水溶液中三氯生的吸附研究进展

doi:10.3969/j.issn.2097-2806.2023.08.011

Abstract

Abstract:

As an antibacterial agent, triclosan （TCS） has been widely used in medicine and personal care products, and has become a ubiquitous pollutant in the water environment. Because it has biological accumulation, endocrine interference effect, reproductive toxicity and other hazards, and has been proved to be the precursor of some more toxic substances, the harmless treatment of TCS in water has attracted wide attention. The adsorption treatment method has the advantages of simplicity, green and high efficiency. The adsorption effects of different types of adsorbents on TCS were summarized, the possible effects of some parameters of water on the adsorption process were analyzed, and the kinetics and thermodynamics of the adsorption process were discussed. Finally, the research direction of TCS adsorption treatment was prospected. In general, the development and application of green, low-cost and renewable adsorbents is an important research direction. The modification and compounding of adsorbents are effective ways to improve the adsorption effect. In order to better apply to the treatment of TCS in the actual environment, the adsorption mechanism of TCS and the influence mechanism of environmental factors need to be further studied.

Key words: triclosan, adsorbents, adsorption mechanism, influencing factors

CLC Number:

X703

An Rui,Zhao Qing. Progress in the adsorption of triclosan in aqueous solution[J].China Surfactant Detergent & Cosmetics, 2023, 53(8): 945-953.

Figures/Tables 2

Tab. 1

Adsorption isotherms and kinetic models of TCS on different materials"

吸附剂	TCS初始质量浓度/（mg/L）	吸附剂用量（固液比）	最大吸附容量/（mg/g）	等温线模型	动力学模型	参考文献
颗粒活性炭	2~20	10 mg/200 mL	273.97	L	拟二级	[23]
活性炭纤维	2~20	10 mg/200 mL	312.50	L	拟二级	[23]
多壁碳纳米管	2~20	10 mg/200 mL	243.31	L	拟二级	[23]
商用粉末活性炭	0.2~1.0	10 mg/L	71.5	F	拟二级	[47]
二十二碳六烯酸改性活性炭	0.2~1.0	10 mg/L	395.2	L, F	拟二级	[48]
玉米秸秆生物炭	1~12	2 g/L	6.123 7	L, F	拟二级	[18]
皇竹草生物炭	1~12	2 g/L	5.347 6	L, F	拟二级	[18]
花生壳生物炭	1~12	2 g/L	3.867 4	L, F	拟二级	[18]
洋麻生物炭（750 ℃热解）	5~200	30 mg/30 mL	77.4	L	拟二级	[49]
多壁碳纳米管	1~12	10 mg/250 mL	171.349	F, P-M	拟二级	[22]
硝酸纯化多壁碳纳米管			19.7	L, F	拟二级	[24]
单壁碳纳米管	0.05~2	0.5~2.0 mg/200 mL	558.2	P-M		[45]
多壁碳纳米管	0.05~2	0.5~2.0 mg/200 mL	434.7	P-M		[45]
氧化多壁碳纳米管	0.05~2	0.5~2.0 mg/200 mL	105.4	P-M		[45]
磁性多孔还原氧化石墨烯	0~30	10 mg/200 mL	1 105.8	L	拟二级	[27]
氧化石墨烯、活性炭、壳聚糖复合材料	0.1~10	25 mg/50 mL	14.5	L	拟二级	[26]
γ-Fe₂O₃碳复合材料	10~50（45 mL）	500 mg/L（5 mL）	892.9	L	拟二级	[50]
炭黑	0.5~5	20 mg/100 mL	18.62	F	拟二级	[51]
纳米羟基磷灰石	5~35	0.5 g/L	133.33	L	拟二级	[52]
溴化十六烷基吡啶改性沸石（OZ 2.5）	0~50	10 mg/10 mL	46.95	L	拟二级	[30]
十六烷基三甲基溴化铵改性沸石	0.5~30	100 mg/10 mL	2.027	L	拟二级	[53]
蒙脱石	0~150	20 mg/100 mL	9	L		[29]
含阳离子酯双子表面活性剂修饰蒙脱石	0~150	20 mg/100 mL	133	L		[29]
二十八烷基二甲基铵改性膨润土	2~10	1.0 mg/60 mL	422	L, F	拟二级	[54]
二十八烷基二甲基铵改性麦羟硅钠石	2~10	1.0 mg/60 mL	534	L, F	拟二级	[54]
MIL-53（Al）	10~60	10 mg/100 mL	447	L	拟二级	[32]
MIL-53（Al）-1	10~60	10 mg/100 mL	488	L	拟二级	[32]
CuTz-1	60~400	12 mg/50 mL	578.5	R-P	拟二级	[34]
CuMtz-2a	60~400	12 mg /50 mL	671.1	R-P	拟二级	[34]
CuMtz-2b	60~400	12 mg /50 mL	743.2	R-P	拟二级	[34]
基于Fe⁰的磁性分子印迹聚合物（TCS-CTS-Fe⁰-MIPs）	1~9	10 mg/100 mL	20.86	L	拟二级	[39]
基于磁性非分子印迹聚合物（TCS-CTS-Fe⁰-NIPs）	1~9	10 mg/100 mL	15.11	L	拟二级	[39]
基于Fe₃O₄的磁性分子印迹聚合物	5.79~115.82	10 mg/5 mL	53.12	F	拟二级	[55]
基于Fe₃O₄的磁性非分子印迹聚合物	5.79~115.82	10 mg/5 mL	26.04	L	拟二级	[55]
聚乙烯	1.8~11	80 mg/20 mL	1.248	T	拟二级	[56]
聚苯乙烯	1.8~11	80 mg/20 mL	1.033	T	拟二级	[56]
磁性共价有机骨架纳米复合材料	0~2	0.8 mg/1 mL	5.481	F,L	拟二级	[40]
小粒径（<1 μm）聚氯乙烯	2~20	10 mg/25 mL	12.7	D-R	拟二级	[41]
大粒径（约74 μm）聚氯乙烯	2~20	10 mg/25 mL	8.98	D-R	拟二级	[41]
聚羟基丁酸酯	5~25	10 mg/10 mL	9.442	F	拟一级	[57]
聚乙烯	5~25	10 mg/10 mL	4.432	F	拟一级	[57]

Tab. 1

Tab. 2

References 59

[1]	Dann A B, Hontel A. Triclosan: environmental exposure, toxicity and mechanisms of action[J]. Journal of Applied Toxicology, 2011, 31 (4) : 285-311. doi: 10.1002/jat.1660 pmid: 21462230
[2]	Yao S R, Wei R, Ni J Z, et al. Concentrations, sources and ecological risks of triclosan and methyl-triclosan in inland river sediments of Fuzhou City[J]. Acta Scientiae Circumstantiae, 2015, 35 (8) : 2519-2525.
[3]	Zarate F M, Schulwitz S E, Stevens K J, et al. Bioconcentration of triclosan, methyl-triclosan, and triclocarban in the plants and sediments of a constructed wetland[J]. Chemosphere, 2012, 88 (3) : 323-329. doi: 10.1016/j.chemosphere.2012.03.005 pmid: 22483729
[4]	Chen Z F, Ying G G, Lai H J, et al. Determination of biocides in different environmental matrices by use of ultra-high-performance liquid chromatography-tandem mass spectrometry[J]. Analytical and Bioanalytical Chemistry, 2012, 404: 3175-3188. doi: 10.1007/s00216-012-6444-2
[5]	Li L P. Toxicity evaluation and by-products identification of triclosan ozonation and chlorination[J]. Chemosphere, 2021, 263: 128223. doi: 10.1016/j.chemosphere.2020.128223
[6]	Dinwiddie M T, Terry P D, Chen J. Recent evidence regarding triclosan and cancer risk[J]. International Journal of Environmental Research and Public Health, 2014, 11 (2) : 2209-2217. doi: 10.3390/ijerph110202209 pmid: 24566048
[7]	Liu H F, Wang F, Yao W Y. Effection of triclosan on the expressions of apoptosis-related genes in male zebrafish gill tissue[J]. Freshwater Fisheries, 2019, 49 (3) : 14-18.
[8]	Fu J, Bae S. The pH-dependent toxicity of triclosan on developing zebrafish (Danio rerio) embryos using metabolomics[J]. Aquatic Toxicology, 2020, 226: 105560. doi: 10.1016/j.aquatox.2020.105560
[9]	Wang C F, Tian Y. Reproductive endocrine-disrupting effects of triclosan: population exposure, present evidence and potential mechanisms[J]. Environmental Pollution, 2015, 206: 195-201. doi: 10.1016/j.envpol.2015.07.001
[10]	Jurewicz J, Radwan M, Wielgomas B, et al. Environmental levels of triclosan and male fertility[J]. Environmental Science and Pollution Research, 2018, 25 (6) : 5484-5490. doi: 10.1007/s11356-017-0866-5
[11]	Wu J L, Ji F F, Zhang H N, et al. Formation of dioxins from triclosan with active chlorine: a potential risk assessment[J]. Journal of Hazardous Materials, 2019, 367: 128-136. doi: 10.1016/j.jhazmat.2018.12.088
[12]	Latch D E, Packer J L, Arnold W A, et al. Photochemical conversion of triclosan to 2, 8-dichlorodibenzo-p-dioxin in aqueous solution[J]. Journal of Photochemistry and Photobiology A: Chemistry, 2003, 158 (1) : 63-66. doi: 10.1016/S1010-6030(03)00103-5
[13]	Ben W W, Sun P Z, Huang C H. Effects of combined UV and chlorine treatment on chloroform formation from triclosan[J]. Chemosphere, 2016, 150: 715-722. doi: S0045-6535(15)30525-7 pmid: 26746417
[14]	Jagini S, Konda S, Bhagawan D, et al. Emerging contaminant (triclosan) identification and its treatment: a review[J]. Sn Applied Sciences, 2019, 1 (6) : 640. doi: 10.1007/s42452-019-0634-x
[15]	Bu Q W, Zhang X, Yu G. Research progress in removal of pharmaceuticals and personal care products by adsorption method[J]. Environmental Engineering, 2021, 39 (2) : 1-9.
[16]	Sharipova A A, Aidarova S B, Bekturganova N E, et al. Triclosan as model system for the adsorption on recycled adsorbent materials[J]. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 2016, 505: 193-196. doi: 10.1016/j.colsurfa.2016.04.049
[17]	Kaur H, Hippargi G, Pophali G R, et al. Biomimetic lipophilic activated carbon for enhanced removal of triclosan from water[J]. Journal of Colloid and Interface Science, 2019, 535: 111-121. doi: S0021-9797(18)31174-3 pmid: 30292102
[18]	Wang X J, Lei Y T, Zeng J W, et al. Adsorption thermodynamics of triclosan by biochar[J]. Acta Scientiae Circumstantiae, 2019, 39 (6) : 1790-1800.
[19]	Ndagijimana P, Liu X, Li Z, et al. The synthesis strategy to enhance the performance and cyclic utilization of granulated activated carbon-based sorbent for bisphenol A and triclosan removal[J]. Environmental Science and Pollution Research, 2020, 27 (13) : 15758-15771. doi: 10.1007/s11356-020-08095-7
[20]	Tian S Y, Wang J N, Li A M. Preparation of new activated carbon fiber with palm fiber for adsorption of triclosan from aqueous solution[J]. Ion Exchange and Adsorption, 2016, 32 (6) : 511-525.
[21]	González-Fernández L A, Medellín-Castillo N A, Ocampo-Pérez R, et al. Equilibrium and kinetic modelling of triclosan adsorption on single-walled carbon nanotubes[J]. Journal of Environmental Chemical Engineering, 2021, 9 (6) : 106382. doi: 10.1016/j.jece.2021.106382
[22]	Zhou S, Shao Y, Gao N, et al. Equilibrium, kinetic, and thermodynamic studies on the adsorption of triclosan onto multi-walled carbon nanotubes[J]. Clean-Soil Air Water, 2013, 41 (6) : 539-547. doi: 10.1002/clen.201200082
[23]	Deng J, Lu Y A, Shang Z J, et al. Adsorption characteristics of triclosan and naproxen in water by carbon-based materials[J]. Journal of Central South University (Science and Technology), 2016, 47 (4) : 1427-1435.
[24]	Hu X, Cheng Z, Sun Z, et al. Adsorption of diclofenac and triclosan in aqueous solution by purified multi-walled carbon nanotubes[J]. Polish Journal of Environmental Studies, 2017, 26 (1) : 87-95. doi: 10.15244/pjoes/63885
[25]	Wang F, Lu X, Peng W, et al. Sorption behavior of bisphenol A and triclosan by graphene: comparison with activated carbon[J]. Acs Omega, 2017, 2 (9) : 5378-5384. doi: 10.1021/acsomega.7b00616 pmid: 31457806
[26]	Delhiraja K, Vellingiri K, Boukhvalov D W, et al. Development of highly water stable graphene oxide-based composites for the removal of pharmaceuticals and personal care products[J]. Industrial & Engineering Chemistry Research, 2019, 58 (8) : 2899-2913. doi: 10.1021/acs.iecr.8b02668
[27]	Li Y, Liu S, Wang C, et al. Effective column adsorption of triclosan from pure water and wastewater treatment plant effluent by using magnetic porous reduced graphene oxide[J]. Journal of Hazardous Materials, 2020, 386: 121942. doi: 10.1016/j.jhazmat.2019.121942
[28]	Behera S K, Oh S-Y, Park H-S. Sorption of triclosan onto activated carbon, kaolinite and montmorillonite: effects of pH, ionic strength, and humic acid[J]. Journal of Hazardous Materials, 2010, 179(1-3): 684-691. doi: 10.1016/j.jhazmat.2010.03.056 pmid: 20381242
[29]	Liu B, Lu J, Xie Y, et al. Microwave-assisted modification on montmorillonite with ester containing Gemini surfactant and its adsorption behavior for triclosan[J]. Journal of Colloid and Interface Science, 2014, 418: 311-316. doi: 10.1016/j.jcis.2013.12.035 pmid: 24461850
[30]	Lei C, Hu Y Y, He M Z. Adsorption characteristics of triclosan from aqueous solution onto cetylpyridinium bromide (CPB) modified zeolites[J]. Chemical Engineering Journal, 2013, 219: 361-370. doi: 10.1016/j.cej.2012.12.099
[31]	Phuekphong A F, Imwiset K J, Ogawa M. Organically modified bentonite as an efficient and reusable adsorbent for triclosan removal from water[J]. Langmuir, 2020, 36 (31) : 9025-9034. doi: 10.1021/acs.langmuir.0c00407 pmid: 32579362
[32]	Dou R, Zhang J, Chen Y, et al. High efficiency removal of triclosan by structure-directing agent modified mesoporous MIL-53(Al)[J]. Environmental Science and Pollution Research, 2017, 24 (9) : 8778-8789. doi: 10.1007/s11356-017-8583-7
[33]	Song J Y, Jhung S H. Adsorption of pharmaceuticals and personal care products over metal-organic frameworks functionalized with hydroxyl groups: quantitative analyses of H-bonding in adsorption[J]. Chemical Engineering Journal, 2017, 322: 366-374. doi: 10.1016/j.cej.2017.04.036
[34]	Yang M, Guo P, Feng X, et al. Solid solution approach to the design of copper mixed-triazolate multivariate-MOFs for the efficient adsorption of triclosan[J]. Microporous and Mesoporous Materials, 2021, 324: 111297. doi: 10.1016/j.micromeso.2021.111297
[35]	Fan W G, Jiang Y F, Zhang Y G, et al. Design and evaluation of functional material for triclosan viamolecular recognition and molecular imprinting technology[J]. China Surfactant Detergent＆Cosmetics, 2018, 48 (8) : 434-438, 449.
[36]	Gao R, Kong X, Su F, et al. Synthesis and evaluation of molecularly imprinted core-shell carbon nanotubes for the determination of triclosan in environmental water samples[J]. Journal of Chromatography A, 2010, 1217 (52) : 8095-8102. doi: 10.1016/j.chroma.2010.10.121 pmid: 21093867
[37]	Kong X, Li F, Li Y, et al. Molecularly imprinted polymer functionalized magnetic Fe₃O₄ for the highly selective extraction of triclosan[J]. Journal of Separation Science, 2020, 43 (4) : 808-817. doi: 10.1002/jssc.v43.4
[38]	Wang X, Huang P, Ma X, et al. Magnetic mesoporous molecularly imprinted polymers based on surface precipitation polymerization for selective enrichment of triclosan and triclocarban[J]. Journal of Chromatography A, 2018, 1537: 35-42. doi: S0021-9673(18)30041-4 pmid: 29342422
[39]	Chen Y, Lei X, Dou R, et al. Selective removal and preconcentration of triclosan using a water-compatible imprinted nano-magnetic chitosan particles[J]. Environmental Science and Pollution Research, 2017, 24 (22) : 18640-18650. doi: 10.1007/s11356-017-9467-6
[40]	Li Y, Zhang H, Chen Y, et al. Core-shell structured magnetic covalent organic framework nanocomposites for triclosan and triclocarban adsorption[J]. Acs Applied Materials & Interfaces, 2019, 11 (25) : 22492-22500.
[41]	Ma J, Zhao J, Zhu Z, et al. Effect of microplastic size on the adsorption behavior and mechanism of triclosan on polyvinyl chloride[J]. Environmental Pollution, 2019, 254: 113104. doi: 10.1016/j.envpol.2019.113104
[42]	Cusioli L F, Quesada H B, de Andrade M B, et al. Application of a novel low-cost adsorbent functioned with iron oxide nanoparticles for the removal of triclosan present in contaminated water[J]. Microporous and Mesoporous Materials, 2021, 325: 111328. doi: 10.1016/j.micromeso.2021.111328
[43]	He M Z, Hu Y Y, Lei C, et al. Adsorptive characteristics of triclosan on HDTMA modified zeolite[J]. Acta Scientiae Circumstantiae, 2013, 33 (1) : 20-29.
[44]	Zhang S J, Shao T, Bekaroglu S K, et al. Adsorption of synthetic organic chemicals by carbon nanotubes: effects of background solution chemistry[J]. Water Research, 2010, 44 (6) : 2067-2074. doi: 10.1016/j.watres.2009.12.017 pmid: 20071001
[45]	Cho H H, Huang H, Schwab K. Effects of solution chemistry on the adsorption of ibuprofen and triclosan onto carbon nanotubes[J]. Langmuir, 2011, 27 (21) : 12960-12967. doi: 10.1021/la202459g
[46]	Bhatnagar A, Anastopoulos L. Adsorptive removal of bisphenol A (BPA) from aqueous solution: a review[J]. Chemosphere, 2017, 168: 885-902. doi: S0045-6535(16)31512-0 pmid: 27839878
[47]	Kaur H, Bansiwal A, Hippargi G, et al. Effect of hydrophobicity of pharmaceuticals and personal care products for adsorption on activated carbon: adsorption isotherms, kinetics and mechanism[J]. Environmental Science and Pollution Research, 2018, 25 (21) : 20473-20485. doi: 10.1007/s11356-017-0054-7
[48]	Kaur H, Hippargi G, Pophali G R, et al. Biomimetic lipophilic activated carbon for enhanced removal of triclosan from water[J]. Journal of Colloid and Interface Science, 2019, 535: 111-121. doi: S0021-9797(18)31174-3 pmid: 30292102
[49]	Cho E J, Kang J K, Moon J K, et al. Removal of triclosan from aqueous solution via adsorption by kenaf-derived biochar: its adsorption mechanism study via spectroscopic and experimental approaches[J]. Journal of Environmental Chemical Engineering, 2021, 9 (6) : 106343. doi: 10.1016/j.jece.2021.106343
[50]	Zhu X, Liu Y, Luo G, et al. Facile fabrication of magnetic carbon composites from hydrochar via simultaneous activation and magnetization for triclosan adsorption[J]. Environmental Science & Technology, 2014, 48 (10) : 5840-5848. doi: 10.1021/es500531c
[51]	Wang J, Man H, Sun L, et al. Carbon black: a good adsorbent for triclosan removal from water[J]. Water, 2022, 14 (4) : 576. doi: 10.3390/w14040576
[52]	Zhao T T, Shen Q Y, Ding Y R, et al. Removal of triclosan by nano-HAP synthesized by biotemplate technology[J]. Environmental Chemistry, 2014, 33 (6) : 1018-1026.
[53]	Sonia A G, Guadalupe M M, Sonia M G, et al. Removal of triclosan by CTAB-modified zeolite-rich tuff from aqueous solutions[J]. Mrs Advances, 2020, 5 (62) : 3257-3264. doi: 10.1557/adv.2020.394
[54]	Phuekphong A, Imwiset K, Ogawa M. Adsorption of triclosan onto organically modified-magadiite and bentonite[J]. Journal of Inorganic and Organometallic Polymers and Materials, 2021, 31 (5) : 1902-1911. doi: 10.1007/s10904-021-01919-0
[55]	Lu Y C, Mao J H, Zhang W, et al. A novel strategy for selective removal and rapid collection of triclosan from aquatic environment using magnetic molecularly imprinted nano-polymers[J]. Chemosphere, 2020, 238: 124640. doi: 10.1016/j.chemosphere.2019.124640
[56]	Chen X, Gu X, Bao L, et al. Comparison of adsorption and desorption of triclosan between microplastics and soil particles[J]. Chemosphere, 2021, 263: 127947. doi: 10.1016/j.chemosphere.2020.127947
[57]	Tong H Y, Hu X S, Zhong X C, et al. Adsorption and desorption of triclosan on biodegradable polyhydroxybutyrate microplastics[J]. Environmental Toxicology and Chemistry, 2021, 40 (1) : 72-78. doi: 10.1002/etc.4902 pmid: 33045102
[58]	Al-Ghouti M A, Da’ana D A. Guidelines for the use and interpretation of adsorption isotherm models: a review[J]. Journal of Hazardous Materials, 2020, 393: 122383. doi: 10.1016/j.jhazmat.2020.122383
[59]	Wang J, Guo X. Adsorption isotherm models: Classification, physical meaning, application and solving method[J]. Chemosphere, 2020, 258: 127279. doi: 10.1016/j.chemosphere.2020.127279

吸附剂	温度/K	ΔG⁰/ （kJ/mol）	ΔH⁰/ （kJ/mol）	ΔS⁰/（J/ （mol·K））	参考文献
玉米秸秆生物炭	283	-4.260 8	-6.675 4	-8.527 5	[18]
	298	-4.132 8
	313	-4.004 9
皇竹草生物炭	283	-1.212 6	-1.601 2	-1.372 2	[18]
	298	-1.192 1
	313	-1.171 5
花生壳生物炭	283	-0.345 2	-3.102 2	-9.736 6	[18]
	298	-0.199 1
	313	-0.053 1
多壁碳纳米管	288	-38.15	-88.08	-173.38	[22]
	298	-36.41
	308	-34.68
十六烷基三甲基溴化铵改性沸石（S200）	298	-10.29	-12.39	-6.9	[43]
	308	-10.16
	318	-10.14
纳米羟基磷灰石	288	-7.852	4.011	41.179	[52]
	298	-8.249
	308	-8.685
	318	-9.079
溴化十六烷基吡啶改性沸石（OZ 0.5）	298	-28.35	-9.698	62.83	[30]
	308	-29.21
	318	-29.59
溴化十六烷基吡啶改性沸石（OZ 1.0）	298	-30.01	-14.58	50.88	[30]
	308	-30.62
	318	-31.02
溴化十六烷基吡啶改性沸石（OZ 2.5）	298	-30.91	-13.65	58.10	[30]
	308	-31.65
	318	-32.07
MIL-53（Al）	283	-8.2	9.1	61.1	[32]
	293	-8.8
	298	-9.1
	303	-9.4
MIL-53（Al）-1	283	-8.8	21.5	107.1	[32]
	293	-9.8
	298	-10.4
	303	-10.9
CuMtz-2b	293	-38.69	-392.6	-1 208	[34]
	298	-32.65
	303	-26.61
	313	-14.53

Progress in the adsorption of triclosan in aqueous solution

RichHTML

PDF (PC)

Like

Knowledge

Abstract

Cite this article

share this article

Figures/Tables 2

References 59

Related Articles 4

Metrics

Comments

Recommended 10

[1]	Zhao Fengtao,Li Xuanjing,Li Enze,Du Zhiping,Li Jianfeng,Shen Jing. Preparation of magnetic nano-Fe₃O₄and its application in wastewater treatment [J]. China Surfactant Detergent & Cosmetics, 2022, 52(8): 882-891.
[2]	WANG Xin-gang,YANG Xiao-yi,SUN Yong-qiang,GUO Chao-hua,LI Ping,LI Jian-bo. Study on the properties of the mixtures of sodium fatty alcohol ether sulfate with narrow ethylene oxide distribution and tetradecyltrimethylammonium bromide [J]. China Surfactant Detergent & Cosmetics, 2019, 49(8): 485-491.
[3]	ZHAI Gong-xun, DING Feng-mei, XING Zhi-qi, ZHOU Xiang. Dynamic surface tension and adsorption behavior of vanillin-based nonionic surfactants at gas-liquid interface [J]. China Surfactant Detergent & Cosmetics, 2018, 48(6): 303-307.
[4]	LI En-ze, DU Zhi-ping, LI Ping, WANG Guo-yong. Dynamic surface tension of trisiloxane ionic liquid aqueous solution [J]. China Surfactant Detergent & Cosmetics, 2014, 44(8): 421-425.