高浓度复合型聚铁硅絮凝剂PFSS和PSFS的形态分布研究

采用紫外分光光度法、逐时络合比色法和红外图谱从不同角度对高浓度聚合硫酸铁硅和聚合硅酸铁的形态分布及转化规律进行了探讨。紫外吸收表明，聚铁硅絮凝剂中主要以Fe（OH）2^＋、Fe2（OH）2^4＋等二聚体为主，而且还有三聚体或其他聚合形态的存在；逐时络合分析显示，复合型聚铁硅体系中硅形态以Si（c）为主，铁形态以Fe（a）和Fe（c）为主；红外图谱证实高浓度聚铁硅是以羟桥为主结构连接的高分子复合物，在1100cm^-1附近M-OH-M的振动证明有铁羟基及其聚合态存在，且其形态区别于PFS。     

聚铁硅型混凝剂的形态分析及性能研究

以水玻璃和聚合硫酸铁为原料制备不同碱化度(B)及不同Fe/Si摩尔比的系列聚合硫酸铁硅混凝剂(PFSS)并对其形态进行分析。采用FeFerron逐时络合比色法发现随熟化时间延长,Fe(a)和Fe(b)的含量逐渐减少,Fe(c)的含量逐渐增多,而碱化度越大,PFSS中铁越易从Fe(a)向Fe(c)转化。采用显微电泳实验发现PFSS随着投加量增加,Zeta电位升高。采用超滤法测定了制备的PFSS分子量的分布情况,并将其与PFS进行了比较,结果发现,PFSS的分子量明显比PFS的分子大。     

聚硅基复合氯化铁絮凝剂的制备及其在采油废水处理中的应用

采用硅酸钠制备聚硅酸,探讨了活化pH、活化剂、硅酸钠浓度(以SiO_2质量分数计)及聚合温度等因素对聚硅酸稳定性的影响.利用聚硅酸及氯化铁制备聚硅基复合氯化铁(PSiF),并通过正交试验分析了活化pH、Si/Fe(摩尔比)、OH/Fe(摩尔比)、制备时间对PSiF絮凝性能的影响.综合考虑絮凝性能、稳定性以及经济性等因素,确定PSiF适宜的制备条件为SiO_2质量分数2%～3%;活化pH为2～3;Si/Fe为0.50～0.75;OH/Fe为0.50～0.75;制备时间为0.5 h;聚合温度低于25℃.对比PSiF、PAC、FeCl_3对采油废水的处理效果,PSiF除浊、除COD效果以及经济性最好,是一种应用前景广阔的新型絮凝剂.     

聚铁硅型混凝剂的形态分析及性能研究

以水玻璃和聚合硫酸铁为原料制备不同碱化度(B)及不同Fe／Si摩尔比的系列聚合硫酸铁硅混凝剂(PFSS)并对其形态进行分析。采用Fe-Ferron逐时络合比色法发现随熟化时间延长，Fe(a)和Fe(b)的含量逐渐减少，Fe(c)的含量逐渐增多，而碱化度越大，PFSS中铁越易从Fe(a)向Fe(c)转化。采用显微电泳实验发现PFSS随着投加量增加，Zeta电位升高。采用超滤法测定了制备的PFSS分子量的分布情况，并将其与PFS进行了比较，结果发现，PFSS的分子量明显比PFS的分子大。     

天然有机物对零价铁去除水体中砷的影响研究

在研究零价铁对水体中砷去除动力学的基础上,着重探讨了天然有机物腐殖酸对零价铁除砷的影响.并对零价铁的腐蚀产物进行了分析.结果表明,水体中的砷可以通过在零价铁腐蚀产物上的吸附得到快速去除.腐殖酸显著降低了砷的去除率,这归因于腐殖酸与零价铁腐蚀产生的铁离子形成络合物,阻止了Fe(OH)3(或Fe(OH)2)沉淀的产生.腐殖酸浓度越高.砷的去除率越低.1.00 mg腐殖酸最多可以络合约0.75 mg铁离子.当铁离子与腐殖酸的络合达到饱和后,零价铁进一步腐蚀产生的铁离子可形成Fe(OH)3(或Fe(OH)2)沉淀,这些沉淀物可吸附水体中的腐殖酸和砷,从而加速砷的去除.冷冻干燥后的零价铁腐蚀产物的结构以无定型为主,含有少量的结晶化合物,包括γ-Fe2O3、γ-FeO(OH)和Fe3O4等.腐殖酸的存在可进一步增加腐蚀产物中的无定型成分.光电能谱(XPS)分析结果显示,吸附在腐蚀产物上的砷为5价,没有发现5价砷被还原成3价砷.在应用零价铁修复砷污染水体时,应考虑腐殖酸的影响.     

聚硅酸铁混凝剂净水效能及机理

采用共聚法制备聚硅酸铁(PSF)混凝剂,同时研究PSF的水解规律,并对比研究PSF与复合铝铁(PFA)的微观品质及对低温低浊水、屠宰废水及含磷模拟水的混凝性能,并初步探讨PSF除磷(或除有机物)的机理.结果表明,混凝剂混凝性能的优劣取决于其微观性质,而PSF独特的微观特征正是其具有优异混凝性能的根本原因.不同pH值对P(或有机物)与PSF之间的络合模式具有不同的影响,3种水解形态Fe(OH)2 、Fe3 及Fe(OH)3在宽泛的pH范围内(5＜pH＜9.5)稳定存在并基本均为定值,这些可能都是PSF在宽泛的近中性范围内及碱性范围内具有优异除磷、除有机物性能的重要原因.可以认为PSF的混凝机理是以电中和(配位)/脱稳为前提条件,以架桥为必要条件,以卷扫网捕为补充条件.     

工业聚合铝的形态分析方法研究

主要探讨了工业聚合铝 (PACl)的形态分析方法 ,即Al Ferron逐时络合比色法。重点研究了 2类Ferron比色液的稳定性及其对工业PACl形态分析的影响特征。     

工业聚合铝的形态分析方法研究

主要探讨了工业聚合铝(PACl)的形态分析方法，即Al-Ferron逐时络合比色法。重点研究了2类Ferron比色液的稳定性及其对工业PACl形态分析的影响特征。     

聚硅硫酸钛（PTSiS）的合成及形貌分析

以硅酸钠和硫酸钛为原料,用共聚法制备了不同硅钛比(硅钛摩尔比分别为3∶1、1∶1和1∶3)的新型绿色无机高分子絮凝剂——聚硅硫酸钛(PTSiS)。用紫外连续扫描光谱仪(UV/Vis)、红外光谱仪(IR)、X-射线衍射(XRD)、扫描电镜(SEM)和倒置生物显微镜对样品中钛硅的微观品貌进行了多方面物性分析。结果表明:当硅钛比为3∶1时,硅酸钠和硫酸钛反应完全。此时,聚硅酸的骨架硅(Si—O—Si)与钛元素发生同晶取代或与钛离子水解形成的表面羟基发生络合,形成的聚硅硫酸钛(PTSiS)是一种高分子的硅钛聚合物,而不是单纯的原料混配。另外,聚硅硫酸钛(PTSiS)具有枝杈长链的网络结构,其骨架主要由框架钛结构(Ti—O—Si)组成。     

铁碳材料还原NO络合吸收体系中Fe(Ⅲ)EDTA的性能

在湿法烟气脱硝中,Fe(Ⅱ)EDTA是一种常用的螯合剂,对NO有良好的络合吸收能力,但是Fe(Ⅱ)EDTA容易被O2氧化成对NO无络合能力的Fe(Ⅲ)EDTA。因此,选择合适的还原剂实现Fe(Ⅲ)EDTA的高效还原是络合脱硝的关键技术之一。比较了铁碳(Fe/AC)和铁粉(Fe)在不同搅拌速度下对Fe(Ⅲ)EDTA的还原,系统探讨了铁碳质量比、O2浓度、铁碳中Fe与Fe(Ⅲ)EDTA的摩尔比、pH值和Fe(Ⅲ)EDTA初始浓度对铁碳还原Fe(Ⅲ)EDTA的影响,考察了Fe/AC投加前后NO吸收效率的变化,同时通过BET、XRD表征技术对铁碳材料进行了分析。结果表明:Fe/AC能很好地再生Fe(Ⅱ)EDTA,从而提高NO吸收效率。提高搅拌速度、铁碳中Fe与Fe(Ⅲ)EDTA的摩尔比、Fe(Ⅲ)EDTA初始浓度,Fe(Ⅲ)EDTA的还原速率会相应增大;O2浓度及pH增大会降低Fe(Ⅲ)EDTA的还原速率。表征结果表明,铁碳表面形成的氢氧化物为γ-Fe OOH。     

Chloroaromatic pollutants in mussels incubated in two finnish watercourses polluted by industry

Concentrations of different chlorinated compounds were measured in mussels incubated in two polluted watercourses, a river (the River Kymijoki) and a lake (Lake Vanaja) for four weeks in summer 1995. The sum concentrations of polychlorinated phenols (PCP) and biphenyls (PCB) were both about 1 μg/g lipid weight (lw) in Lake Vanaja mussels, while in the River Kymijoki mussels PCPs were non-detectable and PCBs were measured 120 ng/g lIw. The concentrations of toxic polychlorinated dibenzo-p-dioxin (PCDD) and dibenzofuran (PCDF) congeners ranged between <17 and 370 pg/g Iw in Lake Vanaja mussels and between <38 and 11,000 pg/g lw in the River Kymijoki mussels. Polychlorinated diphenyl ethers (PCDE) were detected in the mussels incubated in the River Kymijoki (0.4–1.1 ng/g Iw), but not in those incubated in Lake Vanaja. Polychlorinated phenoxyanisoles (PCPA) were measured 33 ng/g lw and polychlorinated phenoxyphenols (PCPP) 300 ng/g lw in the mussels incubated in the River Kymijoki. PCPAs were also detected in reference samples, which were sediment and pike from the River Kymijoki and Baltic salmon, seal and white-tailed sea eagle.     

Book review

The Pesticide Manual ‐ A World Compendium, 8th Edition, C.R. Worthing, Editor and S.B. Walker, Assistant Editor, British Crop Protection Council, BCPC Publications Sales, Bear Farm, Binfield, Bracknell, Berkshire RG12 5QE, England. 1987, 1100 pp., UK £50; Overseas £56. ISBN 0–948404–01–9.     

Organochlorine compounds in a three-step terrestrial food chain

The concentrations of 15 organochlorine chemicals (PCBs and pesticides) were studied in a Central European oak wood food chain system: Great tit (Parus major), caterpillars (Tortrix viridana, Operophtera brumata, Erannis defoliaria), and oak-leaves (Quercus robur). Juvenile tits receive organochlorines from the mother via egg transfer and, eventually to a greater extent, from the caterpillar food source during nestling period. The concentrations of PCB 153 (2,2′,4,4′,5,5′-hexachlorobiphenyl, the most abundant in this study) was found in leaf material at ca. 1 ng/g, in caterpillars 10 ng/g, and in bird eggs 170 ng/g on an average and on a dry mass basis.     

The chemical stability of formulations of some hydrolyzable insecticides in aqueous mixtures with hydrolysis catalysts

Abstract

The active ingredients in commercial formulations of malathion, oxamyl, carbaryl, diazinon, and chlorpyrifos diluted to “spray tank”; concentrations with buffered distilled or natural water of pH 4–9 were stable for at least 24 hr. Formulations of trichlorfon were not stable at pH 7 or above but disappearance rates were slower than for the pure chemical in homogeneous solution. Cupric ion was observed to be an effective catalyst for the hydrolysis of a variety of pure organophosphorus insecticides but did not catalyze hydrolysis of the active ingredients of the formulations examined. Increasing the dilution of the formulation increased the susceptibility of malathion, oxamyl, and carbaryl to hydrolysis.     

Radionuclides in pinon pine (Pinus edulis) nuts from los alamos national laboratory lands and the dose from consumption

Abstract

One of the dominant tree species growing within and around the eastern portion of Los Alamos National Laboratory (LANL), Los Alamos, NM, lands is the pinon pine (Pinus edulis). Pinon pine is used for firewood, fence posts, and building materials and is a source of nuts for food—the seeds are consumed by a wide variety of animals and are also gathered by people in the area and eaten raw or roasted. This study investigated the (1) concentration of ³H, ¹³⁷Cs, ⁹⁰Sr, ^totU, ²³⁸Pu, ^{239, 240}Pu, and²⁴¹ Am in soils (0‐ to 12‐in. [31 cm] depth underneath the tree), pinon pine shoots (PPS), and pinon pine nuts (PPN) collected from LANL lands and regional background (BG) locations, (2) committed effective dose equivalent (CEDE) from the ingestion of nuts, and (3) soil to PPS to PPN concentration ratios (CRs). Most radionuclides, with the exception of ³H in soils, were not significantly higher (p < 0.10) in soils, PPS, and PPN collected from LANL as compared to BG locations, and concentrations of most radionuclides in PPN from LANL have decreased over time. The maximum net CEDE (the CEDE plus two sigma minus BG) at the most conservative ingestion rate (10 lb [4.5 kg]) was 0.0018 mrem (0.018 μSv); this is far below the International Commission on Radiological Protection (all pathway) permissible dose limit of 100 mrem (1000 μSv). Soil‐to‐nut CRs for most radionuclides were within the range of default values in the literature for common fruits and vegetables.     

Degradation and sorption of imidacloprid in dissimilar surface and subsurface soils

Degradation and sorption/desorption are important processes affecting the leaching of pesticides through soil. This research characterized the degradation and sorption of imidacloprid (1-[(6-chloro-3-pyridinyl)-methyl]-N-nitro-2-imidazolidinimine) in Drummer (silty clay loam) and Exeter (sandy loam) surface soils and their corresponding subsurface soils using sequential extraction methods over 400 days. By the end of the incubation, approximately 55% of imidacloprid applied at a rate of 1.0 mg kg^?1 degraded in the Exeter sandy loam surface and subsurface soils, compared to 40% of applied imidacloprid within 300 days in Drummer surface and subsurface soils. At the 0.1 mg kg^?1 application rate, dissipation was slower for all four soils. Water-extractable imidacloprid in Exeter surface soil decreased from 98% of applied at day 1 to > 70% of the imidacloprid remaining after 400 d, as compared to 55% in the Drummer surface soil at day 1 and 12% at day 400. These data suggest that imidacloprid was bioavailable to degrading soil microorganisms and sorption/desorption was not the limiting factor for biodegradation. In subsurface soils > 40% of ¹⁴C-benzoic acid was mineralized over 21 days, demonstrating an active microbial community. In contrast, cumulative ¹⁴CO₂ was less than 1.5% of applied ¹⁴C-imidacloprid in all soils over 400 d. Qualitative differences in the microbial communities appear to limit the degradation of imidacloprid in the subsurface soils.     

Biochemical interaction of six op delayed neurotoxicants with several neurotargets

Abstract

Five organophosphorous insecticides: Leptophos, EPN, Cyano‐fenphos, trichloronate and salithion proved to cause irreversible ataxia not only to chicken but also to mice and sheep. TOCP was included as a reference. Cyanofenphos blocked the catecholamine B‐receptor binding activity with ³H‐norepinephrine at a level similar to that of the specific inhibitor propranolol in the mouse heart preparation. In the lamb heart preparation, the B‐receptor was more sensitive to Leptophos, salithion and TOCP than to propranolol. The six compounds and their oxons were screened for their in‐vitro inhibition to monamine oxidase (MAO), acetyl cholinesterase (AChE) and neurotoxic esterase (NTE) in the brain of either mouse, lamb or chicken. It is believed that their AChE inhibition stands for their acute toxicity, while NTE inhibition is responsible for their paralytic ataxia.     

土壤中砷的化学平衡

本文比较详细地综述了砷的化学特性,环境背景值及来源和循环,土壤中砷的三大化学平衡即沉淀溶解平衡,氧化还原平衡,吸附解吸平衡,以及微生物对砷的转化。     

Elemental uptake by edible herbs and lettuce (Latuca sativa)

The total concentration of toxic elements (aluminum, cadmium, chromium and lead) and selected macro and micro elements (iron, manganese, copper and zinc) are reported in six leafy edible vegetation species, namely lettuce, spinach, cabbage, chards and green and red types of Amaranth herbs. Although spinach and chards had greater than 125 mv of iron, both the amaranthus herbs recorded > than 320 μ g g^{? 1} dry weight. In both the spinach and chard species, the Mn and Zn levels were appreciable recording > 225 μ g g^{? 1} and 150 μ g g^{? 1} dry weight, respectively. Aluminum concentrations were (in μ g g^{? 1} dry weight) lettuce (10), cabbage (11), spinach (167), chards (65), amaranthus green (293) and amaranthus red (233). All the micro and macro elements and the toxic elements (Ni, Cr, Cd and Pb) elements analyzed, were below the recommended maximum permitted levels (RMI) in vegetables. Further the elemental uptake and distribution of the nine elements, at three growth stages of the lettuce plant grown on soil bed under controlled conditions are detailed. In the soil, except for iron (16%), greater than 33% of the other cations were in exchangeable form. Generally in the lettuce plant, roots retained much of the iron (> 224 μ g g^{? 1}) and aluminum (> 360 μ g g^{? 1}), while leaves had less than 200 μ g g^{? 1} of iron and 165 μ g g^{? 1} of Al. Although the concentrations of elements marginally decreased with growth, the lettuce leaves had significant amounts of Mn (30 μ g g^{? 1}), Zn (50 μ g g^{? 1}) and Cu (3.6 μ g g^{? 1}). Some presence of lead in leaves (2.0 μ g g^{? 1}) was noticed, but all the toxic and other elements analyzed were well below the RMI values for the vegetables.     

The dissipation of nonlyphenol in stream and pond water under simulated field conditions

Abstract

The dissipation of 1.0 ppm nonylphenol in stream and pond water, incubated in flasks at 16°C under simulated field conditions up to 44 days indicated that the half‐life was 2.5 days if the flasks were open, and 16 days if they were closed. A transformed product was detected in the closed flasks.

Translocation of nonylphenol in water occurred when treated water samples were incubated in the presence of sediment. After 10 days, nonylphenol was detected only in the sediment, but not in water (detection limit = 10 ppb). About 80% of the nonylphenol was degraded in 71 days, but no degradation occurred if the water and the sediment were autoclaved prior to incubation.