| Literature DB >> 28962374 |
D Grotto1, M Gerenutti1, V C O Souza2, F Barbosa2.
Abstract
Mushroom Lentinula edodes has been widely studied therapeutically. However, there is no data regarding its daily intake level safety. Since L. edodes has many active compounds known to bind to metals, we evaluated macro and micronutrients in liver and kidney of healthy rats after subchronic exposure to L. edodes. Rats were divided into four groups, receiving water and L. edodes at 100, 400 and 800 mg/kg/day. The treatment lasted 30 days. Essential elements (Zn, Cu, Mg, Fe, Mn, Se, Co, Mo, and Li) were analyzed in an inductively coupled plasma mass spectrometer. Our results demonstrated a significant decrease in Cu, Fe, Mn and Co levels in liver of rats receiving L. edodes at the highest doses. In kidney, Mn, Mo and Li concentrations significantly dropped in the groups exposed to the highest doses. In this way, an important point is revealed concerning the food safety from L. edodes, once its chronic and high consumption could contribute to macro and micronutrients deficiency. Additionally, we speculate that the daily use of L. edodes could be unsuccessful for patients in mineral therapy besides being able to be unsafe for individuals with some propensity to mineral deficiency.Entities:
Keywords: Chelating agent; Cobalt (PubChem CID: 104729); Copper (PubChem CID: 23994); Iron (PubChem CID: 23925); Lentinula edodes; Lithium (PubChem CID: 11564465); Macronutrients; Magnesium (PubChem CID: 23994); Manganese (PubChem CID: 23925); Micronutrients; Molibdenium (PubChem CID: 23932); Selenium (PubChem CID: 6337549); Zinc (PubChem CID: 23994)
Year: 2015 PMID: 28962374 PMCID: PMC5598163 DOI: 10.1016/j.toxrep.2015.02.005
Source DB: PubMed Journal: Toxicol Rep ISSN: 2214-7500
Essential elements (mean ± standard deviation) in liver samples from rats exposed to Lentinula edodes in different concentrations. Chemical elements were determined by Inductive Coupled Plasma Mass Spectrometry. Data are reported as μg g−1 or ng g−1 (wet weight).
| Essential elements | Control | |||
|---|---|---|---|---|
| 100 mg/kg | 400 mg/kg | 800 mg/kg | ||
| Zn (μg g−1) | 44.5 ± 3.2 | 46.9 ± 2.4 | 43.1 ± 6.1 | 47.1 ± 3.9 |
| Cu (μg g−1) | 10.1 ± 1.2 | 9.0 ± 0.8 | 8.5 ± 1.0 | 8.0 ± 0.4 |
| Mg (μg g−1) | 261.4 ± 33.5 | 245.2 ± 54.0 | 241.9 ± 53.7 | 274.9 ± 38.8 |
| Fe (μg g−1) | 92.9 ± 15.4 | 85.3 ± 12.9 | 84.4 ± 15.9 | 70.1 ± 16.7 |
| Mn (ng g−1) | 2.879 ± 320 | 2.730 ± 467 | 2.275 ± 394 | 2.560 ± 357 |
| Se (ng g−1) | 781 ± 75 | 835 ± 91 | 743 ± 79 | 788 ± 65 |
| Co (ng g−1) | 146 ± 21 | 165 ± 44 | 130 ± 12 | 122 ± 16 |
| Mo (ng g−1) | 625 ± 62 | 678 ± 102 | 630 ± 93 | 661 ± 102 |
| Li (ng g−1) | 11.6 ± 2.8 | 12.0 ± 1.4 | 9.6 ± 2.5 | 10.6 ± 2.7 |
Statistically significant difference from control group.
Statistically significant difference from L. edodes 100 mg/kg group.
Essential elements (mean ± standard deviation) in kidney samples from rats exposed to Lentinula edodes in different concentrations. Chemical elements were determined by Inductive Coupled Plasma Mass Spectrometry. Data are reported as μg g−1 or ng g−1 (wet weight).
| Essential elements | Control | |||
|---|---|---|---|---|
| 100 mg/kg | 400 mg/kg | 800 mg/kg | ||
| Cu (μg g−1) | 15.9 ± 2.6 | 15.2 ± 1.9 | 16.3 ± 3.5 | 15.6 ± 1.1 |
| Mg (μg g−1) | 253.3 ± 18.8 | 275.1 ± 23.2 | 242.1 ± 21.1 | 233.2 ± 28.6 |
| Fe (μg g−1) | 85.2 ± 19.3 | 72.3 ± 10.1 | 72.6 ± 16.1 | 68.5 ± 15.1 |
| Mn (ng g−1) | 1.032 ± 95 | 1.039 ± 97 | 916 ± 172 | 835 ± 109 |
| Se (ng g−1) | 1.383 ± 95 | 1.589 ± 140 | 1.425 ± 117 | 1.490 ± 165 |
| Co (ng g−1) | 235 ± 34 | 246 ± 34 | 213 ± 32 | 215 ± 40 |
| Mo (ng g−1) | 285 ± 40 | 290 ± 23 | 250 ± 16 | 248 ± 32 |
| Li (ng g−1) | 13.3 ± 1.7 | 12.7 ± 1.2 | 8.9 ± 1.2 | 8.7 ± 1.3 |
Statistically significant difference from control group.