CN102252869A - Passive sampler for organic pollutants in sediments based on ionic liquid - Google Patents
Passive sampler for organic pollutants in sediments based on ionic liquid Download PDFInfo
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- CN102252869A CN102252869A CN2011100609798A CN201110060979A CN102252869A CN 102252869 A CN102252869 A CN 102252869A CN 2011100609798 A CN2011100609798 A CN 2011100609798A CN 201110060979 A CN201110060979 A CN 201110060979A CN 102252869 A CN102252869 A CN 102252869A
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- 239000002608 ionic liquid Substances 0.000 title claims abstract description 26
- 239000013049 sediment Substances 0.000 title claims abstract description 22
- 239000002957 persistent organic pollutant Substances 0.000 title claims abstract description 15
- 238000005070 sampling Methods 0.000 claims abstract description 24
- 229920001684 low density polyethylene Polymers 0.000 claims abstract description 5
- 239000004702 low-density polyethylene Substances 0.000 claims abstract description 5
- 239000012528 membrane Substances 0.000 claims description 12
- VVQNEPGJFQJSBK-UHFFFAOYSA-N Methyl methacrylate Chemical compound COC(=O)C(C)=C VVQNEPGJFQJSBK-UHFFFAOYSA-N 0.000 claims description 9
- 229920005372 Plexiglas® Polymers 0.000 claims description 9
- 150000001768 cations Chemical class 0.000 claims description 2
- 238000003780 insertion Methods 0.000 claims description 2
- 230000037431 insertion Effects 0.000 claims description 2
- RAXXELZNTBOGNW-UHFFFAOYSA-N imidazole Natural products C1=CNC=N1 RAXXELZNTBOGNW-UHFFFAOYSA-N 0.000 claims 5
- 238000007731 hot pressing Methods 0.000 claims 1
- 150000002460 imidazoles Chemical class 0.000 claims 1
- 239000003344 environmental pollutant Substances 0.000 abstract description 10
- 231100000719 pollutant Toxicity 0.000 abstract description 10
- 238000012544 monitoring process Methods 0.000 abstract description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 8
- 239000003960 organic solvent Substances 0.000 abstract description 6
- 238000004458 analytical method Methods 0.000 abstract description 2
- 238000010828 elution Methods 0.000 abstract 1
- 238000002474 experimental method Methods 0.000 abstract 1
- 239000011521 glass Substances 0.000 abstract 1
- VOXZDWNPVJITMN-ZBRFXRBCSA-N 17β-estradiol Chemical compound OC1=CC=C2[C@H]3CC[C@](C)([C@H](CC4)O)[C@@H]4[C@@H]3CCC2=C1 VOXZDWNPVJITMN-ZBRFXRBCSA-N 0.000 description 10
- IISBACLAFKSPIT-UHFFFAOYSA-N bisphenol A Chemical compound C=1C=C(O)C=CC=1C(C)(C)C1=CC=C(O)C=C1 IISBACLAFKSPIT-UHFFFAOYSA-N 0.000 description 10
- 238000000034 method Methods 0.000 description 7
- 229960005309 estradiol Drugs 0.000 description 6
- 238000011160 research Methods 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- -1 1-hexadecyl-3-methylimidazolium hexafluorophosphate Chemical compound 0.000 description 3
- WEVYAHXRMPXWCK-UHFFFAOYSA-N Acetonitrile Chemical compound CC#N WEVYAHXRMPXWCK-UHFFFAOYSA-N 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 229920000742 Cotton Polymers 0.000 description 1
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 238000000944 Soxhlet extraction Methods 0.000 description 1
- XOSXLKOQPJEFHR-UHFFFAOYSA-N [N].CC#N Chemical compound [N].CC#N XOSXLKOQPJEFHR-UHFFFAOYSA-N 0.000 description 1
- 238000012863 analytical testing Methods 0.000 description 1
- 150000001449 anionic compounds Chemical class 0.000 description 1
- 150000001450 anions Chemical group 0.000 description 1
- 230000002124 endocrine Effects 0.000 description 1
- 231100000049 endocrine disruptor Toxicity 0.000 description 1
- 239000000598 endocrine disruptor Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003920 environmental process Methods 0.000 description 1
- 239000003292 glue Substances 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 230000002452 interceptive effect Effects 0.000 description 1
- 150000002632 lipids Chemical class 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000000622 liquid--liquid extraction Methods 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
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- 229910021645 metal ion Inorganic materials 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 150000002891 organic anions Chemical class 0.000 description 1
- 150000002892 organic cations Chemical class 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
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- 239000002861 polymer material Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
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- 150000003839 salts Chemical class 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 239000010935 stainless steel Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
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Abstract
Description
技术领域 technical field
本发明涉及一种以离子液体作为接受相,用以采集监测沉积物中有机污染物存在水平的被动采样新装置。The invention relates to a new passive sampling device which uses ionic liquid as a receiving phase to collect and monitor the existing level of organic pollutants in sediments.
背景技术 Background technique
沉积物是水环境中有机污染物的“汇”,天然水体中绝大多数有机污染物都会最终进入沉积物中。而当环境发生变化时,部分污染物又可能重新进入水相,形成二次污染。因此,对沉积物中有机污染物的环境监测工作,对保障人类健康和维护环境生态都具有非常重要的意义。Sediment is the "sink" of organic pollutants in the aquatic environment, and most of the organic pollutants in natural water bodies will eventually enter the sediment. When the environment changes, some pollutants may re-enter the water phase to form secondary pollution. Therefore, the environmental monitoring of organic pollutants in sediments is of great significance to the protection of human health and the maintenance of environmental ecology.
主动采样监测方法存在诸多限制因素,例如,采集水样体积有限、浓缩倍数不高、干扰物质的去除步骤繁琐、费用昂贵、分析结果往往只能代表水环境中有机污染物的瞬时情况。因此,可连续采集采样周期内环境介质中的污染物积分浓度的被动采样技术,被广泛地应用于环境中痕量有机污染物的监测和环境过程研究中。然而,目前有机污染物被动采样技术中广泛使用的接受相多为中性类脂(针对非极性有机物)或交换树脂(针对极性有机物),其在采样后的前处理过程中往往需要使用大量对环境危害较大的挥发性有机溶剂;并且,用于沉积物中有机污染物被动采样监测的被动采样技术还有待开发。There are many limiting factors in the active sampling monitoring method, for example, the limited volume of water samples collected, the concentration factor is not high, the removal steps of interfering substances are cumbersome and expensive, and the analysis results often only represent the instantaneous situation of organic pollutants in the water environment. Therefore, the passive sampling technology, which can continuously collect the integral concentration of pollutants in the environmental medium within the sampling period, is widely used in the monitoring of trace organic pollutants in the environment and in the research of environmental processes. However, the accepting phases widely used in passive sampling techniques for organic pollutants are mostly neutral lipids (for non-polar organics) or exchange resins (for polar organics), which often need to be used in the pretreatment process after sampling There are a large number of volatile organic solvents that are harmful to the environment; moreover, passive sampling techniques for passive sampling and monitoring of organic pollutants in sediments have yet to be developed.
离子液体是指室温或近于室温(低于100℃)下为液体的盐,通常由含氮、磷的有机阳离子和无机或有机阴离子构成。其具有的一些独特的物理化学性质,例如:蒸气压极小,可溶解许多有机物、无机物及高分子材料;具有较好的热稳定性,不可燃;可通过调节阴、阳离子的组成来调节它的熔点、粘度、密度和在水及其它有机溶剂中的溶解性等。这些独特的性质使其在许多领域完全有可能代替传统有机溶剂,成为安全、环境友好的新型溶剂。由于离子液体具有上述环境友好的特点及结构的“可设计”性,使其具有应用于沉积物中极性有机污染物富集监测的可能。目前,离子液体被成功应用在极性/非极性有机物、金属离子等物质的液液萃取研究中;也有少量采用离子液体对土壤/沉积物中各类污染物进行提取的研究工作发表。Ionic liquids refer to salts that are liquid at or near room temperature (below 100°C), and are usually composed of organic cations containing nitrogen and phosphorus and inorganic or organic anions. It has some unique physical and chemical properties, such as: extremely small vapor pressure, can dissolve many organic, inorganic and polymer materials; has good thermal stability, non-flammable; can be adjusted by adjusting the composition of anions and cations Its melting point, viscosity, density and solubility in water and other organic solvents, etc. These unique properties make it possible to replace traditional organic solvents in many fields and become safe and environmentally friendly new solvents. Due to the above-mentioned environment-friendly characteristics and the "designable" nature of the structure, ionic liquids have the possibility of being applied to the enrichment monitoring of polar organic pollutants in sediments. At present, ionic liquids have been successfully applied in the research of liquid-liquid extraction of polar/non-polar organic substances, metal ions and other substances; there are also a small number of research works published on the use of ionic liquids to extract various pollutants in soil/sediment.
发明内容 Contents of the invention
本发明旨在提供一种以离子液体为接受相的被动采样器,它可对沉积物间隙水中的有机污染物进行连续采集,从而反映沉积物中该污染物的污染水平。此技术简便、经济、高效,并且对有机溶剂消耗较少。The invention aims to provide a passive sampler with ionic liquid as the accepting phase, which can continuously collect the organic pollutants in the interstitial water of sediments, so as to reflect the pollution level of the pollutants in the sediments. This technique is simple, economical, efficient, and consumes less organic solvents.
本发明提供的被动采样装置结构如下:被动采样器整体为平板垂直插入式,由填充离子液体的低密度聚乙烯膜管和带楔形尖头的有机玻璃固定框两部分组成。有机玻璃固定框主体为两块长为120mm、宽为40mm、厚度为3mm的有机玻璃板,板内中空部分为采样窗,采样窗长为70mm、宽为20mm,即有效面积14cm2,固定框前端的楔形尖头底面为长40mm、宽9mm的长方形,尖头高16mm。楔形尖头材质为有机玻璃,用胶水与固定框主体粘合(如图1所示)。称取100mg离子液体填充到长度为80mm、宽度为25mm的低密度聚乙烯膜管中,用热封仪对膜管两端各5mm部分进行热压封口,以此作为被动采样器的接受相(如图2所示)。将接受相膜管置于两片有机玻璃固定框之间,通过不锈钢垫圈、螺钉和螺母对膜管进行固定。The structure of the passive sampling device provided by the present invention is as follows: the passive sampler is a flat vertical insertion type as a whole, and is composed of a low-density polyethylene film tube filled with ionic liquid and a plexiglass fixed frame with a wedge-shaped tip. The main body of the plexiglass fixed frame is two plexiglass plates with a length of 120mm, a width of 40mm, and a thickness of 3mm. The hollow part inside the plate is a sampling window . The bottom surface of the wedge-shaped tip at the front end is a rectangle with a length of 40mm and a width of 9mm, and the tip is 16mm high. The material of the wedge-shaped tip is plexiglass, and it is glued to the main body of the fixed frame with glue (as shown in Figure 1). Weigh 100mg of ionic liquid and fill it into a low-density polyethylene film tube with a length of 80mm and a width of 25mm, and use a heat sealer to seal the 5mm parts at both ends of the film tube with heat and pressure, and use this as the receiving phase of the passive sampler ( as shown in picture 2). Place the receiving phase membrane tube between two plexiglass fixing frames, and fix the membrane tube with stainless steel washers, screws and nuts.
该被动采样器可以直接插入水体沉积物中进行被动采样监测,根据作为监测对象的目标化合物的不同,可以选择填充不同性质的离子液体作为接受相。监测的周期根据实际需要、目标化合物的性质以及污染水平而定。The passive sampler can be directly inserted into the water body sediment for passive sampling and monitoring, and can be filled with ionic liquids of different properties as the receiving phase according to the different target compounds as the monitoring objects. The period of monitoring depends on the actual needs, the nature of the target compound and the pollution level.
被动采样所得样品的前处理方法为:在采样器回收后,用洁净脱脂棉将膜管外表面擦干。剪开膜管,将离子液体转移至试管,并用5ml乙腈分次冲洗膜管内表面,冲洗液也转移至试管中,将试管内的乙腈氮吹至1ml,即可采用仪器对样品中的污染物进行分析检测。The pretreatment method of the sample obtained by passive sampling is as follows: after the sampler is recovered, dry the outer surface of the membrane tube with clean absorbent cotton. Cut the membrane tube, transfer the ionic liquid to the test tube, and rinse the inner surface of the membrane tube with 5ml of acetonitrile, and transfer the rinse solution to the test tube, blow the acetonitrile nitrogen in the test tube to 1ml, and then use the instrument to detect the pollutants in the sample. Perform analytical testing.
经实验室研究证明,使用离子液体1-十六烷基-3-甲基咪唑六氟磷酸盐建立的被动采样装置,对天津市某排污河沉积物中2种内分泌干扰物类有机污染物(17β-雌二醇和双酚A)可实现有效采集(图3);将采样器分别放置于4个采自不同位置、污染水平各不相同的排污河沉积物中,7日后采样器中目标污染物双酚A和17β-雌二醇浓度的对数值,与经索氏提取法提取测试的沉积物中污染物浓度的对数值具有较好的相关性(图4和图5)。Laboratory research has proved that the passive sampling device established by using ionic liquid 1-hexadecyl-3-methylimidazolium hexafluorophosphate can detect two kinds of endocrine disruptor organic pollutants ( 17β-estradiol and bisphenol A) can achieve effective collection (Figure 3); the samplers were placed in four sewage river sediments collected from different locations and with different pollution levels, and the target pollution in the sampler after 7 days The logarithmic values of the concentrations of bisphenol A and 17β-estradiol had a good correlation with the logarithmic values of the pollutant concentrations in the sediments extracted by the Soxhlet extraction method (Fig. 4 and Fig. 5).
附图说明 Description of drawings
图1带楔形尖头的有机玻璃固定框示意图Figure 1 Schematic diagram of a plexiglass fixed frame with a wedge-shaped tip
图2填充离子液体的低密度聚乙烯膜管接受相示意图Fig.2 Schematic diagram of receiving phase of LDPE membrane tube filled with ionic liquid
图3基于离子液体的被动采样装置对2种内分泌干扰物——双酚A和17β-雌二醇的被动采样静态富集曲线Figure 3 The passive sampling static enrichment curves of two endocrine disruptors—bisphenol A and 17β-estradiol—by the passive sampling device based on ionic liquids
图4基于离子液体1-十六烷基-3-甲基咪唑六氟磷酸盐的被动采样装置对天津市某排污河4个不同位置沉积物中双酚A的7日富集浓度对数值(log CP_双酚A)与沉积物中双酚A浓度对数值(log CS_双酚A)的线性关系图Figure 4 is based on the passive sampling device of ionic liquid 1-hexadecyl-3-methylimidazolium hexafluorophosphate to the 7-day enrichment concentration logarithm of bisphenol A in the sediments of 4 different locations of a sewage river in Tianjin ( The linear relationship between log C P_bisphenol A ) and the logarithm value of bisphenol A concentration in the sediment (log C S_bisphenol A )
图5基于离子液体1-十六烷基-3-甲基咪唑六氟磷酸盐的被动采样装置对天津市某排污河4个不同位置沉积物中17β-雌二醇的7日富集浓度对数值(log CP_雌二醇)与沉积物中17β-雌二醇浓度对数值(log CS_雌二醇)的线性关系图Fig. 5 The 7-day enrichment concentration of 17β-estradiol in the sediments of four different locations in a sewage river in Tianjin by passive sampling device based on ionic liquid 1-hexadecyl-3-methylimidazolium hexafluorophosphate The linear relationship between the value (log C P_estradiol ) and the logarithm of the concentration of 17β-estradiol in the sediment (log C S_estradiol )
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Cited By (6)
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CN104729878A (en) * | 2013-12-24 | 2015-06-24 | 南开大学 | Novel passive water body sampling technique based on supported ionic liquid |
CN105241723A (en) * | 2015-10-27 | 2016-01-13 | 中国科学院生态环境研究中心 | Adsorption rod passive sampler for measuring concentrations of water pollutants |
CN107219344A (en) * | 2017-06-02 | 2017-09-29 | 南开大学 | A kind of method for predicting PAHs in soil biological effectiveness |
CN108507830A (en) * | 2018-07-16 | 2018-09-07 | 未名环境分子诊断(常熟)有限公司 | A kind of Passive sampler and the method for sampling for nonpolar organic pollutants acquisition in sewer |
CN110621973A (en) * | 2017-05-19 | 2019-12-27 | 乔治洛德方法研究和开发液化空气有限公司 | Method for analyzing a cryogenic liquid for trace contaminants |
CN117129273A (en) * | 2023-10-24 | 2023-11-28 | 扬州市疾病预防控制中心 | Sewage passive sampling device and sampling method thereof |
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CN1804575A (en) * | 2005-12-27 | 2006-07-19 | 南开大学 | Semipermeable membrane for sampling organic contaminant in enriched water environment |
CN101038249A (en) * | 2006-03-14 | 2007-09-19 | 中国科学院过程工程研究所 | Method and device for measuring absorbing capacity of organic solvent volatile gas in ion liquid |
Cited By (8)
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CN104729878A (en) * | 2013-12-24 | 2015-06-24 | 南开大学 | Novel passive water body sampling technique based on supported ionic liquid |
CN105241723A (en) * | 2015-10-27 | 2016-01-13 | 中国科学院生态环境研究中心 | Adsorption rod passive sampler for measuring concentrations of water pollutants |
CN110621973A (en) * | 2017-05-19 | 2019-12-27 | 乔治洛德方法研究和开发液化空气有限公司 | Method for analyzing a cryogenic liquid for trace contaminants |
CN107219344A (en) * | 2017-06-02 | 2017-09-29 | 南开大学 | A kind of method for predicting PAHs in soil biological effectiveness |
CN108507830A (en) * | 2018-07-16 | 2018-09-07 | 未名环境分子诊断(常熟)有限公司 | A kind of Passive sampler and the method for sampling for nonpolar organic pollutants acquisition in sewer |
CN108507830B (en) * | 2018-07-16 | 2024-03-26 | 未名环境分子诊断(常熟)有限公司 | Passive sampler and sampling method for collecting nonpolar organic pollutants in sewer |
CN117129273A (en) * | 2023-10-24 | 2023-11-28 | 扬州市疾病预防控制中心 | Sewage passive sampling device and sampling method thereof |
CN117129273B (en) * | 2023-10-24 | 2024-03-01 | 扬州市疾病预防控制中心 | Sewage passive sampling device and sampling method thereof |
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