| Literature DB >> 34151153 |
Annabel Guttentag1, Krishothman Krishnakumar1, Nural Cokcetin2, Elizabeth Harry2, Dee Carter1.
Abstract
Many Australian native honeys possess significant antimicrobial properties due to the production of hydrogen peroxide (H2O2) by glucose oxidase, an enzyme derived from the honeybee. The level of H2O2 produced in different honey samples is highly variable, and factors governing its production and stability are not well understood. In this study, highly active Australian honeys that had been stored for >10 years lost up to 54 % of their antibacterial activity, although almost all retained sufficient activity to be considered potentially therapeutically useful. We used a simple colourimetric assay to quantify H2O2 production. Although we found a significant correlation between H2O2 production and antibacterial activity across diverse honey samples, variation in H2O2 only explained 47 % of the variation observed in activity, limiting the assay as a screening tool and highlighting the complexity of the relationship between H2O2 and the killing power of honey. To further examine this, we tested whether H2O2 detection in honey was being inhibited by pigmented compounds and if H2O2 might be directly degraded in some honey samples. We found no correlation between H2O2 detection and honey colour. Some honey samples rapidly lost endogenous and spiked H2O2, suggesting that components in honey, such as catalase or antioxidant polyphenols, may degrade or quench H2O2. Despite this rapid loss of H2O2, these honeys had significant peroxide-based antibacterial activity, indicating a complex relationship between H2O2 and other honey components that may act synergistically to augment activity.Entities:
Keywords: Pfund; catalase; colour; colourimetric assay; honey; horseradish peroxidase; hydrogen peroxide
Year: 2021 PMID: 34151153 PMCID: PMC8209695 DOI: 10.1099/acmi.0.000198
Source DB: PubMed Journal: Access Microbiol ISSN: 2516-8290
Honey samples used in this study, including antimicrobial activity before and after storage and their level of H2O2 production
|
Honey sample* |
Floral source |
Land type |
Region, state |
Original antimicrobial activity† |
Retested antimicrobial activity‡ |
Difference in antimicrobial activity (%) |
Maximum H2O2 production§ |
|---|---|---|---|---|---|---|---|
|
Banksia 11 |
|
State forest |
Illawarra, NSW |
17.1±0.9 |
10.3±0.8 |
−6.8 (−40 %) |
1.14±0.11 |
|
Jarrah 2017 |
|
Woodland |
Northcliffe, WA |
|
12.9±0.9 |
|
1.59±0.18 |
|
Jarrah 5 |
|
Woodland |
Lower West, WA |
25.4±0.4 |
18.4±1.1 |
−7.0 (−28 %) |
2.95±0.08 |
|
Jarrah 8 |
|
Woodland |
Lower West, WA |
25.1±0.9 |
17.1±0.4 |
−8.0 (−32 %) |
2.77±0.18 |
|
Jarrah 10 |
|
Woodland |
Lower West, WA |
25.7±0.5 |
17.5±0.4 |
−8.2 (−32 %) |
2.86±0.31 |
|
Jarrah 13 |
|
Woodland |
Lower West, WA |
28.1±0.1 |
23.4±1.1 |
−4.7 (−17 %) |
3.84±0.24 |
|
Karri 3 |
|
Woodland |
Southwest, WA |
29.6±0.7 |
25.7±0.6 |
−3.9 (−13 %) |
2.22±0.07 |
|
Marri 6 |
|
Urban, nature reserve |
Lower West, WA |
28.6±0.9 |
24.0±0.8 |
−4.6 (−16 %) |
1.44±0.07 |
|
Marri 8 |
|
National Park |
Lower West, WA |
27.2±0.2 |
24.3±0.6 |
−2.9 (−11 %) |
2.38±0.13 |
|
Marri 10 |
|
Farm, agricultural – stock, woodland |
Lower West, WA |
29.3±1.2 |
20.7±0.8 |
−8.6 (−29 %) |
2.06±0.01 |
|
Marri 11 |
|
Farm, agricultural – stock, woodland |
Lower West, WA |
29.7±0.1 |
25.2±0.8 |
−4.5 (−15 %) |
2.54±0.03 |
|
Polyfloral 12 |
Mixed |
Urban |
Metropolitan, NSW |
19.4±0.1 |
9.8±0.7 |
−9.6 (−49 %) |
0.21±0.01 |
|
Polyfloral 13 |
Mixed |
Urban, nature reserve |
Metropolitan, NSW |
21.2±0.6 |
17.7±0.9 |
−3.5 (−17 %) |
0.29±0.03 |
|
Stringybark 11 |
|
Farm, state forest |
North Central, VIC |
23.3±1.1 |
11.1±0.9 |
−12.2 (−52 %) |
0.24±0.06 |
|
Stringybark 19 |
|
Woodland |
Northern Tablelands, NSW |
24.9±1.2 |
11.4±0.4 |
−13.5 (−54 %) |
0.93±0.12 |
|
Barnes 10+ honey |
|
Not known |
Not known |
|
9.6±0.9 |
|
0.08±0.01 |
*Obtained from [8], except for Jarrah 2017 and commercial Barnes 10+ honey.
†Assessed as % phenol equivalence in 2006/7; data are the mean±sem of two biological replicates [8].
‡Assessed as % phenol equivalence in 2018; data are the mean±sem of two biological replicates.
§Quantified in mM using the horseradish peroxidase colourimetric assay; data are the mean±sem of two biological replicates.
Fig. 1.High H2O2 -producing honey samples were diverse in colour. Pfund (mm) values for the 16 honey samples. n=3 technical replicates; bars represent the mean.
Fig. 2.Correlations between antimicrobial activity (% phenol equivalence), H2O2 production and colour (Pfund). (a) A positive correlation was seen between H2O2 production and activity across honey samples (r=0.068, P=0.004; black line), but the explanatory power was low (R 2=0.47). The correlation was strengthened when restricted to jarrah samples (r=0.97, R 2=0.95, P=0.001; green line). (b). Honey colour and H2O2 production had a slight negative trend for all honey samples (black line) and jarrah samples (green line), but neither was significant (P=0.28 and P=0.07, respectively). (c) There was no correlation between honey colour and antimicrobial activity across all honey samples (black line) or jarrah samples (green line) (P=0.79 and 0.14, respectively). n=1 biological replicate (with three technical replicates) for Pfund values, and n=2 biological replicates (each with two technical replicates) for H2O2 readings and % phenol equivalence. The means of these data sets are shown in both graphs.
Fig. 3.Rapid degradation of H2O2 occurred in some honeys. (a) H2O2 in honey samples detected by the HRP assay over 24 h; n=2 biological replicates (each with three technical replicates). The graph shows the mean and error bars represent the standard error of the mean (sem). There was substantial variation in the level and kinetics of H2O2 over the time course. (b) Barnes 10+ and stringybark 11 honey spiked at the 2 h timepoint with H2O2 (final concentration of 500 µM) showed rapid degradation of the H2O2 that was not seen in the artificial honey control. Representative images show colour changes seen in wells at each timepoint. n=3.