危险及可操作性分析在LNG汽车加气站的应用

利用危险及可操作性分析(HAZOP)技术对液化天然气(LNG)汽车加气站卸车、调压和加液流程进行系统的危险分析和探讨,并提出建议措施。应用实例表明,HAZOP技术可有效地辨识LNG汽车加气站的风险,可作为LNG加气站风险管理的有效工具之一。     

黑龙江省放射源安全管理现状及对策研究

在研究放射源安全管理现状的基础上,对现有体制进行了充分的研究,结合实践中遇到的焦点和难点问题,以提高管理效率为目标,着眼于制度创新,针对使用单位、监督管理部门分别进行了制度构建,对黑龙江省移动放射源,低活度放射源的管理进行了管理实践探讨,为黑龙江省放射源管理实践提供了较好的理论和实践的探索。     

基于UML的放射源贮存库管理系统设计

随着放射性同位素在油井钻探、测试等领域中的广泛应用,放射源的种类及数量越来越大,使用频率越来越高,传统的管理方法已经不适应现代条件下的放射源管理需求。本文从放射源管理中的重要环节——贮存库管理系统入手,以UML为工具,对贮存库管理系统的需求模型和系统模型进行了设计,以提高放射源管理水平。     

环境影响评价中公众参与影响因素及方式分析研究

针对环境影响评价中公众参与影响因素及方式分析问题,介绍了环境影响评价中公众参与的特征,包括公开性、双向性和参与性,对公众参与的影响因素进行了分析,主要分析了利害关系人、法律制度、公共政策、市场经济发展水平和社会信息化程度,探讨了公众参与有效性要素的措施,主要有公众人员的选择、公众赋予的权力、参与时间的选择、解决矛盾能力和公众参与形式,在环境影响评价中进行公众参与不仅是环境影响评价本身的需要,同时也是中国民主制度的体现。     

新型活性污泥的培养及其处理高盐有机废水

在好氧反应器中,将海泥通过海水和营养物质培养成新型的活性污泥,在处理含盐废水时有较好的活性和沉降性能,对这种新型的活性污泥我们称其为海洋活性污泥。通过10周的培养,海泥的污泥体积指数（SVI）从最初的19 mL/g升高到70 mL/g,对有机废水处理12 h后高锰酸盐指数（CODMn）降解率达到90%,氨氮降解率达到45%。在污泥培养时,营养物质投加频率为一日一次最有利于污泥的培养,又葡萄糖比淀粉更有利于污泥的培养。对于含盐有机废水的处理,海洋活性污泥也比传统活性污泥有优势,甚至对于含盐量6%的高盐有机废水,处理12 h后能达到CODMn降解率达为70%,氨氮降解率达到30%。当NaCl浓度高于6%,海洋活性污泥仍具有一定的活性,但仍能观察到明显的抑制作用。此外,海洋活性污泥具有比传统活性污泥更强的盐度变化抗性,甚至在低盐度下盐浓度变化时,海洋活性污泥的氨氮降解稳定性也优于传统活性污泥。     

基于优化方法的区域疏散路径规划研究

由于各种灾害的频频发生,对于区域整体及局部的疏散规划方案的研究具有迫切性和必要性。基于传统的迪杰斯特拉算法和回溯法的思想,对矩阵化的地图信息进行处理和计算,得到满足最大疏散人数、总体最短疏散路径、最短疏散时间等优化条件的优化方案。最后将这种方法运用到实际中,得出了某大学校区的路径选择方案。     

崇明岛水源地水质安全与对策

在崇明岛上最不缺的便是水,但崇明岛一年之中却有1/4左右时间被咸潮包围。咸潮期间,原水水源受到影响,崇明岛百姓饱受咸潮之苦。随着"东风西沙"水库建成,整个崇明岛剩余的20多座小水厂将关闭,只保留改造4座较大规模水厂,届时将全面切换输送来自"东风西沙"水库的原水。本文通过对崇明岛水系分析,提出崇明岛水源地以东风西沙为主要水源地,崇明南横引河以及明珠湖、北湖、东滩湖为备用水源地的建议,保障崇明岛饮用水供水安全。     

论重大突发事件应急决策气象服务

随着经济的快速增长和改革的逐渐深入,我国重大突发事件屡见不鲜,事件突发性强、社会关注度高,且部分事件受天气制约因素大,因此做好决策气象保障工作对重大突发事件管理起着非常关键的作用;同时,其服务产品领导阅读率较高,关注度和重要性不可小觑。因此立足于业务实践,对国家级气象部门的重大突发事件应急决策气象服务进行总结、分析和探讨,旨在不断提升决策气象服务产品的质量,展现气象行业的重要性,更好地服务政府和人民。     

An empirical model of soil chemical properties that regulate methane production in Japanese rice paddy soils

To understand which soil chemical properties are the best predictors of CH4 production in rice paddy soils, a model was developed with empirical data from nine types of rice soils collected around Japan and anaerobically incubated at 30 degrees C for 16 wk in laboratory conditions. After 1, 2, 4, 8, and 16 wk of incubation, CO2, CH4, and Fe(II) were measured to understand soil organic matter decomposition and iron (Fe) reduction. Available N (N ava) was also measured at the end of incubation. The results showed that decomposable C and reducible Fe are two key parameters that regulate soil CH(4) production (P CH4). There was a significant relationship between decomposable C and available N (N ava) (r2 = 0.975**). Except for a sandy soil sample, a significant relationship between total Fe (Fe total) and reducible Fe was found. From this experiment, a simple model of soil CH4 production was developed: P CH4 = 1.593N(ava) - 2.460Fe total/1000 (each unit was mg kg(-1) soil). After simulated CH4 production by two soil chemical properties as above, there was a significant consistency between model simulation and actual measurement (r2 = 0.831**).     

Residues and dynamics of pymetrozine in rice field ecosystem

The fate of pymetrozine was studied in rice field ecosystem, and a simple and reliable analytical method for determination of pymetrozine in soil, rice straw, paddy water and brown rice was developed. Pymetrozine residues were extracted from samples, cleaned up by solid phase extraction (SPE) and then determined by high-performance liquid chromatography electrospray ionization tandem mass spectrometry (LC-ESI-MS-MS). The average recovery was 81.2-88.1% from soil, 83.4-88.6% from rice straw, 87.3-94.1% from paddy water and 82.9-85.3% from brown rice. The relative standard deviation (RSD) was less than 15%. The limits of detection (LODs) of pymetrozine calculated as a sample concentration were 0.0003 mg kg⁻¹ (mg L⁻¹) for soil and paddy water, 0.001 mg kg⁻¹ for brown rice and rice straw. The results of kinetics study of pymetrozine residue showed that pymetrozine degradation in water, soil, and rice straw coincided with C = 0.194e^−0.986t, C = 0.044e^−0.099t, and C = 0.988e^−0.780t, respectively; the half-lives were about 0.70 d, 7.0 d and 0.89 d, respectively. The degradation rate of pymetrozine in water was the fastest, followed by rice straw. The highest final pymetrozine residues in brown rice were 0.01 mg kg⁻¹, which was lower than the EU’s upper limit of 0.02 mg kg⁻¹ in rice. Therefore, a dosage of 300-600 g a.i.hm⁻² was recommended, which could be considered as safe to human beings and animals.