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排序方式: 共有42条查询结果,搜索用时 31 毫秒
1.
选取芦苇、菖蒲、美人蕉和香蒲等4种南京地区常见的人工湿地常用植物作为供试植物,对其在春季对生活污水总氮(TN)去除效果的数学模型进行研究.通过监测引种植物后污水中TN浓度,利用回归分析建立湿地植物去除污染物的数学模型.结果表明:在毒季种植植物后污水中的TN浓度按线性关系减少,其中芦苇、菖蒲和香蒲对污染物的去除效果明显,其直线的相关系数分别达到0.927,0.929和0.979;美人蕉在春季对TN的去除能力较差,其线性仅为0.561.  相似文献   
2.
关于植物化学生态信息的开发与利用   总被引:8,自引:0,他引:8  
叶居新  陶勇 《环境与开发》2000,15(3):22-24,31
植物的化学信息,早已被人们所关注和利用,目前,该研究已成为生态学和化学生态学中最活跃,最能为社会与生产服务的领域之一,生态系统中的物质流和能量流是资源,而生态学的信息则是更具开发,利用前景的资源。  相似文献   
3.
分别采用《城市污水处理厂污泥检验方法》(CJ/T221—2005)中平皿计数法和多管发酵法检测分析呼和浩特市周边7个城镇污水处理厂、2个制药企业以及2个乳制品企业污泥中的细菌总教和粪大肠菌群茵值。结果显示:供试样品的细菌总数为1.0×10^6~1.3×10^8个/g,其中细菌含量最高的是乳制品企业l污泥样品,最低的是污水处理厂4污泥样品。粪大肠菌群菌值为2.0×10^5-5.4×10^8个/g,其中粪大肠茵群菌值最高的是污水处理厂2和污水处理厂5污泥样品,最低的是污水处理厂4和制药企业1污泥样品,乳制品企业污泥样品的粪大肠菌群茵值居中。  相似文献   
4.
选取某大型发电企业进行实测,根据测试数据计算颗粒物去除装置对颗粒物的分段去除效率。结果表明:静电除尘器除尘效率为99.91%、湿法脱硫装置除尘效率为60.51%、湿法脱硫装置出口相对静电除尘器进口的颗粒物去除效率为99.61%、湿法脱硫装置出口颗粒物浓度是静电除尘器出口颗粒物浓度的4.18倍。此外,也依据计算结果并结合实际情况分析了影响各除尘段颗粒物去除效率的主要成因,这些成因主要包括各除尘段功能、脱硫剂与脱硫副产品的颗粒物、脱硫装置运行平稳性等,期望本研究成果能对电厂燃煤锅炉大气污染控制设施关系调整、重新设计及大气环境污染治理思路调整提供重要科学依据与指导。  相似文献   
5.
鄱阳湖典型湿地沉水植物的分布格局及其水环境影响因子   总被引:4,自引:0,他引:4  
沉水植物是湖泊湿地生态系统中关键组分,调查研究沉水植物分布格局及其水环境影响因子,对于沉水植被的恢复与重建具有重要的指导意义。2013年5月初期分别对鄱阳湖典型湿地区域中有沉水植物的25个样地进行群落结构调查,采用系统取样方法对沉水植物进行调查采样并监测水环境因子,在野外调查的基础上运用GIS软件制作鄱阳湖典型区域沉水植物的生物量分布图,并采用主成分分析(PCA)和典范对应分析(CCA)方法分析其主要影响因子。结果表明:鄱阳湖湿地沉水植物以苦草(Vallisneria natans)为广布种,其中蚌湖及白沙湖以黑藻(Hydrilla verticillata)为优势种,白沙洲及乐安河龙口段以苦草为优势种,伴生种主要有金鱼藻(Ceratophyllum demersum)、马来眼子菜(Potamogeton malaianus)、菹草(P.crispus)、小茨藻(Najas minor)、大茨藻(N.marina)、刺苦草(V.spinulosa)和水车前(Ottelia alismoides)等。采用双向指示种分析法将研究区沉水植物分为6个群落;5月初大部分沉水植物尚处于生长季初期,生物量相对较低,仅菹草的生物量较大;沉水植物与浮叶植物共存现象明显。主成分分析(PCA)结果显示,第一主成分中水深、总磷和溶解氧等因子的系数值较大,第二主成分中pH值、化学需氧量和水体透明度等因子的系数值较大,是影响沉水植物分布的关键因子;典范对应分析(CCA)结果显示,水深、总磷和总氮对苦草和黑藻的影响显著,水体透明度是马来眼子菜的主要影响因子。  相似文献   
6.
A database has been developed that demonstrates experimental evidence of hormesis. It includes information from a broad range of biological models, including plants, and information on study design, dose-response features, and physical/chemical properties of the agents. An assessment of plant hormetic dose responses is presented based on greater than 3000 plant endpoints. Plant hormetic dose responses were observed for numerous endpoints including disease incidence, reproductive indices, mutagenic endpoints, various metabolic parameters, developmental processes, and a range of growth indicators. Quantitative features of these dose responses typically display a maximum stimulatory response less than two-fold greater than controls and a width of the stimulatory response usually less than 10-fold in dose range. The database establishes that hormetic dose responses commonly occur in plants, are broadly generalizable, and have quantitative features similar to hormetic dose responses found for animals.  相似文献   
7.
The purpose of this research was to determine changes in negative air ion (NAI) concentrations produced by plants grown under different light intensities. NAI concentrations were observed and analyzed in an outdoor green space with five plant species (Aloe arborescens, Clivia miniata, Chlorophytum comosum, Opuntia brunnescens, Crassula portulacea) and A. arborescens was then grown under controlled-light conditions in an enclosed space for the subsequent light intensity experiment.  相似文献   
8.
In situ measurements comparing vertical SO42− profiles in vegetated and non-vegetated sediments showed that SO42− concentrations in vegetated sediments increased significantly at the beginning of the growing season and then gradually decreased during the rest of the growing season. Throughout the growing season, SO42− concentrations remained higher in the vegetated sediments than in the sediments without plants. The higher SO42− concentrations in the vegetated sediments indicate that oxygen release from roots and evapotranspiration-induced advection by plants play an important role in the dynamics of sulfur species in sediments. Since the total pool of solid-phase sulfide is relatively large compared to the mass of SO42− in the sediments, the gradual decrease of SO42− concentrations may result from limitation of the solid-phase sulfide that is in direct contact with or very close to the roots and rhizomes. This would mean that the main pool of solid-phase sulfide and associated trace metals are not affected by the oxygen release from roots, and the associated trace metals will not become bioavailable during the growing season.  相似文献   
9.
To improve phytoremediation processes, multiple techniques that comprise different aspects of contaminant removal from soils have been combined. Using creosote as a test contaminant, a multi-process phytoremediation system composed of physical (volatilization), photochemical (photooxidation) and microbial remediation, and phytoremediation (plant-assisted remediation) processes was developed. The techniques applied to realize these processes were land-farming (aeration and light exposure), introduction of contaminant degrading bacteria, plant growth promoting rhizobacteria (PGPR), and plant growth of contaminant-tolerant tall fescue (Festuca arundinacea). Over a 4-month period, the average efficiency of removal of 16 priority PAHs by the multi-process remediation system was twice that of land-farming, 50% more than bioremediation alone, and 45% more than phytoremediation by itself. Importantly, the multi-process system was capable of removing most of the highly hydrophobic, soil-bound PAHs from soil. The key elements for successful phytoremediation were the use of plant species that have the ability to proliferate in the presence of high levels of contaminants and strains of PGPR that increase plant tolerance to contaminants and accelerate plant growth in heavily contaminated soils. The synergistic use of these approaches resulted in rapid and massive biomass accumulation of plant tissue in contaminated soil, putatively providing more active metabolic processes, leading to more rapid and more complete removal of PAHs.  相似文献   
10.
植物SOD活性变化与其抗污能力的关系   总被引:4,自引:0,他引:4  
研究了模拟酸雨、SO2单独与复合污染对水杉、杉木、龙柏3种抗污能力不同的植物SOD活性、细胞汁酸度、细胞膜透性的影响。结果表明,SOD的活性经污染后变化规律在不同植物有所不同,而这种变化与其抗污能力有关。SOD活性升高者,其抗污能力强,反之则弱,与本底值大小无关。  相似文献   
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