水体中挥发酚自净模式研究

采用均匀设计法设计实验，当实验条件曝气强度（ml/min)、酚的起始浓度（mg/l)、加入底泥量（g)、加入10%HgCl2量（ml)、处理温度（℃）、处理时间（小时）分别用X1、X2、X3、X4、X5、X6表示时，得到它们与含酚污水中总酚去除率Y和挥发除去酚浓度C的关系分别为：Y=-100.67 21.835Lnx1 17.920Lnx2 1.595√x3-0.124x4 1.131x5-1.086e^x6;C=-3.308 0.614Lnx1 0.307Lnx2 0.179√x3 5.100*10^-2x4 2.369*10^-2x5-0.692Lnx6。并讨论了酚在水体中自净的规律。     

浅谈水电工程中混凝土生产系统环保措施

以现在水电工程建设中的混凝土生产系统为基础,从水土保护保持、废水、废气、废油排放,粉尘污染,噪声污染,交通运输,废料,生活废水,垃圾等方面为工程提供混凝土生产系统的环保控制措施.     

Effectiveness evaluation of water-sprinkling in controlling urban fugitive road dust based on TRAKER method: A case study in Baoding, China

Fugitive road dust (FRD) contributes a great deal to urban rainwater and air pollution and is commonly controlled by water-sprinkling in most Chinese cities. However, there is a lack of information on its effectiveness. We used the Testing Re-entrained Aerosol Kinetic Emissions from Roads (TRAKER) method to monitor different types of roads in Baoding city before and within 1 hr after water-sprinkling and obtained the road dirtiness index (a) and PM concentration in the road environment ($T_{\mathrm{T}}^{*}$), to evaluate the removal efficiency for PM deposited on the road surface (${\eta }_a$) and the reduction efficiency for the PM concentration in the road environment (${\eta }_{\text{PM}}$). The results give that the ${\eta }_a$ for three types of roads is ranked: branch road (87%-–100%) > major arterial road (80%-83%) > minor arterial road (68%-77%), and the ${\eta }_{\text{PM}}$ ranked: minor arterial road (70%) > branch road (46%-58%) > major arterial road (37%-53%). The ${\eta }_a$ and ${\eta }_{\text{PM}}$ varied non-linearly with time and presented a quadratic curve. The average effective control time (${\eta }_{\mathit{a}}$> 0) was 62 min on the major and minor arterial roads, and much longer than 1 hr on branch roads. The ${\eta }_{\text{PM}}$ values diminished completely by 72 min on average from the end of sprinkling for the three types of roads. Water-sprinkling can remove PM₁₀ particles from the road surface and reduce their concentration in the road environment more thoroughly than PM_2.5. Our findings could be helpful for controlling urban FRD emissions more efficiently and precisely.     

典型北方高碱度微污染水体强化混凝的示范研究

以高碱度、受有机物污染的典型北方水体为例,探索适宜的强化混凝技术.在水质调查的基础上,提出适合水质特征的强化混凝目标.研究了高碱度水体强化混凝技术方法.研究表明,可以通过3条技术途径提高水体中有机物的去除效率.其一在混凝前优化pH,促进絮凝剂水解形成中聚体,AlCl3在pH 6左右,FeCl3在pH 5左右时,有机物去除率可以提高一倍左右;其二是强化沉淀软化;其三是絮凝剂优化.结合我国实际情况,通过对传统絮凝剂进行改性,研制出了适合我国北方水质特征的高效絮凝剂,能较传统絮凝剂将有机物去除率提高30%以上.     

预处理的铜绿假单胞菌对Cu2+的生物吸附研究

从电镀废水污泥中分离，纯化获一高抗铜菌株，经鉴定为铜绿假单胞菌（Pseudomonas aeruginosa)，采用不同浓度盐酸对铜绿假单胞菌进行预处理，同时考察了不同因素如溶液的pH，温度，摇床转速，接触反应时间对未处理菌和预处理的影响，结果表明，经0．1NHCl预处理的菌体具有最佳吸附效果，pH、摇床转速对菌体的吸附具有较显著影响，温度对菌体吸附影响不大。     

研究单位压边力值对板料成形性能的影响

主要介绍板料在拉深成形过程中单位压边力值对板料成形性能的影响。研究方法采用仿真技术 ,指出板料在成形过程中如按最初设定的单位压边力值进行成形 ,那么 ,板料成形过程中单位压边力值将逐渐增大 ,严重影响板料成形极限。如果采用控制板料在成形过程中压边圈下坯料的单位压边力值 ,将提高板料成形极限。其结论为生产现场提高板料成形性能和表面质量提供了一种可实施的方法。     

深圳:向"雨洪"要水

“到2020年，深圳本地水资源可供水量占总供水量的比重将由目前的27％提高到45％，新增雨洪资源利用量达4．9亿立方米。”这是不久前通过专家鉴定的《深圳雨洪资源利用规划研究》（以下简称规划）提出的目标。     

1952-2016年长江经济带天然与人为氮输入时空演变

过量氮输入是水体氮污染的关键驱动因子，解析氮输入的结构和时空变化模式成为氮素环境管理的重要基础和难点.基于1952—2016年长江经济带各地区氮活动数据，分别构建了天然氮输入和人为氮输入模型，评估了氮输入负荷的时空变化特征.结果表明：①长江经济带氮输入负荷总体越过EKC曲线拐点进入由增长向下降的发展阶段，拐点出现在人均GDP为35777~36299元·人^-1时，发生时间为"十二五"时期，主要原因是化肥和食物输入下降；②氮输入负荷存在显著的时空差异，东部地区表现为倒U型，中部为S型，西部为J型，表明氮负荷存在从东向西的空间转移，西部地区成为氮输入负荷增长的热点地区，这与东部地区化肥施用量下降有关；③人为输入是长江经济带氮输入的主要来源，输入量及其占总输入的比例均呈现显著的增长趋势，空间上表现为从西到东部逐步递增的变化规律，与氮驱动力分布一致；④植被的多年平均固氮量为1771 kg·km^-2·a^-1，其中，非农作物的固氮速率为763 kg·km^-2·a^-1，植被固氮量的年际波动较小，天然输入对长江经济带总体氮输入影响较小.     

Decomplexation of Cu-1-hydroxyethylidene-1,1-diphosphonic acid by a three-dimensional electrolysis system with activated biochar as particle electrodes

The feasibility of decomplexation removal of typical contaminants in electroplating wastewater, complexed Cu(II) with 1-hydroxyethylidene-1,1-diphosphonic acid (Cu-HEDP), was first performed by a three-dimensional electric reactor with activated biochar as particle electrodes. For the case of 50 mg/L Cu-HEDP, Cu(II) removal (90.7%) and PO initial pH 7, acid-treated almond shell biochar (AASB) addition 20 g/L, and reaction time 180 min, with second-order rate constants of 1.10 × 10⁻³ and 1.94 × 10⁻⁵ min⁻¹respectively. The growing chelating effect between Cu(II) and HEDP and the comprehensive actions of adsorptive accumulation, direct and indirect oxidation given by particle electrodes accounted for the enhanced removal of Cu-HEDP, even though the mineralization of HEDP was mainly dependent on anode oxidation. The performance attenuation of AASB particle electrodes was ascribed to the excessive consumption of oxygen-containing functionalities during the reaction, especially acidic carboxylic groups and quinones on particle electrodes, which decreased from 446.74 to 291.48 µmol/g, and 377.55 to 247.71 µmol/g, respectively. Based on the determination of adsorption behavior and indirect electrochemical oxidation mediated by in situ electrogenerated H₂O₂ and reactive oxygen species (e.g., •OH), a possible removal mechanism of Cu-HEDP by three-dimensional electrolysis was further proposed.     

高锰酸盐指数测定中校正系数K值的变化验证

运用数理统计方法,验证了高锰酸盐指数测定的校正系数K值在4～5h内不会随时间和水样的变化而变化,K值不必每个样品都测定。