废弃钻井泥浆的固化处理

废弃钻井泥浆的处理是油气勘探与开发工业中人们极为关注的。文章在分析废弃钻井泥浆性质的基础上，通过化学稳定与固化处理试验研究得出以水泥为主，烟炭，石灰等为添加剂的固化剂配方，实验结果表明，经固化处理的废弃泥浆，其固化产物重金属浸出率低，稳定性好，具有一定的抗氧强度，从而能有效地降低废弃泥浆对环境的污染危害，文中还对各种辅加剂对固化效果的影响进行了分析。     

桥梁抗震主动控制的稳定性研究

主动控制应用于实际结构 ,需要考虑其控制效果的稳定性问题 ,为此 ,分析了桥梁抗震主动控制中可能出现的计算模型误差和系统误差 ,并讨论了应用H2 控制和H∞ 控制两种算法的稳定性。理论分析和仿真计算表明 ,在频谱特性不同的地震激励下 ,H2 控制和H∞ 控制两种算法都可以取得满意的控制效果 ;对于计算模型误差 ,H2 控制和H∞ 控制两种算法的鲁棒性相当 ,控制效果稳定 ;对于系统误差 ,H∞ 控制算法比H2 控制算法鲁棒性强 ,在较大的误差下可以保持控制效果的稳定性     

大中城市震害预测与辅助决策的空间分析

利用GIS的空间分析功能，对大中城市防震减灾示范研究成果进行了空间区划分析，给出了城市高危害街区的计算方法和结果，同时给出了各种结构类型房屋破坏面积、人员伤亡和无家可归人口数在各个街区的空间分布结果，以及基于此空间分布结果的医疗救护、人员疏散和物资供应等辅助决策分析。该分析的主要意义在于能充分了解大中城市潜在震害的空间分布，为震前采取相应预防措施和震后开展应急救灾工作提供了方便。     

对华北GPS监测区近期地壳应变连续分布的估计

直接利用华北ＧＰＳ监测网各个测点的位移观测值,借助高斯型位移协方差函数通过最小二乘配置建立连续分布的位移函数,并根据应变与位移的偏导关系,对华北ＧＰＳ监测区１９９２～１９９５年、１９９５～１９９６年最大剪应变及面膨胀连续分布进行估算,得到其应变场动态图像。     

近断层强震速度脉冲效应及连续梁桥减隔震特性分析

应用非线性时程分析的方法 ,对于减、隔震连续桥梁在近场地震作用下的有效性和响应特性 ,作了深入的研究。通过有代表性的脉冲型近场强震记录时程分析 ,提出了用速度脉冲峰值及其周期之积来表示速度脉冲能量的方法 ,计算表明近场地震速度脉冲波能近似表征地震动破坏能力的大小 ,它和桥梁结构承受的地震响应大体成正比例关系。铅芯橡胶隔震支座在近场地震作用下仍然适用 ,但对于个别脉冲型强震记录效果不够明显 ,支座参数有必要进行优化。     

50所长江沿岸高校实验废液排放情况调查与分析

目的：了解长江沿岸高校实验室废液排放情况及现状。方法：以问卷调查方式，对长江沿岸高校实验室操作程序、管理制度、废液排放情况进行调查。结果：38％的高校管理制度不完善，68％的高校实验操作不规范，44％的学校环保意识宣传不到位，62％的高校实验废液未处理就直接排放。结论：高校实验室正成为长江生态环境恶化的污染源．我国应制定和完善相关法律，加强实验废液处理，杜绝高校成为长江水质污染新的根源。     

废钻井液固化实验研究

利用经实验筛选的固化剂配方对废钻井液进行了固化处理的室内配方研究。结果表明,经该固化剂配方处理后的固结材料在水中浸泡5d后的浸出液在色度、化学需氧量、pH值、石油类、悬浮物含量和重金属含量等指标方面可达到国家《污水综合排放标准》(GB8978-1996)中的二级标准。     

Effect of ozone injection on the long-term performance and microbial community structure of a VOCs biofilter

For biofilters treating waste gases containing volatile organic compounds(VOCs), biomass accumulation is a common problem which will induce bed clogging and significant decrease in VOCs removal efficiency during long-term operation. In this study, ozone injection was developed as a biomass control strategy, and its effects on the biofilter performance and the microbial community structure were investigated in long-term operation. Two biofilters,identified as BF1 and BF2, were operated continuously for 160 days treating gaseous toluene under the same conditions, except that 200 mg/m3 ozone was continuously injected into BF1 during days 45–160. During the operation period, ozone injection did not change the toluene removal efficiency, while the pressure drop of BF1 with ozone injection was significantly lowered compared with BF2. The wet biomass accumulation rate of BF1 was 11 g/m~3/hr, which was only46% of that in BF2. According to the carbon balance result, ozone injection also increased the toluene mineralization rate from 83% to 91%, which could be an important reason for the low biomass accumulation. The PMA-q PCR result indicated that ozone injection increased the microbial viability of the biofilm. The high-throughput sequencing result also revealed that the dominant phyla and genera were not changed significantly by ozone injection, but some ozonetolerant genera such as Rhodanobacter, Dokdonella and Rhodococcus were enhanced by ozone exposure. All the results verified that ozone injection is capable of sustaining the long-term performance of biofilters by lowering the biomass accumulation, increasing the microbial viability and changing the microbial community structure.     

Mobility and sulfidization of heavy metals in sediments of a shallow eutrophic lake, Lake Taihu, China

The technique of DGT (diffusive gradients in thin films) using three diffusive gel thicknesses was applied to estimate the mobility and bioavailability of heavy metals in sediments and porewater of Lake Taihu, China. The DGT results showed significantly positive correlations between Co, Pb, Cd and Mn, and Ni and Fe concentrations in porewater. Cu and Zn showed a significantly negative correlation with Mn, due to Cu combination with carbonates and Zn derived from agricultural pollution, respectively. The rank order of average concentrations of Co, Ni and Cd at each station was DGT_1.92 > DGT_0.78 > DGT_0.39, suggesting stronger resupply from sediments to porewater when using thicker diffusive gels. Comparing centrifugation and DGT measurements, Co, Ni and Cd are highly labile; Mn and Fe are moderately labile; and Cu, Zn and Pb are slightly labile. The variations of AVS concentrations in sediment cores indicate that metal sulfides in deeper layers are easily diffused into surface sediments.