紫外分光光度法在水中阴离子表面活性剂标准样品研制中的应用

研究了阴离子表面活性剂水溶液的紫外吸收特性，并将研究结果用于阴离子表面活性剂水质标样的稳定性，均匀性和定值工作，简化了操作手续，获得了准确的分析结果。     

水中阴离子表面活性剂的测定

偶氮红两相滴定法在ｐＨ＝７．５的条件下,能测定水和废水中的各种阴离子表面活性剂的摩尔浓度。本文通过对硫酸盐、磺酸盐、苯磺酸盐、肥皂和磷酸盐等各类阴离子表面活性剂的测定,以及干扰试验和实际水样测定,表明此法优于亚甲基蓝分光光度法。方法的变异系数为１．０％（ｎ＝１１）,最小检出浓度０．０５２ｍｇ／Ｌ（ｎ＝２１）,加标回收率９２．１％－１１０．２％,平均１００．６％（ｎ＝１４）。建议水中阴离子表面活性剂     

废水中含磷表面活性剂的测定

应用非水电位滴定法测定了废水中各种烷基磷酸酯钾盐及其单、双酯盐。方法的变异系数分别为２．３％和７．８％（ｎ＝１２）。本法可有效地消除非离子表面活性剂的干扰，适用于化纤油剂的质量检验和上油槽中油剂浓度的测定。     

Test for the effects of three surfactants on the penetration ability of the calcium chloride and water glass solutions in dust

１ＩｎｔｒｏｄｕｃｔｉｏｎＣａｌｃｉｕｍｃｈｌｏｒｉｄｅｉｓｏｆｔｅｎｕｓｅｄｉｎｔｈｅｆｉｅｌｄｏｆｓｏｉｌｓｔａｂｉｌｉｚａｔｉｏｎａｎｄｒａｉｓｉｎｇｄｕｓｔｃｏｎｔｒｏｌｂｅｃａｕｓｅｉｔｃａｎｒｅａｃｔｗｉｔｈｗａｔｅｒｇｌａｓ（Ｗｕ，１９...     

Degradation of Poly(Ethylene Glycol)-Based Nonionic Surfactants by Different Bacterial Isolates from River Water

Different bacterial strains able to attack polyoxyethylene-type nonionic surfactants were isolated by enrichment procedure from the surface waters of the Arno River. Alkylphenol polyethoxylates and alkyl polyethoxylates, as well as polyethylene glycols, were degraded and assimilated by bacterial strains in axenic cultures. Degradative routes of polyethyleneoxide chains were investigated by matching each bacterial isolate with several types of nonionic surfactants and polyethers and by the identification of their degradation products isolated during aerobic digestion experiments. In accordance with previous reports, the first attack led to the shortening of the poly(oxyethylene) chains of the nonionic surfactants. It was found that the strains able to degrade PEG segments of nonionic surfactants possess enzymatic systems unable to degrade free PEGs, whereas those degrading the latter substrates cannot degrade PEG segments coupled to hydrophobic moieties.     

Water solubility enhancements of pyrene by single and mixed surfactant solutions

ＩｎｔｒｏｄｕｃｔｉｏｎＳｕｒｆａｃｔａｎｔｓｅｎｈａｎｃｅｔｈｅｒｅｍｅｄｉａｔｉｏｎｏｆＮＡＰＬ ｃｏｎｔａｍｉｎａｔｅｄｓｉｔｅｓｂｙｉｎｃｒｅａｓｉｎｇｔｈｅａｑｕｅｏｕｓ ｐｈａｓｅｃｏｎｃｅｎｔｒａｔｉｏｎｏｆｔｈｅＮＡＰＬｖｉａｍｉｃｅｌｌｅｆｏｒｍａｔｉｏｎ ,ｍｉｃｒｏｅｍｕｌｓｉｆｉｃａｔｉｏｎ ,ｏｒｍｏｂｉｌｉｚｉｎｇｔｈｅＮＡＰＬｐｈａｓｅ (Ｋｉｌｅ ,1989;Ｅｄｗａｒｄｓ,1991;Ｇｕｈａ ,1998ａ ;Ｋｏ ,1998;Ｚｉｍｍｅｒｍａｎ ,1999;Ｂｅｔｔａｈａｒ,1999;Ｗｉｌｌｓｏｎ ,1999;Ｐａ…     

Perfluorinated Surfactants in Surface and Drinking Waters (9 pp)

Background, Aim and Scope In this paper recent results are provided of an investigation on the discovery of 12 perfluorinated surfactants (PS) in different surface and drinking waters (Skutlarek et al. 2006 a, Skutlarek et al. 2006 b). In the last years, many studies have reported ubiquitous distribution of this group of perfluorinated chemicals, especially perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) in the environment, particularly in wildlife animal and human samples (Giesy and Kannan 2001, Houde et al. 2006, Prevedouros et al. 2006). Perfluorinated surfactants (e.g. PFOS and PFOA) have shown different potentials for reproductory interference and carcinogenity in animal experiments as well as partly long half-lives in humans (Guruge et al. 2006, FSA UK 2006a, FSA UK 2006b, 3M 2005, OECD 2002, Yao and Zhong 2005). They possess compound-dependent extreme recalcitrance against microbiological and chemical degradation and, in addition, they show variable potentials for bioaccumulation in animals and humans (Houde et al. 2006). Materials and Methods: Surface and drinking water samples were collected from different sampling sites: - Surface waters: samples taken from the rivers Rhine, Ruhr, Moehne and some of their tributaries. Further samples were taken from the Rhine-Herne-Canal and the Wesel-Datteln-Canal. - Drinking waters: samples taken in public buildings of the Rhine-Ruhr area. After sample clean-up and concentration by solid-phase extraction, the perfluorinated surfactants were determined using HPLC-MS/MS. Results: All measured concentrations (sum of seven mainly detected components) in the Rhine river and its main tributaries (mouths) were determined below 100 ng/L. The Ruhr river (tributary of the Rhine) showed the highest concentration (94 ng/L), but with a completely different pattern of components (PFOA as major component), as compared with the other tributaries and the Rhine river. Further investigations along the Ruhr river showed remarkably high concentrations of PS in the upper reaches of the Ruhr river and the Moehne river (tributary of the Ruhr) (Ruhr: up to 446 ng/L, Moehne: up to 4385 ng/L). The maximum concentration of all drinking water samples taken in the Rhine-Ruhr area was determined at 598 ng/L with the major component PFOA (519 ng/L). Discussion: The surface water contaminations most likely stem from contaminated inorganic and organic waste materials (so-called 'Abfallgemisch'). This waste material was legally applied to several agricultural areas on the upper reaches of the Moehne. Perfluorinated surfactants could be detected in some suchlike soil samples. They contaminated the river and the reservoir belonging to it, likely by superficial run-off over several months or probably years. Downstream, dilution effects are held responsible for decreasing concentrations of PS in surface waters of the Moehne and the Ruhr river. In analogy to the surface water samples, PS (major component PFOA) can be determined in many drinking water samples of the Rhine-Ruhr area where the water supplies are mainly based on bank filtration and artificial recharge. Conclusions: The concentrations found in drinking waters decreased with the concentrations of the corresponding raw water samples along the flow direction of the Ruhr river (from east to west) and were not significantly different from surface water concentrations. This indicates that perfluorinated surfactants are at present not successfully removed by water treatment steps. Recommendations and Perspectives: Because of their different problematic properties (persistence, mobility, toxicity, bioaccumulation), the concentrations of specific perfluorinated surfactants and their precursors in drinking waters and food have to be minimised. Therefore, it is of utmost importance to take the initiative to establish suitable legal regulations (limitations/ban) concerning the production and use of these surfactants and their precursors. Furthermore, it is indispensable to protect water resources from these compounds. A discussion on appropriate limit values in drinking water and foodstuffs is urgently needed. Concerning the assumed soil contamination, the corresponding regulation (Bioabfall-Verordnung 1998 – Regulation on Organic Waste 1998) should be extended to allow the control of relevant organic pollutants.     

PM2.5中类腐殖质表面活性测定方法与实例分析

建立了大气细粒子中类腐殖质（HULIS）表面活性的动态表征方法,并以华北平原乡村站点冬季大气PM_2.5样品为例,对PM_2.5中HULIS的表面活性进行表征.HULIS碳质组分（HULIS-C）浓度为2.0~4.6μg C/m³,占水溶性有机碳和总有机碳的比例分别为31%~40%和20%~26%.浓度为88~200mg C/L的HULIS水溶液,其表面张力相对于纯水降低了18%~22%.HULIS-C浓度在低于70mg C/L时表面张力降低显著,在88~320mg C/L之间降低相对缓慢.动态表面张力随着时间变化逐渐降低,在液滴形成后200s以内表面张力下降迅速,之后趋于平缓,说明表面活性分子在液滴中扩散趋于稳定需要一定的时间,该特征时间可能影响表面活性物质在云凝结核活化时的作用.证实了在污染地区的大气PM_2.5中含有一定量的表面活性物质,这些物质可能对颗粒物活化为云滴、雾滴过程产生显著影响;表面活性物质的存在可能在外界湿度变化过程中导致颗粒物发生液-液相分离现象,在颗粒物表面形成有机膜,影响活性分子摄取以及半挥发性物质的气-粒分配过程,从而影响大气非均相反应过程.     

农药助剂对蚯蚓(Eisenia foetida)的急性毒性

为评价农药助剂对土壤生物的毒性效应,分别采用滤纸接触法和人工土壤法测定了不同类别农药助剂对赤子爱胜蚓(Eis enia foetida)的急性毒性.结果表明:19种非离子表面活性剂中,烷基酚聚氧乙烯醚与脂肪醇聚氧乙烯醚毒性较高,滤纸法48 h-LC50为7.630 ～ 39.65μg·cm-2,人工土壤法14 d-LC50为876.5 ～2 786.6 mg· kg-1,其它类型非离子表面活性剂毒性较低.5种阴离子表面活性剂中,十二烷基硫酸钠、十二烷基苯磺酸钙毒性高于木质素磺酸钠、木质素磺酸钙、亚甲基双萘磺酸钠,滤纸法48 h-LC50为6575 ～ 41.89 μg· cm-2,人工土壤法14 d-LC50为1 195.0～1 911.7 mg·kg-1.13种溶剂中,二甲苯、乙苯、甲苯、正丁醇、环己酮表现出较高的毒性,滤纸法48 h-LC50为6.587 ～ 57.62 μg ·cm-2,密封人工土壤法48 h-LC50为181.9 ～781.5 mg·kg-1.采用两种方法测得的5种填料高岭土、白炭黑、硅藻土、凹凸棒土和轻质碳酸钙的毒性均较低.采用两种方法测得的毒性系统偏差接近,重现性均较好,并且滤纸接触法测得的毒力高于人工土壤法.     

非离子表面活性剂淋洗萘污染土壤的修复研究

采用土柱实验研究了非离子表面活性剂对焦化厂萘污染砂土的淋洗效果,同时研究了超声预处理对非离子表面活性剂土壤淋洗的增强效果及粉土和粘土对非离子表面活性剂土壤淋洗的不利影响.研究表明,1)1g·L-1的TritonX-100、AEO-9和Tween80对同一萘浓度(192.4mg·kg-1)的土壤洗脱效率分别为73.0%、81.5%和59.0%,2g·L-1的表面活性剂的洗脱效率要高于1g·L-1的洗脱率,分别为96.5%、95.1%和88.2%.2)对土壤进行短时超声处理(80Hz)促进了洗脱率的提高,超声10min的淋洗效果要高于超声5min的淋洗效果;土壤分别经5min和10min超声处理后,2g·L-1浓度的TritonX-100对萘的洗脱率从94%分别提高到98.8%和99.6%,洗脱时间从255min分别减少到172min和160min.3)砂土中含有粉土和粘土对洗脱效果有不利影响,且粘土的影响要更严重,当萘污染的砂土混入5%的粘土时,2g·L-1浓度的TritonX-100对萘的洗脱率从94.7%下降至73.8%,洗脱时间从255min增加至605min,而混入20%的粉土洗脱率仅下降到88.4%,洗脱时间增加至512min.