北部湾海域江豚体内重金属含量及分布

应用原子吸收分光光度计对北部湾海域江豚的肌肉、脂肪、肝脏、胰脏、心脏、肺脏、肾脏、胃和肠管道等器官组织样品中的Cd、Cu、Zn、Pb、Cr、Ni、 Fe、Mn、Hg和As的含量进行测定,并使用标准物作了对照分析.结果显示,江豚体内各器官组织中的Cd、Cu、Zn、Pb、Cr、Ni、Fe、Mn、Hg和As的平均含量分别为(0.05～37.9)×10-6、(6.20～101.9 )×10-6、(24.38～181.5) ×10-6、(ND～1.85) ×10-6、(10.60～13.35)×10-6、(1.68～3.15)×10-6、(111.45～1413.8)×10-6、(0.35～12.43)×10-6、(0.21～34.36)×10-6和(0.28～3.81)×10-6(干重).江豚体内重金属含量高低的基本趋势是Fe>Zn>Cu>Cr>Ni>Cd>Mn> Hg>As>Pb.肝、肾脏等内脏器官中的重金属含量普遍高于肌肉及脂肪组织中的含量;胃组织中没有测出Pb的存在.与渤海和黄海江豚比较,北海湾海域江豚体内各种重金属的含量介于渤海和黄海江豚之间,说明该地区海域已受到重金属污染.     

基于国内实测燃煤电厂烟气汞排放估算的不确定度

参照测量不确定度评定与表示的国家技术规范,基于近年来我国燃煤电厂常规污控设备协同脱汞的现场测试数据(文献报道和实测值)及各省原煤w(汞)的实测值,初步构建了国内燃煤电厂烟气汞排放不确定度的计算方法,并以2010年的燃煤量、污控方式布局为基础,计算了该年度汞排放的不确定度. 结果表明:2010年我国燃煤电厂烟气汞排放的总不确定度为48.8t,占平均排放总量的34.3%;其中60.2%源于污控设备脱汞效率的不确定度,39.8%源于原煤w(汞)的不确定度;采用ESP(静电除尘)、ESP+WFGD(静电除尘+湿法脱硫)、SCR+ESP+WFGD(选择性催化还原脱硝+静电除尘+湿法脱硫)和FF(袋式除尘)大气污控组合的机组各存在6.0、32.2、9.7和0.9t的烟气汞排放不确定度,分别占各对应机组烟气汞排放量的19.3%、32.8%、84.6%和53.6%,其中SCR+ESP+WFGD污控组合烟气汞排放的相对不确定度最大. 随着我国烟气脱硝工作全面推行,2015年以后,SCR+ESP+WFGD污控措施(组合)的机组所占比例将会提高到66%以上,如果仍以现有数据为基础,则来自SCR+ESP+WFGD污控措施(组合)机组的烟气汞排放不确定度将会大幅增加,因此急需增加对该类装置脱汞效率的实测样本数量.      

1996年2月3日云南丽江7.0级地震震害调查和损失评估

对1996年2月3日云南丽江7．0级地震进行了震害调查和损失评估，此次地震造成了重大灾害，死亡309人，重伤4070人，轻伤12987人。房屋破坏、室内财产和生命线工程的直接经济损失总计为30．49亿元。     

玉米联合固氮耐铵工程菌Enterobacter gergoviae-7(E7)在不同载体及玉米根际的存活规律

以草炭、腐植酸和水为载体接种玉米联合固氮耐铵工程菌Enterobactergergoviae -7(以下简称E7)制备菌剂 ,在常温条件下放置 5dE7菌数在载体内明显增加 ,1mo后E7菌数略有下降 ,2mo后E7菌数急剧下降 ,半年后E7活菌数降至n(CFU) =5 .0× 10 6～ 93.0× 10 6g- 1 ,3种菌剂中菌数的变化趋势一致 ,E7菌数残留量 :草炭菌剂 >液体菌剂 >腐植酸菌剂 ;用草炭菌剂拌种在生长 2 0d的玉米根区 (包括根系和根际土壤 ) ,E7菌数达到最大值 ,以后E7菌数下降 ,至灌浆期玉米根际未能检测到E7;不同接种方法试验结果表明 ,以草炭菌剂拌种 +种下 2cm穴施使玉米获得最高增产率 .(表 3)     

Integrated energy view of wastewater treatment: A potential of electrochemical biodegradation

• Energy is needed to accelerate the biological wastewater treatment. • Electrical energy input in traditional technology is indirect and inefficient. • Direct injection of electricity can be a game changer to maximize energy efficiency. • Microbial electrochemical unit for decentralized wastewater treatment is proposed. It has been more than one century since the activated sludge process was invented. Despite its proven stability and reliability, the energy (especially the electrical energy) use in wastewater treatment should evolve to meet the increasingly urgent demand of energy efficiency. This paper discusses how the energy utilized in conventional biological wastewater treatment can be altered by switching the indirect energy input to a direct electricity injection, which is achieved by the electrode integration providing extra thermodynamic driving force to biodegradation. By using electrodes instead of oxygen as terminal electron acceptors, the electrical energy can be utilized more efficiently, and the key of direct use of electrical energy in biodegradation is the development of highly active electroactive biofilm and the increase of electron transfer between microbes and the electrode. Furthermore, the synergy of different microbial electrochemical units has additional benefit in energy and resource recovery, making wastewater treatment more sustainable.     

Characteristics of the stabilized/solidified municipal solid wastes incineration fly ash and the leaching behavior of Cr and Pb

Fly ash is a hazardous byproduct of municipal solid wastes incineration (MSWI). An alkali activated blast furnace slag-based cementitious material was used to stabilize/solidify the fly ash at experimental level. The characteristics of the stabilized/solidified fly ash, including metal leachability, mineralogical characteristics and the distributions of metals in matrices, were tested by toxic characteristic leaching procedure (TCLP), X-ray diffraction (XRD) and scanning electron microscopy-energy dispersive spectrometer (SEM-EDS) respectively. Continuous acid extraction was utilized to extract metal ions and characterize their leaching behavior. The stabilization/solidification procedure for MSWI fly ash demonstrates a strong fixing capacity for the metals by the formation of C-S-H phase, hydrated calcium aluminosilicate and ettringite. The stabilized/solidified fly ash shows a dense and homogeneous microstructure. Cr is mainly solidified in hydrated calcium aluminosilicate, C-S-H and ettringite phase through physical encapsulation, precipitation, adsorption or substitution mechanisms, and Pb is mainly solidified in C-S-H phase and absorbed in the Si-O structure.     

循环式超声强化光催化降解双酚A

设计了一种循环式超声强化光催化反应器,以TiO2作为光催化剂,研究了超声功率、TiO2加入量、循环液流速和空气流量对双酚A(BPA)降解效果的影响。实验结果表明:超声与光催化过程在循环式超声强化光催化反应器中实现了较好的协同效应;在初始BPA质量浓度为20.0mg/L、超声功率为600W、TiO2加入量为7g/L、循环液流速为4.05×10-2m/s、空气流量为200mL/min的条件下,反应150min后,BPA降解率可达90.5%,溶液中剩余BPA质量浓度仅为1.8mg/L,反应240min后TOC去除率可达84.5%。     

Te（IV）胁迫对两种螺旋藻生长的影响

对极大螺旋藻(Spirulina maxima)和钝顶螺旋藻(S.platensis),在接种后第1~7 d通过不同时间添加Na2TeO3来施加Te(IV)胁迫,5种Te(IV)胁迫实验组的累计加Te浓度均为250 mg/L,结果表明:两种螺旋藻的最终生物量,从I~V组均呈增加趋势;其中IV、V组对S.platensis的生长有促进作用。利用动力学方程并结合胁迫强度的概念,对实验结果进行了合理的解释。     

云龙水库氮、磷污染原因分析及对策措施

依据云龙水库库区和入库河道水质现状监测结果,对造成云龙水库污染的总磷、总氮的变化情况和污染来源构成进行了初步分析,并提出预防控制污染的对策措施。     

污水处理厂出水中雌激素活性物质浓度与生态风险水平

再生水在环境和景观水体利用中,由微量有毒有害污染物,特别是内分泌干扰物引起的长期生态风险备受关注. 以再生水生态风险控制为目的,对城市污水处理厂出水(再生水)中雌激素活性物质浓度分布情况进行了研究,归纳了8种雌激素活性物质的出水浓度水平,比较分析了各物质的雌激素活性和生态风险. 结果表明:8种物质的质量浓度分布在ng/L～μg/L,其中ρ(类固醇)最低,为nd～50 ng/L;ρ(酚类)及ρ(酞酸酯类)主要在μg/L水平,个别高达40 μg/L. 雌激素活性分析和生态风险评价结果表明,污水处理厂出水(再生水)中3类雌激素活性物质的雌激素活性和生态风险顺序均为类固醇物质＞酚类物质＞酞酸酯类物质. 城市污水再生处理厂应优先控制乙炔基雌二醇(EE2)、雌酮(E1)和雌三醇(E3)等3种雌激素活性物质.