应用瞬变电磁法防治煤矿顶板砂岩水的实践

研究了华北型煤田顶板砂岩的赋水规律,总结出顶板砂岩水的综合防治方法。应用瞬变电磁法探测某煤矿顶板岩层发育的含(导)水构造,为安全生产工作提供了技术指导。     

管制员安全能力模型研究

为准确评价管制员安全能力,基于能力的定义和管制员工作职责,界定管制员安全能力的内涵;依据该内涵及其工作特性,建立由身体素质、业务素质和意识3个结构维度组成的管制员安全能力模型。其中,身体素质包括生理状况和心理状况;业务素质包括教育状况、培训状况、技能状况和经验状况;意识包括安全意识和工作意识。在各项指标性质差异较大情况下,利用功效系数法实现评价指标的标准化以减小误差,客观反映指标情况,同时采用G1-法和熵值法集成的主客观综合赋权法确定指标的权重,在一定程度上弥补主客观单一赋权的不足,最后通过逼近理想解排序法(TOPSIS)评价管制员安全能力。结果表明,按照从大到小排序对管制员安全能力的影响因素依次为意识、身体素质和业务素质。就对所论能力的影响而言,心理状况强于生理状况;技能状况强教育、培训和经验状况;安全意识对意识的影响大于工作意识。     

不同物质对铬价态测定结果的影响

采用单波长法和双波长法,分别考察了KH2PO4、H3PO4、H2SO4、KNO3、牛肉膏和蛋白胨对Cr(III)和Cr(VI)质量浓度测定的影响。结果显示,Cr(III)和Cr(VI)在测量中是相互影响的,并且Cr(III)对Cr(VI)影响较显著。在单波长法测定中,牛肉膏、蛋白胨及2种酸对Cr(III)和Cr(VI)的影响较钾盐对其影响更为显著,H3PO4和H2SO4对Cr(III)和Cr(VI)的特征吸收峰值影响最大,降低幅度在20%～50%。这些物质对双波长法测定Cr(VI)几乎没有影响;但对Cr(III)测定中,H2SO4和H3PO4的影响较大,其相对误差分别为14.57%和8.87%,其余物质产生的相对误差均小于1.6%。因此,双波长法可用于生物样品中Cr(III)和Cr(VI)的测定,线性范围分别为0～160 mg/L和0～80mg/L。     

采煤工作面漏风通道参数研究与应用

采煤工作面漏风会导致采空区缓慢自燃氧化以及有毒有害气体涌入工作面,造成采空区自然发火及工作面工作人员中毒窒息的可能性.工作面不同进风风量下工作面漏风情况会不同.为了具体研究工作面不同进风风量下的漏风情况,测定了元堡煤矿1901工作面停采期间各漏风通道的漏风量,建立了工作面漏风通道网络模型;根据风网解算原理及风阻计算公式计算出各分支风阻及风量值;利用风网解算软件计算出不同风量下工作面漏风通道的风量值.结果发现:元堡煤矿1901工作面风量在500 - 1500m3/min范围内变化时各漏风通道风量占工作面总进风量的比重几乎不变;采空区两巷由于已经打好密闭,漏风较小;工作面中部由于老顶来压漏风量较大,是堵漏风重点.     

北京地铁岛式站台噪声的初步研究

为研究北京岛式站台噪声水平及噪声特点,选取了北京地铁2号线和5号线的10个岛式站台进行了实地的测量,从噪声级以及频谱角度对测量结果进行了分析。结果显示,测量时间内的LAeq,max都高于标准限值80dB(A)。使用独立样本t检验的结果得出,2号线与5号线在LAeq以及LAeq,max上不存在显著差异(P>0.05),说明2号线和5号线噪声在相近的水平上。通过噪声频谱的时程曲线也直观的得出列车在进出站过程中噪声级大于80dB(A),无列车通过且不受相反轨道列车影响时的背景噪声在65dB(A)左右,受影响时在70dB(A)左右。倍频程频谱分析得出,地铁站台噪声具有明显的中频特征。进一步分析,2号线和5号线站台都存在若干的主频,其基频和谐频分别为63、250和1kHz。     

中美实施全球化学品统一分类和标签制度政策对比和分析

对中美实施全球化学品统一分类和标签制度(GHS)的基本情况进行了研究,分别从实施GHS的框架体系、实施GHS的时间节点、GHS的危险类别、符合GHS要求的SDS和标签四个角度,对中美实施GHS的政策进行对比.通过分析,得出我国目前实施GHS主要存在四个方面的问题:各方利益难以协调,缺乏实施GHS的综合性法律法规,实施GHS缓冲期的设置存在问题,“积木原则”尚未合理运用.结合美国实施GHS的做法,为我国实施GHS提出四方面建议,即推动我国GHS配套法律法规体系建设,编制实施GHS的指南文件,灵活合理利用“积木原则”,关注危险化学品全生命周期的安全.     

环境风下太阳能PV板对流散热特性实验研究

在实验室条件下,通过建立环境风道,采用电加热的方式,对PV板在环境风下的对流散热损失进行实验研究。考察倾角a、风向角θ、风速V以及热流密度q对PV板表面对流散热特性的影响,得到了不同条件下PV板表面平均对流热损失努谢尔特数Nu的变化规律。结果表明,在任意风向角下,当风速较小时,Nu对PV板倾角变化并不敏感,但是随着风速的增大,倾角对Nu的影响不断增大。当PV板在背风侧时,Nu随着倾角的增大有一个迅速减小的过程;此外,以风速1 m/s为转折点,低风速下Nu随风速的变化规律与高风速下明显不同。     

Potential CO2 intrusion in near-surface environments: a review of current research approaches to geochemical processes

Environmental Geochemistry and Health - Carbon dioxide (CO2) capture and storage (CCS) plays a crucial role in reducing carbon emissions to the atmosphere. However, gas leakage from deep storage...     

Compositional data analysis and geochemical modeling of CO2–water–rock interactions in three provinces of Korea

Environmental Geochemistry and Health - The CO2-rich spring water (CSW) occurring naturally in three provinces, Kangwon (KW), Chungbuk (CB), and Gyeongbuk (GB) of South Korea was classified based...     

Source attribution for mercury deposition with an updated atmospheric mercury emission inventory in the Pearl River Delta Region,China

Estimated anthropogenic Hg emission was 11.9 tons in Pearl River Delta for 2014. Quantifying contributions of emission sources helps to provide control strategies. More attentions should be paid to Hg deposition around the large point sources. Power plant, industrial source and waste incinerator were priorities for control. A coordinated regional Hg emission control was important for controlling pollution. We used CMAQ-Hg to simulate mercury pollution and identify main sources in the Pearl River Delta (PRD) with updated local emission inventory and latest regional and global emissions. The total anthropogenic mercury emissions in the PRD for 2014 were 11,939.6 kg. Power plants and industrial boilers were dominant sectors, responsible for 29.4 and 22.7%. We first compared model predictions and observations and the results showed a good performance. Then five scenarios with power plants (PP), municipal solid waste incineration (MSWI), industrial point sources (IP), natural sources (NAT), and boundary conditions (BCs) zeroed out separately were simulated and compared with the base case. BCs was responsible for over 30% of annual average mercury concentration and total deposition while NAT contributed around 15%. Among the anthropogenic sources, IP (22.9%) was dominant with a contribution over 20.0% and PP (18.9%) and MSWI (11.2%) ranked second and third. Results also showed that power plants were the most important emission sources in the central PRD, where the ultra-low emission for thermal power units need to be strengthened. In the northern and western PRD, cement and metal productions were priorities for mercury control. The fast growth of municipal solid waste incineration were also a key factor in the core areas. In addition, a coordinated regional mercury emission control was important for effectively controlling pollution. In the future, mercury emissions will decrease as control measures are strengthened, more attention should be paid to mercury deposition around the large point sources as high levels of pollution are observed.