不同热解温度生物炭对 Cd(Ⅱ)的吸附特性

以花生壳和中药渣为原料,分别于300、350、400、500、600℃下慢速热解制备生物炭,并表征其物理化学性质.研究不同p H、吸附时间和Cd(Ⅱ)浓度下生物炭对Cd(Ⅱ)的吸附特征.结果表明,随着热解温度的升高,生物炭的碳化程度增加,比表面积增大,含氧官能团数量减少,π共轭芳香结构更加完备,Ca和Mg等无机元素不断富集,矿物溶解性降低,导致了Cd(Ⅱ)在不同热解温度生物炭上吸附能力及机制的差异.随溶液p H的升高(2.0~6.0),生物炭对Cd(Ⅱ)的吸附量逐渐增加.吸附过程可分为快吸附和慢吸附两个阶段,吸附速度受膜扩散、颗粒内扩散和沉淀作用、离子交换等过程的控制.随热解温度的升高,快吸附在生物炭对Cd(Ⅱ)的吸附中所占比例逐渐降低.高温生物炭(≥500℃)中含氧官能团的锐减及难溶晶体矿物的形成降低了其对Cd(Ⅱ)的快吸附速率.沉淀和离子交换可能是低温生物炭(≤400℃)吸附Cd(Ⅱ)的主要机制;高温生物炭(≥500℃)中更完备的π共轭芳香结构增加了Cd-π作用对吸附的贡献,而难溶磷酸盐和碳酸盐的形成则降低了沉淀作用对吸附的贡献.这些研究结果为筛选对Cd(Ⅱ)具有高效去除或固持能力的功能生物炭(designer biochar)提供了重要的理论数据.     

液相氧化-吸收脱除模拟烟气中NOx的研究

分别采用Na Cl O2和Na2SO3溶液作为氧化液和吸收液,在自行设计的鼓泡塔反应系统进行了液相氧化-吸收脱除模拟烟气NOx的研究,考察了气相SO2浓度、Na Cl O2和Na2SO3投加量以及p H值等因素对NO氧化和NOx脱除的影响.结果表明,SO2会优先于NO与氧化剂反应,从而增大氧化剂消耗量.偏酸性条件有利于NO氧化,但酸性太强会导致Na Cl O2分解为Cl O2逸出.碱性吸收液对NO几乎不具吸收脱除效果,但共存NO2能促进NO的吸收脱除.SO2对NO2吸收脱除具有促进作用.     

哈尔滨市燃煤期PM10和PM2.5比对测试研究

哈尔滨市的地域性决定了气候非常具有代表性。以冬季特为明显,气温早晚温差大,气温低。再加上正是采暖期间,空气质量受供暖期等影响较大,空气质量不稳定。2013年冬季选择哈尔滨市燃煤期PM10和PM2.5比对测试研究分析,对市区内3个监测点位进行的颗粒物（PM10和PM2.5）手工采样与自动仪器的比对监测,以手工监测方法为基准,分析自动监测与手工监测的一致性,并对PM10和PM2.5浓度的比值关系进行了分析,结果表明：监测3个点位的PM10和PM2.5的浓度趋势具有很高的一致性,且以手工和自动数据进行线性回归的各项参数均符合技术规范（HJ 653-2013）的要求。     

一种识别低压电力线载波通信系统中随机脉冲噪声的新方法

目的从电力线载波通信系统中提取随机脉冲噪声并分析其来源。方法建立一个简单的检测随机噪声的测试系统。结果 FSV方法可以成功地识别热水壶在电力线上造成的随机脉冲噪声,同时也证明了统计分析的方法对于识别随机脉冲噪声效果不佳。结论可以通过对MAFFSV方法结果设定阈值来识别低压电力线载波通信系统中的随机脉冲噪声,进而可以确定低压电力线网络拓扑结构的改变。     

降雨条件下河流冲刷型滑坡的基本特征及滑动机制分析——以四川宣汉樊哙大桥滑坡为例

以宣汉樊哙大桥滑坡为例,分析降雨条件下河流冲刷型滑坡的滑动机制。在对滑坡区的地质条件、滑坡的基本特征和滑坡的变形过程等综合分析的基础上,探讨了降雨条件下河流冲刷型滑坡发育特征及形成机理。分析表明,降水对降雨条件下河流冲刷型滑坡起到了双重作用:一方面,河水对坡脚的浸泡、冲刷;另一方面,强降雨形成的雨水沿着坡面渗入坡体,在滑体与基岩接触面上形成滞水带,受地下水的浸泡泥岩极易软化,强度大幅降低,促使坡体滑动。深入研究樊哙滑坡的基本特征和成灾机制,对西南地区临河型滑坡的预防与治理提供一定的技术支持和借鉴作用。     

基于FPGA的电磁多速率仿真通讯接口研究

针对基于现场可编程门阵列(field-programmable gate array,FPGA )的电磁暂态多速率仿真器的海量计算数据与外部系统通讯问题,研究通过定制化的通讯接口硬件和通讯协议,最大限度地利用电力系统仿真的特点,提升小步长仿真的通讯能力,并对通讯接口的可用性和正确性进行测试验证。结果表明:基于 FPGA 的电磁暂态多速率仿真系统通讯接口克服了多速率仿真的通讯瓶颈,实现了高带宽、高稳定性和低延迟的高效通讯,适用于大规模的电磁暂态多速率仿真计算。     

镜泊湖浮游藻类功能群的演替特征及其影响因素

2013年5月、9月及10月采集了镜泊湖26个位点的浮游藻类,并对所采集的藻类进行了功能群划分.结果显示:镜泊湖的浮游藻类可以分为21个功能群,即C、D、F、G、H1、J、L_O、M、MP、N、P、S1、S2、S_N、T、W1、W2、X1、X2、X3、Y[限于篇幅,各功能群的代表性属（种）和生境特征见表 1].不同时期调查的藻类优势功能群存在明显差异,其中,D（适宜较浑浊的浅水水体）、J（适宜混合型高富营养浅水水体）、MP（适宜扰动频繁的浑浊型浅水水体）、X1（适宜混合程度较高的富营养浅水水体）在三次调查中的优势度均>0.02,成为镜泊湖的绝对优势功能群,镜泊湖藻类优势功能群不同时期的演替规律为5月的D+MP+X1+X2经9月的X1+P+MP+L_O+J转变成10月的X1+P+MP.CCA分析结果显示,镜泊湖藻类功能群分布受水环境因子影响较为明显.整体上,水温、ρ（DO）、SD、EC、ρ（COD_Mn）及ρ（NH₃-N）是影响镜泊湖藻类功能群分布格局的主要因素.      

嘉兴市地表水中兽用抗生素的污染现状调查

建立了适合长三角地区重要生猪养殖基地嘉兴市环境水体中4类(四环素类、磺胺类、大环内酯类、喹诺酮类)共10种常用兽用抗生素同时检测的固相萃取与液相色谱质谱(LC-MS/MS)联用技术,对该地区10个典型村镇河道断面和21个市区主要河网监控断面开展调查.结果表明,村镇河道中抗生素污染严重,10种抗生素总浓度为65.6～467.0 ng.L-1.其中,四环素类和磺胺类浓度分别为40.8～253.0 ng.L-1和未检出～165.0 ng.L-1;大环内酯类和喹诺酮类浓度分别为3.1～14.68ng.L-1和未检出～14.54 ng.L-1.市区河网污染相对较轻,10种抗生素总浓度为20.1～61.2 ng.L-1,其中四环素类浓度为未检出～44.0 ng.L-1;磺胺类、大环内酯类和喹诺酮类浓度则分别低于2.7、6.3和21.6 ng.L-1.     

Starch/polyvinyl alcohol blended materials used as solid carbon source for tertiary denitrification of secondary effluent

Starch/polyvinyl alcohol （PVA） blended materials for using as a solid carbon source （SCS） were prepared by blending PVA and gelatinized starch in an aqueous solution system, in which PVA served as framework material and starch as carbon source. The optimization of starch content and temperature effects were investigated. It was indicated that higher denitrification efficiency could be achieved with more starch in the materials. The average specific denitrification rates were 0.93, 0.66, 0.37 and 0.36 mg/（g·day） corresponding to starch content of 70%, 60%, 40% and 30% respectively at 37℃. The denitrification rates increased when operating temperature was raised from 23℃ to 30℃ and then 37℃. The mechanism of carbon release was analyzed incorporating the experimental results of abiotic release in deionized water. The organic carbon was mainly hydrolyzed by microbes, and the biological release efficiencies were at the range of 89.2% to 96.0%. A long-term experiment with a continuous flow reactor with SCS material containing 70% starch was conducted to gain some experience for practical application. When the influent nitrate concentration was in the range of 35.2 to 39.1 mg/L, hydraulic retention time of 4 hr, and operating temperature of 30℃, a nitrogen removal efficiency up to 94.6% and denitrification rate of 0.217 kg/（m3.day） was achieved. The starch-based materials developed in this study can be used as a solid carbon source for tertiary nitrogen removal from secondary effluent.     

Mesopolymer modified with palladium phthalocyaninesulfonate as a versatile photocatalyst for phenol and bisphenol A degradation under visible light irradiation

A novel versatile photocatalyst, FDU-PdPcS, was prepared by immobilizing palladium phthalocyaninesulfonate (PdPcS) onto the FDU-15 mesopolymer via multi-step chemical modification processes involving chloromethylation of the FDU-15 mesopolymer first with chloromethyl methyl ether, a subsequent amination reaction with ethylenediamine, and finally modification with palladium phthalocyaninesulfonate via ionic interaction. The obtained FDU-PdPcS photocatalyst was characterized by the X-ray diffraction (XRD), UV-Vis spectrosopy and inductively coupled plasma (ICP) techniques. This photocatalyst not only affords a high dispersion of monomeric PdPcS molecules, which may further be stabilized by the π-electron of benzene rings of FDU-15, but also provides a number of diamino groups inside the mesopores, which could be advantageous for the photodegradation of phenolic pollutants. In photodegradation studies of phenolic pollutants, the FDU-PdPcS catalyst exhibited excellent visible light photocatalytic activity and reusability. The photodegradation products of phenol and bisphenol A were investigated by the gas chromatoghraphy-mass spectrometry (GC-MS) technique. The results showed that the photodegradation products were composed of carboxylic acids and CO2. Isopropanol, sodium azide and benzoquinone were used as hydroxyl radical (OH.), singlet oxygen (1O2) and superoxide radical (O2.-) scavengers, respectively. The results suggested that 1O2 and O2. were the prominent active species during the photodegradation process. A possible mechanism for the photodegradation of phenol was also discussed.