甘肃白银地区生态区域分异及其恢复途径初步探讨

依据白银地区的水-热及土壤基质等自然环境状况及生态恢复需要,划分白银地区为冷温微润、冷温微干、微温微干、微温干旱、微温极干5个生物气候及生态恢复区、10个恢复亚区.根据各恢复区的基本特征、退化现状和退化主导因子的分异,探讨了区域生态恢复途径.     

苍梧县公益林经营管理现状与可持续经营探讨

调查分析广西苍梧县生态公益林建设的现状和存在的问题，主要有树种结构欠合理、权益关系不清、经营者的意愿未得到尊重、相关法规不完善等，对该县生态公益林可持续发展对策进行探讨。     

An investigation of uncertainty in field habitat mapping and the implications for detecting land cover change

Land cover data for landscape ecological studies are frequently obtained by field survey. In the United Kingdom, temporally separated field surveys have been used to identify the locations and magnitudes of recent changes in land cover. However, such map data contain errors which may seriously hinder the identification of land cover change and the extent and locations of rare landscape features. This paper investigates the extent of the differences between two sets of maps derived from field surveys within the Northumberland National Park in 1991 and 1992. The method used in each survey was the Phase 1 approach of the Nature Conservancy Council of Great Britain. Differences between maps were greatest for the land cover types with the smallest areas. Overall spatial correspondence between maps was found to be only 44.4%. A maximum of 14.4% of the total area surveyed was found to have undergone genuine land cover change. The remaining discrepancies, equivalent to 41.2% of the total survey area, were attributed primarily to differences of land cover interpretation between surveyors (classification error). Differences in boundary locations (positional error) were also noted, but were found to be a relatively minor source of error. The implications for the detection of land cover change and habitat mapping are discussed.     

野生朱红硫磺菌驯化栽培研究

营养试验、菌丝体培养和出菇温度试验、培养基酸碱度试验、出菇条件试验结果表明：朱红硫磺菌菌丝体适宜生长的温度范围为15-32℃，最适温度范围为22～28℃；子实体发生的最适温度为16～25℃，气温低于16℃，子实体色泽为淡橙色，16℃以上，子实体呈鲜橙红色；培养料适宜营养C／N为20-26／1；朱红硫磺菌菌丝体适宜酸碱度范围为pH3．0～8．0，最适酸碱度为pH4．0—6．5；朱红硫磺菌的产量与光照条件无关，但光照强度影响子实体的发生时间和色泽；朱红硫磺菌栽培原料广泛，凡栽培木腐菌的培养料均可用于栽培朱红硫磺菌。     

吉林省荒地资源生态适宜性评价

本文从吉林省荒地资源的实际出发 ,在荒地资源生态适宜性评价基本理论的指导下 ,采用地理信息系统方法 ,对吉林省荒地资源进行了生态适宜性评价。通过空间数据和属性数据的融合、分析、处理 ,可以直观获得荒地资源的生态适宜度等级 ,从而提高评价效率 ,为荒地资源的合理开发利用提供科学依据。     

陕甘宁老区建立生态特区的必要性分析

本文从历史与现状方面分析了陕甘宁老区加强生态环境建设的必要性。阐述了陕甘宁老区历史上范围的变化及其对中国革命和经济建设的贡献。从多方面分析了它的自然条件 ,揭示了其自然环境的脆弱性。说明了该区经济建设取得的成就和存在的问题 ,揭示了其贫困落后的社会经济状况。提出了在该区建立生态特区以促进其生态环境建设的观点。     

乌梁素海生态恢复机理与工程技术的研究

在我国干旱区典型草型湖泊—乌梁素海设立试验基地 ,进行生态恢复工程试验研究。研究表明 :乌梁素海受富营养化影响 ,正在向芦苇沼泽—碱蓬盐化草甸—白刺荒漠方向演化。生态恢复机理是 :( 1 )减少大型水生植物有机氮、磷向底质的沉降 ,削弱内源性营养物负荷的积累与储备 ;( 2 )减少大型水生植物死亡后矿化成氨态氮 ;( 3)控制底质中有机氮向水体释放生成氨态氮。采用机械化方式收割大型水生植物转移营养盐 ,抑制生物促淤效应以及对芦苇区进行园田化生态管理是乌梁素海生态恢复的关键技术 ,也是乌梁素海环境与资源持续发展的核心问题     

我国防沙治沙科研的突破口初探-以河西走廊沙区为例

河西走廊的防沙治沙科研在我国广大沙区具有代表性。河西走廊防沙治沙科研存在的主要问题是 :⑴宏观战略研究薄弱 ,研究缺乏系统性。主要表现在 :治沙措施散件得不到优化组合 ,其功能得不到充分发挥 ;研究客体之间互相割裂 ,缺乏从总体上控制沙漠化的研究 ;农业开发与生态资源保护的结合点问题没有解决 ;研究课题重复。⑵散件成果多属定性结论 ,缺乏操作性。运用系统科学的思想方法是治沙科技发展的突破口 :只有运用系统科学的思想方法才能科学处理生态资源保护、生态环境建设和资源开发利用三方面的关系 ,才能实现各种防沙治沙措施的优化配置 ,才能实现治理结果的持续稳定。运用现代数学方法建立沙区生态环境综合治理数学模型才能科学处理多系统的复杂关系。现代数学方法是系统科学的主要方法。运用系统科学的思想方法和现代数学方法是治沙科技发展必须达到的 ,是治沙科技发展的突破口。     

塔里木河流域生态环境恶化的水文效应

塔里木河是我国最大的内陆河。 4条源流出山口多年平均天然径流量 2 2 4 .9× 10 8m3 (195 7～ 2 0 0 1年 )。在全球变暖的大背景下 ,塔里木河流域山区气候出现变暖增湿的趋势 ,2 0世纪 90年代径流量达 2 4 1.9× 10 8m3 ,增幅 7.6 %。由于源流区人类开发利用水资源的影响 ,使得补给塔里木河干流的水量不断减少 ,水文条件改变 ,造成干流上、中游段耗水严重 ,导致下游生态与环境急剧退化。自 2 0 0 0年以来 ,实施的从开都河—博斯腾湖向下游绿色走廊应急输水 ,已使下游生态环境开始恢复生机。     

Biological and Physical Constraints on Maize Production in the Humid Forest and Western Highlands of Cameroon

The aim was to identify biological and physical factors responsible for reducing maize yield in Cameroon. Two surveys were conducted in 137 fields in two agroecological zones in 1995–1997. In the Humid Forest (HF), Bipolaris maydis, Stenocarpella macrospora, Puccinia polysora, Rhizoctonia solani and soil fertility were factors that reduced maize production in 1995 and 1996. In the Western Highlands (WHL), Cercospora zeae-maydis, and the interaction between soil fertility and maize variety were the most important constraints to maize production in 1996. In 1997, C. zeae-maydis, S. macrospora, physiological spot and stem borer damage (Busseola fusca) were negatively related to ear weight. The combination of these biological factors (diseases and insects), and the physical parameter of soil fertility were responsible for reducing maize yield in these selected benchmarks of Cameroon. Maximum potential yield reductions were estimated at 68% due to B. maydis and 46% due to S. macrospora, respectively, in the HF in 1995. In 1996, maximum potential yield reductions in the HF were estimated at 34%, 41% and 30% due to S. macrospora, P. polysora and R. solani, respectively. In the WHL, C. zeae-maydis had the potential to cause a yield reduction of 79% in 1996. In the WHL in 1997, the interaction between C. zeae-maydis and B. fusca, stem diseases and the physiological spot caused potential reductions of 52%, 34% and 39%, respectively.