Factors driving spatial and temporal variation in production and production / biomass ratio of stream‐resident brown trout (Salmo trutta) in Cantabrian streams

1. The objective was to identify the factors driving spatial and temporal variation in annual production (P_A) and turnover (production/biomass) ratio (P/B_A) of resident brown trout Salmo trutta in tributaries of the Rio Esva (Cantabrian Mountains, Asturias, north‐western Spain). We examined annual production (total production of all age‐classes over a year) (P_A) and turnover (P/B_A) ratios, in relation to year‐class production (production over the entire life time of a year‐class) (P_T) and turnover (P/B_T) ratio, over 14 years at a total of 12 sites along the length of four contrasting tributaries. In addition, we explored whether the importance of recruitment and site depth for spatial and temporal variations in year‐class production (P_T), elucidated in previous studies, extends to annual production. 2. Large spatial (among sites) and temporal (among years) variation in annual production (range 1.9–40.3 g m^?2 per year) and P/B_A ratio (range 0.76–2.4 per year) typified these populations, values reported here including all the variation reported globally for salmonids streams inhabited by one or several species. 3. Despite substantial differences among streams and sites in all production attributes, when all data were pooled, annual (P_A) and year‐class production (P_T) and annual (P/B_A) and year‐class P/B_T ratios were tightly linked. Annual (P_A) and year‐class production (P_T) were similar but not identical, i.e. P_T = 0.94 P_A, whereas the P/B_T ratios were 4 + P/B_A ratios. 4. Recruitment (Rc) and mean annual density (N_A) were major density‐dependent drivers of production and their relationships were described by simple mathematical models. While year‐class production (P_T) was determined (R² = 70.1%) by recruitment (Rc), annual production (P_A) was determined (R² = 60.3%) by mean annual density (N_A). In turn, variation in recruitment explained R² = 55.2% of variation in year‐class P/B_T ratios, the latter attaining an asymptote at P/B_T = 6 at progressively higher levels of recruitment. Similarly, variations in mean annual density (N_A) explained R² = 52.1% of variation in annual P/B_A, the latter reaching an asymptote at P/B_A = 2.1. This explained why P/B_T is equal to P/B_A plus the number of year‐classes at high but not at low densities. 5. Site depth was a major determinant of spatial (among sites) variation in production attributes. All these attributes described two‐phase trajectories with site depth, reaching a maximum at sites of intermediate depth and declining at shallower and deeper sites. As a consequence, at sites where recruitment and mean annual density reached minimum or maximum values, annual (P_A) and year‐class production (P_T) and annual (P/B_A) and year‐class P/B_T ratios also reached minimum and maximum values.     

Nest orientation and hatching success of Black Kites Milvus migrans in Spain

An analysis of the orientation of 182 nest sites of the Black Kite Milvus migrans in two areas in south and central Spain found that orientations toward the east were preferred. In southern Spain an analysis of the relationship between nest orientation and hatching success showed that success was lower among the nests located in non-preferred orientations, with some inter-annual variation. The tendency to orientate nests toward the east was greater among the early nesting pairs and the effect that the orientation had on the hatching success was also greater than in late nesting pairs. The data suggest that rainfall and prevailing winds were the main factors conditioning nest orientation.     

Differential habitat selection by immature and adult Grey Eagle-buzzards Geranoaetus melanoleucus

During the 1992 breeding season, we studied the habitat selection, behaviour, aggressive interactions and diet of immature and adult Grey Eagle-buzzards Geranoaetus melanoleucus in an area of the Argentinean Patagonia. Immature eagles selected areas rich in prey, had no preference for flat or rugged areas and did not avoid areas close to active nests or those used by adult eagles. The density of the European Hare Lepus europaeus was the best predictor of the distribution of immature eagles. Adult eagles preferred rugged to flat areas but were not significantly affected by prey distribution. Immature eagles used flapping flight more frequently than did adult eagles. Wing-flapping frequency of immatures did not differ when flying over slopes or plains. In contrast, adults used a more economic flight with a lower wing-flapping frequency than that of immatures, especially when flying over slopes. Adults, in contrast to immatures, tended to select slopes when flying over predominantly flat country. Only in 22% of the occasions when adult and immatures were seen together were immatures attacked by adults, a rate of aggressive encounters similar to that observed between immatures (32%). This similarity indicates that adults do not actively exclude immatures from certain areas. The main prey of both immature and adult eagles was the introduced European Hare followed by native rodents and birds. Immatures ate significantly more carrion and fewer birds than did adults. These observations suggest that differences in flight behaviour and in the flight silhouette between adult and immature eagles may be responsible for their different habitat selection in relation to topography. While immatures apparently cue on prey density for habitat selection, adults select areas that allow more economic foraging flights