951 resultados para 16 km ENE Cape Roberts
Resumo:
无根萍属(Wolffia )隶属于浮萍科天南星目,是世界上最小的被子植物。该属植物繁殖速度快;易于培养;结构简单,只具有一个雄蕊和一个雌蕊;自然状态下通常为克隆繁殖,遗传结构高度一致,具备特定研究目的模式植物的特点,正在或已经成为一些实验室研究光合作用、生物反应器、毒理学、生态修复和环境监测等的重要模式生物材料;同时还被作为建造航天生活仓和地外生命支撑系统的首选植物。该属植物蛋白含量高且氨基酸组分平衡,营养价值可与大豆相媲美。但该属植物一直是分类学界的疑难类群,不同的学者对该属的分类处理比较混乱;其次,对该属的生物地理研究也很不够,尤其是对国产类群的研究;另外,W. globosa 作为该属中国分布的物种,其生理学特性和形态结构发育还缺乏研究。为此,本文通过mat K 基因测序、RAPD 标记等手段,结合野外和室内的长期观测,对其分类和中国的地理分布以及生理学特性进行了研究。针对浮萍科植物作为水生植物,其对重金属和芳香烃衍生物的耐受逆境能力大小,和对淡水水体环境生态的指示作用。本文研究了W. globosa 具解毒功能的谷胱甘肽转硫酶的活性;最后,探索了从黄鳝(Monpterus albus Zuiew )中分离纯化GSTs 的技术与方法并对maGST 的部分特性进行了研究。主要研究结果如下: 1. Wolffia 系统分类学研究 前人认为,Wolffia 柱头的颜色是重要的分组、分种检索性状。我们对其长期、活体、原位、实时跟踪观测结果表明,柱头颜色是Wolffia 个体发育上的变化过程,不是一个稳定性状,用作Wolffia subgroup 内组的划分特征和种的鉴别特征是不适合的。在此基础上我们重新修定了该属的分种检索表。利用形态分类学性状——气孔、长/宽、高/宽以及最大宽度在水面上还是水面下等性状,认为中国分布的类群应是W. globosa,但亦有W. neglecta 存在的证据。mat K 基因片段结果支持形态学的结论。通过广泛的野外采集,在我国北京、河北和吉林发现Wolffia 的新分布。 2. 中国Wolffia 居群遗传学研究 以RAPD 分子标记对广泛分布的居群遗传多样性研究表明,无根萍属植物主要以无性繁殖方式繁育,居群主要由单一克隆后代组成,如海河流域以及松花江流域居群;但一些居群亦兼有性繁殖方式,并具较高的遗传多样性,如武汉、海南居群。利用MVSP, Popgene 和Ntsys 等分析方法探讨了中国产Wolffia 居群遗传多样性和地理分布格局间关系。 3. W. globosa 的生理学研究 建立了较为完善的W. globosa 的无菌培养和保存体系。W. globosa 在逆境中,会形成休眠体;同时,发现不同居群甚至不同克隆系之间其抗逆性和生长速度存在着显著差异,差异最大的如海南文昌居群的生长速率,是长春居群的4.19 倍;不同的时间统计生长周期存在着不同结果,生长节律每天有两个生长高峰呈双“S”型;W. globosa 的耐受温度范围和pH 范围广;低浓度的IAA,GA,6-BA, EDDHA-Fe 以及EDTA 等物质具有促进W. globosa 生长的特性;但是,所有这些处理均没能促使W. globosa 从营养生长转入生殖生长。 4. W. globosa 的解剖学研究 W. globosa 通常是进行克隆繁殖,通过组织切片发现无性分枝子体还未伸出母株之前就已经完成分化,与此同时分枝子体中又分化出新的子体,分枝呈聚伞状,子体生长方向彼此相对;另外,生殖生长结构的分化也是在母体中完成的;生殖生长点与营养生长点不是同一生长点。 5. 浮萍科植物的毒理学研究 以重金属Cr3+和芳香烃衍生物CDNB 溶液处理Wolffia,Spirodela 和Lemna, 三种水生生物,结果表明Wolffia 比Spirodela, Lemna 对重金属和芳香烃衍生物有更强的抗逆能力,如在同等条件下对于Cr3+Wolffia 的半致死剂量800GB(≈ 80mg/L),而Spirodela 和Lemna 则分别为10mg/L;20mg/L;表明W. globosa 是一个优良的生态环境修复植物。与此同时,研究了W. globosa 中具有解毒功能的GSTs 粗酶液活力在不同浓度的重金属离子(Cu2+和Cd2+)以及芳香烃衍生物(CDNB 和NBD-Cl)随处理时间的变化情况。 6. 从水生生物黄鳝Monpterus albus Zuiew 中分离纯化GSTs 的研究GSTs 活性的变化是环境监测的一个Biomarker,为此研究从M. albus 中分离 纯化GSTs 的技术与方法。经GSH 亲和层析纯化的酶活力为粗酶液的207 倍,进而鉴定了maGST 的部分特性。SDS-PAGE 电泳和MALDI-TOF/MS 表明MaGST 为同源二聚体,分子量约为52kDa,单亚基分子量约为26 kDa。maGST 酶动力学表明对CDNB 为13.07 ± 0.37 微摩尔每分钟每毫克蛋白;对NBD-Cl 为5.54 ± 微摩尔每分钟每毫克蛋白;对ECA、4-NPA 几乎没有活性。在GSH 底物饱和,CDNB 的Km 值和Vmax 分别为0.32 mM 和16.19 微摩尔每分钟每毫克蛋白;CDNB 底物饱和,GSH 的Km 值和Vmax 分别为0.44 mM 和28.83 微摩尔每分钟每毫克蛋白。maGST 的酶活性pH 值较宽,温度范围广:在pH7.0-7.5 具有最大速度,在pH6.5 和pH8.5 时分别具有65%和72%的酶活力;在45℃时具有最大活性,30℃和55℃时为最大活力的80%,60℃几乎完全丧失酶活力。
Resumo:
Through research aimed at understanding the coastal environment, surveys designed to help manage the resource, and national programs to monitor environmental condition, we see a picture of a dynamic ecosystem that is Cape Romain National Wildlife Refuge (CRNWR). Currently, there are efforts underway to protect threatened species; monitor fish populations; and quantify the biological, physical, and chemical characteristics of this environment. The potential impacts to this system are just now being understood as ecological responses to human modification are observed and explained. As a starting point, this document compiles existing information about Cape Romain NWR in five topic areas and addresses the potential impacts to the Refuge. This review is intended to serve as a stepping stone to developing a research agenda in support of management of the Refuge. There are various sources of information on which to build a framework for monitoring conditions and detecting change to this environment. For instance, information on basic ecological function in estuarine environments has evolved over several decades. Long-term surveys of Southeast fisheries exist, as well as shellfish and sediment contaminants data from estuaries. Environmental monitoring and biological surveys at the Refuge continue. Recently, studies that examine the impacts to similar coastal habitats have been undertaken. This document puts past studies and ongoing work in context for Refuge managers and researchers. This report recommends that the next phase of this resource characterization focus on: • compiling relevant tabular and spatial data, as identified here, into a Geographic Information System (GIS) framework • assessing the abundance and diversity of fisheries utilizing CRNWR • delineating additional data layers, such as intertidal habitats and subtidal clam beds, from low-level aerial photography, hard copy maps, and other sources • continued inventories of plant and animal species dependent on the Refuge • monitoring physical and chemical environmental parameters using the methodology employed at National Estuarine Research Reserve System (NERRS) and other coastal sites, where appropriate • further definition of the potential risks to the Refuge and preparing responses to likely impacts.
Resumo:
The US Fish and Wildlife Service Cape Romain National Wildlife Refuge (CRNWR) and the Center for Coastal Environmental Health and Biomolecular Research (CCEHBR) at Charleston are interested in assessing the status of our coastal resources in light of increased coastal development and recreational use. Through an Interagency Agreement (FWS #1448-40181-00-H-001), an ecological characterization was undertaken to describe the status of and potential impacts to resources at CRNWR. This report describes historic fisheries-independent or non-commercial data relevant to CRNWR that can be used to evaluate the role of the Refuge as habitat for nearshore and offshore fish species. The purpose of this document is two-fold, first to give resource managers an understanding of fisheries data that have been collected over the years and, second, to illustrate how these data can be applied to address specific management issues. This report provides an overview of historic fisheries data collected along the southeast coast, as well as basic summaries of that data relevant to CRNWR, indicating how these data can be used to address specific questions of interest to Refuge managers and biologists.