粗媒体颗粒流化床半干法烟气脱硫

开发了粗媒体颗粒流化床半干法烟气脱硫技术。在流化床内加入惰性粗媒体颗粒，改善脱硫剂与烟气的接触。延长脱硫剂在床内的停留时间，促进脱硫反应进行，提高脱硫效率和脱硫剂利用率。以工业用石灰石为脱硫剂，实验研究了粗媒体颗粒的加入量及其他操作条件对此过程脱硫效率的影响。结果表明：随着粗媒体颗粒粒径减小及床内加入量增加，烟气脱硫效率提高；随着Ca／S增大、饱和接近度降低、空速及脱硫剂颗粒粒径减小，脱硫效率提高。当粗媒体颗粒的静止床高为122mm，饱和接近度为15～18℃、空速为2850h^-1、钙硫比为1．0—1．1、脱硫剂粒径为64μm时，脱硫效率可达90％以上。     

钙基半干法燃煤烟气脱硫技术的影响因素

半干法烟气脱硫技术因具有耗水量少、产物易处理等特点而备受关注.基于固定床反应器研究了反应温度、脱硫剂Ca(OH)2颗粒粒径、反应空速及烟气中水蒸气体积分数对Ca(OH)2脱硫性能的影响.结果表明,Ca(OH)2颗粒粒径的减小、反应空速的降低、烟气中水蒸气体积分数的提高及低反应温度等因素,有利于SO2的脱除、Ca(OH)...     

高活性脱硫剂脱硫工艺的实验研究

对以粉煤灰为原料制备的高活性脱硫剂进行了半干法烟气脱硫实验研究,考虑添加剂、脱硫剂加入量、反应温度、烟气流量工艺因素的影响时该活性脱硫剂的脱硫性能;实验结果表明,加入添加剂后,脱硫效率提高1.5%～8.1%;当烟气流量＜2 m3/min,钙硫比取1.5～2.0范围时,脱硫效率较高;一定范围内反应温度变化对脱硫效率影响不大.     

旁通式烟气循环流化床脱硫特性的数值模拟

应用标准k-ε模型、DPM模型和物质输运与化学反应模型模拟烟气循环流化床脱硫的两相流动及化学反应,模拟结果和实验数据符合较好。提出了一种旁通式烟气循环流化床,并进一步研究了钙硫比和脱硫剂粒径对旁通脱硫塔脱硫效率的影响。结果表明,脱硫剂颗粒粒径从15μm增大到300μm时,旁通式脱硫塔的脱硫效率略有降低但变化不大;当钙硫摩尔比从0.8增大到1.3时,脱硫效率随之有明显的增加,当钙硫比大于1.3时,脱硫效率随钙硫比的增大略有增加。     

烧结烟气脱硫剂性能的研究

为了提高脱硫效率和合理利用烧结过程中产生的机头灰,在半干法烟气脱硫剂生石灰中,加入一定量的烧结机头灰作为脱硫催化剂。在测定机头灰与生石灰化学成分、粒度和比表面积的基础上,研究和分析了机头灰与生石灰的质量配比对于脱硫效率的影响。结果表明,脱硫剂与机头灰在粒径分布和比表面积上都较接近,但经过消化活化后的混合脱硫剂的比表面积明显增大。当机头灰添加量为脱硫剂质量的2%～5%时,脱硫效率提高了2%～3%。机头灰与生石灰的胶凝反应以及机头灰中Fe2O3的催化作用是主要的作用机理。     

高活性脱硫剂脱硫工艺的实验研究

对以粉煤灰为原料制备的高活性脱硫剂进行了半干法烟气脱硫实验研究，考虑添加剂、脱硫剂加入量、反应温度、烟气流量工艺因素的影响时该活性脱硫剂的脱硫性能；实验结果表明，加入添加剂后，脱硫效率提高1．5％～8．1％；当烟气流量〈2m^3／min，钙硫比取1．5—2．0范围时，脱硫效率较高；一定范围内反应温度变化对脱硫效率影响不大。     

半干半湿法烟气脱硫主要影响因素分析

建立了半干法气流床烟气脱硫实验反应装置。实验研究了温度、绝对含湿量和飞灰对烟气脱硫的影响。烟气温度在65～130℃之间，绝对含湿量通过改变蒸汽量调节，在0％～10％之间，并且采用飞灰一次加入来模拟返灰，石灰与粉煤灰的比例分别为1：3，1：5和1：8。结果表明，没有水蒸气加入时，温度的升高对脱硫效率影响不大，加入水蒸气后温度为68℃左右时，脱硫效率最高；65℃时，绝对含湿量在7．3％时脱硫效率最高；在T=68℃、Ca／S：1．2时，与不加粉煤灰的脱硫剂相比，利用石灰／粉煤灰=1：8的混合脱硫剂时，脱硫效率提高了12．8％。     

半干半湿法烟气脱硫主要影响因素分析

建立了半干法气流床烟气脱硫实验反应装置。实验研究了温度、绝对含湿量和飞灰对烟气脱硫的影响。烟气温度在65～130℃之间,绝对含湿量通过改变蒸汽量调节,在0%～10%之间,并且采用飞灰一次加入来模拟返灰,石灰与粉煤灰的比例分别为1∶3,1∶5和1∶8。结果表明,没有水蒸气加入时,温度的升高对脱硫效率影响不大,加入水蒸气后温度为68℃左右时,脱硫效率最高;65℃时,绝对含湿量在73%时脱硫效率最高;在T=68℃、Ca/S=12时,与不加粉煤灰的脱硫剂相比,利用石灰/粉煤灰=1∶8的混合脱硫剂时,脱硫效率提高了128%。     

内循环流化床烟气脱硫技术的实验研究

通过对流化床烟气脱硫吸收塔塔顶和塔底结构的改进,开发出一种新的内循环流化床烟气脱硫工艺。该工艺以60～80目细砂作为主要床料,在流化气速为2～5m/s情况下,实现了绝大部分固体颗粒在脱硫塔内的内循环,从而强化了热质传递,避免了粘壁现象。考察了各种因素对脱硫效率的影响,结果表明,绝热饱和温度差是影响脱硫效率的显著因素,颗粒浓度是保证系统稳定运行的关键因素。在Ca/S为12和颗粒浓度为10kg/m3条件下,系统能连续稳定运行,脱硫效率达90%以上。     

内循环流化床烟气脱硫技术的实验研究

通过对流化床烟气脱硫吸收塔塔顶和塔底结构的改进，开发出一种新的内循环流化床烟气脱硫工艺。该工艺以60～80目细砂作为主要床料，在流化气速为2～5m／s情况下，实现了绝大部分固体颗粒在脱硫塔内的内循环，从而强化了热质传递，避免了粘壁现象。考察了各种因素对脱硫效率的影响，结果表明，绝热饱和温度差是影响脱硫效率的显著因素，颗粒浓度是保证系统稳定运行的关键因素。在Ca／S为1．2和颗粒浓度为10kg／m^3条件下，系统能连续稳定运行，脱硫效率达90％以上。     

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.