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1.
针对受低浓度氨氮污染的地下水,实验筛选组合了不同的反应介质,利用串联的多介质填充柱模拟渗透反应格栅,通过物理吸附及生物硝化-反硝化作用来实现氮的去除。结果表明,在进水氨氮浓度为10 mg/L、流速为0.5 m/d的条件下,模拟柱对氨氮的去除率达到98%以上,且不会出现亚硝酸盐及硝酸盐浓度的升高。水体经过释氧柱后溶解氧由2mg/L升高至10 mg/L以上,表明释氧材料可提供硝化细菌所需的好氧环境。好氧柱中填充易于生物挂膜的生物陶粒及对氨氮有较强吸附能力的沸石,二者联用通过生物硝化-物理吸附协同作用实现对氨氮的去除,其中生物作用实现的氨氮去除量占总去除量的50%左右。后续厌氧反应柱填充海绵铁除氧并利用松树皮颗粒作为碳源,创造反硝化菌生长条件,硝酸盐氮浓度可由10 mg/L降低至5 mg/L以下,实现对好氧反应阶段所产生的硝酸盐的去除,避免了地下水的二次污染。  相似文献   

2.
研究了低温条件下,沸石和火山岩为载体,锯末为碳源的生物反应器对地下水中硝酸盐氮的去除效果。结果表明,在(14±1)℃,水力停留时间18 h,进水硝酸盐氮浓度为27 mg/L的条件下,以锯末为碳源能有效去除地下水中的硝酸盐,沸石为载体时对硝酸盐氮的平均去除率为98%;火山岩为载体时对硝酸盐氮的平均去除率为95%。实验过程中出现铵盐和亚硝酸盐的积累,出水中氨氮浓度为1~2.55 mg/L,亚硝酸氮浓度为0~0.98 mg/L。出水pH均介于7~8,满足饮用水标准中pH的要求(6.5~8.5)。  相似文献   

3.
沸石改性及其去除水中氨氮的实验研究   总被引:13,自引:4,他引:9  
通过实验研究了沸石改性条件及其对水中氨氮吸附去除的影响。结果表明,加热改性与无机酸改性不能显著提高沸石对氨氮的吸附量。利用NaOH改性的最佳浓度为1 mol/L,此条件下对氨氮吸附量可提高到650.68 mg/kg,为天然沸石的2.82倍。利用无机盐改性时,对氨氮吸附效果最好的是NaCl改性沸石,其次为KCl改性沸石与CaCl2改性沸石。随着NaCl溶液浓度和改性时间的增加,改性沸石对氨氮的吸附量显著增加,可达天然沸石的3~4倍;在NaCl浓度为150 g/L与改性时间为18 h条件下,改性沸石对氨氮吸附量可达887.35 mg/kg,为天然沸石的3.84倍。  相似文献   

4.
采用孔隙率高、比表面积大的海绵铁作为渗透反应墙(PRB)介质,通过3批动态实验讨论了海绵铁+锰砂单层介质、海绵铁+锰砂+活性炭单层介质,以及海绵铁+锰砂和活性炭的双层介质对地下水中NO3--N的去除效果.结果表明,经过292 h的PRB动态实验,填充海绵铁+锰砂单层介质、海绵铁+锰砂+活性炭单层介质、海绵铁+锰砂与活性炭双层介质的反应器的NO3--N去除率分别达到了70.65%、84.22%、88.09%,采用海绵铁与活性炭的单层介质或双层介质的反应器对地下水中NO3--N和TN的去除效果显著增强,出水中NH4+-N浓度相对也有所降低;扫描电镜和X射线衍射分析结果表明,经过PRB动态实验后,海绵铁表面覆盖了厚厚的膜,微孔隙被许多新的物质堵塞,这会导致海绵铁的氧化还原反应能力减弱,阻碍地下水中NO3--N的进一步还原去除,这也是以后实际应用中需要解决的问题.  相似文献   

5.
建立柱实验装置,探讨了反应柱中填加介质、硝酸盐的初始浓度及不同过水流速时硝酸盐的去除效果及产物的生成情况。4种不同材料,纳米铁、真养产碱杆菌、纳米铁与真养产碱杆菌简单混合体、纳米铁与真养产碱杆菌驯化培养5 d的复合体,分别与初始浓度为65 mg/L硝酸盐溶液反应。结果表明,经培养5 d的纳米铁-真养产碱杆菌复合体对硝酸盐的去除效果最佳,去除率可达到75%,且氨氮的生成量仅为2.99 mg/L;硝酸盐初始浓度分别为32、65和95 mg/L时,32mg/L的体系中硝酸盐的降解效果最好,去除率达78.9%且亚硝酸盐及氨氮的生成量分别为2.34 mg/L和2.89 mg/L,均低于另外2组;溶液流速为6.0 cm/h时,经驯化培养的纳米铁-真养产碱杆菌对硝酸盐的去除率达77%,当控制流速降至2.4cm/h时,亚硝酸盐氮的生成量降至0.34 mg/L。  相似文献   

6.
可吸附生物反应墙修复地下水中BTEX   总被引:1,自引:0,他引:1  
在研究填充介质配比的基础上,考察中砂-膨润土-微生物构成的可吸附生物反应墙对模拟地下水中不同浓度BTEX(苯、甲苯、乙苯和二甲苯)的去除效果,并通过添加硝酸盐考察电子受体对地下水BTEX去除效率的贡献。结果表明,膨润土/中砂的最佳体积比为20∶80,此时渗透性反应墙的渗透系数为2.01×10-5m/s,有效孔隙率为16.71%。添加硝酸盐的生物反应墙对不同浓度下BTEX的去除率较为稳定,没有添加硝酸盐的对照组对BTEX的去除效果波动较大。在进水浓度分别为6、8和10 mg/L时,添加硝酸盐的生物反应墙和对照组对BETX的总去除效率分别约为94%、91%,96%、90%,97%和87%。可吸附生物反应墙对BTEX有较好的去除效果,添加硝酸盐对去除BTEX有一定的促进作用。  相似文献   

7.
海水改性沸石处理氨氮废水   总被引:1,自引:1,他引:0  
沸石因具有独特的架状结构而表现出良好的选择吸附和离子交换性能,在废水处理中被广泛应用,但吸附容量偏低,需要进行改性。针对天然沸石的局限性,研究了不同改性方法对氨氮吸附的影响,确定了最佳的沸石改性方法,并进行了吸附等温模型,吸附动力学研究。结果表明,采用高温300℃焙烧后再用预处理后的海水浸泡24 h改性沸石去除氨氮效果最佳。当活化沸石投配量为10 g/L,接触时间为150 min,进水氨氮浓度为37.91 mg/L时,沸石对氨氮吸附容量为4.08 mg/g,氨氮去除率为90.45%;沸石及改性沸石对氨氮的吸附等温线符合Langmuir方程和准一级动力学方程。用海水来改性沸石的方法,不仅可提高沸石对氨氮的吸附容量和吸附速度,而且无任何添加药剂,具有简单易行、费用低廉的优点,为沸石在水处理工程中的应用提供技术支撑。  相似文献   

8.
粉煤灰合成沸石去除城市暴雨径流中氨氮   总被引:2,自引:1,他引:1  
采用粉煤灰为原料,通过耦合碱熔-两步合成法制得3种合成沸石产品,并以合成沸石制备大粒径的功能填料。通过氨氮吸附速率实验和等温吸附实验探讨了合成沸石及功能填料的氨氮吸附速率和最大吸附容量(Qm),以功能填料构建模拟人工快速渗滤系统,研究其对城市暴雨径流中氨氮的去除效果。结果表明,合成沸石对氨氮的吸附速率极快,5min去除率约达到75%,氨氮最大吸附容量为11.36~16.13 mg/g;功能填料对氨氮的最大吸附容量有所下降,但氨氮吸附速率仍较快,应用于模拟人工快速渗滤系统时能在较高的水力负荷下快速去除城市暴雨径流中的氨氮。碱处理再生法更适于进行合成沸石功能填料原位再生,氨氮吸附容量一次再生率达到67%~87%。  相似文献   

9.
生物墙对地下水中六价铬的去除效果模拟研究   总被引:1,自引:0,他引:1  
通过土柱实验模拟地下水环境,研究以发酵树皮为主要反应介质的渗透性生物墙对地下水中六价铬的去除效果,为六价铬污染地下水的修复提供方法和依据。结果表明,模拟生物墙运行数天后,墙内形成弱碱性(pH 7~8)、强还原(Eh<-100 mV)环境,有利于六价铬转化为三价铬并生成沉淀。在进水六价铬浓度为20 mg/L、水流速度为3.7 cm/d的运行条件下,3周期间生物墙对六价铬的去除率稳定在98%左右,生物墙内沿水流方向三价铬的浓度先上升后下降(最高达6.6 mg/L),出水三价铬约为1.0 mg/L。吸附和微生物转化是生物墙对水中六价铬去除的主要反应。  相似文献   

10.
杨朗  李志丰 《环境工程学报》2012,6(8):2715-2719
分别研究了沸石的等温吸附模型,改性沸石在交换柱中的穿透与再生,通过化学沉淀法对再生废液中氨氮的回收等。结果显示:60~80目单位重量天然斜发沸石对氨氮的饱和交换容量为4.15 mg/g;30 mg/L的氨氮废水经过交换柱后沸石的穿透吸附容量和平衡吸附容量分别为:4.50 mg/g和4.757 mg/g。化学再生后,用化学沉淀法使再生废液中氨氮由202 mg/L降到16.3 mg/L。  相似文献   

11.
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.  相似文献   

12.
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.  相似文献   

13.
Organochlorine compounds in a three-step terrestrial food chain   总被引:1,自引:0,他引:1  
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.  相似文献   

14.
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.  相似文献   

15.
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, 240Pu, 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.  相似文献   

16.
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.  相似文献   

17.
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.  相似文献   

18.
土壤中砷的化学平衡   总被引:2,自引:0,他引:2  
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。  相似文献   

19.
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.  相似文献   

20.
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.  相似文献   

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