Laying date and clutch size of Great Tits(Parus major) in the Mediterranean region: a comparison of four habitat types

Summary Laying data and clutch size of Great Tits were studied in four different habitats in eastern Spain: two holm oak(Quercus ilex) forests, at 500 and 900–950 m a.s.l., a zeen oak(Quercus faginea) forest, at 900–1100 m a.s.l., a pine(Pinus sylvestris) forest, at 1000–1050 m a.s.l., and orange(Citrus aurantium) plantations, at 30 m a.s.l. All sites were placed at about the same latitude (39–41°N), and all were studied during the same years (1992–95). Our results show that (1) laying date did not differ between the natural habitats at the same altitude (range of the means of yearly means 4–8 May); (2) within the same habitat type (holm oak forest) laying date was earlier at low altitude (30 Aprilvs. 8 May); (3) laying date was earlier in the orange plantations (21 April) than in natural habitats; (4) among natural habitats at the same altitude, clutch size decreased from zeen oak (mean of yearly means 7.3 eggs) to holm oak (7.0 eggs) to pine forests (6.4 eggs), though only the difference between zeen oak and pine forests was significant; (5) within the same habitat type (holm oak forest), the clutch size tended to be larger at high altitude (7.0vs. 5.9 eggs); and (6) clutch size in orange plantations (7.7 eggs) did not differ significantly from that of the zeen oak forest, but was larger than in the holm oak and pine forests. We discuss the effect of the habitat type on laying date and clutch size of Great Tits.

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Legedatum und Gelegegröße der Kohlmeise(Parus major) in mediterranen Gebieten: Ein Vergleich zwischen vier verschiedenen Biotopen

Zusammenfassung Legedatum und Gelegegröße der Kohlmeise wurden in vier unterschiedlichen Biotopen in Ostspanien untersucht: zwei Steineichenwälder(Quercus ilex) in 500 m und 900–950 mNN, ein Bergeichenwald(Quercus faginea) in 900–1100 mNN, ein Kiefernwald(Pinus sylvestris) in 1000–1050 mNN und eine Orangenpflanzung(Citrus aurantium) in 30 mNN. Alle fünf Gebiete lagen auf etwa demselben Breitengrad (39–41°N) und wurden 1992–1995 parallel untersucht.(1) Auf gleicher Meereshöhe unterscheidet sich der Legebeginn nicht zwischen den verschiedenen Waldbiotopen (im Mittel 4.–8. Mai). (2) Innerhalb desselben Biotoptyps (Steineichenwald) war der Legebeginn auf niedrigerer Meereshöhe früher als in höheren Lagen (30. April vs. 8. Mai). (3) Im Orangenhain wurde früher mit der Eiablage begonnen (21. April) als in den Waldbiotopen. (4) Auf gleicher Meereshöhe nahm die Gelegegröße vom Bergeichenwald (Mittelwert 7.3 Eier) über die Steineichenwälder (7,0 Eier) zum Kiefernwald hin ab (6.4 Eier), jedoch ist nur der Unterschied zwischen Bergeichenwald und Kiefernwald signifikant. (5) Innerhalb der Steineichenwälder besteht die Tendenz zu größerer Gelegegröße in den höheren Lagen (7.0 vs. 5.9 Eier). (6) Im Orangenhain war die Gelegegröße mit durchschnittlich 7.7 Eier ähnlich der im Bergeichenwald, aber größer als in den Steineichen- und Kiefernwälder.

     

The Quantity and Turnover of Dead Wood in Permanent Forest Plots in Six Life Zones of Venezuela1

Dead wood can be an important component of the carbon pool in many forests, but few measurements have been made of this pool in tropical forests, To fill this gap, we determined the quantity of dead wood (downed and standing dead) in 25 long-term (up to 30 yr) permanent forest plots located in six different life zones of Venezuela. Downed wood was separated into fine (< 10 cm in diameter) and coarse (≥ 10 cm in diameter) classes, and three decomposition states (sound, intermediate, or rotten). The total quantity of dead wood, averaged by life zone, was lowest in the dry (2.43 Mg/ha), reached a peak in the moist (42.33 Mg/ha) and decreased slightly in the wet (34.50 Mg/ha) life zone. Most of the dead wood was in the standing dead category (about 42–76% of the total). The decomposition state of dead wood in all plots was mostly rotten (45%) or intermediate (44%); there was little sound wood (11%). Turnover rates of dead wood generally ranged between 0.03/yr to 0.52/yr with no clear trend with life zone. The large amount of dead wood in some plots was equivalent to about 20 percent or less of aboveground biomass, indicating that dead wood can represent a significant amount of carbon in these forests.     

Biofumigation potential of brassicas

The relationship of global climate change to plant growth and the role of forests as sites of carbon sequestration have encouraged the refinement of the estimates of root biomass and production. However, tremendous controversy exists in the literature as to which is the best method to determine fine root biomass and production. This lack of consensus makes it difficult for researchers to determine which methods are most appropriate for their system. The sequential root coring method was the most commonly used method to collect root biomass data in the past and is still commonly used. But within the last decade the use of minirhizotrons has become a favorite method of many researchers. In addition, due to the high labor-intensive requirements of many of the direct approaches to determine root biomass, there has been a shift to develop indirect methods that would allow fine root biomass and production to be predicted using data on easily monitored variables that are highly correlated to root dynamics. Discussions occur as to which method should be used but without gathering data from the same site using different methods, these discussions can be futile. This paper discusses and compares the results of the most commonly used direct and indirect methods of determining root biomass and production: sequential root coring, ingrowth cores, minirhizotrons, carbon fluxes approach, nitrogen budget approach and correlations with abiotic resources. No consistent relationships were apparent when comparing several sites where at least one of the indirect and direct methods were used on the same site. Until the different root methods can be compared to some independently derived root biomass value obtained from total carbon budgets for systems, one root method cannot be stated to be the best and the method of choice will be determined from researcher's personal preference, experiences, equipment, and/or finances.     

Tropical nematode diversity: vertical stratification of nematode communities in a Costa Rican humid lowland rainforest

Comparisons of nematode communities among ecosystems have indicated that, unlike many organisms, nematode communities have less diversity in the tropics than in temperate ecosystems. There are, however, few studies of tropical nematode diversity on which to base conclusions of global patterns of diversity. This study reports an attempt to estimate nematode diversity in the lowland tropical rainforest of La Selva Biological Research Station in Costa Rica. We suggest one reason that previous estimates of tropical nematode diversity were low is because habitats above the mineral soil are seldom sampled. As much as 62% of the overall genetic diversity, measured by an 18S ribosomal barcode, existed in litter and understorey habitats and not in soil. A maximum-likelihood tree of barcodes from 360 individual nematodes indicated most major terrestrial nematode lineages were represented in the samples. Estimated 'species' richness ranged from 464 to 502 within the four 40 × 40 m plots. Directed sampling of insects and their associated nematodes produced a second set of barcodes that were not recovered by habitat sampling, yet may constitute a major class of tropical nematode diversity. While the generation of novel nematode barcodes proved relatively easy, their identity remains obscure due to deficiencies in existing taxonomic databases. Specimens of Criconematina, a monophyletic group of soil-dwelling plant-parasitic nematodes were examined in detail to assess the steps necessary for associating barcodes with nominal species. Our results highlight the difficulties associated with studying poorly understood organisms in an understudied ecosystem using a destructive (i.e. barcode) sampling method.     

Carbon dioxide increase: the implications at the ecosystem level*

Abstract Possible effects of increased atmospheric concentrations of CO₂ on forest ecosystems are discussed and as an example a simulation case study using a set of mixed-age and mixed-species forest stand models is presented. The responses of the models to a simple scenario (uniform growth increase of all trees as a response to CO₂ enrichment) include increases in biomass that are considerably less than the increases in growth rate of the trees. These simulations and more general discussion of the possible effects of increased photosynthetic production identify the problem of scaling-up small time-scale and space-scale measurements of plant responses to CO₂ enrichment to the ecosystem level.     

Relationships of subalpine forest fires in the Colorado Front Range with interannual and multidecadal‐scale climatic variation

Aim An understanding of past relationships between fire occurrence and climate variability will help to elucidate the implications of climate‐change scenarios for future patterns of wildfire. In the present study we investigate the relationships between subalpine‐zone fire occurrence and climate variability and broad‐scale climate patterns in the Pacific and Atlantic Oceans at both interannual and multidecadal time‐scales. Location The study area is the subalpine zone of Engelmann spruce (Picea engelmannii) and subalpine fir (Abies lasiocarpa), and lodgepole pine (Pinus contorta) in the southern sector of the Rocky Mountain National Park, which straddles the continental divide of the northern Colorado Front Range. Methods We compared years of widespread fire from AD 1650 to 1978 for the subalpine zone of southern Rocky Mountain National Park, with climate variables such as measures of drought, and indices such as the El Niño–Southern Oscillation (ENSO), the Pacific Decadal Oscillation (PDO), and the Atlantic Multidecadal Oscillation (AMO). Results Years of extensive subalpine‐zone fires are significantly related to climate variability, phases of ENSO, the PDO, and the AMO, as well as to phase combinations of ENSO, the PDO, and the AMO at both interannual and centennial time‐scales. Main conclusions Years of extensive fires are related to extreme drought conditions and are significantly related to the La Niña phase of ENSO, the negative (cool) phase of the PDO, and the positive (warm) phase of the AMO. The co‐occurrence of the phase combination of La Niña‐negative PDO‐positive AMO is more important to fire occurrence than the individual influences of the climate patterns. Low‐frequency trends in the occurrence of this combination of climate‐pattern phases, resulting from trends in the AMO, are the primary climate pattern associated with periods of high fire occurrence (1700–89 and 1851–1919) and a fire‐free period (1790–1850). The apparent controlling influence of the AMO on drought and years of large fires in the subalpine forests of the Colorado Front Range probably applies to an extensive area of western North America.     

Mate-locating behaviour, habitat-use, and flight morphology relative to rainforest disturbance in an Afrotropical butterfly

To cope with environmental constraints, organisms can show variation in phenotype, either by genetic adaptation or phenotypic plasticity. These patterns are especially pronounced in ecosystems that are under anthropogenic influence. Due to human-induced disturbances such as logging and deforestation, tropical forests comprise such a system. To date, most studies have dealt with ecological responses at the community level relative to forest disturbance or degradation. However, the evolutionary consequences of tropical forest deterioration on behaviour and functional morphology have received far less attention compared to temporal regions. From a resource-point of view, light conditions are essential for heliotherms such as butterflies. Because degradation of tropical cloud forests in the Taita Hills (Kenya) is very pronounced, the present study tested whether this induced changes in mate-location strategies, habitat-use, and functional flight morphology in a forest butterfly, Salamis parhassus. According to predictions from temperate regions, it was hypothesized that the species would change its mate location strategy from perching to patrolling in more disturbed forests, that this higher mobility results in a faster occupancy of light gaps, and that it accords with a higher wing loading within populations from undisturbed forests. These hypotheses were confirmed by field surveys and experiments. The present study demonstrates that degradation of tropical forests does not only affect communities (e.g. species richness), but also the behaviour and functional morphology of individual species.  © 2009 The Linnean Society of London, Biological Journal of the Linnean Society , 2009, 96 , 830–839.     

Ecological research for development

Uganda is rich in aquatic ecosystems. Commercial fishing involves an off‐take that may not be ultimately sustainable. Aquatic ecosystems, like the forests, are under pressure. Forests, for many years to come, will remain the main source of energy for the people. They also continue to be cleared to make way for agricultural use of the land. Research for development must address problems of this kind as they are at the heart of the development process.     

Variation in the population structure between a natural and a human‐modified forest for a pioneer tropical tree species not restricted to large gaps

The distribution of tree species in tropical forests is generally related to the occurrence of disturbances and shifts in the local environmental conditions such as light, temperature, and biotic factors. Thus, the distribution of pioneer tree species is expected to vary according to the gap characteristics and with human disturbances. We asked whether there was variation in the distribution of a pioneer species under different environmental conditions generated by natural disturbances, and between two forests with contrasting levels of human disturbance. To answer this question, we studied the distribution patterns and population persistence of the pioneer tree species Croton floribundus in the size and age gap range of a primary Brazilian forest. Additionally, we compared the plant density of two size‐classes between a primary and an early successional human‐disturbed forest. Croton floribundus was found to be widespread and equally distributed along the gap‐size gradient in the primary forest. Overall density did not vary with gap size or age (F‐ratio = 0.062, P = 0.941), and while juveniles were found to have a higher density in the early successional forest (P = 0.021), tree density was found to be similar between forests (P = 0.058). Our results indicate that the population structure of a pioneer tree species with long life span and a broad gap‐size niche preference varied between natural and human‐disturbed forests, but not with the level of natural disturbance. We believe this can be explained by the extreme environmental changes that occur after human disturbance. The ecological processes that affect the distribution of pioneer species in natural and human‐modified forests may be similar, but our results suggest they act differently under the contrasting environmental conditions generated by natural and human disturbances.