基于互联网的地震预警问题的社会调查与分析

通过互联网对地震预警问题进行了社会调查,统计和分析问卷10 349份.结果表明,绝大多数的被调查者接受通过地震预警来减轻地震灾害的方式,认同地震预警的主要目标是减少人员伤亡,表示在信息公开及掌握应对措施的情况下,在地震预警时不会产生恐慌.同时,51.2%的被调查者认为,由地震部门发布预警更合适,而政府的责任是根据预警做好应急准备.72.1%的人表示对地震科普知识了解较少的现实表明,我国的地震知识普及率仍然很低.而公众能否理性地接受地震预警的实践,与地震知识普及程度关系很大.     

城镇污水处理厂一级A标准运行评估与再提标重难点分析

截至2019年底,全国共有2913座城镇污水处理厂执行GB 18918-2002《城镇污水处理厂污染物排放标准》的一级A标准,占全国城镇污水处理厂总数的53.2%,一级A标准已成为目前国内城镇污水处理厂执行最广泛的排放标准。通过对近6年太湖流域204座执行一级A标准污水处理厂的深入调研,结合全国100多座污水处理厂的全流程分析工作成果,首先系统评估了执行一级A标准的城镇污水处理厂的运行成效,其中太湖流域城镇污水处理厂在一级A提标改造后由于进水量的不断增加和出水浓度的不断降低,污染物削减总量显著提高,对太湖流域有机物、氮、磷减排及太湖富营养化控制做出了积极贡献。然后总结了城镇污水处理厂在运行过程中的常见问题,在进水水质、工艺设计、设备设施选择和维护以及活性污泥功能菌群性能调控等方面仍有进一步完善和优化空间,并提出了针对性的优化运行措施。最后重点探讨新一轮提标改造工作的重难点和对策,提出在新一轮提标改造中,应当重视污水收集系统的提质增效,提高管网质量和输送效率,并建议提标改造前先开展现有工艺的全流程分析,再在此基础上确定采取工艺优化或工程措施。     

舟山群岛港口发展有广阔前景

舟山海域位于长江水道和我国南北洋通道交汇的前沿,是我国南北海运的要冲与江海联运的枢纽,地理位置非常优越。舟山的三大优势资源“鱼、港、景”中,港的优势得天独厚拥有极为丰富的深水岩线,建设第四、五代大型集装箱泊位及其他大型深水泊位,发展潜能很大。舟山港域的发展提出了三点建议：１、充分利用区域优势,北依上海,南托宁波,定位于华东沿海重要的区域性洪口,成为长江三角洲口群体中的一个重要组成部分。２、利用岛屿     

社会最优可持续发展模型的建立与分析

通过对能源、环境、经济和社会发展4者关系的分析，建立了社会可持续发展模型，进而找到了社会最优可持续发展轨迹，为国家或地区社会发展的战略决策提供了可资参考的理论工具，同时进一步深化了可持续发展概念，提出了唯一的社会最优可持续发展概念。     

纳氏试剂比色法测定污水中氨氮的优化研究

纳氏试剂比色法测定污水中氨氮,其蒸馏预处理过程存在耗时长、馏出液接收不便和操作繁琐等问题.文章对预处理及测定方法进行了优化,提出将水样蒸馏体积减少为50 mL,后期比色体积减少为25 mL,并去除硼酸吸收液,改为直接接收馏出液.经验证,其结果与国标方法无显著性差异,标样验证相对误差为-0.8%~0.9%,实际样品测定结果的相对标准偏差为0.9%~4.4%,加标回收率为94%~107%.优化的方法测量数据稳定,结果准确,在测定污水中氨氮具有实际应用意义.     

微波技术处理试油废液的实验研究

试油废液具有黏度高、COD高、色度深、气味恶臭等特点,常规技术工艺复杂、处理时间长、成本高。微波技术具有加热、诱导催化、辅助絮凝等优势,能产生物理、化学和生物效应。微波应用于试油废液处理可大大提高处理效率,实验表明:应用微波处理试油废液絮凝剂加量减少25%,处理时间仅为常规工艺的1/3,微波作用使COD去除率由常规Fenton氧化的50%提高到80%,反应时间由30min缩短到10min,pH值在3～6之间、FeSO4.·7H2O加量0.15g、活性炭加量2g、H2O2加量2g,COD值可降至100mg/L以下。     

Effect of cadmium alone and in combination with butachlor on soil enzymes

The ecological toxicity of cadmium (Cd, 10 mg kg⁻¹ of dry weight soil) and butachlor (10, 50 and100 mg kg⁻¹ of dry weight soil) in both their single and combined effects on soil urease and phosphatase was studied after 1, 3, 7, 14, 21 and 28 days exposure under controlled conditions in paddy and phaeozem soils. The results showed that Cd reduced the activities of urease and phosphatase at early incubation time (1–7 days), while the reduction almost disappeared at the end of the incubation. The effect of Cd on phosphatase was more pronounced than that on urease. The activities of urease and phosphatase were reduced by butachlor, while urease activity was significantly (P < 0.05 or P < 0.01) improved when the concentrations of butachlor were 10 and 50 mg kg⁻¹ at the end of the incubation. When Cd (10 mg kg⁻¹) was combined with butachlor (50 and 100 mg kg⁻¹), the activities of urease and phosphatase became lower than without combination at early incubation time, which indicated that the toxicity of Cd significantly increased (P < 0.05 or P < 0.01). However, when Cd (10 mg kg⁻¹) was combined with butachlor (10 mg kg⁻¹), the activities of urease and phosphatase became higher than those without combination at the end of the incubation, which indicated that the toxicity of Cd decreased. It was indicated that the combined effects depended largely on the incubation time and the concentration ratio of Cd and butachlor. In addition, it was showed that the combined effects of butachlor and Cd appeared different in paddy from phaeozem, which may be related to the different properties of these soils.     

硝酸银标准滴定溶液的不确定度评定

在掌握JJF1059-1999的基础上，对硝酸银标准滴定溶液浓度的不确定度进行评定，主要从方法概述、确定测量中不确定度的来源、建立数学模型、计算相对标准不确定度分量、合成相对标准不确定度、扩展不确定度等入手，详细介绍了硝酸银标准滴定溶液的不确定度评定过程。     

Concentration, distribution and source apportionment of atmospheric polycyclic aromatic hydrocarbons in the southeast suburb of Beijing, China

Total suspended particle samples and gas phase samples were collected at three representative sampling sites in the southeastern suburb of Beijing from March 2005 to January 2006. The samples were analyzed for 16 US EPA priority PAHs using GC/MS. Concentrations of Sigma PAHs in particle and gas phases were 0.21-1.18 x 10(3) ng m(-3) and 9.5 x 10(2) ng-1.03 x 10(5) ng m(-3), respectively. PAH concentrations displayed seasonal variation in the order of winter>spring>autumn>summer for particle phase, and winter>autumn>summer>spring for gas phase. Partial correlation analysis indicates that PAH concentrations in particle phase are negatively correlated with temperature and positively correlated with air pollution index of SO(2). No significant correlation is observed between gas phase PAHs and the auxiliary parameters. Sources of PAH are identified through principal component analysis, and source contributions are estimated through multiple linear regression. Major sources of atmospheric PAHs in the study area include coal combustion, coke industry, vehicular emission and natural gas combustion.     

Effect-based assessment of passive air samples from four countries in Eastern Europe

Although passive sampling has been previously used for the monitoring of volatile and semi-volatile contaminants in air, there are limited data on the use of this technique coupled with bioassays based on specific biological responses. Biological responses including those mediated by the aryl hydrocarbon (AhR) receptor as well as (anti-)estrogenicity and (anti-)androgenicity of samples from four Eastern European countries (Lithuania, Slovakia, Romania, and Serbia) were determined. To address the potential differences of specific toxic potencies of pollutant mixtures in ambient air in Eastern Europe, each country was characterized by a single more remote location that served to determine regional background conditions and one location in more urbanized and industrialized locations, which were defined as “impacted” areas. Besides samples from Lithuania, a significant gradient in concentrations of AhR-mediated potency from background and impacted localities was observed. Greatest potencies were measured in samples from impacted locations in Romania and Slovakia. Concentrations of polycyclic aromatic hydrocarbons (PAHs) that were quantified accounted for 3–33 % of the 2,3,7,8-tetrachlorodibenzo-p-dioxin equivalents determined by use of the bioassay. No significant estrogenic potency was detected but anti-estrogenic effects were produced by air from two background locations (Lithuania, Slovakia) and three impacted locations (Lithuania, Romania, and Serbia). Anti-androgenic potency was observed in all samples. The greatest anti-estrogenic potency was observed at the background location in Slovakia. Anti-estrogenic and anti-androgenic potencies of studied air samples were probably associated with compounds that are not routinely monitored. The study documents suitability of passive air sampling for the assessment of specific toxic potencies of ambient air pollutants.