Bisphenol S

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Bisphenol S
Bisphenol S
IUPAC name
Other names
BPS, 4,4'-sulfonylbisphenol,
80-09-1 YesY
ChEMBL ChEMBL384441 YesY
ChemSpider 6374 YesY
Jmol-3D images Image
KEGG C14216 YesY
PubChem 6626
Molar mass 250.27 g·mol−1
Appearance White colorless solid; forms needle shaped crystals in water
Density 1.3663 g/cm3
Melting point 245 to 250 °C (473 to 482 °F; 518 to 523 K)
Solubility soluble in ethanol
R-phrases R36
S-phrases S26
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
 YesY verify (what isYesY/N?)
Infobox references

Bisphenol S (BPS) is an organic compound with the formula (HOC6H4)2SO2. It has two phenol functional groups on either side of a sulfonyl group. It is commonly used in curing fast-drying epoxy resin adhesives. It is a bisphenol, and a close analog of bisphenol A (BPA) in which the dimethylmethylene group (C(CH3)2) is replaced with a sulfone group (SO2).


BPS is used in curing fast-drying epoxy glues and as a corrosion inhibitor. It is also commonly used as a reactant in polymer reactions.

BPS has become increasingly common as a plasticizing agent following the widespread bans on the use of BPA due to its estrogen-mimicking properties, and BPS can now be found in a variety of common consumer products.[2][3] In some cases, BPS is used where the legal prohibition on BPA allows products containing BPS to be labelled "BPA free".[4] BPS also has the advantage of being more stable to heat and light than BPA.[5]

To comply with restrictions and regulations on BPA due to its confirmed toxicity, manufacturers are gradually replacing BPA with other related compounds, mainly bisphenol S (BPS; 4,4′-sulfonyldiphenol), as substitutes in industrial applications.[6]

BPS is also used as an anticorrosive agent in epoxy glues. Chemically, BPS is being used as a reagent in polymer reactions. BPS has also been reported to occur in canned foodstuffs, such as tin cans.[7]

In a recent study analyzing BPS in a variety of paper products worldwide, BPS was found in 100% of tickets, mailing envelopes, airplane boarding passes, and airplane luggage tags. In this study, very high concentrations of BPS were detected in thermal receipt samples collected from cities in the United States, Japan, Korea, and Vietnam. The BPS concentrations were large but varied greatly, from a few tens of nanograms per gram to several milligrams per gram. Nevertheless, concentrations of BPS used in thermal paper are usually lower compared to those of BPA.[8] Finally, BPS can get into the human body through dermal absorption from handling banknotes.[9]

Health and safety[edit]

Recent work suggests that, like BPA, BPS also has endocrine disrupting properties.[10] What makes BPS, and BPA, endocrine disruptors is the presence of the alcohol group on the benzene ring. This is called a phenol ring and it allows BPA and BPS to mimic estradiol. In a study of human urine BPS was found in 81% of the samples tested.[11] This percentage is comparable to BPA which was found in 95% of urine samples.[12] Another study done on thermal receipt paper shows that 88% of human exposure to BPS is through receipts.[13] In rodent studies BPS also has shown influenced uterine growth which indicates activation of estradiol.[14]

BPS has been shown to have similar in vitro estrogenic activity to BPA and acts as a xenoestrogen.[5][15][16] One study showed that exposure to low levels of BPS in cultured rat pituitary cells altered the estrogen estradiol signaling pathway to induce inappropriate release of prolactin, which, as a result, affected cell proliferation and apoptosis.[15]

BPS has also been linked to changes in neurodevelopment. In a 2014 study performed by researchers at the University of Calgary, exposure to low levels of BPS disrupted the timing of neurogenesis within the hypothalamus in embryonic zebrafish. The rate at which neurons developed increased by 240 percent.[17]

The recycling of thermal paper can introduce BPS into the cycle of paper production and cause BPS contamination of other types of paper products.[18][19] A recent study showed presence of BPS in more than 70% of the household waste paper samples, potentially indicating spreading of BPS contamination through paper recycling. [20]

BPS is more resistant to environmental degradation than BPA, and although not persistent cannot be characterised as readily biodegradable.[21][22]


BPS was first made in 1869 as a dye [23] and is currently common in everyday consumer products. BPS is an analog of BPA that has replaced BPA in a variety of ways, being present in thermal receipt paper, plastics, and indoor dust.[10] After health concerns associated with bisphenol A grew in 2012, BPS began to be used as a replacement.[24]


It is difficult for consumers to determine if a product contains BPS due to limited labeling regulations.[25]


Bisphenol S is prepared by the reaction of two equivalents of phenol with one equivalent of sulfuric acid or oleum.[26]

2 C6H5OH + H2SO4 → (C6H4OH)2SO2 + 2 H2O
2 C6H5OH + SO3 → (C6H4OH)2SO2 + H2O

This reaction can also produce 2,4'-sulfonyldiphenol, a common isomeric complication in electrophilic aromatic substitution reactions.

Chemical reaction to bisphenol S


  1. ^
  2. ^ Liao, C.; Liu, F.; Kannan, K. (2012). "Bisphenol S, a New Bisphenol Analogue, in Paper Products and Currency Bills and Its Association with Bisphenol a Residues". Environmental Science & Technology 46 (12): 6515–22. Bibcode:2012EnST...46.6515L. doi:10.1021/es300876n. PMID 22591511. 
  3. ^ Liao, C.; Liu, F.; Guo, Y.; Moon, H. B.; Nakata, H.; Wu, Q.; Kannan, K. (2012). "Occurrence of Eight Bisphenol Analogues in Indoor Dust from the United States and Several Asian Countries: Implications for Human Exposure". Environmental Science & Technology 46 (16): 9138–9145. Bibcode:2012EnST...46.9138L. doi:10.1021/es302004w. 
  4. ^ Jenna Bilbrey (Aug 11, 2014). "BPA-Free Plastic Containers May Be Just as Hazardous". Scientific American. 
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  6. ^ Chen, M. Y.; Ike, M.; Fujita, M. Acute toxicity, mutagenicity, and estrogenicity of bisphenol-A and other bisphenols. Environ. Toxicol. 2002, 17 (1), 80−86.
  7. ^ (Viñas, P.; Campillo, N.; Martínez-Castillo, N.; Hernandez- ́ Cordoba, M. Comparison of two derivatization-based methods for ́ solid-phase microextraction-gas chromatography-mass spectrometric determination of bisphenol A, bisphenol S and biphenol migrated from food cans. Anal. Bioanal. Chem. 2010, 397 (1), 115−125.)
  8. ^ Pivnenko, K.; Pedersen, G. A.; Eriksson, E.; Astrup, T. F. (2015-10-01). "Bisphenol A and its structural analogues in household waste paper". Waste Management 44: 39–47. doi:10.1016/j.wasman.2015.07.017. 
  9. ^ Liao, Chunyang; Liu, Fang; Kannan, Kurunthachalam (2012). "Bisphenol S, a new bisphenol analogue, in paper products and currency bills and its association with bisphenol A residues". Environmental science & technology 46 (12): 6515–6522. Bibcode:2012EnST...46.6515L. doi:10.1021/es300876n. 
  10. ^ a b Manjumol Mathew, S. Sreedhanya, P. Manoj, C.T. Aravindakumar, and Usha K. Aravind (2014). "Exploring the interaction of Bisphenol-S with Serum Albumins: A Better or Worse Alternative for Bisphenol A?". The journal of physical chemistry 118 (14): 3832–3843. doi:10.1021/jp500404u. PMID 24635450. 
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  14. ^ Johanna R. Rochester and Ashely L. Bolden (2015). "Bisphenol S and F: A Systematic Review and Comparison of the Hormonal Activity of Bisphenol A Substitutes". Environmental Health Perspectives: 1–33. doi:10.1289/ehp.1408989. 
  15. ^ a b Viñas, R.; Watson, C. S. (2013). "Bisphenol S Disrupts Estradiol-Induced Nongenomic Signaling in a Rat Pituitary Cell Line: Effects on Cell Functions". Environmental Health Perspectives 121 (3): 352–8. doi:10.1289/ehp.1205826. PMID 23458715. 
  16. ^ Ji, K.; Hong, S.; Kho, Y.; Choi, K. (2013). "Effects of Bisphenol S Exposure on Endocrine Functions and Reproduction of Zebrafish". Environmental Science & Technology: 8793–8800. doi:10.1021/es400329t. 
  17. ^ Kinch, Cassandra D; et al. "Low-dose exposure to bisphenol A and replacement bisphenol S induces precocious hypothalamic neurogenesis in embryonic zebrafish". PNAS. Proceedings of the National Academy of Sciences of the United States of America. PMID 25583509. 
  18. ^ Gehring, M.; Tennhardt, L.; Vogel, D.; Weltin, D.; Bilitewski, B. Bisphenol A Contamination of Wastepaper, Cellulose and Recycled Paper Products. In Waste Management and the Environment II. WIT Transactions on Ecology and the Environment; Brebbia, C. A., Kungulos, S., Popov, V., Itoh, H., Eds.; WIT Press: Southampton, Boston, 2004; Vol. 78, pp 294−300.
  19. ^ European Commission-Joint Research Centre. European Union Risk Assessment Report, 4,4′-Isopropylidenediphenol (Bisphenol-A). 2008, available from 325.pdf
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  22. ^ Ike, M.; Chen, M. Y.; Danzl, E.; Sei, K.; Fujita, M. Biodegradation of a variety of bisphenols under aerobic and anaerobic conditions. Water Sci. Technol. 2006, 53 (6), 153−159.
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  24. ^ Liao, C; Liu, F; Alomirah, H; Loi, V. D.; Mohd, M. A.; Moon, H. B.; Nakata, H; Kannan, K (2012). "Bisphenol S in urine from the United States and seven Asian countries: Occurrence and human exposures". Environmental Science & Technology 46 (12): 6860–6. Bibcode:2012EnST...46.6860L. doi:10.1021/es301334j. PMID 22620267. 
  25. ^ Howard, Brian. "Chemical in BPA-Free Products Linked to Irregular Heartbeats". National Geographic. National Geographic. Retrieved 29 March 2015.