平行双样对天然气中硫化物采样的质量控制

为了研究平行双样对天然气中硫化物采样质量控制措施的可靠性,对现场采集的８对硫化物平行样用对氨基二甲基苯胺光度法进行测定。对测定结果及相对偏差进行Ｗ（Ｓｈａｐｉｒｏ－Ｗｉｌｋ）检验,检验结果说明平行双样相对偏差服从正态分布,数据的一致性较好,说明用平行双样对采样进行质量控制是可行的。文中还用Ｇｒｕｂｂｓ检验法计算出在该实验条件下测定天然气中硫化物平行双样的相对偏差质量控制范围为１．９３％±１２．５％。     

热喷处理污泥及其复混肥的养分效率与生物效应

采用室内分析和田间生物试验，研究了热喷处理污泥及其复混肥的养分供应能力及它们在农地上施用对土壤肥力、青菜产量及其品质的影响。结果表明：热喷处理能有效杀灭污泥中病原物，除自，并可使污泥中水溶性有机碳和速效氮含量分别提高87％，19％和35％，施用热喷污泥制成的复混肥不但比等养分的无机复合肥多增产38％，而且青菜体内Vc和水溶性总糖等营养品质也有明显的提高，NO3^-却只有无机复合肥处理的一半左右，污泥经势喷处理有利于提高污泥中养分的生物有效性，特别是热喷污泥制成的复混肥氮磷养分利用率显著高于无机复合肥，施用污泥和污泥复混肥还能提高土壤肥力，比单纯大量施用污泥要安全得多，土地使用年限可延长40倍。     

造纸漂白废水中有机氯化物处理技术

在调研国内外文献资料的基础上，对有关制浆造纸漂白废水污染控制技术研究现状从物化法，化学法，生化法等方面进行了综述，对系统开发研究高效，经济，节能的漂白废水处理工艺有重要的参考作用。     

Compound contamination and secondary ecological effects of Cd and As in soil-alfalfa ecosystems

ＣｏｍｐｏｕｎｄｃｏｎｔａｍｉｎａｔｉｏｎａｎｄｓｅｃｏｎｄａｒｙｅｃｏｌｏｇｉｃａｌｅｆｆｅｃｔｓｏｆＣｄａｎｄＡｓｉｎｓｏｉｌ－ａｌｆａｌｆａｅｃｏｓｙｓｔｅｍｓ（ＺｈｏｕＱｉｘｉｎｇ；ＧａｏＺｈｅｎｇｍｉｎ）（ＩｎｓｔｉｔｕｔｅｏｆＡｐｐｌｉｅ...     

Resourcefulization approaches to pollution control of chromate residues in China

Over 2 million tons of chromate residues as hazardous wastes have been accumulated from chromate production processes during the past more than 30 years in China. Some serious pollution problems have been caused due to no appropriate technology and management. Approaches are reviewed to pollution control of chromate residues by utilizing them as secondary resources in this paper. In addition to legislation for pollution control, chromate residues can be used as raw materials to produce a great diversity of useful industrial products. Strategies are also recommanded for the resourcefulization of chromate residues.     

离子选择电极法与离子色谱法测量低浓度氟化物比较

用离子选择电极法、离子色谱法两种方法对氟化物国家标准样品进行测量,通过比较发现两种方法测量国家标样低浓度样品时有显著差异.     

Phytoremediation of polyaromatic hydrocarbons, anilines and phenols

Phytoremediation technologies based on the combined action of plants and the microbial communities that they support within the rhizosphere hold promise in the remediation of land and waterways contaminated with hydrocarbons but they have not yet been adopted in large-scale remediation strategies. In this review plant and microbial degradative capacities, viewed as a continuum, have been dissected in order to identify where bottle-necks and limitations exist. Phenols, anilines and polyaromatic hydrocarbons (PAHs) were selected as the target classes of molecule for consideration, in part because of their common patterns of distribution, but also because of the urgent need to develop techniques to overcome their toxicity to human health. Depending on the chemical and physical properties of the pollutant, the emerging picture suggests that plants will draw pollutants including PAHs into the plant rhizosphere to varying extents via the transpiration stream. Mycorrhizosphere-bacteria and -fungi may play a crucial role in establishing plants in degraded ecosystems. Within the rhizosphere, microbial degradative activities prevail in order to extract energy and carbon skeletons from the pollutants for microbial cell growth. There has been little systematic analysis of the changing dynamics of pollutant degradation within the rhizosphere; however, the importance of plants in supplying oxygen and nutrients to the rhizosphere via fine roots, and of the beneficial effect of microorganisms on plant root growth is stressed. In addition to their role in supporting rhizospheric degradative activities, plants may possess a limited capacity to transport some of the more mobile pollutants into roots and shoots via fine roots. In those situations where uptake does occur (i.e. only limited microbial activity in the rhizosphere) there is good evidence that the pollutant may be metabolised. However, plant uptake is frequently associated with the inhibition of plant growth and an increasing tendency to oxidant stress. Pollutant tolerance seems to correlate with the ability to deposit large quantities of pollutant metabolites in the 'bound' residue fraction of plant cell walls compared to the vacuole. In this regard, particular attention is paid to the activities of peroxidases, laccases, cytochromes P450, glucosyltransferases and ABC transporters. However, despite the seemingly large diversity of these proteins, direct proof of their participation in the metabolism of industrial aromatic pollutants is surprisingly scarce and little is known about their control in the overall metabolic scheme. Little is known about the bioavailability of bound metabolites; however, there may be a need to prevent their movement into wildlife food chains. In this regard, the application to harvested plants of composting techniques based on the degradative capacity of white-rot fungi merits attention.     

生态农业园区废弃物资源化处理利用研究

本文介绍了蟹岛生态园区农业废气物及生活污水的资源化处理工艺方案 ,通过对沼气池和生活污水厌氧 -好氧 -生态塘处理系统进行综合设计 ,实现了节能环保和废弃物无害化综合处理利用。形成了种植业、养殖业、肥料加工、能源利用和休闲度假有机结合的生态农业经济 ,为实现农村经济可持续发展提供了一种新模式     

Residues and dissipation kinetic of abamectin,chlorfenapyr and pyridaben acaricides in green beans (Phaseolus vulgaris L.) under field conditions using QuEChERS method and HPLC

Abstract

The current study estimated the dissipation rates of abamectin, chlorfenapyr and pyridaben acaricides in pods of green beans (Phaseolus vulgaris L.) under field conditions in Egypt. Pesticides were extracted and cleaned-up by QuEChERS method and were analyzed by HPLC. The dissipation of these acaricides followed the first order kinetics model with half-life (t_1/2) values 1.00, 3.50 and 1.50?days for abamectin, chlorfenapyr and pyridaben, respectively. The lowest residues, at different time intervals of field application rate of each pesticide, were observed with abamectin followed by pyridaben and then chlorfenapyr. Pre-harvest intervals (PHIs) were 10.00, 13.50 and 6.00?days for abamectin, chlorfenapyr and pyridaben, respectively and were below the established European maximum residue limits (EU MRLs) 10–14, 14–21 and 7–10?days after application, respectively. If the fresh pods will be consumed after harvest, it is expected that the presence of these pesticides in the food will have a negative impact on human health. Therefore, the elimination of the residues of these harmful pesticides must be carried out.