色谱 ›› 2020, Vol. 38 ›› Issue (2): 255-263.DOI: 10.3724/SP.J.1123.2019.07012
• 研究论文 • 上一篇
叶曦雯1, 何静1, 李莹1, 牛增元1,*(), 张甜甜1, 罗忻1, 邹立2, 连素梅3
收稿日期:
2019-07-08
出版日期:
2020-02-08
发布日期:
2020-12-10
通讯作者:
牛增元
作者简介:
牛增元.Tel:(0532)58653540, E-mail:zyniuqd@163.com基金资助:
YE Xiwen1, HE Jing1, LI Ying1, NIU Zengyuan1,*(), ZHANG Tiantian1, LUO Xin1, ZOU Li2, LIAN Sumei3
Received:
2019-07-08
Online:
2020-02-08
Published:
2020-12-10
Contact:
NIU Zengyuan
Supported by:
摘要:
建立了液液萃取-分散液液微萃取-气相色谱-质谱联用技术测定纺织废水中痕量偶氮染料的方法。废水中的偶氮染料在碱性条件下经连二亚硫酸钠还原成芳香胺后,先用叔丁基甲醚液液萃取、盐酸反萃进行预浓缩及净化;再以乙腈-氯苯体系进行分散液液微萃取,气相色谱-质谱测定。对前处理条件进行了优化,考察了酸碱度及盐效应对芳香胺萃取效率的影响,结果表明:液液萃取过程中加入30 g NaCl,分散液液微萃取过程中加入1 mL 5 mol/L的NaOH调节体系至碱性才能达到较好的萃取效率。在优化的实验条件下,21种目标物均呈现良好的线性关系,其中13种芳香胺的线性范围为0.05~10 μg/L,7种芳香胺的线性范围为0.05~5 μg/L,2,4-二氨基苯甲醚的线性范围为20~100 μg/L,相关系数为0.996~0.999。20种芳香胺的检出限可达0.05 μg/L,2,4-二氨基苯甲醚检出限为20 μg/L。印染、机织、印花等实际废水加标试验表明,方法的回收率为75.6%~115.1%。该方法富集倍数高,检出限低,适用于纺织废水中痕量禁用偶氮染料的检测。
叶曦雯, 何静, 李莹, 牛增元, 张甜甜, 罗忻, 邹立, 连素梅. 液液萃取-分散液液微萃取-气相色谱-质谱联用测定纺织废水中痕量禁用偶氮染料[J]. 色谱, 2020, 38(2): 255-263.
YE Xiwen, HE Jing, LI Ying, NIU Zengyuan, ZHANG Tiantian, LUO Xin, ZOU Li, LIAN Sumei. Determination of trace azo dyes in textile wastewater by liquid-liquid extraction and dispersive liquid-liquid microextraction coupled with gas chromatography-mass spectrometry[J]. Chinese Journal of Chromatography, 2020, 38(2): 255-263.
No. | Compound | CAS No. | Retention time/min | Quantitative ion (m/z) | Qualitative ions (m/z) |
1) The CAS Nos. 97-56-3 (No. 23) and 99-55-8 (No. 22) are further reduced to CAS Nos. 95-53-4 (No. 2) and 95-80-7 (No. 9). 2) AZO colorants that can form 4-aminoazobenzene generate aniline (CAS No. 62-53-3) and 1, 4-phenylenediamine (CAS No. 106-50-3) under the conditions used in this method. Due to the detection limit, only aniline can be detected. | |||||
1 | aniline | 62-53-3 | 5.360 | 93 | 66, 65 |
2 | o-toluidine | 95-53-4 | 7.349 | 106 | 77, 107 |
3 | 2, 4-xylidine/2, 6-xylidine | 95-68-1/87-62-7 | 9.028 | 121 | 106, 120 |
4 | o-anisidine/2-methoxyaniline | 90-04-0 | 9.151 | 123 | 108, 80 |
5 | 4-chloroaniline | 106-47-8 | 9.634 | 127 | 92, 129 |
6 | 6-methoxy-m-toluidine | 120-71-8 | 10.863 | 137 | 122, 94 |
7 | 2, 4, 5-trimethylaniline | 137-17-7 | 11.192 | 135 | 120, 134 |
8 | 4-chloro-o-toluidine | 95-69-2 | 11.318 | 141 | 106, 143 |
9 | 2, 4-toluylendiamine | 95-80-7 | 12.739 | 121 | 104, 122 |
10 | 2, 4-diaminoanisole | 615-05-4 | 14.183 | 138 | 123, 95 |
11 | 2-naphthylamine | 91-59-8 | 15.470 | 143 | 115, 144 |
12 | 4-aminobiphenyl | 92-67-1 | 18.341 | 169 | 168, 141 |
13 | 4, 4′-oxydianiline | 101-80-4 | 24.240 | 200 | 171, 108 |
14 | benzidine | 92-87-5 | 24.485 | 184 | 92, 185 |
15 | 4, 4′-methylenedianiline | 101-77-9 | 24.685 | 198 | 182, 197 |
16 | 4, 4′-methylenedi-o-toluidine | 838-88-0 | 28.394 | 226 | 211, 225 |
17 | 3, 3′-dimethylbenzidine | 119-93-7 | 28.785 | 212 | 180, 211 |
18 | 4, 4′-thiodianiline | 139-65-1 | 29.608 | 216 | 184, 215 |
19 | 3, 3′-dichlorobenzidine | 91-94-1 | 30.804 | 252 | 254, 154 |
20 | 4, 4′-methylene-bis-(2-chloro-aniline) | 101-14-4 | 30.896 | 266 | 231, 252 |
21 | 3, 3′-dimethoxybenzidine | 119-90-4 | 30.932 | 244 | 229, 201 |
221) | 5-nitro-o-toluidine | 99-55-8 | 152 | 77, 106 | |
231) | o-aminoazotoluene | 97-56-3 | 123 | 108, 80 | |
242) | 4-aminoazobenzene | 60-09-3 | 197 | 92, 65 |
表1 芳香胺化合物的名称、CAS号、保留时间和特征离子
Table 1 Compound names, CAS Nos., retention times, and characteristic ions of the aromatic amines
No. | Compound | CAS No. | Retention time/min | Quantitative ion (m/z) | Qualitative ions (m/z) |
1) The CAS Nos. 97-56-3 (No. 23) and 99-55-8 (No. 22) are further reduced to CAS Nos. 95-53-4 (No. 2) and 95-80-7 (No. 9). 2) AZO colorants that can form 4-aminoazobenzene generate aniline (CAS No. 62-53-3) and 1, 4-phenylenediamine (CAS No. 106-50-3) under the conditions used in this method. Due to the detection limit, only aniline can be detected. | |||||
1 | aniline | 62-53-3 | 5.360 | 93 | 66, 65 |
2 | o-toluidine | 95-53-4 | 7.349 | 106 | 77, 107 |
3 | 2, 4-xylidine/2, 6-xylidine | 95-68-1/87-62-7 | 9.028 | 121 | 106, 120 |
4 | o-anisidine/2-methoxyaniline | 90-04-0 | 9.151 | 123 | 108, 80 |
5 | 4-chloroaniline | 106-47-8 | 9.634 | 127 | 92, 129 |
6 | 6-methoxy-m-toluidine | 120-71-8 | 10.863 | 137 | 122, 94 |
7 | 2, 4, 5-trimethylaniline | 137-17-7 | 11.192 | 135 | 120, 134 |
8 | 4-chloro-o-toluidine | 95-69-2 | 11.318 | 141 | 106, 143 |
9 | 2, 4-toluylendiamine | 95-80-7 | 12.739 | 121 | 104, 122 |
10 | 2, 4-diaminoanisole | 615-05-4 | 14.183 | 138 | 123, 95 |
11 | 2-naphthylamine | 91-59-8 | 15.470 | 143 | 115, 144 |
12 | 4-aminobiphenyl | 92-67-1 | 18.341 | 169 | 168, 141 |
13 | 4, 4′-oxydianiline | 101-80-4 | 24.240 | 200 | 171, 108 |
14 | benzidine | 92-87-5 | 24.485 | 184 | 92, 185 |
15 | 4, 4′-methylenedianiline | 101-77-9 | 24.685 | 198 | 182, 197 |
16 | 4, 4′-methylenedi-o-toluidine | 838-88-0 | 28.394 | 226 | 211, 225 |
17 | 3, 3′-dimethylbenzidine | 119-93-7 | 28.785 | 212 | 180, 211 |
18 | 4, 4′-thiodianiline | 139-65-1 | 29.608 | 216 | 184, 215 |
19 | 3, 3′-dichlorobenzidine | 91-94-1 | 30.804 | 252 | 254, 154 |
20 | 4, 4′-methylene-bis-(2-chloro-aniline) | 101-14-4 | 30.896 | 266 | 231, 252 |
21 | 3, 3′-dimethoxybenzidine | 119-90-4 | 30.932 | 244 | 229, 201 |
221) | 5-nitro-o-toluidine | 99-55-8 | 152 | 77, 106 | |
231) | o-aminoazotoluene | 97-56-3 | 123 | 108, 80 | |
242) | 4-aminoazobenzene | 60-09-3 | 197 | 92, 65 |
Sample No. | Compound | pH 1 | pH 7 | pH 14 | |||||
Average/(mg/L) | RSD/%(n=3) | Average/(mg/L) | RSD/%(n=3) | Average/(mg/L) | RSD/%(n=3) | ||||
ND: not detected. | |||||||||
1 | aniline | 0.03 | 1.5 | 2.54 | 1.5 | 2.87 | 1.5 | ||
4-chloroaniline | 0.36 | 5.1 | 0.35 | 12.2 | 0.42 | 13.1 | |||
2, 4-diaminoanisole | ND | ND | 0.85 | 11.2 | 1.14 | 10.2 | |||
benzidine | 0.82 | 8.2 | 2.13 | 12.2 | 4.51 | 2.2 | |||
2 | o-toluidine | 0.55 | 9.1 | 14.77 | 2.1 | 20.15 | 2.1 | ||
2-naphthylamine | 0.05 | 2.3 | 0.48 | 8.2 | 0.50 | 12.2 |
表2 pH对还原效率的影响
Table 2 Effect of pH on reduction efficiency
Sample No. | Compound | pH 1 | pH 7 | pH 14 | |||||
Average/(mg/L) | RSD/%(n=3) | Average/(mg/L) | RSD/%(n=3) | Average/(mg/L) | RSD/%(n=3) | ||||
ND: not detected. | |||||||||
1 | aniline | 0.03 | 1.5 | 2.54 | 1.5 | 2.87 | 1.5 | ||
4-chloroaniline | 0.36 | 5.1 | 0.35 | 12.2 | 0.42 | 13.1 | |||
2, 4-diaminoanisole | ND | ND | 0.85 | 11.2 | 1.14 | 10.2 | |||
benzidine | 0.82 | 8.2 | 2.13 | 12.2 | 4.51 | 2.2 | |||
2 | o-toluidine | 0.55 | 9.1 | 14.77 | 2.1 | 20.15 | 2.1 | ||
2-naphthylamine | 0.05 | 2.3 | 0.48 | 8.2 | 0.50 | 12.2 |
No. | Linear range/ (μg/L) | Regression equation | R2 | LOD/ (μg/L) |
The Nos. are the same as those in | ||||
1 | 0.05-10 | y=103498.5x+5111.4 | 0.998 | 0.05 |
2 | 0.05-10 | y=248843.3x+3260.7 | 0.999 | 0.05 |
3 | 0.05-10 | y=338628.3x-159.7 | 0.999 | 0.05 |
4 | 0.05-10 | y=140760.7x-5512.0 | 0.999 | 0.05 |
5 | 0.05-10 | y=281289.1x-338.1 | 0.999 | 0.05 |
6 | 0.05-10 | y=416686.4x-7416.7 | 0.999 | 0.05 |
7 | 0.05-10 | y=418311.6x-12659.7 | 0.999 | 0.05 |
8 | 0.05-10 | y=258808.0x-4836.0 | 0.996 | 0.05 |
9 | 0.05-10 | y=9115.7x-107.1 | 0.998 | 0.05 |
10 | 20-100 | y=78.8x-67.5 | 0.999 | 20 |
11 | 0.05-10 | y=697123.5x-12653.0 | 0.999 | 0.05 |
12 | 0.05-5 | y=556980.9x-30674.0 | 0.999 | 0.05 |
13 | 0.05-5 | y=22919.6x-927.1 | 0.999 | 0.05 |
14 | 0.05-5 | y=45833.2x-934.4 | 0.999 | 0.05 |
15 | 0.05-5 | y=38125.2x-278.0 | 0.999 | 0.05 |
16 | 0.05-5 | y=111010.1x-13125.3 | 0.999 | 0.05 |
17 | 0.05-5 | y=265786.7x-23342.6 | 0.997 | 0.05 |
18 | 0.05-10 | y=221751.1x-37595.2 | 0.999 | 0.05 |
19 | 0.05-10 | y=407537.4x-45364.7 | 0.999 | 0.05 |
20 | 0.05-5 | y=292462.3x-43139.3 | 0.999 | 0.05 |
21 | 0.05-10 | y=52379.8x-6213.0 | 0.999 | 0.05 |
表3 芳香胺的线性范围、线性方程、相关系数和检出限
Table 3 Linear ranges, linear equations, correlation coefficients and limits of detection (LOD) of aromatic amines
No. | Linear range/ (μg/L) | Regression equation | R2 | LOD/ (μg/L) |
The Nos. are the same as those in | ||||
1 | 0.05-10 | y=103498.5x+5111.4 | 0.998 | 0.05 |
2 | 0.05-10 | y=248843.3x+3260.7 | 0.999 | 0.05 |
3 | 0.05-10 | y=338628.3x-159.7 | 0.999 | 0.05 |
4 | 0.05-10 | y=140760.7x-5512.0 | 0.999 | 0.05 |
5 | 0.05-10 | y=281289.1x-338.1 | 0.999 | 0.05 |
6 | 0.05-10 | y=416686.4x-7416.7 | 0.999 | 0.05 |
7 | 0.05-10 | y=418311.6x-12659.7 | 0.999 | 0.05 |
8 | 0.05-10 | y=258808.0x-4836.0 | 0.996 | 0.05 |
9 | 0.05-10 | y=9115.7x-107.1 | 0.998 | 0.05 |
10 | 20-100 | y=78.8x-67.5 | 0.999 | 20 |
11 | 0.05-10 | y=697123.5x-12653.0 | 0.999 | 0.05 |
12 | 0.05-5 | y=556980.9x-30674.0 | 0.999 | 0.05 |
13 | 0.05-5 | y=22919.6x-927.1 | 0.999 | 0.05 |
14 | 0.05-5 | y=45833.2x-934.4 | 0.999 | 0.05 |
15 | 0.05-5 | y=38125.2x-278.0 | 0.999 | 0.05 |
16 | 0.05-5 | y=111010.1x-13125.3 | 0.999 | 0.05 |
17 | 0.05-5 | y=265786.7x-23342.6 | 0.997 | 0.05 |
18 | 0.05-10 | y=221751.1x-37595.2 | 0.999 | 0.05 |
19 | 0.05-10 | y=407537.4x-45364.7 | 0.999 | 0.05 |
20 | 0.05-5 | y=292462.3x-43139.3 | 0.999 | 0.05 |
21 | 0.05-10 | y=52379.8x-6213.0 | 0.999 | 0.05 |
Analyte No. | Spiked level/ (μg/L) | Recoveries (RSDs)/% | ||
Printing water | Weaving water | Dyeing water | ||
The Nos. are the same as those in | ||||
1 | 0.5 | 75.9 (5.4) | 94.7 (7.8) | 94.0 (5.2) |
1 | 85.5 (6.1) | 92.8 (13.7) | 92.6 (9.6) | |
5 | 89.2 (6.4) | 93.9 (11.5) | 98.7 (4.5) | |
2 | 0.5 | 76.8 (6.5) | 98.9 (8.4) | 82.8 (11.2) |
1 | 81.6 (9.1) | 96.4 (10.7) | 87.0 (8.0) | |
5 | 89.6 (7.4) | 96.5 (11.7) | 88.9 (13.8) | |
3 | 0.5 | 94.7 (6.4) | 96.1 (7.1) | 94.1 (10.3) |
1 | 84.2 (4.5) | 98.0 (10.9) | 90.7 (7.3) | |
5 | 82.3 (6.5) | 97.1 (12.2) | 88.9 (8.1) | |
4 | 0.5 | 78.2 (9.1) | 97.9 (7.7) | 77.1 (8.3) |
1 | 78.8 (6.2) | 100.6 (10.2) | 99.6 (11.4) | |
5 | 82.9 (8.1) | 98.1 (10.0) | 78.5 (5.6) | |
5 | 0.5 | 78.3 (2.7) | 95.0 (6.5) | 91.4 (6.1) |
1 | 86.2 (6.3) | 95.6 (13.3) | 105.4 (10.6) | |
5 | 91.3 (4.7) | 99.7 (10.1) | 106.7 (11.8) | |
6 | 0.5 | 82.1 (5.1) | 95.1 (8.0) | 89.2 (4.4) |
1 | 83.2 (7.4) | 110.2 (9.8) | 79.5 (9.2) | |
5 | 85.5 (3.1) | 99.4 (13.5) | 75.9 (8.1) | |
7 | 0.5 | 77.2 (5.9) | 97.1 (5.5) | 79.7 (6.6) |
1 | 85.1 (7.4) | 103.6 (13.7) | 88.3 (5.4) | |
5 | 92.4 (6.9) | 100.2 (11.0) | 97.5 (6.2) | |
8 | 0.5 | 79.4 (5.2) | 91.7 (9.0) | 100.9 (7.3) |
1 | 81.1 (5.6) | 85.2 (7.5) | 82.1 (4.7) | |
5 | 84.5 (5.1) | 107.7 (13.1) | 93.8 (11.1) | |
9 | 0.5 | 78.9 (7.2) | 93.2 (6.8) | 105.2 (10.3) |
1 | 76.9 (9.0) | 104.1 (12.0) | 93.9 (6.0) | |
5 | 81.5 (6.8) | 100.1 (12.7) | 104.4 (12.2) | |
10 | 50 | 85.7 (4.9) | 87.7 (4.9) | 85.0 (5.7) |
11 | 0.5 | 84.6 (11.2) | 94.2 (9.9) | 96.3 (4.5) |
1 | 76.2 (8.1) | 115.1 (4.6) | 99.0 (11.2) | |
5 | 87.2 (5.5) | 99.4 (10.7) | 81.3 (9.4) | |
12 | 0.5 | 81.1 (4.2) | 82.0 (5.7) | 76.5 (13.3) |
1 | 82.6 (7.5) | 101.0 (9.8) | 96.0 (5.6) | |
5 | 90.3 (7.2) | 94.1 (11.6) | 87.2 (9.3) | |
13 | 0.5 | 80.5 (6.9) | 102.9 (12.5) | 82.3 (5.2) |
1 | 89.8 (7.2) | 99.8 (7.2) | 99.1 (9.0) | |
5 | 89.2 (4.3) | 97.8 (12.6) | 95.9 (9.7) | |
14 | 0.5 | 75.6 (7.8) | 84.2 (7.8) | 79.4 (11.4) |
1 | 79.5 (3.1) | 105.8 (10.3) | 104.9 (6.4) | |
5 | 84.3 (6.9) | 91.3 (12.7) | 77.1 (6.8) | |
15 | 0.5 | 80.4 (2.7) | 85.5 (7.4) | 79.1 (8.9) |
1 | 84.9 (9.4) | 110.4 (5.1) | 86.5 (7.8) | |
5 | 86.6 (6.1) | 99.0 (7.8) | 88.5 (7.4) | |
16 | 0.5 | 86.5 (4.2) | 96.7 (5.7) | 82.4 (6.5) |
1 | 83.4 (11.5) | 103.4 (13.9) | 99.9 (11.2) | |
5 | 94.7 (10.9) | 105.8 (11.9) | 82.6 (10.5) | |
17 | 0.5 | 92.1 (6.2) | 99.1 (6.5) | 78.5 (5.8) |
1 | 81.6 (8.7) | 101.6 (9.1) | 87.9 (9.2) | |
5 | 90.6 (9.2) | 99.6 (7.4) | 93.8 (9.9) | |
18 | 0.5 | 91.8 (11.5) | 95.8 (12.0) | 84.5 (11.0) |
1 | 89.2 (10.5) | 109.2 (3.4) | 84.7 (12.3) | |
5 | 92.0 (9.4) | 99.0 (10.3) | 80.0 (11.7) | |
19 | 0.5 | 94.1 (9.4) | 94.1 (12.2) | 79.1 (8.2) |
1 | 76.0 (8.4) | 86.0 (9.1) | 83.3 (9.4) | |
5 | 79.6 (7.9) | 99.6 (9.5) | 100.6 (9.1) | |
20 | 0.5 | 85.4 (8.6) | 95.4 (5.1) | 76.7 (8.5) |
1 | 88.8 (8.9) | 98.8 (9.4) | 105.7 (8.8) | |
5 | 84.8 (7.9) | 104.8 (12.2) | 105.4 (7.6) | |
21 | 0.5 | 91.5 (11.9) | 99.5 (5.9) | 81.7 (12.1) |
1 | 90.8 (12.1) | 101.8 (12.0) | 90.8 (8.9) | |
5 | 90.8 (7.9) | 97.8 (9.7) | 107.5 (6.5) |
表4 21种芳香胺在废水中的加标回收率和RSD (n=6)
Table 4 Recoveries and RSDs of 21 aromatic amines spiked in wastewater samples (n=6)
Analyte No. | Spiked level/ (μg/L) | Recoveries (RSDs)/% | ||
Printing water | Weaving water | Dyeing water | ||
The Nos. are the same as those in | ||||
1 | 0.5 | 75.9 (5.4) | 94.7 (7.8) | 94.0 (5.2) |
1 | 85.5 (6.1) | 92.8 (13.7) | 92.6 (9.6) | |
5 | 89.2 (6.4) | 93.9 (11.5) | 98.7 (4.5) | |
2 | 0.5 | 76.8 (6.5) | 98.9 (8.4) | 82.8 (11.2) |
1 | 81.6 (9.1) | 96.4 (10.7) | 87.0 (8.0) | |
5 | 89.6 (7.4) | 96.5 (11.7) | 88.9 (13.8) | |
3 | 0.5 | 94.7 (6.4) | 96.1 (7.1) | 94.1 (10.3) |
1 | 84.2 (4.5) | 98.0 (10.9) | 90.7 (7.3) | |
5 | 82.3 (6.5) | 97.1 (12.2) | 88.9 (8.1) | |
4 | 0.5 | 78.2 (9.1) | 97.9 (7.7) | 77.1 (8.3) |
1 | 78.8 (6.2) | 100.6 (10.2) | 99.6 (11.4) | |
5 | 82.9 (8.1) | 98.1 (10.0) | 78.5 (5.6) | |
5 | 0.5 | 78.3 (2.7) | 95.0 (6.5) | 91.4 (6.1) |
1 | 86.2 (6.3) | 95.6 (13.3) | 105.4 (10.6) | |
5 | 91.3 (4.7) | 99.7 (10.1) | 106.7 (11.8) | |
6 | 0.5 | 82.1 (5.1) | 95.1 (8.0) | 89.2 (4.4) |
1 | 83.2 (7.4) | 110.2 (9.8) | 79.5 (9.2) | |
5 | 85.5 (3.1) | 99.4 (13.5) | 75.9 (8.1) | |
7 | 0.5 | 77.2 (5.9) | 97.1 (5.5) | 79.7 (6.6) |
1 | 85.1 (7.4) | 103.6 (13.7) | 88.3 (5.4) | |
5 | 92.4 (6.9) | 100.2 (11.0) | 97.5 (6.2) | |
8 | 0.5 | 79.4 (5.2) | 91.7 (9.0) | 100.9 (7.3) |
1 | 81.1 (5.6) | 85.2 (7.5) | 82.1 (4.7) | |
5 | 84.5 (5.1) | 107.7 (13.1) | 93.8 (11.1) | |
9 | 0.5 | 78.9 (7.2) | 93.2 (6.8) | 105.2 (10.3) |
1 | 76.9 (9.0) | 104.1 (12.0) | 93.9 (6.0) | |
5 | 81.5 (6.8) | 100.1 (12.7) | 104.4 (12.2) | |
10 | 50 | 85.7 (4.9) | 87.7 (4.9) | 85.0 (5.7) |
11 | 0.5 | 84.6 (11.2) | 94.2 (9.9) | 96.3 (4.5) |
1 | 76.2 (8.1) | 115.1 (4.6) | 99.0 (11.2) | |
5 | 87.2 (5.5) | 99.4 (10.7) | 81.3 (9.4) | |
12 | 0.5 | 81.1 (4.2) | 82.0 (5.7) | 76.5 (13.3) |
1 | 82.6 (7.5) | 101.0 (9.8) | 96.0 (5.6) | |
5 | 90.3 (7.2) | 94.1 (11.6) | 87.2 (9.3) | |
13 | 0.5 | 80.5 (6.9) | 102.9 (12.5) | 82.3 (5.2) |
1 | 89.8 (7.2) | 99.8 (7.2) | 99.1 (9.0) | |
5 | 89.2 (4.3) | 97.8 (12.6) | 95.9 (9.7) | |
14 | 0.5 | 75.6 (7.8) | 84.2 (7.8) | 79.4 (11.4) |
1 | 79.5 (3.1) | 105.8 (10.3) | 104.9 (6.4) | |
5 | 84.3 (6.9) | 91.3 (12.7) | 77.1 (6.8) | |
15 | 0.5 | 80.4 (2.7) | 85.5 (7.4) | 79.1 (8.9) |
1 | 84.9 (9.4) | 110.4 (5.1) | 86.5 (7.8) | |
5 | 86.6 (6.1) | 99.0 (7.8) | 88.5 (7.4) | |
16 | 0.5 | 86.5 (4.2) | 96.7 (5.7) | 82.4 (6.5) |
1 | 83.4 (11.5) | 103.4 (13.9) | 99.9 (11.2) | |
5 | 94.7 (10.9) | 105.8 (11.9) | 82.6 (10.5) | |
17 | 0.5 | 92.1 (6.2) | 99.1 (6.5) | 78.5 (5.8) |
1 | 81.6 (8.7) | 101.6 (9.1) | 87.9 (9.2) | |
5 | 90.6 (9.2) | 99.6 (7.4) | 93.8 (9.9) | |
18 | 0.5 | 91.8 (11.5) | 95.8 (12.0) | 84.5 (11.0) |
1 | 89.2 (10.5) | 109.2 (3.4) | 84.7 (12.3) | |
5 | 92.0 (9.4) | 99.0 (10.3) | 80.0 (11.7) | |
19 | 0.5 | 94.1 (9.4) | 94.1 (12.2) | 79.1 (8.2) |
1 | 76.0 (8.4) | 86.0 (9.1) | 83.3 (9.4) | |
5 | 79.6 (7.9) | 99.6 (9.5) | 100.6 (9.1) | |
20 | 0.5 | 85.4 (8.6) | 95.4 (5.1) | 76.7 (8.5) |
1 | 88.8 (8.9) | 98.8 (9.4) | 105.7 (8.8) | |
5 | 84.8 (7.9) | 104.8 (12.2) | 105.4 (7.6) | |
21 | 0.5 | 91.5 (11.9) | 99.5 (5.9) | 81.7 (12.1) |
1 | 90.8 (12.1) | 101.8 (12.0) | 90.8 (8.9) | |
5 | 90.8 (7.9) | 97.8 (9.7) | 107.5 (6.5) |
Sample No. | Sample type | Compound | Average content/(μg/L) | RSD/% (n=3) |
1 | weaving water | 2, 4-diaminoanisole | 580.46 | 5.7 |
benzidine | 26.54 | 5.0 | ||
4, 4′-diaminodiphenylmethane | 33.69 | 2.1 | ||
2 | dyeing water | o-toluidine | 74.08 | 8.6 |
2, 4-diaminoanisole | 43.09 | 4.9 | ||
4, 4′-diaminodiphenylmethane | 86.73 | 5.8 | ||
3 | printing water | 2, 4-diaminoanisole | 252.32 | 6.8 |
4 | weaving water | 4, 4′-diaminodiphenylmethane | 257.32 | 3.1 |
5 | knitting water | 4-chloroaniline | 1.90 | 6.3 |
2, 4-toluylendiamine | 1.62 | 5.2 | ||
4, 4′-diaminodiphenylmethane | 1.57 | 4.3 | ||
6 | printing water | 2, 4, 5-trimethylaniline | 0.98 | 5.1 |
4-chloro-o-toluidine | 0.94 | 1.9 | ||
4, 4′-diaminodiphenylmethane | 2.76 | 7.4 |
表5 实际样品中芳香胺的检测结果(n=3)
Table 5 Analytical results for aromatic amines in real samples (n=3)
Sample No. | Sample type | Compound | Average content/(μg/L) | RSD/% (n=3) |
1 | weaving water | 2, 4-diaminoanisole | 580.46 | 5.7 |
benzidine | 26.54 | 5.0 | ||
4, 4′-diaminodiphenylmethane | 33.69 | 2.1 | ||
2 | dyeing water | o-toluidine | 74.08 | 8.6 |
2, 4-diaminoanisole | 43.09 | 4.9 | ||
4, 4′-diaminodiphenylmethane | 86.73 | 5.8 | ||
3 | printing water | 2, 4-diaminoanisole | 252.32 | 6.8 |
4 | weaving water | 4, 4′-diaminodiphenylmethane | 257.32 | 3.1 |
5 | knitting water | 4-chloroaniline | 1.90 | 6.3 |
2, 4-toluylendiamine | 1.62 | 5.2 | ||
4, 4′-diaminodiphenylmethane | 1.57 | 4.3 | ||
6 | printing water | 2, 4, 5-trimethylaniline | 0.98 | 5.1 |
4-chloro-o-toluidine | 0.94 | 1.9 | ||
4, 4′-diaminodiphenylmethane | 2.76 | 7.4 |
Sample | Method | Instrument | Compound types | LOD/ (μg/L) | Reference |
DLLME-SFO: dispersive liquid-liquid microextraction based on solidification of floating organic drop; MEPS: microextraction by packed sorbent; PTFE: polytetrafluoroethylene; WCX: weak cation exchange; IL-DLLME: ionic liquid based dispersive liquid-liquid microextraction; LLE-DLLME: liquid-liquid extraction-dispersive liquid-liquid microextraction. * mg/L | |||||
Natural water | DLLME-SFO | UPLC-MS/MS | 4 | 0.7-2.9 | [ |
Natural water | MEPS-gas phase evaporator | GC-MS | 12 | 0.5 | [ |
1 | 0.25 | ||||
2 | 1-1.5 | ||||
Surface water | 0.22 μm membrane filtration with PTFE | UPLC-MS/MS | 7 | 0.01-0.05 | [ |
9 | 0.1-0.5 | ||||
7 | 1-2 | ||||
Natural water | application of an ultrasound-assisted polymer | GC-MS | 6 | 0.1 | [ |
surfactant-enhanced emulsification microextraction | |||||
1 | 0.08 | ||||
1 | 0.3 | ||||
Natural water | silica-WCX adsorption | HPLC | 5 | 0.08-0.28* | [ |
Waste water | IL-DLLME | HPLC | 4 | 0.45-2.6 | [ |
Textile wastewater | LLE-DLLME | GC-MS | 20 | 0.1 | this method |
1 | 20 |
表6 本文方法与其他分析方法的比较
Table 6 Comparison of this method with other analytical methods
Sample | Method | Instrument | Compound types | LOD/ (μg/L) | Reference |
DLLME-SFO: dispersive liquid-liquid microextraction based on solidification of floating organic drop; MEPS: microextraction by packed sorbent; PTFE: polytetrafluoroethylene; WCX: weak cation exchange; IL-DLLME: ionic liquid based dispersive liquid-liquid microextraction; LLE-DLLME: liquid-liquid extraction-dispersive liquid-liquid microextraction. * mg/L | |||||
Natural water | DLLME-SFO | UPLC-MS/MS | 4 | 0.7-2.9 | [ |
Natural water | MEPS-gas phase evaporator | GC-MS | 12 | 0.5 | [ |
1 | 0.25 | ||||
2 | 1-1.5 | ||||
Surface water | 0.22 μm membrane filtration with PTFE | UPLC-MS/MS | 7 | 0.01-0.05 | [ |
9 | 0.1-0.5 | ||||
7 | 1-2 | ||||
Natural water | application of an ultrasound-assisted polymer | GC-MS | 6 | 0.1 | [ |
surfactant-enhanced emulsification microextraction | |||||
1 | 0.08 | ||||
1 | 0.3 | ||||
Natural water | silica-WCX adsorption | HPLC | 5 | 0.08-0.28* | [ |
Waste water | IL-DLLME | HPLC | 4 | 0.45-2.6 | [ |
Textile wastewater | LLE-DLLME | GC-MS | 20 | 0.1 | this method |
1 | 20 |
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