发展乡村旅游对乡村生态环境影响研究

针对发展乡村旅游对乡村生态环境的影响,介绍了乡村旅游的发展现状,探讨了乡村旅游发展对乡村环境的影响,主要包括乡村旅游带来的环境问题分析和环境问题的原因分析,乡村旅游作为旅游行业一支新生力量,异军突起,在中国已形成很大的发展趋势.发展乡村旅游可以提高农民收入、合理利用乡村资源,提出对策建议,主要是充分发挥政府职能,建立健全乡村环境保护体系,制定合理的乡村旅游发展规划,加强乡村旅游的环境管理,为乡村旅游发展提出了对策建议.     

民用燃煤源中多环芳烃排放因子实测及其影响因素研究

民用燃煤是我国目前关注较多的多环芳烃(polycyclic aromatic hydrocarbons,PAHs)排放源.根据我国民用燃煤所涉及的煤种、燃烧方式和炉灶类型,利用全流稀释采样系统对5种不同成熟度的煤种,分别以散块煤和蜂窝煤形式在3种炉灶类型中燃烧产生的烟气进行了采样和分析,初步获取了我国民用燃煤烟气中PAHs排放因子(EFPAHs)的实测数据.结果表明,烟煤的EFPAHs在块煤燃烧方式下的变化范围为1.1～3.9 mg.kg-1,在蜂窝煤燃烧方式下的变化范围为2.5～21.1 mg.kg-1,无烟煤的EFPAHs在块煤与蜂窝煤燃烧方式下分别为0.2 mg.kg-1与0.6 mg.kg-1.在民用燃煤的EFPAHs的各种影响因素中,煤的地质成熟度起主导作用,不同成熟度煤种的EFPAHs差异幅度高达1～2个数量级.其次是燃烧形态(块煤/蜂窝煤),主要表现为同一种地质成熟度的煤在蜂窝煤燃烧方式下排放的PAHs比块煤高2～6倍.炉灶类型的影响最小.     

壬基酚在污灌土壤中吸附行为研究

采用序批式室内实验研究了壬基酚(NP)在污灌土壤中的吸附行为,同时探讨了壬基酚在土壤中吸附行为的影响因素,包括pH、离子强度、黑炭和矿物质.水溶液中NP检测方法为液液萃取-高效液相方法(LLE-HPLC).研究结果表明,土壤中有机质含量在吸附过程中起决定作用,土壤自身矿物组成成分对NP吸附行为具有一定影响.NP在土壤中吸附反应6h后达到平衡,吸附动力学都符合准二级线性模式;吸附等温线符合线性模式.壬基酚在污灌和清灌土壤中有机质吸附系数(Koc)分别为3.1×104 L·kg-1和3.2 ×104 L·kg-1,在土壤中很难移动.pH改变对壬基酚在土壤中吸附行为影响程度要高于离子强度,碱性条件下影响结果更为显著.NP在土壤黑炭和矿物质中吸附行为均符合线性模式,分配系数都有所下降.     

城市主干道交通噪声影响因素分析

选取了沈阳市lO条主干道,通过实地调查监测与文献资料分析相结合的方法,分析了主干道交通噪声的影响因素,结果表明,车流量与车型是影响城市主干道交通噪声的重要因素,并提出控制城市主干道交通噪声的防治措施,改善声环境质量。     

高温高湿环境对车辆装备的影响及防护对策

高温高湿环境条件对车辆装备性能有着至关重要的影响。为了提高新时期我军车辆装备保障能力,就必须做好车辆装备的的防护管理。首先介绍了高温高湿地区气候环境的特点,分析了其对车辆装备的主要影响,最后提出了车辆装备防护管理的对策。     

小城镇建设项目环境影响评价相关问题探讨——以聊城经济开发区蒋官屯小城镇建设项目为例

在中国的城市化进程中,小城镇建设发挥了重要的作用,引起了各级政府的重视。本文以聊城经济开发区蒋官屯小城镇建设项目为例,结合小城镇建设项目的特点,就小城镇建设项目的环境影响评价中相关问题进行了探讨,主要从环境影响评价的特点、评价的主要内容、评价重点、项目建设对环境的影响分析及外环境对项目的影响分析、生态及社会环境影响分析、公众参与、项目选址合理性分析、应特别关注的环境问题等几个方面进行阐述,以期为小城镇建设项目环境影响评价提供参考。     

水葫芦大面积种植对滇池浮游植物的影响研究

对滇池水葫芦大面积种植区域开展了浮游植物群落结构和细胞丰度变化的调查研究,经过数据统计分析发现水葫芦大面积种植对水体浮游植物种群种类组成影响不显著,但对蓝藻生长具一定的抑制作用,对绿藻和硅藻可能具一定促进作用。     

生产安全事故责任认定定量化方法的探讨

当前,我国生产安全事故的责任认定是在事故调查组分析调查事故原因后,对事故责任者承担的责任进行定性的责任认定,受一定的主观因素影响。为了避免主观因素的影响,本文提出了一种责任认定定量化方法,该方法首先从安全管理、安全技术和职业健康卫生三方面建立了完善的事故影响因素集;然后在分析事故原因后采用专家打分法(德尔菲法)确定各影响因素的影响度,并计算出与事故相关的责任者的累加影响度,即责任大小;最后根据事故造成的人员伤亡和经济损失情况对事故责任者作出处理。此方法对生产安全事故责任认定更加公正客观。     

Degradation of metabolites accumulated of benzo[a]pyrene by coupling Penicillium Chrysogenum with KMnO4

Several main metabolites of benzo[a]pyrene （BaP） formed by Penicillium chrysogenum, Benzo[a]pyrene-1,6-quinone （BP 1,6- quinone）, trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene （BP 7,8-diol）, 3-hydroxybenzo[a]pyrene （3-OHBP）, were identified by high-performance liquid chromatography （HPLC）. The three metabolites were liable to be accumulated and were hardly further metabolized because of their toxicity to microorganisms. However, their further degradation was essential for the complete degradation of BaP. To enhance their degradation, two methods, degradation by coupling Penicillium chrysogenum with KMnO4 and degradation only by Penicillium chrysogenum, were compared; Meanwhile, the parameters of degradation in the superior method were optimized. The results showed that （1） the method of coupling Penicillium chrysogenum with KMnO4 was better and was the first method to be used in the degradation of BaP and its metabolites; （2） the metabolite, BP 1,6-quinone was the most liable to be accumulated in pure cultures; （3） the effect of degradation was the best when the concentration of KMnO4 in the cultures was 0.01% （w/v）, concentration of the three compounds was 5 mg/L and pH was 6.2. Based on the experimental results, a novel concept with regard to the bioremediation of BaP-contaminated environment was discussed, considering the influence on environmental toxicity of the accumulated metabolites.     

Debromination of decabromodiphenyl ether by organo-montmorillonite-supported nanoscale zero-valent iron：Preparation, characterization and influence factors

An organo-montmorillonite-supported nanoscale zero-valent iron material(M-NZVI) was synthesized to degrade decabromodiphenyl ether(BDE-209). The results showed that nanoscale zero-valent iron had good dispersion on organo-montmorillonite and was present as a core-shell structure with a particle size range of nanoscale iron between 30–90 nm, characterized by XRD, SEM, TEM, XRF, ICP-AES, and XPS. The results of the degradation of BDE-209 by M-NZVI showed that the efficiency of M-NZVI in removing BDE-209 was much higher than that of NZVI. The efficiency of M-NZVI in removing BDE-209 decreased as the pH and the initial dissolved oxygen content of the reaction solution increased, but increased as the proportion of water in the reaction solution increased.