| Literature DB >> 28640190 |
Tomasz Kulik1, Kinga Stuper-Szablewska2, Katarzyna Bilska3, Maciej Buśko4, Anna Ostrowska-Kołodziejczak5, Dariusz Załuski6, Juliusz Perkowski7.
Abstract
Plant-derived compounds limiting mycotoxin contamination are currently of major interest in food and feed production. However, their potential application requires an evaluation of their effects on fungal secondary metabolism and membrane effects. In this study, different strains of Fusarium culmorum and F. graminearum sensu stricto were exposed to trans-cinnamic and chlorogenic acids on solid YES media. Fusaria produced phenolic acids, whose accumulation was lowered by exogenous phenolic compounds. In addition, fungi reduced exogenous phenolic acids, leading either to their conversion or degradation. trans-Cinnamic acid was converted to caffeic and ferulic acids, while chlorogenic acid was degraded to caffeic acid. The latter underwent further degradation to protocatechuic acid. Fungal-derived trans-cinnamic acid, as the first intermediate of the shikimate pathway, increased after chlorogenic acid treatment, presumably due to the further inhibition of the conversion of trans-cinnamic acid. Exogenous trans-cinnamic and chlorogenic acid displayed the inhibition of mycotoxin production by Fusaria, which appeared to be largely dependent on the phenolic compound and its concentration and the assayed strain. Exogenous phenolic acids showed different effects on ergosterol biosynthesis by fungi. It was found that the production of this membrane sterol was stimulated by trans-cinnamic acid, while chlorogenic acid negatively impacted ergosterol biosynthesis, suggesting that phenolic acids with stronger antifungal activities may upregulate ergosterol biosynthesis by Fusaria. This paper reports on the production of phenolic acids by Fusaria for the first time.Entities:
Keywords: Fusarium culmorum; Fusarium graminearum sensu stricto; chlorogenic acid; ergosterol; phenolic acids; trans-cinnamic acid; trichothecenes
Mesh:
Substances:
Year: 2017 PMID: 28640190 PMCID: PMC5535145 DOI: 10.3390/toxins9070198
Source DB: PubMed Journal: Toxins (Basel) ISSN: 2072-6651 Impact factor: 4.546
Figure 1Schematic representation of some of the core biochemical pathways of major phenolic acids (based on Kaushik et al. [30,31,32,33,34,35,36,37,38,39,40,41,42]) with an indication of the routes of the conversion and degradation of phenolic acids by fungi. Red arrows indicate the routes of either the conversion or degradation of phenolic acids by fungi. The numbers near the red arrows indicate the literature from which the data originates.
Trichothecene accumulation and RQ (relative quantification) of Tri transcripts of fungal strains incubated with different concentrations of trans-cinnamic and chlorogenic acids after a 21-day incubation period.
| Phenolic Acid Concentration | Strain | Tri Genotype | Trichothecene Levels (mg/kg) ( | RQ ( | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| DON | 3ADON | 15ADON | NIV | 4ANIV | Sum of Trichothecenes | ||||||
| YES + fungal controls | MUCL 53469 | 3ADON | 17.5 ± 0.4 (a) | 23.1 ± 0.9 (a) | 40.6 | ||||||
| CBS 173.31 | 3ADON | 63.7 ± 3.8 (b) | 9.9 ± 0.4 (a) | 73.6 | |||||||
| CBS 139512 | NIV | 79.2 ± 3.2 (a) | 96.4 ± 4.8 (a) | 175.6 | |||||||
| CBS 119173 | 3ADON | 49.6 ± 3.6 (a) | 12.2 ± 0.8 (a) | 61.8 | |||||||
| CBS 138561 | 15ADON | 1.5 ± 0.7 (a) | 1.5 ± 0.7 (a) | 3 | |||||||
| MUCL 53455 | NIV | 4.4 ± 0.2 (a) | 4.4 | ||||||||
| MUCL 53469 | 3ADON | 4.62 ± 0.14 (c) | 16.41 ± 0.33 (b) | 21.03 | 0.21 (0.12–0.38) | 0.26 (0.14–0.46) | NS | ||||
| CBS 173.31 | 3ADON | 52.48 ± 1.57 (b) | 9.9 ± 0.22 (a) | 62.38 | 0.13 (0.11–0.16) | 0.19 (0.16–0.23) | NS | ||||
| CBS 139512 | NIV | 68.63 ± 1.37 (b) | 15.45 ± 0.62 (b) | 84.08 | 0.14 (0.07–0.28) | 0.17 (0.12–0.26) | NS | ||||
| CBS 119173 | 3ADON | 2.7 ± 0.2 (b) | 0.5 ± 0.03 (b) | 3.2 | NS | NS | NS | ||||
| CBS 138561 | 15ADON | 0.34 ± 0.01 (b) | 0.005 ± 0.0002 (b) | 0.35 | NS | NS | NS | ||||
| MUCL 53455 | NIV | 2.07 ± 0.12 (b) | 2.07 | NS | NS | NS | |||||
| MUCL 53469 | 3ADON | 8 ± 0.2 (b) | 17.5 ± 0.5 (b) | 25.5 | 0.02 (0.006–0.038) | 0.03 (0.02–0.07) | 0.15 (0.1–0.26) | ||||
| CBS 173.31 | 3ADON | 44.01 ± 0.88 (c) | 7.47 ± 0.37 (c) | 51.48 | 0.02 (0.007–0.055) | 0.02 (0.01–0.046) | 0.18 (0.1–0.36) | ||||
| CBS 139512 | NIV | 37.26 ± 2.23 (c) | 14.12 ± 0.57 (c) | 51.38 | 0.046 (0.044–0.047) | 0.023 (0.02–0.03) | NS | ||||
| CBS 119173 | 3ADON | 1.8 ± 0.1 (b) | 1.3 ± 0.05 (b) | 3.1 | 0.15 (0.089–0.255) | 0.21 (0.083–0.541) | NS | ||||
| CBS 138561 | 15ADON | 0.22 ± 0.01 (b) | 0.003 ± 0.0001 (b) | 0.22 | 0.086 (0.058–0.212) | 0.039 (0.028–0.076) | NS | ||||
| MUCL 53455 | NIV | 0.59 ± 0.01 (c) | 0.59 | 0.023 (0.019–0.023) | 0.022 (0.02–0.024) | NS | |||||
| chlorogenic acid 0.3 mM(100 μg/g) | MUCL 53469 | 3ADON | 9.62 ± 0.57 (b) | 21.51 ± 0.43 (ab) | 31.13 | NS | NS | NS | |||
| CBS 173.31 | 3ADON | 84.13 ± 3.37 (a) | 11.52 ± 0.46 (a) | 95.65 | NS | NS | NS | ||||
| CBS 139512 | NIV | 32.3 ± 1.9 (d) | 10.3 ± 0.4 (c) | 42.6 | NS | NS | NS | ||||
| CBS 119173 | 3ADON | 3.2 ± 0.2 (b) | 1.0 ± 0.1 (b) | 4.2 | NS | NS | NS | ||||
| CBS 138561 | 15ADON | 1.88 ± 0.11 (a) | 0.12 ± 0.01 (b) | 2 | NS | NS | NS | ||||
| MUCL 53455 | NIV | 2.41 ± 0.15 (c) | 2.41 | NS | NS | NS | |||||
| chlorogenic acid 1.1 mM (400 μg/g) | MUCL 53469 | 3ADON | 7.93 ± 0.32 (c) | 15.66 ± 0.47 (c) | 23.59 | NS | NS | NS | |||
| CBS 173.31 | 3ADON | 54.88 ± 1.31 (b) | 4.27 ± 0.02 (a) | 59.15 | 0.68 (0.65–0.71) | NS | NS | ||||
| CBS 139512 | NIV | 49.6 ± 3 (c) | 22.1 ± 1.3 (b) | 71.7 | NS | NS | NS | ||||
| CBS 119173 | 3ADON | 5 ± 0.3 (b) | 1.7 ± 0.1 (b) | 6.7 | 0.43 (0,36–0,5) | 0.59 (0.55–0.65) | 0.89 (0.85–0.93) | ||||
| CBS 138561 | 15ADON | 0.29 ± 0,01 (b) | 0.07 ± 0.01 (b) | 0.36 | NS | NS | NS | ||||
| MUCL 53455 | NIV | 3.14 ± 0.1 (b) | 3.14 | NS | NS | NS | |||||
| chlorogenic acid 2.3 mM (800 μg/g) | MUCL 53469 | 3ADON | 7.42 ± 0.37 (c) | 20.3 ± 0.81 (b) | 27.72 | NS | NS | NS | |||
| CBS 173.31 | 3ADON | 41.97 ± 1.68 (c) | 2.6 ± 0.16 (b) | 44.57 | 0.05 (0.04–0.05) | 0.12 (0.11–0.14) | 0.17 (0.15–0.2) | ||||
| CBS 139512 | NIV | 57 ± 1.1 (b) | 16.5 ± 0.8 (bc) | 73.5 | NS | NS | NS | ||||
| CBS 119173 | 3ADON | 4.9 ± 0.3 (b) | 1.8 ± 0.1 (b) | 6.7 | 0.47 (0.45–0.49) | 0.71 (0.65–0.71) | 0.82 (0.77–0.86) | ||||
| CBS 138561 | 15ADON | 1.16 ± 0.07 (ab) | 0.05 ± 0.002 (b) | 1.21 | NS | NS | NS | ||||
| MUCL 53455 | NIV | 1.85 ± 0.1 (d) | 1.85 | NS | NS | NS | |||||
Degree of inhibition: <25%; 25–50%; 50–75%; >75%. Increase of mycotoxin accumulation. (a), (b), (c) letters indicate homogenous groups at p < 0.05 followed by the Tukey test. NS—not significant.
Antioxidant capacity (VCEAC/L), radical scavenging activity (ABTS), and retention times (min) of the trans-cinnamic and chlorogenic acids analyzed in this study.
| Phenolic Acid | VCEAC/L | ABTS (μmol TROLOX/100 g s.m.) | Retention Times (min) * |
|---|---|---|---|
| 812.3 | 314.9 | 9.6 | |
| Chlorogenic acid | 12.3 | 57.1 | 2.6 |
* From Labronici Bertin et al. [54].
List of fungal isolates used in this study.
| Species | Strain | Trichothecene Genotype | Origin, Host and Year of Isolation |
|---|---|---|---|
| CBS 173.31, NRRL 26853 | 3ADON | Canada, oat, 1927 | |
| MUCL 53469 | 3ADON | Belgium, corn, 2007 | |
| CBS 139512 | NIV | Poland, wheat kernel, 2003 | |
| CBS 119173, NRRL 38369 | 3ADON | USA, Louisiana, wheat head, 2005 | |
| CBS 138561 | 15ADON | Poland, wheat kernel, 2010 | |
| MUCL 53455 | NIV | Belgium, corn, 2007 |