Global patterns of diversity among the specialist birds of riverine landscapes

1. Despite the growing view that biodiversity provides a unifying theme in river ecology, global perspectives on richness in riverine landscapes are limited. As a result, there is little theory or quantitative data on features that might have influenced global patterns in riverine richness, nor are there clear indications of which riverine landscapes are important to conservation at the global scale. As conspicuous elements of the vertebrate fauna of riverine landscapes, we mapped the global distributions of all of the world's specialist riverine birds and assessed their richness in relation to latitude, altitude, primary productivity and geomorphological complexity (surface configuration). 2. Specialist riverine birds, typical of high‐energy riverine landscapes and dependent wholly or partly on production from river ecosystems, occur in 16 families. They are represented by an estimated 60 species divided equally between the passerines and non‐passerines. Major radiation has occurred among different families on different continents, indicating that birds have evolved several times into the niches provided by riverine landscapes. 3. Continental richness varies from four species in Europe to 28 in Asia, with richness on the latter continent disproportionately larger than would be expected from a random distribution with respect to land area. Richness is greatest in mountainous regions at latitudes of 20–40°N in the riverine landscapes of the Himalayan mountains, where 13 species overlap in range. 4. Family, genus and species richness in specialist riverine birds all increase significantly with productivity and surface configuration (i.e. relief). However, family richness was the best single predictor of the numbers of species or genera. In keeping with the effect of surface configuration, river‐bird richness peaks globally at 1300–1400 m altitude, and most species occur typically on small, fast rivers where they feed predominantly on invertebrates. Increased lengths of such streams in areas of high relief and rainfall might have been responsible for species–area effects. 5. We propose the hypothesis that the diversity in channel forms and habitats in riverine landscapes, in addition to high temperature and primary productivity, have been prerequisites to the development of global patterns in the richness of specialist riverine organisms. We advocate tests of this hypothesis in other taxonomic groups. We draw attention, however, to the challenges of categorically defining riverine organisms in such tests because (i) rivers grade into many other habitat types across several different ecotones and (ii) `terrestrialisation' processes in riverine landscapes means that they offer habitat for organisms whose evolutionary origins are not exclusively riverine.     

Vertical and horizontal distribution patterns of the giant sea anemone Heteractis crispa with symbiotic anemonefish on a fringing coral reef

The distribution patterns of the leathery sea anemone, Heteractis crispa, which contains an algal endosymbiont (zooxanthellae) and anemonefish, were investigated in relation to size distribution on a shallow fringing reef (3.2 ha, 0–4 m depth) in Okinawa, Japan. Individual growth and movements were also examined. Large individuals (>1,000 cm²) inhabited reef edges up to a depth of 4 m, while small anemone (<500 cm²) inhabited shallow reefs including inner reef flats. Individuals rarely moved, and their sizes were significantly correlated with their water depths. Growth of small anemones was negatively correlated with their distance from the reef edge, suggesting that reef edges provide more prey and lower levels of physiological stress. This study suggested that deep reef edges are suitable habitats for H. crispa. Large anemones were inhabited by large Amphiprion perideraion or large Amphiprion clarkii, both of which are effective defenders against anemone predators. Anemones that settle in deep reef edges may enjoy a higher survival rate and attain a large size because of their symbiotic relationship with anemonefish. However, early settlers do not harbor anemonefish. Their mortality rate would be higher in the deep edges than in shallow edges, the complicated topography of which provides refuge.     

Electrogenic membrane transport in plants a review

This review treats some examples of electrogenic transport across the outer plasmamembrane (plasmalemma) of plant cells. The selection includes primary active uniport by membrane ATPases (e.g., the proton pump), secondary active transport of hexoses by proton-dependent cotransport, and passive uniport of amines. Primacy is given to the presentation of electrophysiological data and to the discussion of voltage-dependence of the transport mechanisms.Lecture from the Annual Meeting of the Deutsche Gesellschaft für Biophysik at Konstanz     

On the biology of bream, Abramis brama (L.) in Lake Peipsi in 1994

The population of bream in L. Peipsi was studied with respect to age, growth rate, condition factor (according to Fulton) and length-weight relationship in 1994. That autumn the bream population in L. Peipsi consisted of fishes aged from 0+ to 15+. During the first year bream reached an average body length of 7.9 cm (the commercial legal size (30 cm) was usually attained by the end of the 5th–6th year. The condition of bream in this lake was above the average of Estonian lakes. The relatively good growth rate and condition of bream in the lake indicates that the waterbody is appropriate for this fish.     

Genomic complexity and plasticity of Burkholderia cepacia

Abstract Burkholderia cepacia has attracted attention because of its extraordinary degradative abilities and its potential as a pathogen for plants and for humans. This bacterium was formerly considered to belong to the genus Pseudomonas in the γ-subclass of the Proteobacteria , but recently has been assigned to the β-subclass based on rrn gene sequence analyses and other key phenotypic characteristics. The B. cepacia genome is comprised of multiple chromosomes and is rich in insertion sequences. These two features may have played a key role in the evolution of novel degradative functions and the unusual adaptability of this bacterium.     

The structural features of effective antagonists of the luteinizing hormone releasing hormone

Summary The structure-activity data of 6 years on 395 analogs of the luteinizing hormone releasing hormone (LHRH) have been studied to determine effective substituents for the ten positions for maximal antiovulatory activity and minimal histamine release. The numbers of substituents studied in the ten positions are as follows: (41)¹-(12)²-(12)³-(5)⁴-(47)⁵-(52)⁶-(16)⁷-(18)⁸-(4)⁹-(8)¹⁰. In position 1, DNal and DQal were effective with the former being more frequently the better substituent. DpClPhe was uniquely effective in position 2. Positions 3 and 4 are very sensitive to change. D3Pal in position 3 and Ser in position 4 of LHRH were in the best antagonists. PicLys and cPzACAla were the most successful residues in position 5 with cPzACAla being the better substituent. Position 6 was the most flexible and many substituents were effective; particularly DPicLys. Leu⁷ was most often present in the best antagonists. In position 8, Arg was effective for both antiovulatory activity and histamine release; ILys was effective for potency and lesser histamine release. Pro⁹ of LHRH was retained. DAlaNH₂ ¹⁰ was in the best antagonists.Abbreviations AABLys N -(4-acetylaminobenzoyl)lysine - AALys N -anisinoyl-lysine - AAPhe 3-(4-acetylaminophenyl)lysine - Abu 2-aminobutyric acid - ACLys N -(6-aminocaproyl)lysine - ACyh 1-aminocyclohexanecarboxylic acid - ACyp 1-aminocyclopentanecarboxylic acid - Aile alloisoleucine - AnGlu 4-(4-methoxy-phenylcarbamoyl)-2-aminobutyric acid - 2ANic 2-aminonicotinic acid - 6ANic 6-aminonicotinic acid - APic 6-aminopicolinic acid - APh 4-aminobenzoic acid - APhe 4-aminophynylalanine - APz 3-amino-2-pyrazinecarboxylic acid - Aze azetidine-2-carboxylic acid - Bim 5-benzimidazolecarboxylic acid - BzLys N -benzoyllysine - Cit citrulline - Cl₂Phe 3-(3,4-dichlorphenyl)alanine - cPzACAla cis-3-(4-pyrazinylcarbonylaminocyclohexyl)alnine - cPmACAla cis-3-[4-(4-pyrimidylcarbonyl)aminocyclohexyl]alanine - Dbf 3-(2-dibenzofuranyl)alanine - DMGLys N -(N,N-dimethylglycyl)lysine - Dpo N -(4,6-dimethyl-2-pyrimidyl)-ornithine - F₂Ala 3,3-difluoroalanine - hNal 4-(2-naphthyl)-2-aminobutyric acid - HOBLys N -(4-hydroxybenzoyl)lysine - hpClPhe 4-(4-chlorophenyl)-2-amino-butyric acid - Hse homoserine, 2-amino-4-hydroxybutanoic acid - ICapLys N -(6-isopropylaminocaproyl)lysine - ILys N -isopropyllysine - Ind indoline-2-carboxylic acid - INicLys N -isonicotinoyllysine - IOrn N -isopropylornithine - Me₃Arg N^G,N^G,N^G-trimethylarginine - Me₂Lys N ,N -dimethyllysine - MNal 3-[(6-methyl)-2-naphtyl]alanine - MNicLys N -(6-methylpicolinoyl)lysine - MPicLys N -(6-methylpicolinoyl)lysine - MOB 4-methoxybenzoyl - MpClPhe N-methyl-3-(4-chlorphenyl)lysine - MPZGlu glutamic acid,-4-methylpiperazine - Nal 3-(2-naphthyl)alanine - Nap 2-naphthoic acid - NicLys N -nicotinoyllysine - NO₂B 4-nitrobenzoyl - NO₂Phe 3-(4-nitrophenyl)alanine - oClPhe 3-(2-chlorphenyl)alanine - Opt O-phenyl-tyrosine - Pal 3-(3-pyridyl)alanine - 2Pal 3-(2-pyridyl)alanine - 2PALys N -(3-pyridylacetyl)lysine - pCapLys N -(6-picolinoylaminocaproyl)lysine - pClPhe 3-(4-chlorophenyl)alanine - pFPhe 3-(4-fluorophenyl)-alanine - Pic picolinic acid - PicLys N -picolinoyllysine - Pip piperidine-2-car-boxylic acid - PmcLys N -(4-pyrimidylcarbonyl)lysine - Ptf 3-(4-trifluromethyl phenyl)alanine - Pz pyrazinecarboxylic acid - PzAla 3-pyrazinylalanine - PzAPhe 3-(4-pyrazinylcarbonylaminophenyl)alanine - Qal 3-(3-quinolyl)alanine - Qnd-Lys N -quinaldoyllysine - Qui 3-quinolinecarboxylic acid - Qux 2-quinoxalinecarboxylic acid - Tic 1,2,3,4-tetrahydroisoquinoline-3-carboxylic acid - TinGly 2-thienylglycine - tNACAla trans-3-(4-nicotinoylaminocyclohexyl)-alanine - tPACAla trans-3-(4-picolinoylaminocyclohexyl)alanine     

Terrestrial bird community patterns on the coralline islands of the Dahlak Archipelago, Red Sea, Eritrea

Aim This study aims to explain the patterns of species richness and nestedness of a terrestrial bird community in a poorly studied region. Location Twenty‐six islands in the Dahlak Archipelago, Southern Red Sea, Eritrea. Methods The islands and five mainland areas were censused in summer 1999 and winter 2001. To study the importance of island size, isolation from the mainland and inter‐island distance, I used constrained null models for the nestedness temperature calculator and a cluster analysis. Results Species richness depended on island area and isolation from the mainland. Nestedness was detected, even when passive sampling was accounted for. The nested rank of islands was correlated with area and species richness, but not with isolation. Idiosyncrasies appeared among species‐poor and species‐rich islands, and among common and rare species. Cluster analysis showed differences among species‐rich islands, close similarity among species‐poor and idiosyncratic islands, and that the compositional similarity among islands decreased with increasing inter‐island distance. Thus, faunas of species‐poor, smaller islands were more likely to be subsets of faunas of species‐rich, larger islands if the distance between the islands was short. Main conclusions Species richness and nestedness were related to island area, and nestedness also to inter‐island distances but not to isolation from the mainland. Thus, nestedness and species richness are not affected in the same way by area and distance. Moreover, idiosyncrasies may have been the outcome of species distributions among islands being influenced also by non‐nested distributions of habitats, inter–specific interactions, and differences in species distributions across the mainland. Idiosyncrasies in nested patterns may be as important as the nested pattern itself for conservation – and conservation strategies based on nestedness and strong area effects (e.g. protection of only larger islands) may fail to preserve idiosyncratic species/habitats.     

Low‐dose linearity: The rule or the exception?

In 1976, Crump, Hoel, Langley, and Peto described how almost any dose‐response relationship for carcinogens becomes linear at low doses when background cancers are taken into account. This has been used, by the U.S. Environmental Protection Agency, USEPA, as partial justification for a regulatory posture that assumes low‐dose linearity, as is illustrated by a discussion of regulation of benzene as a carcinogen. The argument depends critically on the assumption that the pollutant and the background proceed by the same biological mechanism. In this paper we show that the same argument applies to noncancer end points also. We discuss the application to a number of situations: reduction in lung function and consequent increase in death rate due to (particulate) air pollution; reduction in IQ and hence (in extreme cases) mental deficiency due to radiation in utero; reduction of sperm count and hence increase in male infertility due to DBCP exposure. We conclude that, although the biological basis for the health effect response is different, in each case low‐dose linearity might arise from the same mathematical effect discussed by Crump et al. (1976). We then examine other situations and toxic end points where low‐dose linearity might apply by the same argument. We urge that biologists and chemists should concentrate efforts on comparing the biological and pharmacokinetic processes that apply to the pollutant and the background. Finally, we discuss some public policy implications of the possibility that low dose linearity may be the rule rather than the exception for environmental exposures.     

Steady-state kinetics of the overall oxidative phosphorylation reaction in heart mitochondria. Determination of the coupling relationships between the respiratory reactions and miscellaneous observations concerning rate-limiting steps

The linear sequence of steps involved in the oxidation of extramitochondrial succinate by O₂ in bovine heart mitochondria was examined by a steady-state kinetic method to determine whether or not freely diffusible intermediates occur between the various inhibitor-sensitive steps. The kinetic method is based on the facts (1) that if two inhibitor-sensitive steps within a sequence are linked by a freely diffusible intermediate, inhibition of one will make the other less rate limiting in the overall reaction and thus will increase the amount of inhibitor of the other step required for half-maximal inhibition of the overall reaction, and (2) that if the two steps are not linked in this manner, inhibition of one will make the other more rate limiting and thus will decrease the amount of inhibitor of the other required for half-maximal inhibition. These two types of coupling relationships between steps were designated as sequential and fixed, respectively. The results indicate the existence of freely diffusible intermediates (sequential coupling relationships) between the succinate transport and succinate dehydrogenase reactions, between the succinate dehydrogenase and cytochromebc ₁ reactions, and between the cytochromesbc ₁ andaa ₃ reactions. Uncoupling respiration from phosphorylation results in the coupling relationship between thebc ₁ andaa ₃ reactions becoming partially fixed. This change is accompanied by marked decreases in the degrees to which thebc ₁ andaa ₃ reactions limit the overall reaction and appears to account for the large uncoupler-induced releases of inhibition at the levels of thebc ₁ andaa ₃ reactions observed previously by others. It is suggested that cytochromec is the freely diffusible intermediate between thebc ₁ andaa ₃ reactions and that the uncoupler-induced changes occur as a result of formation of functional and highly efficient supercomplexes between cytochromec and the cytochromesbc ₁ andaa ₃ complexes.