Patterns of resource partitioning by nesting herons and ibis: How are odonata exploited?

Herons and ibis are colonially nesting waders which, owing to their number, mobility and trophic role as top predators, play a key role in aquatic ecosystems. They are also good biological models to investigate interspecific competition between sympatric species and predation; two processes which structure ecological communities. Odonata are also numerous, diverse, mobile and can play an important role in aquatic ecosystems by serving as prey for herons and ibis. A relationship between prey size and bird predator has been observed in Numidia wetlands (NE Algeria) after analyzing food boluses regurgitated by six species of birds (Purple Heron, Black-crowned Night Heron, Glossy Ibis, Little Egret, Squacco Heron and Cattle Egret) during the breeding period, which also shows a temporal gradient for the six species. Both the Levins index and preliminary multivariate analysis of the Odonata as prey fed to nestling herons and ibis, indicated a high degree of resource overlap. However, a distinction of prey based on taxonomy (suborder and family) and developmental stage (larvae or adults) reveals a clear size dichotomy with large-sized predators (Purple Heron, Black-crowned Night Heron and Glossy Ibis) preying on large preys like Aeshnids and Libellulids and small-sized predators feeding mainly on small prey like Zygoptera. Overall, the resource utilization suggests a pattern of resource segregation by coexisting nesting herons and ibis based on the timing of reproduction, prey types, prey size and foraging microhabitats.     

Genotoxic evaluation in two amphibian species from Brazilian subtropical wetlands

Biomarkers analysis serves as an early warning system for the presence of pollutants because their responses appear before irreversible damage to the ecosystem takes place. The genotoxic effects of pollutants may occur at cellular pollutant concentrations that are well below levels that would cause gross cytotoxicity, making this a useful tool to detect early effects of toxic environmental agents. Combining the importance of Brazilian wetlands to the conservation of amphibian biodiversity with the potential negative impacts of irrigated rice fields in the surrounding areas, the aim of the present study was to evaluate genotoxic damage in two amphibian species, Pseudis minuta, and Leptodactylus gr latrans, from the southern Brazilian wetlands. Adult specimens from both Anuran species were captured from preserved (Taim Ecological Station = TAIM) and non-preserved (Senandes) wetlands. Nuclear abnormalities were quantified in erythrocytes, and the results were compared using the Mann–Whitney U test. There was a higher incidence of micronucleated erythrocytes in P. minuta, and of notched nuclei in L. gr latrans that were collected in TAIM when compared to those that were collected in Senandes, despite the fact that TAIM is a conservation unit. These findings indicate that Anurans are coping with genotoxic substances in their habitats, and underscore the need to implement monitoring programs in TAIM to determine which compounds or mixtures might be causing cell damage and to investigate the effects of such compounds on other anuran species and animal groups.     

Satellite remote sensing of wetlands

To conserve and manage wetland resources, it is important to inventoryand monitor wetlands and their adjacent uplands. Satellite remote sensing hasseveral advantages for monitoring wetland resources, especially for largegeographic areas. This review summarizes the literature on satellite remotesensing of wetlands, including what classification techniques were mostsuccessful in identifying wetlands and separating them from other land covertypes. All types of wetlands have been studied with satellite remote sensing.Landsat MSS, Landsat TM, and SPOT are the major satellite systems that have beenused to study wetlands; other systems are NOAA AVHRR, IRS-1B LISS-II and radarsystems, including JERS-1, ERS-1 and RADARSAT. Early work with satellite imageryused visual interpretation for classification. The most commonly used computerclassification method to map wetlands is unsupervised classification orclustering. Maximum likelihood is the most common supervised classificationmethod. Wetland classification is difficult because of spectral confusion withother landcover classes and among different types of wetlands. However,multi-temporal data usually improves the classification of wetlands, as doesancillary data such as soil data, elevation or topography data. Classifiedsatellite imagery and maps derived from aerial photography have been comparedwith the conclusion that they offer different but complimentary information.Change detection studies have taken advantage of the repeat coverage andarchival data available with satellite remote sensing. Detailed wetland maps canbe updated using satellite imagery. Given the spatial resolution of satelliteremote sensing systems, fuzzy classification, subpixel classification, spectralmixture analysis, and mixtures estimation may provide more detailed informationon wetlands. A layered, hybrid or rule-based approach may give better resultsthan more traditional methods. The combination of radar and optical data providethe most promise for improving wetland classification.     

State and management of wetlands in Bangladesh

Wetlands are a vital link between land and water in Bangladesh. A majority of the people of Bangladesh are critically dependent on wetlands. In this paper, the values of wetlands, causes and effects of wetlands degradation, as well as the present wetlands management approach, are analyzed and recommendations for wetlands management are suggested based on participatory rural appraisal (PRA), field visit, personal experience, and existing literature and information. Wetlands play a crucial role in maintaining the ecological balance of ecosystems, but wetlands habitat of Bangladesh is under constant threat due to increase of population, intensive agriculture, overfishing, siltation, pollution, ill-planned infrastructures, lack of institutional coordination, lack of awareness, etc. As a result biodiversity is reducing, many species of flora and fauna are threatened, wetlands-based ecosystem is degenerating, and the living conditions of local people are deteriorating as livelihoods, socioeconomic institutions, and cultural values are affected. Wetlands management is not addressed separately in water management activities of Bangladesh. In order to balance human needs and wetlands conservation, a mainly community-based wetlands management approach has been taken in Bangladesh, but this is not enough to prevent the degradation of wetlands. Therefore, Bangladesh now needs a comprehensive strategy combining political, economic, social, and technological approaches to stop further degradation of wetlands. Therefore, wetlands management should be incorporated into a system of integrated land and water use and, indeed, into the socioeconomic system of the country. Policies, strategies, and management plans for sustainable use and conservation of wetlands of Bangladesh must be based on solid knowledge and understanding of their ecological and socioeconomic functions and processes.     

高原湿地沼泽化草甸土壤真菌与理化性质的关系

以高原湿地纳帕海沼泽化草甸为研究对象, 采用稀释培养结合形态鉴定比较分析0—20 cm、20—40 cm土层的土壤真菌多样性及群落结构组成, 以及土壤理化性质对土壤真菌多样性及群落结构组成的影响。结果表明: 0—20 cm和20—40 cm土层中的真菌数量、Shannon-Wiener多样性指数(H')、均匀度指数(JSW)和丰富度指数(DMA)均表现为0—20 cm土层> 20—40 cm土层; 分别分离得到土壤真菌12属和10属, 其中木霉属、青霉属、腐霉属、曲霉属同为沼泽化草甸两个土层的优势类群, 表现出较高的相似性, 同时20—40 cm未发现枝孢菌属和壳囊孢属, 又表现出一定的差异性。经RDA冗余分析, 土壤有机质、全氮、速效钾、速效磷、pH、容重和自然含水率可能是影响沼泽化草甸土壤真菌群落结构组成的主要因子。     

A new tool for the assessment of severe anthropogenic eutrophication in small shallow water bodies

Unlike in deep stratified lakes, the assessment of eutrophication in shallow aquatic systems (i.e., wetlands, marshes, ponds) should be based on the interaction between water and sediment. The availability of P to primary producers is naturally higher in shallow systems, because the sediment plays an active part via adsorption, precipitation and release processes. Thus, many wetlands in protected areas are naturally eutrophic and have a high trophic status due to intrinsic features and thus, display a high concentration of total-P in the water without necessarily implying pollution or poor quality. We have provided a diagnostic tool based on the chemical equilibrium of dissolved reactive P (operationally-defined as o-P) between water and sediment that distinguish anthropogenic eutrophication from a background of natural eutrophy. When the P-binding capacity of the sediment becomes saturated, the o-P concentration increases in the water as long as both the biological uptake and the sediment adsorption are unable to cope with the rate of P-release from the sediment under a long-term P load (or severe anthropogenic eutrophication). In such conditions, we have found that the ratio of total-P/particulate-P exceeds 2.0 in the water, and have used this threshold to validate this tool in other sets of wetlands.     

On threats analysis approach applied to a Mediterranean remnant wetland: Is the assessment of human-induced threats related to different level of expertise of respondents?

Naming, listing and measuring human-induced threats in protected areas are crucial in conservation. Here, we defined a check-list of direct threats in a Mediterranean remnant wetland (central Italy), managed as nature reserve, grouping them according to a taxonomically-oriented nomenclature. We assessed three regime parameters (scope, severity, and magnitude) applying an experience-based method, then comparing the assessments obtained from two different level of expertise: a panel of independent people, upper level “university students” in an applied ecology class; and a panel of “experts” as nature reserve biologists and managers. Despite observing a significant correlation among values assigned from students and experts for each regime parameter, students underestimated the scope of feral dogs, the severity of fires and the magnitude of feral dogs and water stress. Considering only the magnitude values (sum of scope and severity), students assigned the higher values to alien species, antropophilous species, aircraft, and pollution, while the experts assigned the higher values to antropophilous species, aircraft, alien species, and water stress. In an order of priority, there was an agreement between students and experts with a coincidence for three threats out of four. We suppose that a panel of students with a short academic training could be useful to a get a first order of priority in regard to a set of local selected threats, with much similarity to the assessment obtained from a panel of experts. When threat metrics are difficult to compare, experience-based approach obtained from technicians trained ad hoc (“students”) could be useful to define priorities for management strategies in nature reserves, but data obtained should be examined critically. Indeed, students may assign higher scores to regime parameters of threats more readily identified and perceivable, underestimating the threats with an inconstant regime, localized in time and space, mobile, or cryptic. If experience-based methods are used to define scale of priorities, these issues need to be considered.     

Phenology and autumnal accumulation of N reserves in belowground organs of wetland helophytes Phragmites australis and Glyceria maxima affected by nutrient surplus

Two co-occurring dominant wetland helophytes and potential competitors, Phragmites australis and Glyceria maxima, were cultivated under N, P availabilities simulating the trophic status of wetlands with different fertility (oligo- and eutrophic). The long-term outdoor cultivation was performed with the goal to characterise the extent to which the nutrient enrichment affects plant growth, phenology, and particularly, the accumulation of N storage compounds in belowground organs of wetland rhizomatous plants prior to the onset of winter dormancy. In the present study, both species responded similarly to nutrient surplus. The enhanced growth, delayed shoot senescence, and delayed retranslocation of N into belowground organs were found in both species in eutrophic treatment. Furthermore, N levels remaining in dry leaves were proportionally related to those in living ones, being significantly higher in eutrophic treatment. The efficiency of N retranslocation from senescing leaves varied around 60% in both species and treatments. The formation of N reserves was, however, not disrupted in either species. Although plants in eutrophic treatments accumulated N in their belowground organs significantly later in the season (in the September–December period), the amount of accumulated N was sufficient to reach high belowground N standing stock. Considering formation of N reserves, the differences in species response to treatments were negligible. Phragmites and Glyceria accumulated similar belowground N standing stock prior to the winter. Glyceria may, however, additionally profit from N standing stock of over-wintering green leaves and from the potential of growth and N assimilation during a mild winter period, which is not possible in fully dormant Phragmites.     

Achieving Restoration Success: Myths in Bottomland Hardwood Forests

Restoration of bottomland hardwood forests is the subject of considerable interest in the southern United States, but restoration success is elusive. Techniques for establishing bottomland tree species are well developed, yet problems have occurred in operational programs. Current plans for restoration on public and private land suggest that as many as 200,000 hectares could be restored in the Lower Mississippi Alluvial Valley alone. The ideal of ecological restoration is to reestablish a completely functioning ecosystem. Although some argue that afforestation is incomplete restoration, it is a necessary and costly first step but not an easy task. The 1992 Wetlands Reserve Program in Mississippi, which failed on 90% of the area, illustrates the difficulty of broadly applying our knowledge of afforestation. In our view, the focus for ecological restoration should be to restore functions, rather than specifying some ambiguous natural state based on reference stands or pre‐settlement forest conditions. We view restoration as one element in a continuum model of sustainable forest management, allowing us to prescribe restoration goals that incorporate landowner objectives. Enforcing the discipline of explicit objectives, with restoration expectations described in terms of predicted values of functions, causal mechanisms and temporal response trajectories, will hasten the development of meaningful criteria for restoration success. We present our observations about current efforts to restore bottomland hardwoods as nine myths, or statements of dubious origin, and at best partial truth.