| Literature DB >> 32226882 |
Danica J Walsh1,2, Tom Livinghouse1, Greg M Durling1, Yenny Chase-Bayless3, Adrienne D Arnold4, Philip S Stewart2.
Abstract
The recalcitrance exhibited by microbial biofilms to conventional disinfectants has motivated the development of new chemical strategies to control and eradicate biofilms. The activities of several small phenolic compounds and their trichloromethylsulfenyl ester derivatives were evaluated against planktonic cells and mature biofilms of Staphylococcus epidermidis and Pseudomonas aeruginosa. Some of the phenolic parent compounds are well-studied constituents of plant essential oils, for example, eugenol, menthol, carvacrol, and thymol. The potency of sulfenate ester derivatives was markedly and consistently increased toward both planktonic cells and biofilms. The mean fold difference between the parent and derivative minimum inhibitory concentration against planktonic cells was 44 for S. epidermidis and 16 for P. aeruginosa. The mean fold difference between the parent and derivative biofilm eradication concentration for 22 tested compounds against both S. epidermidis and P. aeruginosa was 3. This work demonstrates the possibilities of a new class of biofilm-targeting disinfectants deploying a sulfenate ester functional group to increase the antimicrobial potency toward microorganisms in biofilms.Entities:
Year: 2020 PMID: 32226882 PMCID: PMC7098047 DOI: 10.1021/acsomega.9b04392
Source DB: PubMed Journal: ACS Omega ISSN: 2470-1343
Scheme 1Representative Synthesis, Using Eugenol (8a)
Figure 1Parent phenols and corresponding sulfenate esters and their MICs and BECs.
MICs of Phenols 7a, 9a, 10a, 11a, 12a, and 24a
| MICs (mM) | ||
|---|---|---|
| compounds | ||
| 0.3 | 1.5 | |
| 15.6 | 7.8 | |
| 15.6 | 7.8 | |
| 15.6 | 31.2 | |
| 12.5 | 25 | |
| 4.5 | 7.8 | |
MICs of Phenols 17a, 18a, 19a, 20a
| MICs (mM) | ||
|---|---|---|
| compounds | ||
| 6.2 | 31.2 | |
| 12.5 | 25 | |
| 3.8 | 7.8 | |
| 3.8 | 15.6 | |
MICs of Sulfenates 7b, 9b, 10b, 11b, 12b, and 24b
| MICs (mM) | ||
|---|---|---|
| compounds | ||
| 0.24 | 0.49 | |
| 0.24 | 0.7 | |
| 0.24 | 0.95 | |
| 1.9 | 3.8 | |
| 0.95 | 1.9 | |
| 0.24 | 0.49 | |
MICs of Sulfenates 17b, 18b, 19b, and 20b
| MICs (mM) | ||
|---|---|---|
| compounds | ||
| 0.49 | 1.9 | |
| 1.9 | 3.8 | |
| 1.9 | 3.8 | |
| 1.9 | 6.5 | |
BECs of Phenols 7a, 9a, 10a, 11a, 12a, and 24a
| BEC (mM) | ||
|---|---|---|
| compounds | ||
| 1.9 | 7.5 | |
| 31.2 | 31.2 | |
| 31.2 | 62.5 | |
| 50 | 50 | |
| 31.2 | 62.5 | |
| 6.2 | 50 | |
BECs of Phenols 17a, 18a, 19a, and 20a
| BEC (mM) | ||
|---|---|---|
| compounds | ||
| 12.5 | 50 | |
| 100 | 100 | |
| 6.2 | 37 | |
| 15.6 | 50 | |
BECs for Allyl- and Halo-Phenols and Hydroquinone
| BEC (mM) | ||
|---|---|---|
| compounds | ||
| 4 | 15.6 | |
| 15 | 30 | |
| 31.2 | 62.5 | |
| 31.2 | 62.5 | |
| 1.5 | 7.5 | |
| 62.5 | 31.2 | |
| 37.5 | 75 | |
| 16 | 25 | |
BECs for Sulfenates 7b, 9b, 10b, 11b, 12b, and 24b
| BEC (mM) | ||
|---|---|---|
| compounds | ||
| 0.15 | 2.5 | |
| 3 | 6.5 | |
| 12.5 | 31.2 | |
| 12.5 | 12.5 | |
| 15.8 | 31.2 | |
| 4.6 | 25 | |
BEC for Sulfenates 17b, 18b, 19b, and 20b
| BEC (mM) | ||
|---|---|---|
| compounds | ||
| 6.2 | 25 | |
| 25 | 25 | |
| 3.1 | 6.2 | |
| 7.8 | 15.6 | |
BECs for Allyl- and Halo-Sulfenates as Well as the Bis(sulfenate) 25b
| BEC (Mm) | ||
|---|---|---|
| compounds | ||
| 3.2 | 6.5 | |
| 4.6 | 8.7 | |
| 12.5 | 12.5 | |
| 2 | 4 | |
| 3 | 12.5 | |
| 14 | 14 | |
| 12.5 | 25 | |
| 0.91 | 3.9 | |
Figure 2(A) 19F NMR of p-fluorophenol (15a) in D2O; (B) 19F NMR of (4-fluorophenoxy) (trichloromethyl)sulfane (15b) in D2O at 0 h; (C) 19F NMR of (4-fluorophenoxy)(trichloromethyl)sulfane in D2O after 12 h; (D) 19F NMR of (4-fluorophenoxy) (trichloromethyl)sulfane in D2O after 24 h; (E) 19F NMR of (4-fluorophenoxy) (trichloromethyl)sulfane in D2O after 48 h; (F) 19F NMR of (4-fluorophenoxy) (trichloromethyl)sulfane in D2O after 144 h.