基于噪声指数的首都经济贸易大学校园声环境评价

文章在对首都经济贸易大学校园进行声功能区环境噪声监测的基础上,分析和计算了各区域测点噪声超标值（△LAeq）、噪声指数（LKZ）和噪声污染指数（PN）;从强度和影响人群人数两个角度评价校园声环境质量。结果表明,首都经济贸易大学校园声环境质量处于较差的水平,噪声强度超标率达到82％;据此,课题对校园噪声污染现状进行了影响分析和声环境质量的等级评定,最后针对污染现状提出了相关措施和建议。     

高温下好氧污泥接种启动UASB的试验研究

采用高温UASB处理柠檬酸废水,研究利用好氧脱水污泥接种启动高温UASB的可行性。试验结果表明,在温度55℃,HRT为6天的条件下,UASB反应器能降解的柠檬酸废水浓度为10000mg/L,容积负荷为1.67gCOD/(L.d),柠檬酸废水的去除率达到90%以上。     

一次环境污染司法鉴定的测试与分析

受人民法院的委托,环境监测部门对一起汽车尾气致人死亡案件的现场进行大气污染物和空气质量的模拟测试。测试表明,在密闭的车库内,汽车外和汽车内CO浓度都会迅速增加,达到致人死亡的浓度,O2浓度迅速减少,最终使汽车发动机熄火。测试为司法部门提供案件审理现场空气质量数据,也提醒人们不要在密闭的车库内开启汽车空调取暖或纳凉休息。     

徐州市气象因子与空气质量和PM_（10）浓度的相关性分析

通过对徐州市空气质量及其对应的气象因子进行统计分析,得出空气质量与相对湿度、风速,降水等气象因子的关系。分析特殊气象天气出现时空气中主要污染物PM10的变化规律.得到一些初步结果,为减轻和防止污染提供参考。     

土地利用总体规划环境影响评价技术方法的研究

从国内外土地利用总体规划环境影响评价的技术方法研究出发,总结了各技术方法的优势和缺点。最后提出了完善土地利用总体规划环境影响技术方法的建议。     

条形荷载下三明治形加筋土挡墙的变形特性分析∗

为了研究条形荷载作用下三明治形混合填土方式对加筋土挡墙变形特性的影响,采用 FLAC3D建立了数值计算模型,分析了三明治形加筋土挡墙的黏土弹性模量 E1、砂土弹性模量 E2、砂土厚度 d、筋材长度 L 以及荷载距面板距离 D 对挡墙变形特性的影响。结果表明：相对于加筋黏土挡墙,三明治形加筋土挡墙变形大幅减小,减少其墙顶沉降约 32%,减少面板位移约 44%;其土压力分布规律为墙后水平土压力大体上随填土深度的增加而增大;适当增大黏土弹性模量有利于减小挡墙顶面差异沉降;砂土存在一个最优弹性模量,使得面板水平位移最小;三明治形加筋土挡墙存在一个最优砂土厚度,使得三明治加筋土挡墙工作性能最佳;当 L/H≥0.7 时,继续增加筋材长度或当 D/H≥0.3 时,继续增大荷载距面板距离对挡墙影响相对较小。     

软土地区高墩梁桥抗震支座选型及横向约束构造研究∗

为了研究软土地区地震作用下高墩先简支后桥面连续梁桥的支座选型及横桥向抗震约束问题,选取了普通板式橡胶支座、钢阻尼滑板支座、LNR 橡胶支座和 HDR 高阻尼支座四种支座类型,以软土地区某(4×30)m 跨径高墩先简支后桥面连续梁桥为例,进行了延性抗震体系和减隔震体系抗震设计对比以及设置挡块的横桥向抗震约束效果研究。结果表明：软土地区高墩先简支后桥面连续梁桥墩柱配筋率主要由 E1 地震作用下墩底截面偏心受压检算工况决定,采用减隔震体系并不能降低桥墩配筋率。通过对采用四种不同支座桥梁的内力、墩梁相对位移以及配筋率方面综合分析可知,软土地区高墩先简支后桥面连续梁桥的周期较长,这类桥梁抗震关键问题是防止落梁、减小墩顶位移。采用普通板式橡胶支座并合理的设计纵横向防落梁装置的延性抗震体系更适宜于软土地区高墩梁式桥,合理设计抗震挡块可以起到很好的横向约束作用,避免横向落梁的发生。     

Expression of sulfur uptake assimilation-related genes in response to cadmium, bensulfuron-methyl and their co-contamination in rice roots

The responses of sulfur （S） uptake assimilation-related genes＇ expression in roots of two rice cultivars to cadmium （Cd）, bensulfuron-methyl （BSM） and their co-contamination （Cd＋BSM） were investigated by gene-chip microarray analysis and quantitative real-time PCR （QRT-PCR） technology. Treatments of Cd and Cd＋BSM induced expression of sulfate transporter and permease genes, and promoted sulfate uptake in rice roots. Cd＋BSM could alleviate Cd toxicity to cv. Fengmeizhan seedlings, probably due to Cd＋BSM promoting greater S absorption by seedlings. Cd and Cd＋BSM induced expression of sulfate assimilation-related genes, and thus activated the sulfur assimilation pathway. Cd and Cd＋BSM induced expression of phytochelatin synthase and metallothionein genes, and induced expression of glutathione S-transferases （GSTs）, glutathione synthase （GS） and S- containing antioxidation enzyme genes, which detoxified Cd2＋. It is suggested that （to cope with the toxicity of Cd, BSM and their co-contamination） the S uptake and assimilation pathway was activated in rice roots by increased expression of related genes, thus enhancing the supply of organic S for synthesis of Cd or BSM resistance-related substances.     

Comparison of quartz sand, anthracite, shale and biological ceramsite for adsorptive removal of phosphorus from aqueous solution

The choice of substrates with high phosphorus adsorption capacity is vital for sustainable phosphorus removal from waste water in constructed wetlands. In this study, four substrates were used： quartz sand, anthracite, shale and biological ceramsite. These substrate samples were characterized by X- ray diffractometry and scanning electron microscopy studies for their mineral components （chemical components） and surface characteristics. The dynamic experimental results revealed the following ranking order for total phosphorus （TP） removal efficiency： anthracite 〉 biological ceramsite 〉 shale 〉 quartz sand. The adsorptive removal capacities for TP using anthracite, biological ceramsite, shale and quartz sand were 85.87, 81.44, 59.65, and 55.98 mg/kg, respectively. Phosphorus desorption was also studied to analyze the substrates＇ adsorption efficiency in wastewater treatment as well as the substrates＇ ability to be reused for treatment. It was noted that the removal performance for the different forms of phosphorus was dependent on the nature of the substrate and the adsorption mechanism. A comparative analysis showed that the removal of particulate phosphorus was much easier using shale. Whereas anthracite had the highest soluble reactive phosphorus （SRP） adsorptive capacity, biological ceramsite had the highest dissolved organic phosphorus （DOP） removal capacity. Phosphorus removal by shale and biological ceramsite was mainly through chemical adsorption, precipitation or biological adsorption. On the other hand, phosphorus removal through physical adsorption （electrostatic attraction or ion exchange） was dominant in anthracite and quartz sand.     

Enhanced struvite recovery from wastewater using a novel cone-inserted fluidized bed reactor

The feasibility of struvite recovery at low （12.5 mg/L） and high （120 mg[L） phosphorus concentrations was studied by constructing a novel fluidized bed reactor with cones （FBRwc） and without cones （FBRwoc）. The crystallization process was continuously operated for 133 days under different hydraulic retention times （HRT = 1-10 hr）, pH （7.5-10）, and molar ratios of Mg/P （0.75-1.75）, N/P （1-10） and Ca/Mg （0-2）. The optimum operating conditions of HRT, pH, Mg/P and N/P molar ratios were found to be 2 hr, 9, 1.25, and 7.5, respectively. Under these optimum conditions, the phosphorus precipitation efficiencies of FBRwc were 93% for low and 98% for high phosphorus influent; however, the efficiencies were 78% and 81% for FBRwoc, respectively. Due to crystal losses at each junction （17%-31%）, the crystal recovery efficiency of FBRwoc was relatively low （47%-65%） for both influent concentrations. However, the losses were minimal in FBRwc, which showed 75% and 92% crystal recovery for low and high phosphorus concentrations, respectively. At low calcium concentration, crystal chemical analysis showed the product to be pure struvite （〉 99%）. The scanning electron microscope and X-ray diffraction results further confirmed that the crystal recovered from FBRwc contained pure struvite, which could be considered a high quality fertilizer. Except HRT, all parameters （pH, Mg/P, N/P and Ca/Mg） were found to be influencing factors for FBRwc performance. Overall, inserting cones in each part of the reactor played a significant role in enhancing struvite recovery from a wide range of phosphorus-containing wastewater.