国内成功运营的餐厨垃圾处理厂臭气排放特征研究简

选择目前国内成功运营的餐厨垃圾资源化处理厂为采样点,采用气相色谱-质谱联用（GC/MS）技术对该厂的主要工段,如卸料室、破碎室、湿热反应器出气口、好氧发酵仓、厌氧发酵区以及厂界的臭气进行了定性和定量的分析。结果表明,6个采样点共检测出包括芳香烃、硫化物、卤代物、烯烃、烷烃、醇、醛、酮和酯在内的9类66种物质,各采样点臭气总浓度分别为：11.738、18.390、30.917、25.097、4.737和2.635 mg/m³。其中湿热反应器出气口处恶臭气体浓度最高,其芳香烃、硫化物、卤代物、烯烃、烷烃、酮及酯类物质均高于其他检测点,需对该工段进行重点监测和控制。恶臭排放特征分析表明,各点的H₂S浓度均超过嗅觉阈值,除厂界外甲硫醇和二甲二硫检测值均超过嗅觉阈值。     

国内成功运营的餐厨垃圾处理厂臭气排放特征研究

选择目前国内成功运营的餐厨垃圾资源化处理厂为采样点,采用气相色谱．质谱联用（GC／MS）技术对该厂的主要工段,如卸料室、破碎室、湿热反应器出气口、好氧发酵仓、厌氧发酵区以及厂界的臭气进行了定性和定量的分析。结果表明,6个采样点共检测出包括芳香烃、硫化物、卤代物、烯烃、烷烃、醇、醛、酮和酯在内的9类66种物质,各采样点臭气总浓度分别为：11．738、18．390、30．917、25．097、4．737和2．635mg／m3。其中湿热反应器出气口处恶臭气体浓度最高,其芳香烃、硫化物、卤代物、烯烃、烷烃、酮及酯类物质均高于其他检测点,需对该工段进行重点监测和控制。恶臭排放特征分析表明,各点的H2S浓度均超过嗅觉阈值,除厂界外甲硫醇和二甲二硫检测值均超过嗅觉阈值。     

天津市不同功能区大气挥发性有机物污染特征及来源分析

利用天津市某交通居民混合区(以下简称混合区)和某废旧机电拆解加工工业区(以下简称工业区)的大气挥发性有机物(VOCs)在线监测数据,分析了天津市不同功能区大气VOCs的浓度水平、组成特征、季节变化和污染来源。结果表明,混合区监测的烷烃、不饱和脂肪烃和芳香烃3类VOCs的质量浓度分别为48.26、15.34、34.45μg/m3,总VOCs质量浓度为98.05μg/m3;工业区监测的烷烃、不饱和脂肪烃、芳香烃、卤代烷烃、卤代烯烃和卤代芳香烃6类VOCs的质量浓度分别为18.79、10.76、9.41、43.24、12.86、2.16μg/m3,总VOCs质量浓度为97.22μg/m3。混合区和工业区的大气VOCs浓度均为夏季最高,但混合区秋季次高,冬季最低,而工业区冬季次高,春季最低。混合区VOCs主要来源于机动车尾气排放和化石燃料的燃烧;工业区VOCs主要来源于有机溶剂和氟利昂等制冷剂、发泡剂的挥发。     

郑州市环境空气中挥发性卤代烃污染特征与健康风险评价

用苏玛罐采样、气相色谱/质谱法分析,研究郑州市环境空气中挥发性卤代烃(VHCs)的污染特征并对其健康风险进行评价。结果显示,郑州市环境空气中共定性检出43种VHCs,其中卤代烷烃28种,卤代烯烃9种,卤代芳香烃6种,卤代烷烃、卤代烯烃、卤代芳香烃的年均质量浓度分别为67.40、34.70、20.30μg/m~3,郑州市各功能区环境空气中VHCs化合物种类稍有差异,背景点VHCs浓度与其他功能区并无显著差异,说明VHCs污染呈现区域性特征;垂直方向上,卤代烷烃浓度随高度呈先降后升趋势,卤代烯烃和卤代芳香烃浓度随高度呈先升后降趋势。健康风险评价结果显示,VHCs单体化合物对人体的非致癌风险均在安全范围内,而总风险超出了安全范围,氯乙烯、三氯乙烯、四氯化碳、氯仿、1,2-二溴乙烷、1,2-二氯乙烷和1,1,2-三氯乙烷的致癌风险超出美国环境保护署规定的可接受值;致癌风险合计为5.32×10~(-4),说明长期暴露于环境空气中对人群健康具有一定危害。     

天津市滨海新区夏季挥发性有机物的污染特征分析

对天津市滨海新区夏季挥发性有机物(VOCs)进行在线观测,分析其夏季污染特征。结果表明:83种检出VOCs平均质量浓度为288.14μg/m3,各类化合物浓度贡献排序为烷烃(39.8%)卤代链烃(26.5%)芳香烃(13.9%)烯烃(13.1%)炔烃(4.4%)卤代芳香烃(2.3%),各组分中浓度最高的为正丁烷和正戊烷,占VOCs比例高达8.1%和7.0%;苯和甲苯也有相当含量,平均质量浓度均超过7μg/m3,分别占VOCs的2.5%和2.4%。天津市滨海新区VOCs日变化呈单谷型,与交通早晚高峰关系不大,苯/甲苯(体积比)为1.32,说明化石工业排放等对天津市滨海新区大气中VOCs影响较机动车尾气显著。聚类分析发现,天津市滨海新区VOCs来源分为3类,一类是汽油挥发和液化石油气、天然气泄漏,一类是化石工业和其他工业生产过程排放,一类是机动车尾气及植物排放,其中前两类为主要来源。     

生活垃圾填埋场填埋气中挥发性有机物释放规律分析

于2007年2月在上海老港垃圾填埋场选取10个不同填满年限的填埋单元进行填埋气的采样分析,用色谱-质谱技术检测了填埋气中的挥发性有机物(VOCs).检测到脂肪烃、卤代脂肪烃、单环芳烃、醚和酮等5类22种化合物,其中11种为美国环境保护署优先控制污染物,甲苯、乙苯和间,对二甲苯的浓度较高.填满时间距采样时间较近(1～2年)的填埋单元检出的VOCs种类较多,脂肪烃和单环芳烃的浓度随填满时间的增加呈现较明显的衰减特征,而卤代脂肪烃、醚和酮的浓度与填满时间的相关性不显著.检出的5种化合物中,1,1,1三氯乙烷、甲苯和间,对-二甲苯的浓度均低于美国加利福尼亚州环保局推荐的健康阈值,氯乙烯和苯则超过该阈值.     

餐厨垃圾两相厌氧发酵产甲烷相恶臭排放规律

为了研究餐厨垃圾两相厌氧发酵产甲烷相恶臭排放规律,在中温(35℃)条件下,以餐厨垃圾为发酵底物进行中试规模的两相连续式厌氧发酵试验,并对一个周期内不同时间段产甲烷相产生的气体进行采样,分析其臭气浓度和物质浓度,结合各组分的阈稀释倍数,筛选出主要的恶臭污染物。结果表明,在发酵系统稳定运行阶段,产甲烷相产生的臭气浓度较大,都在23万以上;产甲烷相产生的恶臭物质主要包括硫化物、萜烯类、含氧类和芳烃类四类化合物,其中质量浓度最高的恶臭物质是硫化氢,超过了150 mg/m3;产甲烷相的主要致臭物质是硫化物,其中贡献最大的是硫化氢,其阈稀释倍数都在26万以上,其次为乙硫醇﹥甲硫醇﹥乙硫醚,这3种物质的阈稀释倍数都在4 000以上;除了这4种硫化物,丁醛对恶臭的贡献也比较大,其阈稀释倍数也在4 000以上。     

上海城郊大气挥发性有机物污染特征、活性组分及风险评估

为了解上海城郊大气中挥发性有机物(VOCs)的时空污染特征及其对人体潜在健康风险,选取上海某城郊10个点位进行连续6年(2012—2017年)的采样分析。结果表明,上海该城郊大气VOCs平均质量浓度为(243.80±151.52)μg/m3,其中烷烃、卤代烃、芳香烃、含氧VOCs和不饱和脂肪烃依次占VOCs总浓度的45.72%、20.04%、18.84%、11.19%、4.21%。上海郊区不同功能区VOCs总浓度年际变化趋势较为一致,总体呈下降趋势;在空间上,化工区主干道路附近的两采样点VOCs质量浓度最高,分别为307.81、340.97μg/m~3。O3生成潜势和等效丙烯浓度计算结果显示,芳香烃为上海城郊大气中最主要的活性物种,且关键活性组分为甲苯、间/对-二甲苯和异丁烷等。上海城郊大气中27种风险VOCs的总致癌风险值为3.02×10~(-4),高于可接受限值(1.00×10~(-4)),长期暴露可能有致癌风险。     

山西省典型炼焦企业化产工段挥发性有机物排放特征及臭氧生成潜势

选取山西省某典型焦化企业化产工段的冷鼓工序、洗脱苯工序、脱硫工序、压滤车间4个工序,采样监测其挥发性有机物(VOCs)排放特征,并运用等效丙烯浓度法和最大增量反应活性(MIR)法综合评价其VOCs的化学反应活性和臭氧生成潜势。结果表明:(1)冷鼓工序、洗脱苯工序、脱硫工序、压滤车间4个工序共检测出32种VOCs,各工序的总VOCs分别为64 809.50、4 933.80、4 610.20、6 346.90μg/m~3。(2)4个工序检出的VOCs物种均以芳香烃和卤代烃为主,其中芳香烃以苯、甲苯、二甲苯为主,卤代烃以1,2-二氯乙烷为主。(3)芳香烃为4个工序中化学反应活性最大的污染物质,且各工序中1,2,4-三甲苯和1,3,5-三甲苯均有较高的化学反应活性和臭氧生成潜势。(4)在排放浓度和臭氧生成潜势方面,冷鼓工序的贡献均为最大,是化产工段需要进行VOCs治理的重点工序。     

沈阳市某工业园区挥发性有机物活性及来源解析

利用沈阳市某工业园区大气监测数据,依据等效丙烯浓度(PEC)和臭氧生成潜势(OFP)法识别园区挥发性有机物(VOCs)活性物种,基于主成分分析(PCA)法和正定矩阵因子分析(PMF)模型进行VOCs来源解析.结果表明:芳香烃、烯烃和C5烷烃为园区活性较强的组分;PCA法和PMF模型的VOCs来源解析结果基本一致,园区V...     

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.     

Evaluation of trichloroethene recovery processes in heterogeneous aquifer cells flushed with biodegradable surfactants

The ability of two biodegradable surfactants, polyoxyethylene (20) sorbitan monooleate (Tween 80) and sodium dihexyl sulfosuccinate (Aerosol MA), to recover a representative dense non-aqueous-phase liquid (DNAPL), trichloroethene (TCE), from heterogeneous porous media was evaluated through a combination of batch and aquifer cell experiments. An aqueous solution containing 3.3% Aerosol MA, 8% 2-propanol and 6 g/l CaCl(2) yielded a weight solubilization ratio (WSR) of 1.21 g TCE/g surfactant, with a corresponding liquid-liquid interfacial tension (IFT) of 0.19 dyn/cm. Flushing of aquifer cells containing a TCE-DNAPL source zone with approximately two pore volumes of the AMA formulation resulted in substantial (>30%) mobilization of TCE-DNAPL. However, a TCE mass recovery of 81% was achieved when the aqueous-phase flow rate was sufficient to displace the mobile TCE-DNAPL toward the effluent well. Aqueous solutions of Tween 80 exhibited a greater capacity to solubilize TCE (WSR=1.74 g TCE/g surfactant) and exerted markedly less reduction in IFT (10.4 dyn/cm). These data contradict an accepted empirical correlation used to estimate IFT values from solubilization capacity, and indicate a unique capacity of T80 to form concentrated TCE emulsions. Flushing of aquifer cells with less than 2.5 pore volumes of a 4% T80 solution achieved TCE mass recoveries ranging from 66 to 85%, with only slight TCE-DNAPL mobilization (<5%) occurring when the total trapping number exceeded 2 x 10(-5). These findings demonstrate the ability of Tween 80 and Aerosol MA solutions to efficiently recover TCE from a heterogeneous DNAPL source zone, and the utility of the total trapping number as a design parameter for a priori prediction of DNAPL mobilization and bank angle formation when flushing with low-IFT solutions. Given their potential to stimulate microbial reductive dechlorination at low concentrations, these surfactants are well-suited for remedial action plans that couple aggressive mass removal followed by enhanced bioremediation to treat chlorinated solvent source zones.     

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。     

The variation of street air levels of PAH and other mutagenic PAC in relation to regulations of traffic emissions and the impact of atmospheric processes

The occurrence of particle associated PAH and other mutagenic PAC was determined in 1996 in the street air of Copenhagen. In addition, particle extracts were tested for mutagenicity. The measurements were compared with previous measurements in 1992/1993. The levels had decreased in this period. The decrease was caused by an implementation of light diesel fuels for buses and the exchange of older petrol-driven passenger cars with catalystequipped new ones. About 65% of the reduction was caused by the application of the light diesel fuels. Under special conditions, chemical processes in the atmosphere produced many more mutagens than the direct emissions. The concentrations of S-PAC and N-PAC were 10 times lower than those of PAH, while the levels of oxy-PAH were in the same order of magnitude as those of PAH. Benzanthrone, an oxy-PAH, is proposed to be formed in the atmosphere in addition to direct emissions. Benzo(a)pyrene, often applied as an air quality criteria indicator, was photochemically degraded in the atmosphere. A strong increase in the mutagenic activities was observed to coincide with a depletion of benzo(a)pyrene.