Chinese Journal of Chromatography ›› 2026, Vol. 44 ›› Issue (9): 991-1000.DOI: 10.3724/SP.J.1123.2026.02013
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LIU Sisi*(
), LI Zijun, WEI Hongbo, XU Piaoli, LI Lina, CHEN Changer, YING Guangguo
Received:2026-02-27
Online:2026-09-08
Published:2026-09-17
Supported by:CLC Number:
LIU Sisi, LI Zijun, WEI Hongbo, XU Piaoli, LI Lina, CHEN Changer, YING Guangguo. Recent advances on environmental occurrence, risk and analytical methodologies of synthetic phenolic antioxidants[J]. Chinese Journal of Chromatography, 2026, 44(9): 991-1000.
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URL: https://www.chrom-china.com/EN/10.3724/SP.J.1123.2026.02013
| Synthetic phenolic antioxidant | Abbreviation | Structure | Water solubility/(mg/L) | BCF/(L/kg wet weight) | log KOW | log KOA | Half-life /d |
|---|---|---|---|---|---|---|---|
| 4-tert-Octylphenol | 4-tOP | ![]() | 4.8 | 1406 | 5.28 | 9.02 | 0.25 |
| 2,4,6-Tri-tert-butylphenol | AO246 | ![]() | 35.0 | 2776 | 6.39 | 9.46 | 0.67 |
| 4,4-Thiobis(6-tert-butyl-m-cresol) | AO300 | ![]() | 0.0019 | 1961 | 8.24 | 18.19 | 0.082 |
| 2-tert-Butyl-4-methoxyphenol | BHA | ![]() | 743 | 57 | 3.50 | 8.96 | 0.30 |
| 2,6-di-tert-butyl-4-methylphenol | BHT | ![]() | 19.4 | 2.8 | 5.10 | 8.87 | 0.59 |
| 2,6-Di-tert-butyl-p-benzoquinone | BHT-Q | ![]() | 3.5 | 18.2 | 4.42 | 7.95 | 172 |
| 3,5-Di-tert-butyl-4-hydroxybenzaldehyde | BHT-CHO | ![]() | 28.4 | 164 | 4.2 | 10.6 | 0.50 |
| 2,6-Di-tert-butyl-4-carboxyphenol | BHT-COOH | ![]() | 16.8 | 3.16 | 4.36 | 12.87 | 3.18 |
| 2,6-Di-tert-butyl-4-hydroxy-4-methylcyclohexa-2,5-dien-1-one | BHT-OH | ![]() | 60.7 | 132 | 3.72 | 10.24 | 0.17 |
| 2,4-Di-tert-butyl-phenol | DBP | ![]() | 5.7 | 740 | 5.33 | 9.01 | 0.22 |
| Dodecyl 3,4,5-trihydroxybenzoate | DG | ![]() | 0.042 | 246 | 6.21 | 19.70 | 0.10 |
| tert-Butylhydroquinone | TBHQ | ![]() | 748 | 24.3 | 2.84 | 11.10 | 0.21 |
| Pentaerythritol tetrakis(3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionate) | AO1010 | ![]() | 0.0052 | 2.2 | 19.60 | 27.40 | 0.10 |
| N,N′-Bis[3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionyl]hydrazine | AO1024 | ![]() | 0.027 | 3264 | 7.79 | 24.1 | 0.20 |
| Octadecyl-3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionate | AO1076 | ![]() | 6.1×10-9 | 5.8 | 13.4 | 17.6 | 0.25 |
| 1,3,5-Tris(3′,5′-di-tert-butyl-4-hydroxybenzyl)isocyanuric acid | AO3114 | ![]() | 4.0×10-12 | 3.16 | 15.18 | 39.35 | 0.16 |
Table 1 Physicochemical properties of typical synthetic phenolic antioxidants (SPAs)*
| Synthetic phenolic antioxidant | Abbreviation | Structure | Water solubility/(mg/L) | BCF/(L/kg wet weight) | log KOW | log KOA | Half-life /d |
|---|---|---|---|---|---|---|---|
| 4-tert-Octylphenol | 4-tOP | ![]() | 4.8 | 1406 | 5.28 | 9.02 | 0.25 |
| 2,4,6-Tri-tert-butylphenol | AO246 | ![]() | 35.0 | 2776 | 6.39 | 9.46 | 0.67 |
| 4,4-Thiobis(6-tert-butyl-m-cresol) | AO300 | ![]() | 0.0019 | 1961 | 8.24 | 18.19 | 0.082 |
| 2-tert-Butyl-4-methoxyphenol | BHA | ![]() | 743 | 57 | 3.50 | 8.96 | 0.30 |
| 2,6-di-tert-butyl-4-methylphenol | BHT | ![]() | 19.4 | 2.8 | 5.10 | 8.87 | 0.59 |
| 2,6-Di-tert-butyl-p-benzoquinone | BHT-Q | ![]() | 3.5 | 18.2 | 4.42 | 7.95 | 172 |
| 3,5-Di-tert-butyl-4-hydroxybenzaldehyde | BHT-CHO | ![]() | 28.4 | 164 | 4.2 | 10.6 | 0.50 |
| 2,6-Di-tert-butyl-4-carboxyphenol | BHT-COOH | ![]() | 16.8 | 3.16 | 4.36 | 12.87 | 3.18 |
| 2,6-Di-tert-butyl-4-hydroxy-4-methylcyclohexa-2,5-dien-1-one | BHT-OH | ![]() | 60.7 | 132 | 3.72 | 10.24 | 0.17 |
| 2,4-Di-tert-butyl-phenol | DBP | ![]() | 5.7 | 740 | 5.33 | 9.01 | 0.22 |
| Dodecyl 3,4,5-trihydroxybenzoate | DG | ![]() | 0.042 | 246 | 6.21 | 19.70 | 0.10 |
| tert-Butylhydroquinone | TBHQ | ![]() | 748 | 24.3 | 2.84 | 11.10 | 0.21 |
| Pentaerythritol tetrakis(3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionate) | AO1010 | ![]() | 0.0052 | 2.2 | 19.60 | 27.40 | 0.10 |
| N,N′-Bis[3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionyl]hydrazine | AO1024 | ![]() | 0.027 | 3264 | 7.79 | 24.1 | 0.20 |
| Octadecyl-3-(3,5-di-tert-butyl-4-hydroxyphenyl)propionate | AO1076 | ![]() | 6.1×10-9 | 5.8 | 13.4 | 17.6 | 0.25 |
| 1,3,5-Tris(3′,5′-di-tert-butyl-4-hydroxybenzyl)isocyanuric acid | AO3114 | ![]() | 4.0×10-12 | 3.16 | 15.18 | 39.35 | 0.16 |
Fig. 1 Release and fate of synthetic phenolic antioxidants in the environment Gemini Nano Banana 3 Pro was employed to produce the images except texts and structures.
| Sample type | Sample source | DF range/% | Total concentrations | Dominant congeners | Ref. |
|---|---|---|---|---|---|
| House dust (n=83) | Toronto, Canada, 2018 | 11-100 | ∑8SPAs: 67.2-15540 ng/g (GM: 1490 ng/g); ∑4TPs: 40.4-12700 ng/g (GM: 883 ng/g) | BHT: 658 ng/g (GM); BHT-Q: 4770 ng/g (max), 325 ng/g (GM) | [ |
| Indoor dust (n=226) | 10 provinces, China, 2018-2023 | 1.8-97 | ∑6SPAs: 15.4-3210 ng/g (GM: 169 ng/g, median: 149 ng/g) | BHT: 11.5 ng/g(GM); BHT-Q: 78.9 ng/g (GM) | [ |
| Indoor dust (n=75) | Jinan, China, 2014 | urban: 16-100; rural: n.d. -100 | urban: ∑7SPAs: 1560-20300 ng/g (GM: 3120 ng/g);rural: ∑7SPAs: 668-4390 ng/g (GM: 1970 ng/g) | BHT (GM): 2270 ng/g (urban), 1700 ng/g (rural); AO246 (GM): 229 ng/g (urban), 323 ng/g (rural) | [ |
| Indoor dust (n=80) | Toronto, Canada, 2018 | 4-95 | ∑10SPAs: 239-213000 ng/g (GM: 1770 ng/g) | BHT: 749 ng/g(GM) | [ |
Sewage effluent (n=3) | Beijing, China, 2014 | 100 | ∑9SPAs: 1500 ng/L (mean) | BHT: 262 ng/L (mean); BHT-CHO: 534 ng/L (mean); BHT-Q: 108 ng/L (mean) BHT-quinol: 556 ng/L (mean) | [ |
| Sewage sludge (n=56) | 33 cities, China, 2010-2011 | 1.8-100 | ∑14SPAs: 183-41000 ng/g (mean: 4960 ng/g) | BHT: 4140 ng/g (GM); AO246: 374 ng/g (GM); BHT-Q: 562 ng/g (GM) | [ |
| River water (n=9) | Germany, Oder River, 2000-2001 | 100 | ∑2SPAs: 88-520 ng/L (GM: 256 ng/L; mean: 281 ng/L) | BHT: 178 ng/L (mean); BHT-CHO: 102 ng/L (mean) | [ |
| Surface water (n=23) | PRD, China, 2024 | 4.5-100 | ∑4SPAs (median): 95 ng/L (dry seasons)/42 ng/L (wet seasons) | BHT-COOH, BHT-OH | [ |
| Surface water (n=32) | YRD, China, 2024 | 25-100 | ∑18SPAs: 2700 ng/L (GM) | AO3114: 1420 ng/L (median) | [ |
| Sediments (n=32) | YRD, China, 2024 | 49-100 | ∑18SPAs: 1270 ng/g (GM) | AO1010: 609 ng/L (median) | [ |
| Soils (n=32) | YRD, China, 2024 | n.d.-100 | ∑18SPAs: 2440 ng/g (GM) | AO1010: 794 ng/L (median); AO1076: 1600 ng/L (median) | [ |
| Sewage sludge (n=45) | 6 cities, China, 2017-2018 | 49-100 | ∑10SPAs: 94.6-6024 ng/g | AO246: 547 ng/g (GM); AO1010: 212 ng/g (GM); AO1076: 35.2 ng/g (GM) | [ |
| Dumping site soils (n=12) | 6 Asian countries, 2006 and 2015 | 100 | ∑1SPAs: 3.2-3300 ng/g | BHT: 3300 ng/g (max) | [ |
| Human serum (n=50) | Temecula, CA, US, 2016-2017 | 4-100 | ∑5SPAs: 0.46-34.7 µg/L (GM: 7.77 µg/L) ∑4BHT-metabolites: n.d.-3.66 µg/L (GM: 0.77 µg/L) | BHT: 2.66 µg/L (GM); 2,4-DTBP: 3.65 µg/L (GM) | [ |
| Human urine (n=60) | Fort Lauderdale and Miami, US, 2018 | 30-100 | ∑3SPAs: 6.19-70.2 µg/L (GM: 18.6 µg/L); ∑4BHT-metabolites: 0.54-8.61 µg/L (GM: 1.68 µg/L) | BHT-COOH: 0.68 µg/L (GM); 2,4-DTBP: 18.3 µg/L (GM) | [ |
| Human blood (n=30) | Stockholm, Sweden, 2020 | 17-100 | ∑13SPAs: 333-896 ng/g (median: 594 ng/g) | AO2246: 520 ng/g (median); 4-tOP: 14 ng/g (median) | [ |
| Breast milk (n=80) | Guangzhou, China, 2020 | 34-100 | ∑8SPAs: 1.96-64.9 µg/L (GM: 14.7 µg/L); ∑4BHT-metabolites: 0.21-5.55 µg/L (GM: 1.83 µg/L) | BHT: 4.48 µg/L (GM);2,4-DTBP: 9.94 µg/L (GM) | [ |
Table 2 Contents of SPAs in different environmental matrices
| Sample type | Sample source | DF range/% | Total concentrations | Dominant congeners | Ref. |
|---|---|---|---|---|---|
| House dust (n=83) | Toronto, Canada, 2018 | 11-100 | ∑8SPAs: 67.2-15540 ng/g (GM: 1490 ng/g); ∑4TPs: 40.4-12700 ng/g (GM: 883 ng/g) | BHT: 658 ng/g (GM); BHT-Q: 4770 ng/g (max), 325 ng/g (GM) | [ |
| Indoor dust (n=226) | 10 provinces, China, 2018-2023 | 1.8-97 | ∑6SPAs: 15.4-3210 ng/g (GM: 169 ng/g, median: 149 ng/g) | BHT: 11.5 ng/g(GM); BHT-Q: 78.9 ng/g (GM) | [ |
| Indoor dust (n=75) | Jinan, China, 2014 | urban: 16-100; rural: n.d. -100 | urban: ∑7SPAs: 1560-20300 ng/g (GM: 3120 ng/g);rural: ∑7SPAs: 668-4390 ng/g (GM: 1970 ng/g) | BHT (GM): 2270 ng/g (urban), 1700 ng/g (rural); AO246 (GM): 229 ng/g (urban), 323 ng/g (rural) | [ |
| Indoor dust (n=80) | Toronto, Canada, 2018 | 4-95 | ∑10SPAs: 239-213000 ng/g (GM: 1770 ng/g) | BHT: 749 ng/g(GM) | [ |
Sewage effluent (n=3) | Beijing, China, 2014 | 100 | ∑9SPAs: 1500 ng/L (mean) | BHT: 262 ng/L (mean); BHT-CHO: 534 ng/L (mean); BHT-Q: 108 ng/L (mean) BHT-quinol: 556 ng/L (mean) | [ |
| Sewage sludge (n=56) | 33 cities, China, 2010-2011 | 1.8-100 | ∑14SPAs: 183-41000 ng/g (mean: 4960 ng/g) | BHT: 4140 ng/g (GM); AO246: 374 ng/g (GM); BHT-Q: 562 ng/g (GM) | [ |
| River water (n=9) | Germany, Oder River, 2000-2001 | 100 | ∑2SPAs: 88-520 ng/L (GM: 256 ng/L; mean: 281 ng/L) | BHT: 178 ng/L (mean); BHT-CHO: 102 ng/L (mean) | [ |
| Surface water (n=23) | PRD, China, 2024 | 4.5-100 | ∑4SPAs (median): 95 ng/L (dry seasons)/42 ng/L (wet seasons) | BHT-COOH, BHT-OH | [ |
| Surface water (n=32) | YRD, China, 2024 | 25-100 | ∑18SPAs: 2700 ng/L (GM) | AO3114: 1420 ng/L (median) | [ |
| Sediments (n=32) | YRD, China, 2024 | 49-100 | ∑18SPAs: 1270 ng/g (GM) | AO1010: 609 ng/L (median) | [ |
| Soils (n=32) | YRD, China, 2024 | n.d.-100 | ∑18SPAs: 2440 ng/g (GM) | AO1010: 794 ng/L (median); AO1076: 1600 ng/L (median) | [ |
| Sewage sludge (n=45) | 6 cities, China, 2017-2018 | 49-100 | ∑10SPAs: 94.6-6024 ng/g | AO246: 547 ng/g (GM); AO1010: 212 ng/g (GM); AO1076: 35.2 ng/g (GM) | [ |
| Dumping site soils (n=12) | 6 Asian countries, 2006 and 2015 | 100 | ∑1SPAs: 3.2-3300 ng/g | BHT: 3300 ng/g (max) | [ |
| Human serum (n=50) | Temecula, CA, US, 2016-2017 | 4-100 | ∑5SPAs: 0.46-34.7 µg/L (GM: 7.77 µg/L) ∑4BHT-metabolites: n.d.-3.66 µg/L (GM: 0.77 µg/L) | BHT: 2.66 µg/L (GM); 2,4-DTBP: 3.65 µg/L (GM) | [ |
| Human urine (n=60) | Fort Lauderdale and Miami, US, 2018 | 30-100 | ∑3SPAs: 6.19-70.2 µg/L (GM: 18.6 µg/L); ∑4BHT-metabolites: 0.54-8.61 µg/L (GM: 1.68 µg/L) | BHT-COOH: 0.68 µg/L (GM); 2,4-DTBP: 18.3 µg/L (GM) | [ |
| Human blood (n=30) | Stockholm, Sweden, 2020 | 17-100 | ∑13SPAs: 333-896 ng/g (median: 594 ng/g) | AO2246: 520 ng/g (median); 4-tOP: 14 ng/g (median) | [ |
| Breast milk (n=80) | Guangzhou, China, 2020 | 34-100 | ∑8SPAs: 1.96-64.9 µg/L (GM: 14.7 µg/L); ∑4BHT-metabolites: 0.21-5.55 µg/L (GM: 1.83 µg/L) | BHT: 4.48 µg/L (GM);2,4-DTBP: 9.94 µg/L (GM) | [ |
| Sample type | Target analytes | Preparation methods | Analysis methods | Recoveries/% | MDL | Ref. |
|---|---|---|---|---|---|---|
| Indoor dust | 6 SPAs & 3 TPs | ultrasonication (DCM/hexane, 1∶1) | GC-MS/MS+LC-MS/MS (ESI) | 90.5-105 | 0.21-22.5 ng/g (MQL) | [ |
| Sewage Sludge | 12 SPAs & 3 TPs | ASE (90 ℃, 1500 psi; DCM/hexane, 3∶1) | LC-MS/MS (ESI) | 65-103 | 0.1-15 ng/g | [ |
| Human serum | 13 SPAs | protein precipitation+SPE (EMR-Lipid) | LC-MS/MS (ESI)+GC-MS | 42-112 | 0.047-36.7 ng/g (MQL) | [ |
| Human breast milk | 10 SPAs & 4 TPs | ultrasonication (ACN/hexane, 3∶5)+SPE (Florisil) | LC-MS/MS (ESI)+GC-MS | 58-95 | 0.006-1.2 ng/g (MQL) | [ |
| River water and sewage water | 11 SPAs | liquid-liquid extraction (MTBE)+silica gel column | LC-MS/MS (ESI) | river water: 65.8-117;sewage water: 59.5-118 | river water: 0.3-0.9 ng/L;sewage water: 0.9-2.4 ng/L | [ |
| Surface water | 2 SPAs & 5 TPs | SPE (HLB) | GC-MS | 76-116 | 1.93-3.10 ng/L (MQL) | [ |
| Bottled drinking water | BHT | SPME (polydimethylsiloxane) | GC-MS (headspace injection) | 84-119 | 4.2 μg/L | [ |
| Sediment | BHT & TPs | ultrasonication (DCM/hexane, 3∶1)+derivatization | GC-MS | 71-118 | 0.02-0.34 ng/g | [ |
| Mollusks | 9 SPAs & 4 TPs | ultrasonication (DCM/hexane, 3∶1)+SPE (HLB) | LC-MS/MS (ESI)+GC-MS/MS | 61-92 | 0.7-1.9 ng/g (MQL) | [ |
| Indoor dust | 8 SPAs & 4 TPs | ultrasonication (DCM/hexane, 3∶1) | LC-MS/MS+ trap column (APCI+ESI) | 67-98 | 0.002-0.09 μg/L (IDL) | [ |
Table 3 Pretreatment and instrument detection methods for SPAs
| Sample type | Target analytes | Preparation methods | Analysis methods | Recoveries/% | MDL | Ref. |
|---|---|---|---|---|---|---|
| Indoor dust | 6 SPAs & 3 TPs | ultrasonication (DCM/hexane, 1∶1) | GC-MS/MS+LC-MS/MS (ESI) | 90.5-105 | 0.21-22.5 ng/g (MQL) | [ |
| Sewage Sludge | 12 SPAs & 3 TPs | ASE (90 ℃, 1500 psi; DCM/hexane, 3∶1) | LC-MS/MS (ESI) | 65-103 | 0.1-15 ng/g | [ |
| Human serum | 13 SPAs | protein precipitation+SPE (EMR-Lipid) | LC-MS/MS (ESI)+GC-MS | 42-112 | 0.047-36.7 ng/g (MQL) | [ |
| Human breast milk | 10 SPAs & 4 TPs | ultrasonication (ACN/hexane, 3∶5)+SPE (Florisil) | LC-MS/MS (ESI)+GC-MS | 58-95 | 0.006-1.2 ng/g (MQL) | [ |
| River water and sewage water | 11 SPAs | liquid-liquid extraction (MTBE)+silica gel column | LC-MS/MS (ESI) | river water: 65.8-117;sewage water: 59.5-118 | river water: 0.3-0.9 ng/L;sewage water: 0.9-2.4 ng/L | [ |
| Surface water | 2 SPAs & 5 TPs | SPE (HLB) | GC-MS | 76-116 | 1.93-3.10 ng/L (MQL) | [ |
| Bottled drinking water | BHT | SPME (polydimethylsiloxane) | GC-MS (headspace injection) | 84-119 | 4.2 μg/L | [ |
| Sediment | BHT & TPs | ultrasonication (DCM/hexane, 3∶1)+derivatization | GC-MS | 71-118 | 0.02-0.34 ng/g | [ |
| Mollusks | 9 SPAs & 4 TPs | ultrasonication (DCM/hexane, 3∶1)+SPE (HLB) | LC-MS/MS (ESI)+GC-MS/MS | 61-92 | 0.7-1.9 ng/g (MQL) | [ |
| Indoor dust | 8 SPAs & 4 TPs | ultrasonication (DCM/hexane, 3∶1) | LC-MS/MS+ trap column (APCI+ESI) | 67-98 | 0.002-0.09 μg/L (IDL) | [ |
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