气候变化与自然灾害

气候变化与自然灾害是当今科学研究的两大热点，两者之间在一定程度上具有相关性，但目前要确切地定量计算气候变化对自然灾害的强度和出现频率的影响还很困难。本文在分析气候变化与自然灾害关系的基础上，研究了气候变化对我国自然灾害的影响。研究结果显示：１．在千年尺度上，长江流域的大旱和气候变冷成正相关，而长江流域的大涝以及黄河流域的大旱和大涝与气候冷暖过渡期成正相关；２．在百年尽度上，近１０４２年来，共出现２８１次全国性大旱和大涝，平均每百年出现２７次，在地域分布上以南涝北旱为主；３．就百年至千年尺度的气候变化对自然灾害的影响而言，气候冷冷组合期（１３０１～１９００）易发生全国性大涝，而冷暖组合期（９５０～１３００年，１９０１～１９９１年）易发生全国性大旱。总的来说，冷冷组合期的大旱大涝发生频率明显大于暖期，但不同地区有差异；４．在其它影响方面，台风、地震与海啸灾害在冷暖组合期（２０世纪）均有比冷冷组合期（１４和１９世纪）多的趋势。因此，气候变暖将使防灾任务更加艰巨。     

全球增暖对自然灾害的可能影响

近年来，气候对环境的影响已受到全球科学家越来越多的重视，中国是一个有１１亿人口的大国，生态环境较为脆弱，全球变暖将严重影响我国社会与经济生活的各个方面。本文初步研究了全球变暖对自然灾害的可能影响。结果表明，在大气ＣＯ２含量加倍的情况下，全球变暖将可能导致暴雨频度和洪涝风险增加，西北干旱趋势仍将延续；森林火灾、台风、滑坡与泥石泫灾害可能加剧；农林病虫害危害增加，范围扩大。同时，全球变暖导致的海平面上     

四川彭州铜尾矿库植被特征分析与植物群落演替初探

本文分析了四川彭州铜矿尾矿库的植被特征、群落特征与演替。在该尾矿库上自然定居的高等植物共91种，隶属38科79属，以菊科（Compositae）和禾本科（Gramineae）植物为主。形成6种相对稳定的群落类型；在2003年弃耕后形成的地段分布有史蒿＋小飞蓬群落（Artemisia argyi＋Conyza conadensis Comm．）、艾蒿＋打破碗花花群落（Artemisia argyi＋Anemone hupehensis Comm．）、艾蒿群落（Artemisia argyi Comm．）和白车轴苹群落（Trifolium repens Comm．）；在经过30～40年自然演替的地段分布有芭茅＋羊耳菊群落（Miscanthus sinensis＋Inula cappa Comm．）和羊耳菊＋千里光＋密蒙花群落（Inula cappa＋Senecio scandens＋Buddleja officinalis Comm．）；在近十年内新形成的地段现主要覆盖地衣和葫芦藓（Funaria hygrometrica）。通过对群落结构和不同地段植被特征的对比，对本铜尾矿库的演替现状和规律进行了分析，井讨论了人为影响对演替进程的影响，提出了人工恢复措施的建议。     

乌鲁木齐市东南部荒山植被类型及其特征

采用典型样地法对乌鲁木齐市东部荒山植被进行了调查.依据中国植被和新疆植被分类的原则,遵循群落学-生态学原则,用重要值优势度分类方法确定各层片优势种.将此地区自然植被划分为5个植被型,8个植被亚型、20个群系和24个群丛.并对植被型的基本特征进行了分析和描述.     

罗布泊野骆驼自然保护区的建设及生物多样性保护

新疆罗布泊野骆驼自然保护区位于我国西部极旱荒漠带 ,以保护世界濒危物种———野双峰驼为主要对象 ,同时也保护当地特有的地貌、盐泉、丝绸之路遗迹及其他珍稀动植物物种 ,面积 7 8× 10 4km2 。该保护区在世界生物多样性保护中有重大作用。由于周边地区经济的发展 ,对该保护区的影响逐渐扩大 ,威胁到野生动植物的生存安全 ,急需加强宣传、建卡、检查、巡护等保护管理措施 ,同时需要提高周边贫困社区人民生活水平 ,强化管制非法采矿业     

Change in vegetation cover in East Timor, 1989–1999

Forest resources play a key role and provide many basic needs to communities in developing economies. To assess the patterns of vegetation cover change, as a corollary of resource utilization, satellite imagery, ground truth data, and image processing techniques can be useful. This article is concerned with identifying change in major vegetation types in East Timor between 1989 and 1999, using Landsat Thematic Mapper data. The results highlight a significant level of deforestation and decline in foliage cover. All major vegetation cover types declined from 1989 to 1999, and there was a sizeable increase in degraded woodlands. This decline has had considerable impact on the livelihoods of rural and urban communities. Causes for these changes include: economic exploitation of abundant resources; and implications of transmigration policies implemented during Indonesian rule, resulting in increased competition for land and woodland resources. As the new nation of Timor‐Leste establishes itself, it must consider its current stock and distribution of natural capital to ensure that development efforts are geared towards sustainable outcomes. Without the knowledge of historical patterns of resource consumption, development efforts may, unwittingly, lead to continuing decline in forest resources.     

给水管道振动信号的小波分析及消振研究

某核发电厂部分蒸汽和给水管道振动情况非常严重 ,以致影响到正常的安全生产。笔者从给水管道的测振出发 ,并利用 3层Daubechise对振动信号进行了小波消噪、滤波、重构处理 ,以找到影响管系振动的激励源的主要频域成分。进而利用比较成熟的结构分析软件ANSYS对管系进行了模态分析 ,得到系统的低阶固有频率和振型。根据管道振动的原因 ,在不改变管系主要特征的基础上 ,给出了简单易行的消振措施 ,实际运行情况表明消振方法效果良好。     

黄荆自然保护区植物区系的初步研究

黄荆自然保护区地处四川盆地与云贵高原的过渡地带,地带性植被为亚热带偏湿性常绿阔叶林,有种子植物165科745属1521种,其中裸子植物9科19属24种,被子植物156科726属1497种.该区特殊的自然条件和复杂的地质构造,使其成为多种植物地理成分的汇集地,并成为我国乃至全世界亚热带(同纬度)地区保存较好的常绿阔叶林植被群落,具有极高的研究价值和生态价值.根据近年来的科学考察,认为黄荆自然保护区植物区系的种类丰富、珍稀特有植物较多、起源古老、区系成分复杂,显示出多方植物交汇的特点.     

自然生态小区建设指导原则及其建设内容探讨--以筠连县大雪山自然生态小区为例

自然生态小区是构建优美生态环境区域的生态“细胞工程”。它根据当地的自然状况和社会经济状况,以较小的经济和社会代价实现一定区域生态环境优美、生态文明有序、生态系统良性循环的社会经济生态综合体。由于自然生态小区的建设是新兴事物,其建设途径还有很多问题值得探讨。在自然生态小区建设投资方面,应当明确生态环境建设投资和生产赢利建设投资,对于前者应当以政府和政策性投资为主,而后者应当是在政策法规规范下的企业投资为主;在发展模式方面,应当促进环境友好的规模化高效益产业,包括有机绿色产业、地方特色产业、民族文化产业等;在效益分配方面,必须要充分考虑整个社区居民资源共享和利益合理分配,实现整个社区生态文明建设和经济发展目标的一致。     

Quantifying and Evaluating Ecosystem Health: A Case Study from Moreton Bay, Australia

As part of the program monitoring the ecosystem health of Moreton Bay, Queensland, Australia, we developed a means for assessing ecosystem health that allows quantitative evaluation and spatial representations of the assessments. The management objectives for achieving ecosystem health were grouped into ecosystem objectives, water quality objectives, and human health objectives. For the first two groups, aspects of the ecosystem (e.g., trophic status) were identified, and an indicator was chosen for each aspect. Reference values for each indicator were derived from management objectives and compared with the mapped survey values. Subregions for which the indicator statistic was equal to or better than the assigned reference value are referred to as “compliant zones.” High-resolution surface maps were created from spatial predictions on a fine hexagonal grid for each of the indicators. Eight reporting subregions were established based on the depth and predicted residence times of the water. Within each reporting subregion, the proportion that was compliant was calculated. These results then were averaged to create an integrated ecosystem health index. The ratings by a team of ecosystem experts and the calculated ecosystem health indices had good correspondence, providing assurance that the approach was internally consistent, and that the management objectives covered the relevant biologic issues for the region. This method of calculating and mapping ecosystem health, relating it directly to management objectives, may have widespread applicability for ecosystem assessment.