国家标准GB／T3840—91中城市大气污染物总量控制A—P值法的应用

本文叙述了在大气总悬浮微粒物实行总量控制时使用GB/T384-91中A-P值方法的经验,给出了一些计算公式及参数,同时还介绍了使用上述国家标准时对求算允许排放总量的主要参数土地面积进行人口订正的经验公式和确定经验系数的方法.     

臭氧氧化降解水溶液中1—萘酚的动力学研究

本文研究了水溶液中１－萘酚在鼓泡反应釜内臭氧氧化的消失动力学,考察了ｐＨ值、温度、自由基清除剂和１－萘酚的起始反应浓度等因素对反应的影响。结果表明,ｐＨ值、反应温度的提高有利于１－萘酚的降解。１－萘酚初始浓度低时其消失速率较高。该反应是有自由基反应贡献的分子臭氧氧化反应。在重碳酸盐存在下,１－萘酚的臭氧氧化降解符合一级反应动力学。     

南岳森林群落生物多样性研究(Ⅱ)广济寺森林群落植物物种多样性测定

本文根据实地调查资料及其统计分析结果,选用了24个物种多样性指数公式,并采用重要值、株数或鲜重以及优势度或盖度等作为测度指标,对南岳广济寺森林群落植物物种多样性进行了研究。结果表明,南岳广济寺森林属落多样性较高,接近山地季雨林的水平;此外,不同测度指标对物种多样性指数计算值并无明显的规律性。     

Processing and Physical Properties of Plastics Made from Soy Protein Polyester Blends

Blending soy protein with polyesters using a polyvinyllactam as a compatibilizer successfully made soy protein-based plastics. The polyesters used to produce blends included polycaprolactone (PCL) and Biomax (a commercial biodegradable polyester). The blends were processed by compounding extrusion and injection molding. Blends containing soy protein/Biomax-poly(vinyl alcohol) had tensile strengths ranging from 16–22 MPa, with samples containing larger percentages of the synthetic polymer exhibiting greater strengths. Blends made from soy protein, Biomax, and PCL had tensile strengths ranging from 27–33 MPa. All the blends had high Young's moduli but demonstrated brittle characteristics as evident from their low elongations at break, ranging from 1.8–3.1%. Plastics made from soy protein/polyester blends exhibited low water absorption and had good stability under ambient conditions relative to the plastics made from soy protein alone. Blends made from soy protein flour produced plastics with the lowest water absorption.     

铱涂层钛电极电催化氧化降解喹啉

采用电催化氧化降解模拟焦化废水中的喹啉,研究了电极种类、废水初始质量浓度、废水pH、极板间距和电流密度对喹啉去除率的影响.实验结果表明,在以铱涂层钛电极为阳极、废水中喹啉初始质量浓度为100 mg/L、废水pH为9、电流密度为20 mA/cm2、极板间距为1 cm、反应时间为720 min时,喹啉去除率达88.1％.并...     

纤维板厂废水处理实验

用明矾作混凝剂，生石灰为助凝剂剂对纤维板厂生产废水进行混凝处理，COD去除率达67％，其上清液用延时生化法，曝气12h后，出水COD，SS，PH，色度均达到行业排放标准，沉淀用低速离心脱水，效果显著，泥饼可作为燃料综合利用。     

“入世”对环境保护和对外贸易的影响及对策措施

着重分析了中国加入WTO应遵循的环境与贸易政策取向 ,系统评价了WTO及其贸易协定可能对环境与贸易产生的积极作用和消极影响 ,提出了利用贸易手段加强环境保护的对策措施。     

加强生态建设 促进经济发展--关于县域经济可持续发展的几点思考

党的十六大提出的要在本世纪头20年集中精力全面建设小康社会的宏伟目标，对于我们这样一个经济欠发达地区来说，既是一种强大的压力，也是一次难得的机遇，要实现这一目标，既要充分肯定我县目前已拥有的经济实力，更要理性的分析所存在的差距。面临的形势与任务只有充分发挥现有各方面的优势，把潜能发挥出来才能后来居上。     

Formation and cytotoxicity of a new disinfection by-product (DBP) phenazine by chloramination of water containing diphenylamine

Disinfection by-products (DBPs) in drinking water have caused worldwide concern due to their potential carcinogenic effects. The formation of phenazine from diphenylamine (DPhA) chloramination was studied and its cytotoxicities for two human cancer cells were also investigated. Phenazine was detected synchronously with the consumption of DPhA by chloramination, which further confirmed that the new DBP phenazine can be produced along with N-nitrosodiphenylamine (NDPhA) from DPhA chloramination. The formation of phenazine had a maximum molar yield with solution pH increasing from 5.0 to 9.0, with phenazine as the main product for DPhA chloramination at lower pH, but higher pH favored the formation of NDPhA. Thus, solution pH is the key factor in controlling the formation of phenazine and NDPhA. Both the initial DPhA and chloramine concentrations did not show a significant effect on the molar yields of phenazine, although increasing the chloramine concentration could speed up the reaction rate of DPhA with chloramines. The cytotoxicity assays showed that phenazine had significant cell-specific toxicity towards T24 (bladder cancer cell lines) and HepG2 (hepatic tumor cell lines) cells with IC50 values of 0.50 and 2.04 mmol/L, respectively, and T24 cells being more sensitive to phenazine than HepG2 cells. The IC50 values of phenazine, DPhA, and NDPhA for T24 cells were of the same order of magnitude and the cytotoxicity of phenazine for T24 cells was slightly lower than that of NDPhA (IC50, 0.16 mmol/L), suggesting that phenazine in drinking water may have an adverse effect on human health.     

A review of rapid transport of pesticides from sloping farmland to surface waters:Processes and mitigation strategies

Pesticides applied to sloping farmland may lead to surface water contamination through rapid transport processes as influenced by the complex topography and high spatial variability of soil properties and land use in hilly or mountainous regions. However, the fate of pesticides applied to sloping farmland has not been sufficiently elucidated. This article reviews the current understanding of pesticide transport from sloping farmland to surface water. It examines overland flow and subsurface lateral flow in areas where surface soil is underlain by impervious subsoil or rocks and tile drains. It stresses the importance of quantifying and modeling the contributions of various pathways to rapid pesticide loss at catchment and regional scales. Such models could be used in scenario studies for evaluating the effectiveness of possible mitigation strategies such as constructing vegetated strips, depressions, wetlands and drainage ditches, and implementing good agricultural practices. Field monitoring studies should also be conducted to calibrate and validate the transport models as well as biophysical-economic models, to optimize mitigation measures in areas dominated by sloping farmland.