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eISSN: 2469 - 2786

Bacteriology & Mycology: Open Access

Research Article Volume 6 Issue 4

Heavy metals content and the role of Lepiota cristata as antioxidant in oxidative stress

Dinka Ayana

Department of Biology, Akdeniz University, Turkey

Correspondence:

Received: June 03, 2018 | Published: July 6, 2018

Citation: Sevindik M. Heavy metals content and the role of lepiota cristata as antioxidant in oxidative stress. J Bacteriol Mycol Open Access. 2018;6(4):237-239. DOI: 10.15406/jbmoa.2018.06.00211

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Abstract

The present study aimed to determine antioxidant/oxidant potential and heavy metal content of Lepiota cristata (Bolton) P. kumm. Total antioxidant status (TAS), total oxidant status (TOS) and oxidative stress index (OSI) of the mushroom were determined using Rel Assay kits. Fe, Zn, Cu, Pb and Ni content were measured by a wet decomposition method using a Perkin Elmer AAnalyst 400 AA spectrometer. The study findings demonstrated that TAS value of L. cristata was 2.210±0.068, TOS value was 24.357±0.129 and OSI was 1.103±0.030. It was also determined that Fe content was 381.07±4.847, Zn content was 73.93±2.078, Cu content was 14.16±0.876, Pb content was 8.517±0.623, and Ni content was 3.09±0.30. Thus, it was determined that the mushroom had antioxidant potential. However, due to the high oxidant content, it was considered that the mushroom could only be used as an antioxidant source by collecting samples that grow in adequate regions where the mushroom exhibits low oxidative stress index after determination of the compounds with antioxidant effect in these samples. Furthermore, it was determined that L. cristata Fe, Zn and Ni content were within the ranges reported previously in the literature, however Cu content was lower and Pb content was higher when compared to the ranges reported in the literature.

Keywords: lepiota cristata, antioxidant, oxidant, oxidative stress, heavy metals.

Introduction

Mushrooms have been significant natural sources over the years due to their taste, economic and ecological significances, as well as their medical properties.1 Mushrooms contain several essential amino acids as well as vitamins (thiamin, riboflavin, ascorbic acid, ergosterol and niacin).2,3 Mushrooms can be considered functional nutrients that provide health benefits due to their medical properties in addition to their nutritional value. It was reported that several mushrooms possess antioxidant properties as well. Mushroom organism also contains antioxidant compounds such as phenolics, polysaccharides, tocopherols, flavonoids, carotenoids, glycosides, ergothioneine and ascorbic acid.3–5 Due to these compounds, mushrooms are natural antioxidant sources that alleviate the effects of oxidative stress induced by oxidant compounds in living organisms. Thus, the determination of antioxidant potential of mushrooms is very important for the identification of new natural resources that could be used against diseases induced by oxidative stress. Mushrooms are significant saprotrophic organisms in addition to their use as medical and nutritional sources. Mushrooms store several elements based on the substrate content in their habitat. Due to these properties, mushrooms could also be used as pollution indicators. Thus, the pollution in their habitats could be detected by identifying the elements accumulated in this organisms.6 In their natural habitat, the fruiting bodies of L. cristata are scattered or clustered over the land and they are usually observed in late summer or early fall. L. cristata is a saprophyte that commonly grows in paths, ditches, lawns, roads, gardens and roadsides.7 In the present study, total antioxidant status (TAS), total oxidant status (TOS), oxidative stress index (OSI) and Fe, Cu, Zn, Pb and Ni content were determined in L. cristata (Bolton) P. Kumm ethanol extracts.

Material and methods

Laboratory studies

Lepiota cristata samples used in the study were collected in Gaziantep province. Morphological (shape, color, size) and ecological characteristics of the samples were recorded in the field conditions. The microscopic characteristics of the specimens transported to the laboratory under appropriate conditions were determined by light microscopy using a%3 KOH solution (Leica DM750). The specimen was identified morphologically using the references of Breitenbach et al.8–11 After the identification of the collected mushroom samples, they were dried at 40°C. Then, they were pulverized in a mechanical grinder. Pulverized mushroom samples were extracted with ethanol (EtOH) in a Soxhlet apparatus (Gerhardt EV 14). The mushroom extracts were then concentrated under pressure at 40°C in a rotary evaporator (Heidolph Laborator 4000 Rotary Evaporator) and stored at +4°C.

TAS, TOS and OSI tests

TAS, TOS and OSI values of the mushroom ethanol extracts were measured with Rel Assay brand commercial kits (Assay Kit Rel Diagnostics, Turkey). TAS and TOS tests were conducted on 5 different mushroom samples in 5 replicates. In TAS tests, Trolox was used as calibrator and hydrogen peroxide was used as calibrator in TOS tests.12,13 OSI (Arbitrary unit: AU) values were calculated with the following formula and the results were indicated in percentages.13

OSI( AU )= TOS,μmol H 2 O 2 equiv./L TAS,mmolTroloxequiv./LX10 MathType@MTEF@5@5@+= feaagKart1ev2aaatCvAUfeBSjuyZL2yd9gzLbvyNv2CaerbuLwBLn hiov2DGi1BTfMBaeXatLxBI9gBaerbd9wDYLwzYbItLDharqqtubsr 4rNCHbGeaGqiVCe9Ff0Jb9YrFfeuY=Hhbbf9v8qqaqFr0xc9pk0xbb a9q8WqFfeaY=biLkVcLq=JHqpepeea0=as0Fb9pgeaYRXxe9vr0=vr 0=vqpWqaaeaabiGaciaacaqabeaadaqaaqaaaOqaaKqbakaad+eaca WGtbGaamysamaabmaabaGaamyqaiaadwfaaiaawIcacaGLPaaacqGH 9aqpdaWcaaqaaiaadsfacaWGpbGaam4uaiaacYcacqaH8oqBcaWGTb Gaam4BaiaadYgacaaMc8UaamisamaaBaaajuaibaGaaGOmaaqcfaya baGaam4tamaaBaaajuaibaGaaGOmaaqabaqcfaOaaGPaVlaadwgaca WGXbGaamyDaiaadMgacaWG2bGaaiOlaiaac+cacaWGmbaabaGaamiv aiaadgeacaWGtbGaaiilaiaaykW7caWGTbGaamyBaiaad+gacaWGSb GaaGPaVlaadsfacaWGYbGaam4BaiaadYgacaWGVbGaamiEaiaaykW7 caWGLbGaamyCaiaadwhacaWGPbGaamODaiaac6cacaGGVaGaamitai aaykW7caWGybGaaGPaVlaaigdacaaIWaaaaaaa@71D0@

Determination of heavy metal content

The mushroom samples were dried in an incubator at 40°C. Dried mushroom samples were pulverized in a grinder. Three 1gr specimens were taken from the mushroom samples in three replicates and 50mL glass beakers. Then, 10ml concentrated HNO3 was added to the beakers and stored at room temperature for 24-48 hours. These samples were heated on the heating plate until they turned into sediment. Then, 10mL concentrated HCI was added and the heating process was reconducted. After the reheating, 20mL of diluted HCI was added into the beakers and the samples were filtered. Heavy metal analysis was conducted with a Perkin Elmer (AAnalyst 400) device.14

Results and discussion

TAS, TOS and OSI

In the present study, the TAS value of L. cristata was determined as 2.210±0.068, the TOS value was determined as 24.357±0.129 and the OSI value was determined as 1.103±0.030. There were no previous studies that determined the total antioxidant and oxidant potential and oxidative stress status of L. cristata. Oxidative stress studies on different mushroom species reported that Cyclocybe cylindracea TAS value was 4.325, the TOS value was 21.109 and the OSI was 0.488.15 It was reported that the TAS value of Pholiota limonella was 2.378, TOS value was 4.742 and the OSI value was 0.199.16 In previous studies, it was determined that the TAS values of Auricularia auricula and Trametes versicolor were 1.010 and 0.820, TOS values were 23.910 and 17.760, and OSI values were 2.367 and 2.166, respectively.17 In other studies, the TAS value of Pleurotus eryngii was reported as 1.93 and the TAS value of Auricularia polytricha was reported as 0.93.18,19 It was found in the present study that the antioxidant potential of L. cristata was higher when compared to previous studies conducted on A. auricula, T. versicolor, P. eryngii and A. polytricha. It was also determined that the antioxidant potential of L. cristata was lower when compared to C. cylindracea and P. limonella mushrooms. It was considered that the above-mentioned differences were due to the differences in the potential of these mushrooms to produce antioxidant compounds. Analysis of the oxidant compounds produced by L. cristata and the environmental and physical factors demonstrated that the mushroom had higher TOS value when compared to that of A. auricula, T. versicolor, C. cylindracea and P. limonella mushrooms. It was suggested that the the differences among the TOS values were due to the differences between the regions they were collected and metabolic differences between the mushroom species and resulting variances in oxidant compound production capacities. The OSI value demonstrates the rate the antioxidant compounds produced by the mushrooms inhibit the oxidant compounds produced by the mushroom. Analysis of the oxidative stress levels demonstrated that L. cristata exhibited a lower OSI value when compared to A. auricula and T. versicolor mushrooms. On the other hand, it was observed that L. cristata had a higher OSI value when compared to C. cylindracea and P. limonella mushrooms. Thus, it was determined that L. cristata had antioxidant potential. In this context, it was suggested that L. cristata could be consumed as a natural source after the antioxidant compounds in samples collected in regions with suitable oxidative stress index are determined.

Heavy metal content

Mushrooms have the capacity to biologically store most heavy metals in their fruiting body. Mushrooms could absorb the metals from the substrate via their mycelia. The metal concentrations in the fruiting bodies are affected by the age of mycelium and the interval between fructification (formation of the fruiting body).20 These properties of the mushrooms vary across the species. Thus, different species of mushrooms might indicate the presence of various elements in the environment. In the present study, Fe, Cu, Zn, Pb and Ni content of L. cristata were investigated. The present study findings are presented in Table 1 as mg/kg±Std. In previous studies, it was reported that the Cu content of Lepiota cristata collected in Balıkesir province (Turkey) was 41.67 and the Zn content was 45.58.21 In a different study, it was found that the Fe content in L. cristata collected at Larger Menderes River Basin (Turkey) was 444.8, Cu content was 26.41, Ni content was 3.866, Zn content was 50.04, and Pb content was 2.413.22 Furthermore, in previous studies, the lowest and highest element content of different mushroom species were determined as 14.6-835 for Fe, 29.8-306 for Zn, 64.8-290 for Cu, 0.04-6.88 for Pb and 1.18-5.14 mg.kg-1 for Ni.23–25 L. cristata used in the present study was collected in Gaziantep province (Turkey) and it was determined that its Fe, Cu and Ni content were lower when compared to samples collected at Larger Menderes River Basin. It was also determined that Zn and Pb content were higher when compared to those collected at Larger Menderes River Basin. Furthermore, it was observed that L. cristata mushroom used in our study had higher Zn content and lower Cu content when compared to the samples collected in Balikesir. On the other hand, it was found that Fe, Zn and Ni content of L. cristata collected in Gaziantep province were within the ranges reported in the literature. It was also determined that the Cu content was lower and the Pb content was higher when compared to the values reported in the literature. It was suggested that the differences among the findings could be due to the differences between regional pollution, even though the investigated mushroom species was the same. It was observed that the mushroom stored more Pb when compared to the findings in the literature and samples collected in different regions. Thus, it was suggested that L. cristata mushroom could be utilized as a Pb pollution indicator.

 

Fe

Zn

Cu

Pb

Ni

L. cristata

381.07±4.847

73.93±2.078

14.16±0.876

8.517±0.623

3.09±0.30

Table 1 Heavy metal content of L. cristata
Values are presented as mean±SD; number of mushroom samples n=6; experiments were made as 3 parallels.

Conclusion

In the present study, total antioxidant status, total oxidant status, oxidative stress index of L. cristata mushroom was determined for the first time in the literature. Furthermore, Fe, Zn, Cu, Pb and Ni content of L. cristata mushroom collected in Gaziantep province were determined. It was observed that the mushroom demonstrated antioxidant potential in the study. In addition, it was identified that the oxidative stress index was high due to high levels of oxidant compounds. It was considered that the mushroom could only be used as an antioxidant source by collecting samples that grow in adequate regions where the mushroom exhibits low oxidative stress index after determination of the compounds with antioxidant effect in these samples. Furthermore, it was determined that the heavy metal levels in the mushroom were in the value ranges reported in the literature in general, however Pb levels were higher in the mushroom when compared to the other elements. Thus, it was considered that the mushroom could be used as a Pb pollution indicator.

Acknowledgements

We would like to express our gratitude to Dr. Ömer F. Çolak for his contributions.

Conflict of interest

Author declares that there is no conflict of interest.

References

  1. Tabbouche SA, Gürgen A, Yildiz S, et al. Antimicrobial and anti-quorum sensing activity of some wild mushrooms collected from turkey. MSU Fen Bil Dergi. 2017;5(2):453–457.
  2. Metin I, Güngör H, Colak OF. Ülkemizdeki bazı mantar ve mantar ürünlerinin dış ticareti üzerine bir araştırma ve küresel pazarlanmasına yönelik öneriler. Mantar Dergisi. 2013;4(2): 1–9.
  3. Sánchez C. Reactive oxygen species and antioxidant properties from mushrooms. Synthetic and systems biotechnology. 2017;2(1):13–22.
  4. Adejumo TO, Awosanya OB. Proximate and mineral composition of four edible mushroom species from South Western Nigeria. African Journal of Biotechnology. 2005;4(10):1084–1088.
  5. Sevindik M, Akgul H, Korkmaz AI, Sen I (2018) Antioxidant Potantials of Helvella leucomelaena and Sarcosphaera coronaria. J Bacteriol Mycol Open Access. 2018;6(1):00173.
  6. Stihi C, Radulescu C, Busuioc G, et al. Studies on accumulation of heavy metals from substrate to edible wild mushrooms. Romanian Journal of Physics. 2011;56(1-2):257–264.
  7. Liang JF, Xu J, Yang ZL. Divergence, dispersal and recombination in Lepiota cristata from China. Fungal Diversity. 2009;38(105):e124.
  8. Breitenbach J, Kränzlin F. Fungi of Switzerland. Agarics. 2nd part, Mykologia, Luzern. 1995;4.
  9. Vellinga EC (2001) Studies in Lepiota IV. Lepiota cristata and L. castaneidisca. Mycotaxon. 80:297–306.
  10. Lange C Lepiota Gray. In Funga Nordica. Knudsen and Vesterholt, editors. Agaricoid, boletoid and cyphelloid genera. Copenhagen: Nordsvamp; 2008:537–548.
  11. Boccardo F, Traverso M, Vizzini A, et al. Funghi d'Italia. Zanichelli. 2008.
  12. Erel O. A novel automated direct measurement method for total antioxidant capacity using a new generation, more stable ABTS radical cation. Clin Biochem. 2004;37(4):277–285.
  13. Erel O. A new automated colorimetric method for measuring total oxidant status. Clin Biochem. 2005;38(12):1103–111.
  14. Akgül H, Nur AD, Sevindik M, Doğan M (2016) Tricholoma terreum ve Coprinus micaceus’un bazı biyolojik aktivitelerinin belirlenmesi. Artvin Çoruh Üniversitesi Orman Fakültesi Dergisi. 2016;17(2):158–162.
  15. Sevindik M, Akgül H, Bal C, et al. Phenolic contents, oxidant/antioxidant potential and heavy metal levels in cyclocybe cylindracea. Indian journal of pharmaceutical education. 2018;52(3):437–441.
  16. Sevindik M, Akgul H, Bal C, et al. Oxidative stress and heavy metal levels of pholiota limonella mushroom collected from different regions. Current Chemical Biology. 2018.
  17. Akgul H, Sevindik M, Coban Cl. New approaches in traditional and complementary alternative medicine practices: Auricularia auricula and Trametes versicolor. J Tradit Med Clin Natur. 2017;6(239):2.
  18. Yildirim NC, Turkoglu S, Yildirim N, et al. Antioxidant properties of wild edible mushroom Pleurotus eryngii collected from Tunceli province of Turkey. Digest Journal of Nanomaterials and Biostructures. 2012;7(4):1647–1654.
  19. Avci E, Cagatay G, Avci GA, Cevher SC, Suicmez M (2016) An edible mushroom with medicinal significance; Auricularia polytricha. Hittite Journal of Science and Engineering. 3(2):111–116.
  20. Raj DD, Mohan B, Vidya Shetty. Mushrooms in the remediation of heavy metals from soil. Int J Environ Pollut Control Manag. 2011;3(1):89–101.
  21. Sen I, Alli H, Col B, et al. Trace metal contents of some wild-growing mushrooms in Bigadiç (Balıkesir), Turkey. Turkish Journal of Botany. 2012;36(5):519–528.
  22. Durkan N, Dogan Y, Unver MC, et al. (2012) Levels of trace metals in some macrofungi from buyuk menderes river basin. Natura Montenegrina. 9(3):753–759.
  23. Kalac P, Staskova I. Concentrations of lead, cadmium, mercury and copper in mushrooms in the vicinity of a lead smelter. Science of the Total Environment. 1991;105:109–119.
  24. Mallikarjuna SE, Ranjini A, Haware DJ, et al. Mineral composition of four edible mushrooms. Journal of Chemistry. 2012;2013:1-5.
  25. Sevindik M, Eraslan CE, Akgül H. Bazı makrofungus türlerinin ağır metal içeriklerinin belirlenmesi. Ormancılık Dergisi. 2015;11(2):48–53.
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