爆炸螺栓分离对热防护系统冲击响应分析

目的考察在爆炸螺栓分离过程中,作用在TPS(热防护系统)上的冲击响应是否会导致其破坏,从而影响航天器飞行安全,对过程进行数值仿真分析。方法提出四阶段仿真方案,基于MSC.Dytran软件,采用流固耦合方法对爆炸螺栓分离过程进行动力学仿真;根据单个爆炸螺栓地面分离试验的结构进行建模和分析,获取结构响应曲线;再根据实测的冲击响应数据,对爆炸过程中炸药及JWL方程的参数等设置进行调整,获取准确爆炸螺栓的分析模型;最后应用于对真实结构中TPS(热防护系统)在分离过程里受爆炸螺栓冲击响应的动力学分析与评估。结果通过参数调整,获得的仿真模型与爆炸螺栓地面分离试验实测结果一致,证明了仿真模型的有效性和四阶段仿真方案的可行性。结论提取的真实结构爆炸螺栓分离过程中作用在TPS(热防护结构)上的最大加速度响应曲线,可用于指导TPS(热防护系统)的设计。     

应用计算机模拟的大气环境污染物浓度分析研究

大气环境污染物浓度的分析,对提高大气环境质量具有重要意义。利用计算机模拟软件对大气环境污染物浓度的分析过程进行模拟还原,分为网格划分与构建边界条件两部分。以某市2017年9月6日至2017年10月7日的监测数据为模拟数据,并通过这些数据构建大气环境污染物浓度分析模型,对当前大气环境中污染物的浓度进行分析,得出污染源与大气环境污染物程度成正相关性,依据环境污染物浓度数据分析的结果,从两方面对大气污染物浓度的分析结果进行验证,并提出大气环境污染控制的措施。     

大豆过敏原P34蛋白基因检测技术与环境污染的关系研究

环境污染易引起大豆种植区域出现过敏原P34蛋白基因变异情况,当前蛋白基因检测方法不能满足检测需求,提出基于探针引物的大豆过敏原P34蛋白基因荧光PCR定量检测技术,针对大豆过敏原特异性基因P34蛋白基因序列进行设计;通过DNA提取、浓度测定,荧光定量PCR检测,实现大豆过敏原P34蛋白基因检测。实验结果表明,所提方法能够准确检测出包括环境污染区域在内的大豆食品过敏原P34蛋白基因成分,具有很好的应用前景,满足市场监督检测的需要。     

发光细菌生物毒性抑制率优化研究

发光细菌生物毒对水生生态环境有极大的破坏作用,为保护水体环境,提出发光细菌生物毒性抑制率优化研究。完成测试样品调制;设置菌悬液特征参数,利用pH、RLU及D600进行同步检测,完成发光细菌生物毒性重现;分析磺胺类药品于根际土壤的形态分布和生态毒性,完成发光细菌生物毒性抑制率优化研究。实验证明,三种磺胺类药品对发光细菌生物毒性的相对抑制率都小于30%,为低毒性;其中有机溶剂对发光细菌生物毒性的抑制率最大,水溶态较大,结合态最小。     

环保新形势下的经济增长方式改革研究

为了均衡环保和经济增长间的关系,对环保压力下的经济增长方式进行改革。分析了资源与经济增长的关系、经济增长方式的内涵和经济增长方式的类型,介绍了国内外相关文献综述。对传统粗放型经济增长方式进行分析,发现其具有高投入、高消耗、低效益的特性,且中国单位产值所需的生产要素较其他发达国家和部分发展中国家高,但生产率与资金、资源利用率却比其他发达国家低。在面临环保压力时,中国因传统粗放型经济增长方式造成资源利用效率降低,影响经济增长,需对经济增长方式做出以下改革:转变生产函数,增加要素生产率,改变要素间相对地位;扩展价值链,使产业升级,提高附加值;改善产业结构,发展服务业。     

旅游风景区大型体育赛事的环境保护措施研究

结合旅游风景区举办大型体育赛事对环境的危害性,从减少污染排放源、从源头治理污染、加大管理层的监管力度等三方面进行环境污染监控管理。采用统计分析方法对环保治理效果进行量化评估,分析旅游风景区举办大型体育赛事期间的空气污染指数、废弃物排放数量以及水质污染情况,结合分组样本检验方法进行环保措施的有效性评价,并根据实际情况制定最优的环保措施,实现对旅游风景区的全方面环境治理,确保举办体育赛事对旅游景区的生态环境污染影响降到最低。     

基于医疗大数据的空气污染类疾病信息分析研究

世界卫生组织表示,空气污染为造成全球疾病负担的一项重要因素,能够导致心血管疾病、呼吸系统疾病等各种疾病的发生,空气污染问题已经成为公共卫生领域关注的重点问题,对基于医疗大数据的空气污染类疾病信息进行分析。利用半参数广义相加的泊松回归模型,在控制时间、长期趋势、气象因素等一些复杂条件的基础上,对2012年1月1日至2016年12月31日,某市空气中SO2、PM10和NO2等一些主要空气污染物的监测浓度值与呼吸系统疾病(肺炎以及支气管炎与哮喘)住院人数的相关性进行研究,研究结果表明,空气颗粒物PM10对患病率的影响相对于气态污染物SO2、NO2更为严重。     

8-氨基喹啉-5-偶氮-对苯酚荧光光度法测定微量铬(Ⅵ)

在盐酸介质中,铬(Ⅵ)与AQAPOH形成可被氯仿萃取的荧光化合物,其λex/λem=295nm/400nm.线性范围为0-1.0μg Cr(Ⅵ)/25ml(水相),检测限为0.7μg/L.除Mn(Ⅶ)外,常见金属离子无干扰,可在数千倍Cr(Ⅲ)存在下测定废水中微量铬(Ⅵ).初步探讨了荧光反应的机理.     

Analysing the sensitivity behaviour of two hydrology models

Recently, the New Morris Method has been presented as an effective sensitivity analysis tool for mathematical models. The New Morris Method estimates the sensitivity of an output parameter to a given set of input parameters (first-order effects) and the extent these parameters interact with each other (second-order effects). This method requires the specification of two parameters (runs and resolution) that control the sampling of the output parameter to determine its sensitivity to various inputs. The criteria for these parameters have been set on the analysis of a well-behaved analytical function (see Cropp and Braddock, Reliab. Eng. Syst. Saf. 78:77–83, 2002), which may not be applicable to other physical models that describe complex processes. This paper will investigate the appropriateness of the criteria from (Cropp and Braddock, 2002) and hence the effectiveness of the New Morris Method to determine the sensitivity behaviour of two hydrologic models: the Soil Erosion and Deposition System and Griffith University Representation of Urban Hydrology. In the first case, this paper will separately analyse the sensitivity of an output parameter on a set of input parameters (first- and second-order effects) for each model and discuss the physical meaning of these sensitivities. This will be followed by an investigation into the sampling criteria by exploring the convergence of the sensitivity behaviour for each model as the sampling of the parameter space is increased. By comparing these trends to the convergence behaviour from Cropp and Braddock (2002), we will determine how well the New Morris Method estimates the sensitivity for each model and whether the sampling criteria are appropriate for these models. It will be shown that the New Morris Method can provide additional insight into the functioning of these models, and that, under a different metric, the sensitivity behaviour of these models does converge confirming the sampling criteria set by Cropp and Braddock.     

Microbiological characteristics in a zero-valent iron reactive barrier

Zero-valent iron (Fe⁰)-based permeable reactive barriertreatment has been generating great interest for passivegroundwater remediation, yet few studies have paid particularattention to the microbial activity and characteristics withinand in the vicinity of the Fe⁰-barrier matrix. The presentstudy was undertaken to evaluate the microbial population andcommunity composition in the reducing zone of influence byFe⁰ corrosion in the barrier at the Oak Ridge Y-12 Plantsite. Both phospholipid fatty acids and DNA analyses were usedto determine the total microbial population and microbialfunctional groups, including sulfate-reducing bacteria,denitrifying bacteria, and methanogens, in groundwater andsoil/iron core samples. A diverse microbial community wasidentified in the strongly reducing Fe⁰ environment despitea relatively high pH condition within the Fe⁰ barrier (up topH 10). In comparison with those found in the backgroundsoil/groundwater samples, the enhanced microbial populationranged from 1 to 3 orders of magnitude and appeared to increase from upgradient of the barrier to downgradient soil. Inaddition, microbial community composition appeared to change overtime, and the bacterial types of microorganismsincreased consistently as the barrier aged. DNA analysisindicated the presence of sulfate-reducing and denitrifyingbacteria in the barrier and its surrounding soil. However, theactivity of methanogens was found to be relatively low,presumably as a result of the competition by sulfate/metal-reducing bacteria and denitrifying bacteria because of the unlimited availability of sulfate and nitrate in the site groundwater. Results of this study provide evidenceof a diverse microbial population within and in the vicinity ofthe iron barrier, although the important roles of microbial activity, either beneficially or detrimentally, on the longevityand enduring efficiency of the Fe⁰ barriers are yet to be evaluated.