甘肃河西保护地水热资源及其在栽培中的再利用研究

通过试验,用气候学原理,对保护地内水热资源的再利用作了系统分析,定量得出再利用资源值后,将其结果应用到瓜菜生产中,得出当地瓜菜生产的适播期和部分热量指标,为保护地设计提供了理论依据。     

浅析生物物种多样性与生态环境--辉河自然保护区鸟类物种多样性与生态环境

作为保护区管理局的科研人员，通过理论与实践结合，运用景观生态学原理，探讨了辉河自然保护区鸟类多样性。     

广西大瑶山自然保护区旅游资源开发与生态环境保护

介绍了大瑶山自然保护区的资源特色,分析了旅游开发中存在的制约因素和保护区开发旅游可能产生的环境影响,提出了旅游资源开发的重点和建议,以及生态环境保护的对策。     

Man in the Light of Current Ecological Problems

The interaction of man and nature is considered in terms of classical ecology, which is becoming a synthetic systemic science based on a set of other sciences. The divisions of modern human ecology that deal with different organizational levels of ecological systems have been developed to different degrees. Attention is given to the necessity of discrediting the mechanistic concept of opposition between man and nature and taking into account the specific ecological functions of man related to group adaptation (culture), as well as the global role of all living organisms in the maintenance of environmental conditions on Earth.     

Balancing Forest‐Regeneration Probabilities and Maintenance Costs in Dry Grasslands of High Conservation Priority

Abstract: Abandonment of agricultural land has resulted in forest regeneration in species‐rich dry grasslands across European mountain regions and threatens conservation efforts in this vegetation type. To support national conservation strategies, we used a site‐selection algorithm (MARXAN) to find optimum sets of floristic regions (reporting units) that contain grasslands of high conservation priority. We sought optimum sets that would accommodate 136 important dry‐grassland species and that would minimize forest regeneration and costs of management needed to forestall predicted forest regeneration. We did not consider other conservation elements of dry grasslands, such as animal species richness, cultural heritage, and changes due to climate change. Optimal sets that included 95–100% of the dry grassland species encompassed an average of 56–59 floristic regions (standard deviation, SD 5). This is about 15% of approximately 400 floristic regions that contain dry‐grassland sites and translates to 4800–5300 ha of dry grassland out of a total of approximately 23,000 ha for the entire study area. Projected costs to manage the grasslands in these optimum sets ranged from CHF (Swiss francs) 5.2 to 6.0 million/year. This is only 15–20% of the current total estimated cost of approximately CHF30–45 million/year required if all dry grasslands were to be protected. The grasslands of the optimal sets may be viewed as core sites in a national conservation strategy.     

Land Development in and around Protected Areas at the Wilderness Frontier

Protected areas’ chief conservation objectives are to include species within their boundaries and protect them from negative external pressures. Many protected areas are not achieving these goals, perhaps in part due to land development inside and outside protected areas. We conducted spatial analyses to evaluate the ability of Canadian protected areas to mitigate the effects of nearby land development. We investigated correlations of national patterns of land development in and around protected areas and then examined national patterns of roads, urban area, and croplands in protected areas. We calculated the amount of developed land in protected areas and within 25–100 km of protected‐area borders, the density of roads, and extent of urban and cropland area in protected areas. We constructed logistic‐regression models to test whether development in a protected area was associated with landscape and protected‐area characteristics. Land development was far less extensive inside than outside protected areas. However, several protected areas, particularly small southern areas near small urban centers had substantial development inside their boundaries, and nearly half of protected areas had roads. The cumulative extent of development within 50 km of protected areas was the best predictor of the probability of land development in protected areas. Canadian First Nations, industries, government, and nongovernmental organizations are currently planning an unprecedented number of new protected areas. Careful management of areas beyond protected‐area boundaries may prove critical to meeting their long‐term conservation objectives. Desarrollo de Tierras Dentro y Alrededor de Áreas Protegidas en la Frontera Silvestre     

Influence of Representation Targets on the Total Area of Conservation-Area Networks

Abstract:  Systematic conservation planning typically requires specification of quantitative representation targets for biodiversity surrogates such as species, vegetation types, and environmental parameters. Targets are usually specified either as the minimum total area in a conservation-area network in which a surrogate must be present or as the proportion of a surrogate's existing spatial distribution required to be in the network. Because the biological basis for setting targets is often unclear, a better understanding of how targets affect selection of conservation areas is needed. We studied how the total area of conservation-area networks depends on percentage targets ranging from 5% to 95%. We analyzed 12 data sets of different surrogate distributions from 5 regions: Korea, Mexico, Québec, Queensland, and West Virginia. To assess the effect of spatial resolution on the target-area relationship, we also analyzed each data set at 7 spatial resolutions ranging from 0.01°× 0.01° to 0.10°× 0.10°. Most of the data sets showed a linear relationship between representation targets and total area of conservation-area networks that was invariant across changes in spatial resolution. The slope of this relationship indicated how total area increased with target level, and our results suggest that greater surrogate representation requires significantly more area. One data set exhibited a highly nonlinear relationship. The results for this data set suggest a new method for setting targets on the basis of the functional form of target-area relationships. In particular, the method shows how the target-area relationship can provide a rationale for setting targets solely on the basis of distributional information about surrogates.     

扎龙自然保护区游客生态旅游行为调查分析

通过对扎龙自然保护区游客的问卷调查,分析了游客的生态旅游行为特征,进而对扎龙自然保护区生态旅游市场营销策略提出了相应的建议。     

考虑期权采购的应急物资多种供应方式协调优化模型

突发事件的不确定性为灾后应急物资供应带来巨大挑战，而灾前政府难以控制相关应急物资的储备量及成本。实物储备、期权采购和市场化采购3种应急物资供应方式在灾前灾后应急物资保障具备各自的优势和弊端。仅靠单种物资供应方式难以权衡当前应急物资保障对经济性和时效性的要求，因此，需要将3种物资供应方式进行协调优化。对比3种供应方式在成本与效率方面的差异，利用期权采购弥补其他方式在成本和时效方面的不足，将3种物资采购方式协调整合。以政府和供应商双方签订期权契约为前提建立多种采购方式协调优化模型，通过优化算法求解模型。最后通过算例分析验证得出结论。研究结果表明:存在基于期权采购的多种采购方式并存的应急物资保障机制，可使应急物资供应的成本和效率得以权衡。     

Factors influencing incidental representation of previously unknown conservation features in marine protected areas

Spatially explicit information on species distributions for conservation planning is invariably incomplete; therefore, the use of surrogates is required to represent broad‐scale patterns of biodiversity. Despite significant interest in the effectiveness of surrogates for predicting spatial distributions of biodiversity, few researchers have explored questions involving the ability of surrogates to incidentally represent unknown features of conservation interest. We used the Great Barrier Reef marine reserve network to examine factors affecting incidental representation of conservation features that were unknown at the time the reserve network was established. We used spatially explicit information on the distribution of 39 seabed habitats and biological assemblages and the conservation planning software Marxan to examine how incidental representation was affected by the spatial characteristics of the features; the conservation objectives (the minimum proportion of each feature included in no‐take areas); the spatial configuration of no‐take areas; and the opportunity cost of conservation. Cost was closely and inversely correlated to incidental representation. However, incidental representation was achieved, even in a region with only coarse‐scale environmental data, by adopting a precautionary approach that explicitly considered the potential for unknown features. Our results indicate that incidental representation is enhanced by partitioning selection units along biophysical gradients to account for unknown within‐feature variability and ensuring that no‐take areas are well distributed throughout the region; by setting high conservation objectives that (in this case >33%) maximize the chances of capturing unknown features incidentally; and by carefully considering the designation of cost to planning units when using decision‐support tools for reserve design. The lessons learned from incidental representation in the Great Barrier Reef have implications for conservation planning in other regions, particularly those that lack detailed environmental and ecological data.