supported, however. This is probably because several of the taxa are represented from quite narrow latitudinal ranges only (Fig. 2), which increases the uncertainty of their slopes. The effect of latitude remained at least marginally significant in all – and highly significant in most – of the modified models (Table A2). The variances in slopes explained by latitude varied between 16% and 39%, depending on the statistical assumptions made.

Although SSTs were at least as important for breeding success as NAO, the variance in slopes of breeding success against SST were less readily accounted for by the covariates considered (Table 3). In other words, the relationship between SST and breeding success does not vary much across latitudes or taxa. This can, of course, have many reasons. However, it rather strengthens than weakens the interpretation that SST is an important climatic variable affecting seabird breeding success (e.g. Murphy & Schauer, 1994; Guinet et al., 1998; Gjerdrum et al., 2003; Inchausti et al., 2003; Frederiksen et al., 2004; but see Jenouvrier et al., 2003). Assuming that SST indeed is the single most important nonbiological variable, one cannot expect the remaining variables to explain the residual variation after the effect of SST is taken into account.

The signs of the correlations between SST (unlagged) and breeding success are positive. This would be compatible with a direct effect of weather on breeding performance (i.e. an increased mortality of chicks in colder-than-average breeding seasons). Alternatively, the effect of SST is mediated through the food chain. The availability of many marine prey species of seabirds is affected by SST, even though the signs of those correlations vary with species and region (Alheit & Hagen, 1997; Ottersen & Loeng, 2000; Genner et al., 2004; Hjermann et al., 2004; Cook & Heath, 2005; Rose, 2005). Finally, it may be the case that both summer SST and the performance of adult breeders are correlated with a third factor, such as weather conditions during the winter before the respective breeding attempt, operating through an effect on body condition (e.g. Durant et al., 2006). However, this interpretation is unlikely because of the absence of any clear effect of winter SST on breeding success (Table 1).

A number of earlier studies has found negative correlations between SST and breeding success. These results are not in direct conflict with our positive relationship, however, because the other studies either stem from the Pacific (Kitaysky & Golubova, 2000; Gaston & Smith, 2001; Gjerdrum et al., 2003; Smithers et al., 2003), where warm water events co-occur with collapses in the upwelling systems; from the Southern Ocean (Inchausti et al., 2003; Jenouvrier et al., 2003), where many seabirds feed at the ice edge; or considered SST at higher time lags (Frederiksen et al., 2004). On the other hand, Durant et al. (2003, 2006) reported a positive relationship between SST and breeding success of Atlantic puffins (Fratercula arctica) in the Norwegian Sea.

According to the above interpretation, the significant effect of NAO on the breeding success of the following year may be predominantly due to the correlation between NAO and SST. Other meteorological parameters that covary with the NAO, such as precipitation and wind speed, are of less importance for marine organisms. This would make sense of the finding that models with NAO only become significant when latitude is included as a covariate. The reason is that the covariation between NAO and SST is geographically variable (‘tripole’ pattern; cf. Hurrell et al., 2003; Hurrell & Dickson, 2004; Cohen & Barlow, 2005;Fig. 1), so that the same NAO index value has different oceanographic and, thus, biological meanings in different parts of the North Atlantic Ocean. If this view is correct, however, it is not latitude per se that interacts with NAO to influence breeding success, but the correlation between NAO and SST. To test this hypothesis, we also carried out analyses with local NAO–SST correlations as covariates. Those were the best supported models in all cases and under all statistical assumptions (Tables 2 and A2). Figure 3 illustrates this relationship: with an increasing local correlation between NAO and SST, the slope of breeding success on NAO decreases. This decline is surprisingly coherent across the different taxa of seabirds.

Overall, however, the model incorporating both NAO and latitude performed better than the SST models (Table 1), suggesting that most, but not all, relevant climatic information is contained in the SST variable (cf. Hallett et al., 2004; Stenseth & Mysterud, 2005). This is also visible from the fact that the intercept in Fig. 3 is significantly larger than zero: in the absence of any strong correlation between NAO and SST, NAO can still explain noteworthy amounts of variation in breeding success. Those are, by inference, unrelated to SSTs, at least at the time lag considered. What the causal links are in these cases is still an open question. On the other hand, when NAO and SST are correlated (right-hand side of Fig. 3), negative NAO values 1 year earlier (and, thus, low SSTs 2 years earlier) coincide with high breeding success. This, in turn, illustrates that one obvious advantage of the NAO index, methodologically speaking, is that it captures information from several seasons. Mechanistically speaking, however, even this larger amount of biological variance explained seems to be due to a large degree to SSTs, only at different time lags (positive at lag 0, negative at lags 1 and especially 2).

The time lags at which effects of NAO and SST were considered, were between zero and two years. The strongest effects were found at a time lag of zero and 1 year (i.e. breeding success was most strongly influenced by SSTs during the breeding season, and by the winter NAO 16 months before the breeding season). The correlation between December–March NAO and April–July SST was estimated for time lags between −1 and +1 years (or, more specifically, for time lags of −16, −4 and +8 months). The correlation that proved most relevant was the one in which the SST preceded NAO by 8 months (cf. Fig. 1). This is in accordance with oceanographic and climatological findings that the long-term atmospheric patterns constituting the NAO are forced by SSTs rather than the other way around (Wang et al., 2004). The presence of these time lags indicates that the effect of climate cannot be restricted to a direct influence of weather on seabird breeding success. Instead, an influence on the local food source around the breeding colony is suggested. The negative sign of the lagged correlations are compatible with many findings of poorer prey abundance or prey recruitment in warmer-water years (Alheit & Hagen, 1997; Frederiksen et al., 2004; Hjermann et al., 2004; Cook & Heath, 2005). This effect might carry over to the following breeding season(s) both because seabirds often prey upon earlier fish cohorts (e.g. Hjermann et al., 2004) and by affecting the body condition of breeders (e.g. Frederiksen et al., 2004). In order to get a better understanding of the precise size of the time lags, it might be an interesting exercise to incorporate the seabirds' major prey species into future comparative analyses (cf. Kitaysky & Golubova, 2000).

The effect of climatic variables on breeding success documented in this study is compatible with the ‘tap’ hypothesis (Sæther et al., 2004), which poses that climate influences population dynamics by affecting recruitment (Crespin et al., 2006) rather than survival (‘tub’ hypothesis). As long-lived species with a comparatively low reproductive output per breeding attempt, seabirds have been hypothesized to be more strongly affected by climatic effects on survival (Lebreton & Clobert, 1991; Wooller et al., 1992). Previous findings are in accordance with this assumption (Grosbois & Thompson, 2005; Harris et al., 2005; Sandvik et al., 2005; cf. Sandvik & Erikstad, 2008). As the tap and tub hypothesis are not mutually exclusive, the current findings do of course not contradict that evidence, and indicate that population dynamics even of long-lived birds may be affected by climate both through a tap and a tub effect.

To conclude, we have shown the intercolony variation of breeding success of North Atlantic seabirds to be related to both NAO and SST. The main abiotic determinant is hypothesized to be SST, because the effect of NAO depends on latitude and, ultimately, SST. The strength of these findings is that they are derived from a comparative analysis of several populations of a dozen species of seabirds, rather than single colonies.

Acknowledgements

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References

We thank the referees for improvements in the manuscript. The study was funded by the Norwegian Research Council (programmes FRIMUF and NORKLIMA).

References

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References
  • Abraham CL, Sydeman WJ (2004) Ocean climate, euphausiids and auklet nesting: inter-annual trends and variation in phenology, diet and growth of a planktivorous seabird Ptychoramphus aleuticus. Marine Ecology Progress Series, 274, 235250.
  • Alheit J, Hagen E (1997) Long-term climate forcing of European herring and sardine populations. Fisheries Oceanography, 6, 130139.
  • Barber RT, Chavez FP (1983) Biological consequences of El Niño. Science (Washington, DC), 222, 12031210.
  • Cohen J, Barlow M (2005) NAO, AO and global warming: how closely related? Journal of Climate, 18, 44984513.
  • Cook RM, Heath MR (2005) The implications of warming climate for the management of North Sea demersal fisheries. International Council for the Exploration of the Sea Journal of Marine Science, 62, 13221326.
  • Crespin L, Harris MP, Lebreton J-D, Frederiksen M, Wanless S (2006) Recruitment to a seabird population depends on environmental factors and on population size. Journal of Animal Ecology, 75, 228238.
  • Duffy DC (1990) Seabirds and the 1982–1984 El Niño-Southern Oscillation. In: Global Ecological Consequences of the 1982–83 El Niño-Southern Oscillation (ed. GlynnPW), pp. 395415. Elsevier, Amsterdam.
  • Durant JM, Anker-Nilssen T, Stenseth NC (2003) Trophic interactions under climate fluctuations: the Atlantic puffin as an example. Proceedings of the Royal Society, Biological Sciences, 270, 14611466.
  • Durant JM, Anker-Nilssen T, Stenseth NC (2006) Ocean climate prior to breeding affects the duration of the nestling period in the Atlantic puffin. Biology Letters, 2, 628631.
  • Durant JM, Stenseth NC, Anker-Nilssen T, Harris MP, Thompson PM, Wanless S (2004) Marine birds and climate fluctuation in the North Atlantic. In: Marine Ecosystems and Climate Variation: The North Atlantic – a Comparative Perspective (eds StensethNC, OttersenG, HurrellJW, BelgranoA), pp. 95105. Oxford University Press, Oxford.
  • Frederiksen M, Wanless S, Harris MP, Rothery P, Wilson LJ (2004) The role of industrial fisheries and oceanographic change in the decline of North Sea black-legged kittiwakes. Journal of Applied Ecology, 41, 11291139.
  • Gaston AJ, Smith JL (2001) Changes in oceanographic conditions off northern British Columbia (1983–1999) and the reproduction of a marine bird, the Ancient Murrelet (Synthliboramphus antiquus). Canadian Journal of Zoology, 79, 17351742.
  • Genner MJ, Sims DW, Wearmouth VJ, Southall EJ, Southward AJ, Henderson PA, Hawkins SJ (2004) Regional climatic warming drives long-term community changes of British marine fish. Proceedings of the Royal Society, Biological Sciences, 271, 655661.
  • Gjerdrum C, Vallée AMJ, St Clair CC, Bertram DF, Ryder JL, Blackburn GS (2003) Tufted puffin reproduction reveals ocean climate variability. Proceedings of the National Academy of Sciences of the United States of America, 100, 93779382.
  • Grosbois V, Thompson PM (2005) North Atlantic climate variation influences survival in adult fulmars. Oikos, 109, 273290.
  • Guinet C, Chastel O, Koudil M, Durbec JP, Jouventin P (1998) Effects of warm sea-surface temperature anomalies on the blue petrel at the Kerguelen Islands. Proceedings of the Royal Society, Biological Sciences, 265, 10011006.
  • Hallett TB, Coulson T, Pilkington JG, Clutton-Brock TH, Pemberton JM, Grenfell BT (2004) Why large-scale climate indices seem to predict ecological processes better than local weather. Nature (London), 430, 7175.
  • Harris MP, Anker-Nilssen T, McCleery RH, Erikstad KE, Shaw DN, Grosbois V (2005) Effect of wintering area and climate on the survival of adult Atlantic puffins Fratercula arctica in the eastern Atlantic. Marine Ecology Progress Series, 297, 283296.
  • Hjermann DØ, Stenseth NC, Ottersen G (2004) Indirect climatic forcing of the Barents Sea capelin: a cohort effect. Marine Ecology Progress Series, 273, 229238.
  • Hurrell JW (2005) Climate indices. (URL, http://www.cgd.ucar.edu/cas/jhurrell/indices.html, accessed 3 November 2005.) [Climate Analysis Section, National Center for Atmospheric Research, Boulder, Colorado].
  • Hurrell JW, Dickson RR (2004) Climate variability over the North Atlantic. In: Marine Ecosystems and Climate Variation: the North Atlantic – a Comparative Perspective (eds StensethNC, OttersenG, HurrellJW, BelgranoA), pp. 1531. Oxford University Press, Oxford.
  • Hurrell JW, Kushnir Y, Ottersen G, Visbeck M (2003) An overview of the North Atlantic Oscillation. In: The North Atlantic Oscillation: Climatic Significance and Environmental Impact (eds HurrellJW, KushnirY, OttersenG, VisbeckM), pp. 135. American Geophysical Union, Washington, DC.
  • Inchausti P, Guinet C, Koudil M et al. (2003) Inter-annual variability in the breeding performance of seabirds in relation to oceanographic anomalies that affect the Crozet and the Kerguelen sectors of the Southern Ocean. Journal of Avian Biology, 34, 170176.
  • Jenouvrier S, Barbraud C, Weimerskirch H (2003) Effects of climate variability on the temporal population dynamics of southern fulmars. Journal of Animal Ecology, 72, 576587.
  • Kitaysky AS, Golubova EG (2000) Climate change causes contrasting trends in reproductive performance of planktivorous and piscivorous alcids. Journal of Animal Ecology, 69, 248262.
  • Lebreton J-D, Clobert J (1991) Bird population dynamics, management, and conservation: the role of mathematical modelling. In: Bird Population Studies: Relevance to Conservation and Management (eds PerrinsCM, LebretonJ-D, HironsGJM), pp. 105125. Oxford University Press, Oxford.
  • Murphy EC, Schauer JH (1994) Numbers, breeding chronology, and breeding success of Common Murres at Bluff, Alaska, in 1975–1991. Canadian Journal of Zoology, 72, 21052118.
  • Mysterud A, Yoccoz NG, Stenseth NC, Langvatn R (2000) Relationships between sex ratio, climate and density in red deer: the importance of spatial scale. Journal of Animal Ecology, 69, 959974.
  • Ottersen G, Loeng H (2000) Covariability in early growth and year-class strength of Barents Sea cod, haddock, and herring: the environmental link. International Council for the Exploration of the Sea Journal of Marine Science, 57, 339348.
  • Peck DR, Smithers BV, Krockenberger AK, Congdon BC (2004) Sea surface temperature constrains wedge-tailed shearwater foraging success within breeding seasons. Marine Ecology Progress Series, 281, 259266.
  • Post E, Stenseth NC (1999) Climatic variability, plant phenology, and northern ungulates. Ecology (Washington, DC), 80, 13221339.
  • R development core team (2005) R: a language and environment for statistical computing, version 2.1.1. (URL, http://www.r-project.org). R Foundation for Statistical Computing, Wien.
  • Reid JB, Becker PH, Furness RW (1999) Evidence for decadal scale variations in seabird population ecology and links with the North Atlantic Oscillation. In: Diets of Seabirds and Consequences of Changes in Food Supply (eds FurnessRW, TaskerML), pp. 4750. International Council for the Exploration of the Sea, København.
  • Rose GA (2005) Capelin (Mallotus villosus) distribution and climate: a sea “canary” for marine ecosystem change. International Council for the Exploration of the Sea Journal of Marine Science, 62, 15241530.
  • Sandvik H, Erikstad KE (2008) Seabird life histories and climatic fluctuations: a phylogenetic-comparative time series analysis of North Atlantic seabirds. Ecography, 31, in press, doi: DOI: 10.1111/j.2007.0906-7590.05090.x.
  • Sandvik H, Erikstad KE, Barrett RT, Yoccoz NG (2005) The effect of climate on adult survival in five species of North Atlantic seabirds. Journal of Animal Ecology, 74, 817831.
  • Schreiber EA (2002) Climate and weather effects on seabirds. In: Biology of Marine Birds (eds SchreiberEA, BurgerJ), pp. 179215. CRC, Boca Raton.
  • Schreiber EA, Burger J (2002) Data on life-history characteristics, breeding range, size and survival for seabird species. In: Biology of Marine Birds (eds SchreiberEA, BurgerJ), pp. 665685. CRC, Boca Raton.
  • Schreiber RW, Schreiber EA (1984) Central Pacific seabirds and the El Niño Southern Oscillation: 1982 to 1983 perspectives. Science (Washington, DC), 225, 713716.
  • Smith TM, Reynolds RW (2006) Extended reconstructed sea surface temperatures, version 2. (URL, http://lwf.ncdc.noaa.gov/oa/climate/research/sst/sst.html, accessed 20 March 2006.)
  • Smithers BV, Peck DR, Krockenberger AK, Congdon BC (2003) Elevated sea-surface temperature, reduced provisioning and reproductive failure of wedge-tailed shearwaters (Puffinus pacificus) in the southern Great Barrier Reef, Australia. Marine and Freshwater Research, 54, 973977.
  • Sokal RR, Rohlf FJ (1995) Biometry: The Principles and Practice of Statistics in Biological Research, 3rd edn. Freeman, New York.
  • Stenseth NC, Mysterud A (2005) Weather packages: finding the right scale and composition of climate in ecology. Journal of Animal Ecology, 74, 11951198.
  • Sæther B-E, Engen S, Møller AP et al. (2003) Climate variation and regional gradients in population dynamics of two hole-nesting passerines. Proceedings of the Royal Society, Biological Sciences, 270, 23972404.
  • Sæther B-E, Sutherland WJ, Engen S (2004) Climate influences on avian population dynamics. Advances in Ecological Research, 35, 185209.
  • Walker GT (1924) Correlations in seasonal variations of weather, IX. A further study of world weather. Memoirs of the India Meteorological Department, 24, 275332.
  • Wang W, Anderson BT, Kaufmann RK, Myneni RB (2004) The relation between the North Atlantic Oscillation and SSTs in the North Atlantic Basin. Journal of Climate, 17, 47524759.
  • Weimerskirch H, Inchausti P, Guinet C, Barbraud C (2003) Trends in bird and seal populations as indicators of a system shift in the Southern Ocean. Antarctic Science, 15, 249256.
  • Wooller RD, Bradley JS, Croxall JP (1992) Long-term population studies of seabirds. Trends in Ecology and Evolution, 7, 111114.

Appendix A

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References
Table TableA1.   Studies of seabird breeding success used in the analyses
SpeciesEnglish nameColonyClusterLatitudeLongitudeYearsLengthSource
  1. ‘Cluster’ refers to geographically close colonies. Time series with the same ‘cluster’ number were combined in certain analyses (see ‘Material and methods’, and test 7 of Table A2).

Alca tordaRazorbillIsle of May156.2°N2.6°W1982–19876Harris & Wanless (1989)
Calonectris diomedeaCory's shearwaterSelvagem Grande230.2°N15.9°W1983–199614Mougin et al. (2000)
Fratercula arcticaAtlantic puffinIsle of May356.2°N2.6°W1977–199014Harris & Bailey (1992)
Fratercula arcticaAtlantic puffinDùn457.8°N8.6°W1973–199417Harris et al. (1998)
Fratercula arcticaAtlantic puffinRunde562.4°N5.6°E1980–19834Barrett et al. (1987)
Fulmarus glacialisNorthern fulmarEynhallow659.1°N3.1°W1958–197821Ollason & Dunnet (1980)
Larus argentatusHerring gullTryskärsgrund760.0°N23.0°E1983–19886Kilpi (1989)
Larus fuscusLesser black-backed gullSöderskär860.0°N25.0°E1980–198910Hario (1990)
Morus bassanusNorthern gannetBempton954.1°N0.1°W1961–197616Nelson (1978)
Morus bassanusNorthern gannetBass Needle1056.2°N2.6°W1971–19766Nelson (1978)
Morus bassanusNorthern gannetBass Rock 51056.2°N2.6°W1970–19767Nelson (1978)
Morus bassanusNorthern gannetBass Rock 61056.2°N2.6°W1970–19734Nelson (1978)
Morus bassanusNorthern gannetTroup Head1157.7°N2.3°W1988–19958Wanless et al. (1996)
Pterodroma madeiraZino's petrelMadeira1232.8°N16.9°W1986–200015Zino et al. (2001)
Puffinus puffinusManx shearwaterSkokholm 11351.7°N5.3°W1973–19764Brooke (1978)
Puffinus puffinusManx shearwaterSkokholm 21351.7°N5.3°W1973–19764Brooke (1978)
Puffinus puffinusManx shearwaterCanna1457.0°N6.6°W1976–199722Swann (1995); Swann (2000)
Rissa tridactylaBlack-legged kittiwakeS Shields1555.0°N1.4°W1954–198229Coulson & Thomas (1985a, 1985b)
Rissa tridactylaBlack-legged kittiwakeIsle of May1656.2°N2.6°W1989–19968Harris & Wanless (1997)
Sterna hirundoCommon ternLittle Island1739.6°N74.2°W1976–19805Burger & Gochfeld (1991)
Sterna hirundoCommon ternW Ham1739.6°N74.2°W1979–19856Burger & Gochfeld (1991)
Sterna hirundoCommon ternE Carvel1739.7°N74.2°W1976–19838Burger & Gochfeld (1991)
Sterna hirundoCommon ternPettit1739.7°N74.2°W1980–19856Burger & Gochfeld (1991)
Sterna hirundoCommon ternW Carvel1739.7°N74.2°W1976–19805Burger & Gochfeld (1991)
Sterna hirundoCommon ternW Vol1739.7°N74.1°W1976–19859Burger & Gochfeld (1991)
Sterna hirundoCommon ternN Lavallette1739.8°N74.1°W1976–19849Burger & Gochfeld (1991)
Sterna hirundoCommon ternNW Lavallette1739.8°N74.1°W1976–19794Burger Gochfeld (1991)
Sterna hirundoCommon ternS Lavallette1739.8°N74.1°W1976–19794Burger & Gochfeld (1991)
Sterna hirundoCommon ternSW Lavallette1739.8°N74.1°W1976–19849Burger & Gochfeld (1991)
Sterna hirundoCommon ternMinsener Oldeoog1853.8°N8.0°E1981–199616Becker (1998)
Sterna paradisaeaArctic ternMachias Seal Island1944.5°N67.1°W1978–19814Newell (1985)
Uria aalgeCommon murreIsle of May2056.2°N2.6°W1981–199818Harris & Bailey (1992); Rindorf et al. (2000)
Uria aalgeCommon murreStora Karlsö2157.3°N18.0°E1974–19774Hedgren (1980)
Table TableA2.   Variations of the models presented in Table 2
ModelFPdfr2ΔAICC
  • The three models from Table 2 were rerun using different methods or under different statistical assumptions. Results are largely in agreement with Table 2 and each other. Only model statistics are provided. See Table 1 for further explanations.

  • *

    The slopes were z-transformed (Sokal & Rohlf, 1995, p. 575) prior to analyses in all but two cases: in analysis 4, z-transformation was neither applicable nor necessary (the distribution did not differ from normality and slopes were processed untransformed); in analysis 5, z*-transformation (Sokal & Rohlf, 1995, p. 579) was required to yield approximately normally distributed values.

(1) Weighting each slope by the inverse variance of the underlying time series
  Latitude9.170.00491, 310.23−6.12
  Latitude × taxon3.770.00489, 230.60+0.26
  Local correlation with SST17.700.000201, 310.36−12.48
(2) Excluding slopes derived from times series shorter than 5 years
  Latitude14.500.000911, 230.39–9.62
  Latitude × taxon2.220.0829, 150.57+16.57
  Local correlation with SST19.530.000201, 230.46–12.77
(3) Excluding slopes derived from times series shorter than 6 years
  Latitude12.690.00181, 210.38–8.21
  Latitude × taxon1.900.149, 130.57+22.07
  Local correlation with SST17.310.000441, 210.45–11.16
(4) Using NAO slopes derived from multivariate analysis including both NAO and SST*
  Latitude9.690.00401, 310.24–6.55
  Latitude × taxon2.010.0859, 230.44+11.02
  Local correlation with SST14.530.000621, 310.32–10.26
(5) Using slopes derived from first year differentials of the time series rather than raw data*
  Latitude4.680.0411, 230.17–2.03
  Latitude × taxon3.260.0219, 150.66+10.68
  Local correlation with SST18.290.000281, 230.44–12.03
(6) Using robust fitting of linear models (R function rlm; Venables & Ripley, 2002)
  Latitude10.800.00251, 310.26–7.41
  Latitude × taxon3.470.00769, 230.58+2.00
  Local correlation with SST15.100.000501, 310.33–10.64
(7) Treating geographically close colonies as single data points
  Latitude3.570.0741, 190.16–0.87
  Latitude × taxon1.790.189, 110.59+27.70
  Local correlation with SST5.570.0291, 190.23–2.66

References

  1. Top of page
  2. Abstract
  3. Introduction
  4. Materials and methods
  5. Results
  6. Discussion
  7. Acknowledgements
  8. References
  9. Appendix A
  10. References
  • Barrett RT, Anker-Nilssen T, Rikardsen F, Valde K, Røv N, Vader W (1987) The food, growth and fledging success of Norwegian Puffin chicks Fratercula arctica in 1980–1983. Ornis Scandinavica, 18, 7383.
  • Becker PH (1998) Langzeittrends des Bruterfolges der Flußseeschwalbe Sterna hirundo und seiner Einflußgrößen im Wattenmeer. Vogelwelt, 119, 223234.
  • Brooke MdL (1978) Some factors affecting the laying date, incubation and breeding success of the manx shearwater, Puffinus puffinus. Journal of Animal Ecology, 47, 477495.
  • Burger J, Gochfeld M (1991) The common tern: its breeding biology and social behavior. Columbia University Press, New York413 pp.
  • Coulson JC, Thomas C (1985a) Differences in the breeding performance of individual Kittiwake gulls, Rissa tridactyla (L.). In: Behavioural ecology: ecological consequences of adaptive behaviour (eds SiblyRM, SmithRH), pp. 489503. Blackwell, Oxford.
  • Coulson JC, Thomas CS (1985b) Changes in the biology of the kittiwake Rissa tridactyla: a 31–year study of a breeding colony. Journal of Animal Ecology, 54, 926.
  • Hario M (1990) Breeding failure and feeding conditions of Lesser Black-backed Gulls Larus f. fuscus in the Gulf of Finland. Ornis Fennica, 67, 113129.
  • Harris MP, Bailey RS (1992) Mortality rates of puffin Fratercula arctica and guillemot Uria aalge and fish abundance in the North Sea. Biological Conservation, 60, 3946.
  • Harris MP, Murray S, Wanless S (1998) Long-term changes in breeding performance of Puffins Fratercula arctica on St Kilda. Bird Study, 45, 371374.
  • Harris MP, Wanless S (1989) The breeding biology of Razorbills Alca torda on the Isle of May. Bird Study, 36, 105114.
  • Harris MP, Wanless S (1997) Breeding success, diet, and brood neglect in the kittiwake (Rissa tridactyla) over an 11–year period. International Council for the Exploration of the Sea Journal of Marine Science, 54, 615623.
  • Hedgren S (1980) Reproductive success of Guillemots Uria aalge on the island of Stora Karlsö. Ornis Fennica, 57, 4957.
  • Kilpi M (1989) The effect of varying pair numbers on reproduction and use of space in a small Herring Gull Larus argentatus colony. Ornis Scandinavica, 20, 204210.
  • Mougin J-L, Jouanin C, Roux F (2000) Mate fidelity in Cory's Shearwater Calonectris diomedea on Selvagem Grande. Ibis, 142, 421427.
  • Nelson JB (1978) The Sulidae: gannets and boobies, Aberdeen University Studies Series, 154. Oxford University Press, Oxford, 1012 pp.
  • Newell RB (ed, 1985) Nesting ecology of Arctic Terns Sterna paradisaea Pontoppidan in relation to habitat on Machias Seal Island. MSc thesis, Department of Biology, Acadia University, Wolfville, 167 pp.
  • Ollason JC, Dunnet GM (1980) Nest failures in the Fulmar: the effect of observers. Journal of Field Ornithology, 51, 3954.
  • Rindorf A, Wanless S, Harris MP (2000) Effects of changes in sandeel availability on the reproductive output of seabirds. Marine Ecology Progress Series, 202, 241252.
  • Swann B (2000) Integrated seabird monitoring studies on the Isle of Canna, Scotland 1969–99. Atlantic Seabirds, 2, 151164.
  • Swann RL (1995) Numbers and breeding success of Manx Shearwaters on the Isle of Canna, 1973–94. Scottish Birds, 18, 5657.
  • Venables WN, Ripley BD (2002) Modern Applied Statistics With S, 4th edn. Springer, New York.
  • Wanless S, Matthews J, Bourne WRP (1996) The Troup Head gannetry. Scottish Birds, 18, 214221.
  • Zino F, Oliveira P, King S, Buckle A, Biscoito M, Costa Neves H, Vasconcelos A (2001) Conservation of Zino's petrel Pterodroma madeira in the archipelago of Madeira. Oryx, 35, 128136.