浙江秀山岛湿地生态系统初探

秀山岛位于东海舟山渔场海域,岛上有大片的湿地资源分布,其滨海部分与舟山渔场的生物资源特别是渔业生物资源密切联系,具有罕见的海岛特色。海岛的特殊地理位置为秀山岛湿地赋予了独特的生态特征。秀山岛湿地内动植物资源丰富,生物多样性高,共有植物种类300余种,栖息的鸟类共有26个科108种,包括国家一级保护动物东方自鹳（Ixobrychus minutus）。还有国家二级保护动物獐（Hydropotes inermis）等珍贵动物自然栖息。秀山岛湿地包括潮下带湿地（浅海湾）、潮间带湿地（泥滩、芦苇丛）、潮上带湿地（咸水沼泽、半咸水沼泽）、异化湿地（盐田、养殖池、稻田）等几个紧密联系的部分。具有多方面的生态功能。由于对湿地的生态功能重视不够,湿地生态系统破碎化严重。目前在秀山岛湿地已经建立了湿地自然保护区,湿地生态系统得到了较好的发展。     

基于生态足迹模型的延边林区可持续发展评价

生态足迹是评价可持续发展状况和能力的重要指标之一。本文以统计年鉴和林业年鉴为主要数据来源,对延边林区1996~2002年的生态足迹进行了计算和分析。结果表明,该区人均生态足迹逐年下降,人均生态承载力波动较小,而人均生态盈余逐年增长。人均万元GDP生态足迹逐年递减,同西部地区相当,而明显高于东部。人均林地生态足迹变化平稳,天然林保护工程实施前后林地生产足迹和林地出口足迹的平均值分别降低了0.341和0.327 hm2.人-1,降幅分别为46.32%和54.94%。延边区域和林业的发展是可持续的,天然林保护工程的实施有助于增强其可持续发展能力,但同林业发达国家相比,仍有很大差距。依靠科技,提高单位面积林地产量和资源利用率,合理经营和管理森林生态系统是今后的工作重点。     

青藏高原东南部天然草地主要有毒植物调查研究

对青藏高原东南部的川西北天然草地主要有毒植物的种类、毒物成分和分布作了系统的调查与研究,首次报道了该区域天然草地有毒植物名录,统计出该区主要有毒植物226种,隶属于33科77属。有毒植物所含主要毒物成分可分为生物碱、苷类化合物、萜类化合物、苯酮类化合物、酚类及其衍生物和简单有机物等6大类。有毒植物在亚高山草甸草地中分布最多,有157种,其次是亚高山灌丛草地、高山草甸草地、高山灌丛草地和高寒沼泽化草甸草地。本调查研究为青藏高原东南部天然草地主要有毒植物的防除和开发利用奠定了基础。     

天然产物在新药开发中的应用--HMG-CoA还原酶抑制剂新药的发现对天然产物研究与开发的启示

自1973年发现第一个作用于HMG-CoA还原酶的化合物mevastatin以来,多个具有HMG-CoA还原酶抑制活性的抗高血脂新药被开发成功,并成为治疗高血脂症的首选药物。在此简单介绍该类新药的发现与开发过程,并就天然产物的研究与开发提出一点个人见解。     

互花米草入侵九段沙河口湿地对当地昆虫多样性的影响

为认识因互花米草(Spartinaalterniflora)入侵而给九段沙河口湿地昆虫多样性带来的影响,我们于2004年5月到2005年10月间用网捕和收割植株两种方法对3个典型植物群落中昆虫多样性作了连续调查。研究期间,共采集到昆虫11,300头。经鉴定为97个种,隶属于12目69科。互花米草群落中昆虫的物种数、个体数量以及Shannon-Wiener多样性指数均显著低于土著植物芦苇(Phragmitesaustralis)群落和海三棱藨草(Scirpusmariqueter)群落中的;而Simpson优势度指数较土著植物群落中高。聚类分析结果表明:芦苇与海三棱藨草群落中昆虫群落结构更为相似。互花米草的入侵将可能导致九段沙湿地昆虫多样性的降低和群落结构的改变。     

Deficiency in African plant distribution data – missing pieces of the puzzle

Biodiversity is spatially unevenly distributed and so is the information on its spatial patterns. This uneven distribution of information on species occurrences is an important impediment to the conservation of biodiversity. Based on 185 427 collection records of 5873 plant species in sub-Saharan Africa, we analyse the availability of distribution data suitable for the GIS-based mapping of plant diversity patterns at a one-degree resolution. Using the bioclimatic model GARP, distribution ranges for each species were modelled. In order to identify data-deficient areas, the documented and modelled diversity patterns were compared. Only for a few, well-known centres of plant diversity are there comparatively many data collection records available. For several of the areas with very few collection records, such as the Guinean montane forests, the north-western Congolian lowland forests, and the southern Albertine Rift montane forests, the model predicts a species richness much higher than currently documented. In many of the data deficient areas, difficult conditions for scientific research appear to have limited collection activities for decades. Only strategic field collections can fill these gaps. Another cause of data deficiency is that data collected and digitized do not match the quality requirements for GIS-based work at the super-regional scale. In particular, regional databases documenting partial ranges of species are rarely connected. One challenge for the Global Strategy for Plant Conservation is therefore to establish international collaborative structures and technical standards that will allow analysis of biogeographical patterns across political boundaries.  © 2006 The Linnean Society of London, Botanical Journal of the Linnean Society , 2006, 150 , 355–368.     

Dissolved humic substances – ecological driving forces from the individual to the ecosystem level?

1. This review focuses on direct and indirect interactions between dissolved humic substances (HS) and freshwater organisms and presents novel opinions and hypotheses on their ecological significance. Despite their abundance in freshwaters, the role of HS is still inadequately understood. These substances have been considered too large to be taken up by freshwater organisms. On the contrary, here we present evidence that dissolved HS are indeed taken up and interact directly and/or indirectly with freshwater organisms. 2. We show that dissolved HS exert a mild chemical stress upon aquatic organisms in many ways; they induce molecular chaperones (stress shock proteins), induce and modulate biotransformation enzymes and modulate (mainly inhibiting) the photosynthetic release of oxygen by freshwater plants. Furthermore, they produce an oxidative stress, which may lead to membrane oxidation. HS modulate the multixenobiotic resistance activity and probably other membrane‐bound pumps. This property may lead to the increased bioaccumulation of xenobiotic chemicals. Furthermore, they can modulate the numbers of offspring in a nematode and feminise fish and amphibians. The ecological consequences of this potential remain obscure at present. HS also have the potential to act as chemical attractants (as shown with a nematode). 3. In some macrophytes and algae we show that HS interfere with photosynthesis and growth. For instance, the presence of HS suppresses cyanobacteria more than eukaryotic algae. By applying a quantitative structure activity relationship approach, we show that quinones in the HS interfere with photosynthetic electron transport. We show that even Phragmites leachate can act as a kind of phytotoxin. HS also have the potential to suppress fungal growth, as shown with the water mould Saprolegnia parasitica and force the fungus to respond by spore production. 4. In very soft, humic freshwaters, such as the Rio Negro, Brazil, HS stimulate the uptake of essential ions, such as Na and Ca, at extremely low pH (3.5–4.0) and prevent the ionoregulatory disturbance induced by acid waters, thereby enabling fish to survive in these environments. 5. We discuss whether or not HS are directly utilised by aquatic microorganisms or via exoenzymes, which may be washed in from the terrestrial catchment. There is accumulating evidence that the quality of the HS controls microbial growth. In total, net‐heterotrophy may result from HS‐mediated suppression of primary production by the quinone structures and/or from HS‐mediated support of microbial growth. As there is also evidence that HS have the potential to support photoautotrophic growth and suppress microbial growth, the opposite community effect could result. Consequently, dissolved organic carbon (DOC) has to be chemically characterised, rather than simply measuring bulk DOC concentration. 6. In sum, dissolved HS interact with freshwater organisms in a variety of ways in unenriched humic lakes. In addition to the well known effects of HS on light regime, for example, and the direct and indirect supply with carbon (energy), other interactions may be much more subtle. For instance, HS may induce internal biochemical stress defence systems and have the potential to cause acclimatisation and even adaptation. We are just at the beginning of understanding these interactions between dissolved HS and freshwater organisms.     

Plantago lanceolata and Plantago rugelii Extracts are Toxic to Meloidogyne incognita but not to Certain Microbes

Extracts from the plants Plantago lanceolata and P. rugelii were evaluated for toxicity to the root-knot nematode Meloidogyne incognita, the beneficial microbes Enterobacter cloacae, Pseudomonas fluorescens and Trichoderma virens, and the plant-pathogenic fungi Fusarium oxysporum f. sp. gladioli, Phytophthora capsici, Pythium ultimum, and Rhizoctonia solani. Wild plants were collected, roots were excised from shoots, and the plant parts were dried and ground to a powder. One set of extracts (10% w/v) was prepared in water and another in methanol. Treatments included extract concentrations of 25%, 50%, 75% and 100%, and water controls. Meloidogyne incognita egg hatch was recorded after 7-day exposure to the treatments, and second-stage juvenile (J2) activity after 48 hours. All extracts were toxic to eggs and J2, with P. lanceolata shoot extract tending to have the most activity against M. incognita. Numbers of active J2 remained the same or decreased in a 24-hour water rinse following the 48-hour extract treatment, indicating that the extracts were lethal. When data from water- and methanol-extracted roots and shoots of both plant species were combined for analysis, J2 tended to be more sensitive than eggs to the toxic compounds at lower concentrations, while the higher concentrations (75% and 100%) were equally toxic to both life stages. The effective concentrations causing 50% reduction (EC₅₀) in egg hatch and in J2 viability were 44.4% and 43.7%, respectively. No extract was toxic to any of the bacteria or fungi in our assays.     

Evaluation of Food Additives and Low-toxicity Compounds for the Control of Bean Rust and Wheat Leaf Rust

The efficacy of low‐toxicity chemicals as possible alternatives to synthetic fungicides for the control of Uromyces appendiculatus and Puccinia triticina was evaluated. A preliminary selection of food additives was performed through in vitro and in vivo preliminary screenings. The ED₅₀ and minimum inhibition concentration (MIC) values showed that most of the food additives used in this study were more toxic to U. appendiculatus than to P. triticina. Acetic acid, potassium carbonate, sodium carbonate and sodium molybdate were the food additives that were more toxic to the urediniospores of P. triticina. Selected compounds and concentrations were tested on bean and wheat plants grown in pots under controlled conditions. Acetic acid, ammonium bicarbonate, potassium acetate, potassium benzoate, potassium bicarbonate, potassium carbonate, sodium acetate and sodium citrate at 0.03, 0.09, 0.03, 0.006, 0.012, 0.012, 0.03 and 0.03 m , respectively, significantly reduced the disease severity of U. appendiculatus without causing any injury to bean leaves. Ammonium bicarbonate, potassium bicarbonate, sodium bicarbonate and sodium citrate at 0.12, 0.03, 0.12 and 0.03 m , respectively, were the most effective in reducing the disease severity caused by P. triticina without causing any injury to wheat leaves.