Article Versions
Export Article
Cite this article
  • Normal Style
  • MLA Style
  • APA Style
  • Chicago Style
Original Article
Open Access Peer-reviewed

Heavy Metal Determination and Health Risk Assessment of Oyster Mushroom Pleurotus tuberregium (Fr.) Singer, Collected from Selected Markets in Imo State. NIGERIA

Uloma A. Ihugba, Chris O. Nwoko , Feechi R. Tony-Njoku, Adaeze A. Ojiaku, Lucy Izunobi
American Journal of Environmental Protection. 2018, 6(1), 22-27. DOI: 10.12691/env-6-1-4
Published online: February 26, 2018

Abstract

Oyster mushroom Pleurotus tuberregium (Fr.)(Sing), Ǫsu, is a common mushroom which is used as food or medicine, more commonly as a soup thickener. This study investigated the presence of heavy metals (Zn, Pb, Ni, Cu) in wild samples of Pleurotus tuberregium sclerotia consumed within Imo state. The oyster mushrooms purchased from different markets from Imo State were mineralized with H2SO4 and HNO3 and analyzed using flame Atomic Absorption Spectrophotometer (AAS) Thermo Scientific model. The mean concentrations of Pb: 0.13 mg/kg (ranged 0.04±0.005mg/kg to 0.35±0.005mg/kg), Zn: 1.26mg/kg (ranged from 0.03 ± 0.007 mg/kg to 3.25 ± 0.01 mg/kg) and Ni and Cu were 0.0001mg/kg, 0.164mg/kg, respectively. These results were compared with the data from literature and levels set by regulatory authorities, with the conclusion that the consumption of oyster mushroom sclerotium does not pose a toxicological risk. The Zn, Pb, Ni and Cu content of the studied products would contribute to only about 7.4%, 30.3%, 0.001% and 1.91%, respectively of the provisional tolerable weekly intake of Zn, Pb, Ni and Cu. The Cu and Zn contents would contribute to nutritional intake of the metal in the general population. It is recommended that the outer layers of the sclerotia be properly scrapped and washed before use to reduce air-borne metal contamination.

1. Introduction

Edible Oyster Mushrooms (Pleurotus tuber-regium) from the family of Pleurotaceae, contains high concentrations of nutritional trace elements and mineral constituents in human diets, helps in growth and tissue repair in the body of humans 1. It represents part of natural forest ecosystems and plays an important role in the cyclic pathways of elements and organic matter 2. Oyster Mushroom is characterized to have low energy value and high concentration of essential biologically valuable elements, specific ß-glucans and antioxidant substances 3, 4. Moreover, they provide a valuable source of fiber, vitamins and minerals such as thiamin, riboflavin, vitamin D, potassium, phosphorus, iron and calcium 5, 6. It has been known for long that mushrooms are able to accumulate large amounts of heavy metals 7 what makes them ideal for biomonitoring of environmental pollution- particularly contamination of forest ecosystems 8 . There are many factors that influence the presence of metals in mushrooms, for example climate, environmental conditions and concentration of macromolecules in the cell wall of each specific species 9. Under natural conditions, the concentration of heavy metals in certain species of Oyster mushrooms can be higher even if the soil contamination level is low 1. The highest concentrations of trace elements are mostly found in the hemosphere, lower values are in the spores and the lowest values are in the stem 10, 11.

Edible Mushrooms are valued for their unique taste, aroma, nutritional value and medicinal potentials 12. Mushrooms of the genus Pleurotus tuberregium are among the very popular edible varieties not only due to their properties but also to their rapid growth and ease of cultivation 13. Consumers of delicacies such as Mushrooms, which may not have been extensively investigated for toxic metal contents, could be exposed via the diet. Information about heavy metal concentrations in foods and their consumers dietary intake is very important for assessing their health risks to humans. In Imo state, southestern Nigeria, oyster mushroom is a predominant delicacy, mainly used as soup thickener and /or prepared into local cake. There is urgent need to continuously monitor heavy metal load in this fungi species so as to reduce risk of human heavy metal poisoning. The aim of this research work therefore was to assess heavy metal concentration of oyster mushroom and its risk to human health.

2. Materials and Methods

2.1. Study Area

The study was carried out in Imo State, Southeastern Nigeria. It falls within the geographical coordinates of longitude 7o2'15'' – 7o3'00''E and latitude 5o27'80'' – 5o28'00''N. Imo State is underlain by the Benin Formation. This formation which is Pliocene to Miocene in age consists of coastal plain sands, which is about 0.05 – 2.0 mm in size, with minor clay beds; and this type of soil has good drainage and is well aerated, causing it to dry out quickly 14. It contains some isolated gravels, conglomerates, and very coarse sandstone in some places. Thickness of the formation is about 800 m at its depocenter, while the mean depth to water table is about 24 m 15. Benin Formation is overlain by alluvium deposits and underlain by Ogwashi-Asaba Formation which consists of lignite, sandstones, clays and shale

2.2. Sample Collection

Imo state formed the sample frame and was stratified into three (3) zones along the senatorial districts. Four (4) samples of P. tuberregium (osu) were randomly collected from each of the senatorial zones, making a total of 12 oyster mushrooms from the following markets: Okigwe zone: Okigwe market, Anara, Mbano, Obowo, Owerri Zone: Eke-ukwu Owerri, Mbaise, Mbieri, Ohaji, Orlu zone: Umuaka, Ideato, Orlu market, Awo-idemilli . These were all preserved until analysis.

2.3. Sample Preparation and Analysis

The samples from each zone were crushed and blended using ceramics mortar, air dried and later sieved through 2mm and labeled. One gram of the sieved samples were weighed accurately and transferred to a 250ml conical flask and thereafter digested with 10 ml of concentrated acid mixture (ratio 1:1, nitric and sulphuric acids). The digests were subsequently used to determine the concentration of Cu, Pb, Zn, Ni, using Atomic Absorption Spectrophotometer (AAS.) Thermo Scientific AA 301 version.

2.4. Quality Assurance

Appropriate quality assurance procedures and precautions were carried out to ensure the reliability of the results of the present study. Samples were generally handled carefully to avoid contamination. All chemicals used were of analytical grade: H2SO4 (98%, BDH Laboratory Supplies, Poole, England); HNO3 (69%, BDH Laboratory Supplies, Poole, England). Reagent blank determinations were used to correct the instrument readings. With every set of 10 samples examined, one blank sample was run and no interference was noted. The accuracy of the analytical method was calculated by analyzing reference standards (Accu Standards, New Haven Connecticut, USA). Also, a replicate test was carried out for some of the metals. Recoveries for the reference standards varied from 99.5-100%, and for the replicate study, from 95.5 - 99.1%. Additional data on results of QC/QA protocols in the determination of heavy metal contents of selected Nigerian foodstuff have been reported elsewhere 16.

2.5. The Pollution Index (PI) [17]

Where PI =heavy metal pollution index, HC is the concentration of n heavy metals in soil samples

2.6. Estimated Weekly Intake (EWI)

The estimated weekly intake (EWI, mg/kg body weight/week) of trace metals through consuming oyster mushroom was calculated using the following equation:

The average weekly edible fungi intake was assumed to be 210 g/week 18 and the average body weight was assumed to be 60 kg, according to USEPA 19 guidelines. The results of the intake calculations were assessed based on the provisional tolerable weekly intake (PTWI) Joint FAO/WHO Expert Committee on Food Additives 20.

2.7. Target Hazard Quotient (THQ)

The method used for the evaluation of target hazard quotient (THQ) as described by Chien et al., 21 by the equation below:

EF is exposure frequency (365 days/year); ED is the exposure duration (70 years), equivalent to the average lifetime 22, FIR is the oyster mushroom ingestion rate (g/person/day), assuming 0.5 g for an average level consumer (ALC), and 1.0 g for a high level consumer (HLC); C is the metal concentration in Oyster mushroom (mg/kg dry weight); RfDo is the Oral Reference Dose (mg/kg/day); WAB is the average body weight (70 kg), and TA is the averaged exposure time for non-carcinogens (365 days/year × ED).

The RfDo values in mg/kg body wt/day for Copper, Zinc, Nickel, and Lead were 0.04, 0.3, 0.02 and 0.0035 19, respectively. An index more than 1 is considered as not safe for human health 19. This THQ marker connects the metals concentrations in food with their toxicity, quantity and quality of food consumption and body mass of consumers. The use of this complex parameter is more extensive in evaluating the potential health risk of trace metals present in various foods 23.

2.8. Statistical Analysis

Data from three replicates were subjected to ANOVA using Minitab Statistical software version. 16 and significant (p<0.05) means were separated using Tukey pairwise comparison.

3. Results and Discussion

The results of this study showed varying trace metal concentrations across the localities where samples were purchased. In some instances, the variations were wide for some metals compared to others and this likely depends on the geological composition of the areas where the oyster mushroom was obtained (Table 1). The oyster mushroom from Imo state contained varied concentrations of heavy metals. The Zinc concentration ranged from 0.03 ± 0.007 mg/kg to 3.25 ± 0.01mg/kg. The lowest concentration occurred at Mbieri (0.03 ± 0.007 mg/kg) while the highest was recorded in Ohaji (3.25 ± 0.01mg/kg). Zinc concentration significantly differed among different locations in Imo state except the following locations: Okigwe market, Anara , Obowo , Eke-ukwu, Mbaise, Mbano, Mbieri , Umuaka and Awo idemili (Table 1). Lead (Pb) mushroom concentration ranged from (0.04±0.01mg/kg to 0.36 ± 0.01mg/kg). The highest concentration of 0.36mg/kg occurred in Mbaise and followed by Ohaji (0.35 mg/kg). Lowest Pb concentrations were recorded in Okigwe market, Anara , ideato and Awo-Idemili (0.04mg/kg). Lead (Pb) concentration did not significantly (p<0.05) differ among the following locations Okigwe market, Anara, Mbano, Ideato and Awo-Idemili. But differed among Mbaise , Ohaji and Mbieri. Nickel (Ni) concentration in oyster mushroom was negligible across the locations (0.0001 mg/kg).

Copper (Cu) concentration varied in the locations sampled. The concentration varied from 0.03mg/kg to 0.83mg/kg. The highest concentration occurred in Anara market followed by Okigwe market. The lowest of 0.03 mg/kg was recorded at Mbieri market followed by Ohaji, Umuaka, Ideato and Eke-ukwu Owerri market. However, Cu concentration did not differ among all the locations. The pollution index indicated varied level of heavy metal contamination of oyster mushroom across the state. The highest pollution index of 0.046 was recorded in Ohaji market. Whereas the lowest was observed in Umuaka (0.019). With the PI <1in all the locations , it indicated very low level of Zn, Cu, Pb and Ni contamination of oyster mushroom.

The results of the one-way ANOVA indicated that sampling location influenced the concentration of all heavy metal determined except Ni and Cu (P<0.0001) (Table 1). Tukey family error test at 5% level of significance was used to separate those mean metal concentrations impacted by the locations. For Zn, three distinct groups emerged where Ohaji differed from Ideato, Orlu market and the rest of the locations. Also for Pb, four groups emerged with Ohaji the superior group followed by Mbieri, Eke-ukwu and Obowo, Umuaka and the rest locations.

Provisional tolerable weekly intake (PTWI) is a value set by the FAO and WHO 20 and defined as the maximum quantity of contaminants that a consumer weighing 60 kg may take per week. The legislation states the following PTWI indices for individual heavy metals: Zn: 1.0 mg/kg of bodyweight (60 mg Zn.person-1), Pb: 0.025 mg.kg-1 of bodyweight (1.50 mg Pb.person-1), Ni: 0.5 mg/kg of body weight (30 mg Ni. Person -1), Cu: 0.5mg/kg of bodyweight (30.0 mg Cu. Person-1). The estimated weekly intake (EWI) of Zn, Pb, Ni, and Cu by a 60 kg adult consuming 210 g of oyster mushroom each week, and the provisional tolerable weekly intake (PTWI) for the metals investigated is presented in Table 2.

The estimated weekly intake of Zn, Pb, Ni , Cu from eating the tested fungi was lower than the PTWI. Zn (4.41 mg/kg body weight/week), Pb (0.46 mg/kg body weight/week), Ni ( 0.00035mg/kg body weight/week), Cu (0.574mg/kg body weight/week) from which the weekly intake accounted for 7.35%, 30.3%, 0.001% and 1.91% of the PTWI for Zn, Pb, Ni and Cu, respectively.

The THQs have been recognized as useful parameters for risk assessment of metals associated with the intake of contaminated food and foodstuff. It represents the ratio between the estimated dose of a contaminant and the reference dose below which there will be no appreciable risk.

THQ values on the consumption of meals prepared with oyster mushroom by average level consumer (ALC) who consumes a 0.5g of oyster mushroom from a meal and a high level consumer (HLC) who consumes 1.0g of oyster mushroom from a meal (using the mean of data obtained) are presented in Table 2. For the high level consumer (HLC), mean value for Zn, Pb, Cu and Ni are 0.0042, 0.025, 0.00388, 0.000005, respectively. Similarly, for average level consumer (ALC) mean value for Zn, Pb, Cu and Ni are 0.00021, 0.018, 0.00182 and 0.0000025, respectively.

In China, 29 investigated 285 samples of 9 species of edible mushroom species collected from markets in Beijing China for levels of selected heavy metals. The values compared favourably with the present work except Zn with higher values in China. Daniel-Umeri et al., 25 also observed higher Zn concentrations in P. tuberregium in Nigeria. Similar trends in Zn metal were also recorded in Turkey Zn: 35mg/kg , Ethiopia :51mg/kg (Table 4). In China, Cu mean value was 26.7 mg/kg as recorded by Zhu et al., 30, in Ethiopia mean value of Cu was 89.7 mg/kg 28 whereas in Turkey Cu mean value was 8.0mg/kg 27.

4. Discussion

Oyster mushroom Pleurotus Tuberregium (Sing) is a common mushroom which is used as food or medicine, more commonly as a soup thickener. This study investigated the presence of heavy metals (Zn, Pb, Ni and Cu) in wild samples of Pleurotus tuberregium sclerotia consumed within our localities. All the metals assessed were found to be above the method detection limit. However, Ni recorded the least mean concentration of 0.0001mg/kg and this concentration is negligible. The mean Zinc concentration of 1.26 mg/kg is recommended as Zn is one of the most important minerals needed by our body systems due to the fact that it is highly associated with protein and carbohydrate rich foods. Zinc is also used in medicines to treat rashes, acne, dandruff and athlete’s foot 31. It has biological significance for living organisms and mushrooms are known as good zinc accumulators 32. The mean value for zinc in the investigated mushroom sample is slightly above the permissible limit of 0.3-1.0 mg/kg recommended in food 20. Zinc concentrations of edible mushroom samples in the literature have been reported to be: 38.2 mg/kg in Nigeria 25, and 6.4-27.33 mg/kg 26, 33, 35 mg/kg in Turkey 27, 51.2 mg/kg in Ethiopia 28, in China 86.4mg/kg 29 and, 48.4 mg/kg 30. This reveals that the findings of this study are in agreement with the results reported for similar studies.

Copper is essential metal, which serve as a constituent of some metalloenzymes, and is required in hemoglobin synthesis and catalysis of metabolic growth 34. Copper was detected in the sclerotia of the oyster mushroom at varied concentrations. The mean concentration of 0.164 mg/kg is below the permissible value of 0.05-0.5 mg/kg set by FAO/WHO, (2004) in foods. Other workers presented copper contents of the mushroom samples in the literature to be in the ranges: 3.12-26.7 mg/kg 30, 2.6 - 72.4 mg/kg, 1.8 - 22.3 mg/kg 31, 5.0 - 83.0 mg/kg 35 and 13.7 - 182.4 mg/kg 36, 8.0 mg/kg 27 Table 3. The results obtained, in the current study, indicated that copper content of the investigated mushroom samples were found to be comparable with those reported in the literature.

Lead creates health disorders such as sleeplessness, tiredness, hearing, and weight loss 26. Unfortunately, the concentrations of Pb in some locations were relatively higher than the permissible limits in food items. According to FAO/WHO 20 tolerable weekly intake of lead is 0.025 mg/kg body weight. From the study, Pb concentration of the oyster mushroom exceeded threshold limit of 0.025mg/kg in all the locations. This result may be attributed to air borne lead arising from vehicular and industrial emissions. Air borne Pb often gets deposited on the oyster mushroom while displayed openly in the market place. Nwoko and Mgbeahuruike, 37 reported higher trace metal concentration on ready-to-use herbal remedies exposed to air borne trace metal contamination than those not exposed to air borne metal contamination.

Nickel is introduced into the environment from both natural and man-made sources and is circulated throughout all environmental compartments by means of chemical and physical processes, as well as by being biologically transported by living organisms. Mean nickel concentration of 0.0001 mg/kg in this present study is below the recommended limit of 0.5mg/kg set by FAO/WHO, 20.

The trace metal pollution index of the entire locations of less than 1 (PI <1) indicated relatively low trace metal contamination of oyster mushroom within Imo state. Trace metal contamination of food items such as mushroom is normally influenced by a number of chemical and environmental factors: geochemical and physical parameters including the type of soil, soil pH, humidity, the organic matter content of the soil, and the concentration of extractable trace metal 38, 39.

The Target Hazard Quotient (THQ) for trace metal present in oyster mushroom for average and high level consumers showed mean values below reference dose (Table 3). The RfDo values in mg/kg body wt/day for Copper, Zinc, Nickel, and Lead were 0.04, 0.3, 0.02 and 0.0035 19, respectively. An index more than 1 is considered as not safe for human health 19. This result indicated that there is no appreciable risk in the consumption of the oyster mushroom throughout life. The THQ marker connects the metals concentrations in food with their toxicity, quantity and quality of food consumption and body mass of consumers. The use of this complex parameter is more extensive in evaluating the potential health risk of trace metals present in various foods 23. For the metals determined in oyster mushroom the THQ were far below 1. A small value of the index (<1) shows reduced health hazard and a value between 1 and 5 represents a concern level for health hazard 23.

Comparison of the present result with data available from the literature showed that trace metal accumulation by oyster mushroom species varied across regions and ecological boundaries (Table 4). However, results for some metals from oyster mushroom species considered, in this study, were observed to differ greatly. This difference in the contents of the metals could be associated to the variation in the composition of the substrate from which the mushrooms got their nutrients, the site where the samples collected from, age of the fruiting bodies and mycelium, and distance from the source of pollution 8. Besides, the metal concentrations in the mushroom samples could also mainly be affected by the pH or organic matter content of the substrates 40.

5. Conclusion

Oyster mushroom Pleurotus Tuberregium (Sing) is a common mushroom which is used as food or medicine, more commonly as a soup thickener. Oyster Mushroom trace metal contamination varied across the state, mean values of Zn and Pb only exceeded recommended threshold limits while Cu and Ni were within acceptable limits. However, estimated weekly intake (EWI) for an adult consuming 210g of mushroom, having 60kg body weight was found to be lower than PTWI for Zn, Pb, Ni and Cu. Also, target hazard quotient was found to be below the reference dose (Rfdo) and also less 1 (THQ<1).

References

[1]  Falandysz, J., Kawano, M., Swieczkowski, A., Brzostowski, A., & Dadej, M. Total mercury in wild-grown higher mushrooms and underlying soil from Wdzydze Landscape Park, Northern Poland. Food Chemistry, 2003. 81, 21-26.
In article      View Article
 
[2]  Petkovšek, S. A. S., Pokorny, B.. Lead and cadmium in mushrooms from the vicinity of two large emission sources in Slovenia. Science of the Total Environment, 2013.vol. 443, p. 944-954.
In article      View Article  PubMed
 
[3]  Kalač, P.. A review of chemical composition and nutritional value of wild growing and cultivated mushrooms. Journal of science food and Agriculture in Nitra. 2013, vol. 93,
In article      PubMed
 
[4]  Kalač, P.. Chemical composition and nutritional value of European species of wild growing mushrooms: a review. Food Chemistry, 2009.vol. 113, p. 9-16.
In article      View Article
 
[5]  Wang, X. M., Zhang, J., Wu, L. H., Zhao, Y. L., Li, T., Li, J. Q., et al.. A mini-review of chemical composition and nutritional value of edible wild-grown mushroom from China. Food Chemistry, 2014.vol. 151, p. 279-285.
In article      View Article  PubMed
 
[6]  Falandysz, J., Borovička, J.. Macro and trace mineral constituents and radionuclides in mushrooms: Health benefits and risks. Applied Microbiology and Biotechnology, 2013.vol. 97, no. 2, p. 477-501.
In article      View Article  PubMed
 
[7]  Zhang, D., Gao, T., Ma, P., Luo, Y., Su, P. Bioaccumulation of heavy metal in wild growing mushrooms from Liagshan Yi nationality autonomous prefecture, China. Journal of Natural Science, 2008. vol. 13, no. 3, p. 267-272.
In article      View Article
 
[8]  Radulescu, C., Stihi, C., Busuioc, G., Gheboianu, A. I., Popescu, I. V. Studies concerning heavy metals bioaccumulation of wild edible mushrooms from industrial area by using spectrometric techniques. Bulletin of Environmental Contamination and Toxicology, 2010. vol. 84, p. 641-646.
In article      View Article  PubMed
 
[9]  Ostos, C., Pérez-Rodríguez, F., Arroyo, B. M., Moreno-Rojas, R.. Study of mercury content in wild edible mushrooms and its contribution to the Provisional Tolerable Weekly Intake in Spain. Journal of Food Composition and Analysis, 2015.vol. 37, p. 136-142.
In article      View Article
 
[10]  Árvay, J., Záhorcová, Z., Tomáš, J., Hauptvogl, M., Stanovič, R., Harangozo, Ľ.. Mercury in edible wild-grown mushrooms from historical mining area-Slovakia: bioaccumulation and risk assessment. J. Microbiol. Biotech. Food Sci., 2015.vol. 4, special issue 3, p. 1-4.
In article      View Article
 
[11]  Krasińska, G., Falandysz, J.. Mercury in Orange Birch Bolete Leccinum versipelle and soil substratum: bioconcentration by mushroom and probable dietary intake by cosumers. Environmental Science and Pollution Research (in press). 2015
In article      PubMed  PubMed
 
[12]  Jonathan, S.G. and Fasidi, I.O. Antimicrobial activities of two Nigeria edible macro-fungi: Lycoperdon pusilum (Bat. Ex) and Lycoperdon giganteum (Pers.), African Journal of Biomedical Research, 2003. 6: 85 – 90
In article      View Article
 
[13]  Garcia, M. A., Alonso, J., Fernandez, M. I., & Melgar, M. J. Lead content in edible wild mushrooms in Northwest Spain as indicator of environmental contamination. Archives Environmental Contaminatian and Toxicology, 1998. 34, 330-335.
In article      View Article  PubMed
 
[14]  Onweremadu, E.U. and Duruigbo, C.I. Assessment of Cd concentration of crude oil polluted arable soil. International Journal of Environmental Science and Technology, 2007. 4(3), 409-412.
In article      View Article
 
[15]  Nwachukwu, A.M., Feng, H., and Achilike, K. Integrated study for automobile wastes management and environmentally friendly mechanic villages in the Imo River Basin, Nigeria. African Journal of Environmental Science and Technology, 2010. 4(4), 234-294.
In article      View Article
 
[16]  Nnorom I. C. , J. E. Alagbaoso U. H. Amaechi, C. Kanu and U. Ewuzie Determination of Beneficial and Toxic Metals in Fresh Palm Oil (Elaeis guineensis Jacq.) from South-Eastern Nigeria: Estimation of Dietary Intake Benefits and Risks. Journal of Scientific Research & Reports. 2014. 3(16): 2216-2226.
In article      View Article  PubMed
 
[17]  Usero, J., E. Gonza-Regalado and I. Gracia, Trace metal in the bivalve molluscs Ruditapes decussates and Ruditapes philippinarum from the Atlantic Coast of Southern Spain. Environ. Int., 1997. 23: 291-298.
In article      View Article
 
[18]  Svoboda L, Zimmermannov´a K, Kalaˇc P. Concentrations of mercury, cadmium, lead, and copper in fruiting bodies of edible mushrooms in an emission area of a copper smelter and a mercury smelter. Sci Total Environ. 2000. 246(1): 61-7.
In article      View Article
 
[19]  US EPA (Environmental Protection Agency). A review of the reference dose and reference concentration processes. Risk Assessment Forum, Washington, DC; EPA/630/P-02/002F, 2002. Available online at https://www.epa.gov/ncea/raf.
In article      View Article
 
[20]  FAO/WHO, Joint Expert Committee on Food Additives, Fifty-ninth meeting, 2002, (2004). p (www.fao.org/es/ESN/Jecfa/59corr.pdf) accessed 20th June, 2017.
In article      View Article
 
[21]  Chien LC, Hung TC, Choang KY, Choang KY, Yeh CY, Meng PJ, Shieh MJ, Han BC Daily intake of TBT, Cu, Zn, Cd and As for fishermen in Taiwan. Sci Total Environ .2002. 285:177-185.
In article      View Article
 
[22]  Bennett DH, Kastenberg WE, McKone TE A multimedia, multiple pathway risk assessment of atrazine: the impact of age differentiated exposure including joint uncertainty and variability. Reliability Eng Sys Saf. 1999. 63:185-198.
In article      View Article
 
[23]  Naughton DP, Petróczi A. Heavy metal ions in wines: meta-analysis of target hazard quotients reveals health risks. Chem Cent J, 2008: 2:22.
In article      View Article  PubMed
 
[24]  Quarcoo A, Adotey G. Determination of heavy metals in Pleurotus ostreatus (Oyster mushroom) and Termitomyces clypeatus (Termite mushroom) sold on selected markets in Accra, Ghana. Mycosph. 2013. 4(5): 960-967.
In article      View Article
 
[25]  Daniel-Umeri R. A., K. Emumejaye and C.K Ojebah. Assessment of Heavy Metals in Some Wild Edible Mushrooms Collected from Ozoro and its Environs, Delta State, Nigeria. International Journal of Science and Technology. 2015. Vol. 5(10): 1-9.
In article      View Article
 
[26]  Udochukwu U, Nekpen B.O, Udinyiwe O.C, Omeje FI. Bioaccumulation of Heavy metals and pollutants by edible mushroom collected from Iselu market Benin-city. Int Jour. Current Microbiol App Sci. 2014. 3(10): 52-7.
In article      View Article
 
[27]  Akyuz M, Kirbag S. Nutritive value of wild edible and cultured mushrooms. Turkish Jour. Bio. 2010. 34: 97-102.
In article      View Article
 
[28]  Gebrelibanos, M Negussie Megersa2 and Abi M. Taddesse3. Levels of essential and non-essential metals in edible mushrooms cultivated in Haramaya, Ethiopia. International Journal of Food Contamination .2016. 3:2. 1-12.
In article      View Article
 
[29]  Huang Q, Y. Jia, Y. Wan, H. Li, and R. Jiang Market Survey and Risk Assessment for Trace Metals in Edible Fungi and the Substrate Role in Accumulation of Heavy Metals. Journal of Food. 2015. Vol. 80(7): 1612-1618.
In article      View Article  PubMed
 
[30]  Zhu F., Li Q, Wenxiu F, Meiying Q, Hailing H, XuejingW. .Assessment of heavy metals in some wild edible mushrooms collected from Yunnan Province, China Environ Monit Assess. 2010. 3 : 1-9.
In article      View Article
 
[31]  Okwulehie IC, Ogoke JABioactive, nutritional and heavy metal constituents of some edible mushrooms found in Abia State of Nigeria. Int J App Microbio Biotech Res.2013. .1:7–15.
In article      View Article
 
[32]  Isıloglu M, Yılmaz F, Merdivan M.. Concentrations of trace elements in wild edible mushrooms. Food Chem. 2001. 73(2): 169-75.
In article      View Article
 
[33]  Nnorom IC, Jarzyñska G, Drewnowska M, Kojta AK, Pankavec S, Falandysz J Trace elements in sclerotium of Pleurotus tuber-regium (Ósu) mushroom-dietary intake and risk in Southeastern Nigeria. J Food Comp Anal. 2013. 29:73-81.
In article      View Article
 
[34]  Silvestre MD, Lagarda MJ, Farra R, Martineze-Costa C, Brines J. Copper, iron and zinc determination in human milk using FAAS with microwave digestion.Food Chem. 2000. 68:95-9.
In article      View Article
 
[35]  Uzun Y, Genccelep H, Kaya A, Akcay ME. The mineral contents of some wild edible mushrooms. Eko. 2011; 20(80): 6-12.
In article      View Article
 
[36]  George P.L, Ranatunga T.D, Reddy S.S, Sharma G.C.. A comparative analysis of mineral elements in the mycelia and the fruiting bodies of Shiitake mushrooms. Am J Food Tech. 2014; 9(7): 360-9.
In article      View Article
 
[37]  Nwoko C.O and L.O Mgbeahuruike Heavy metal Contamination of ready-to-use herbal remedies in South eastern Nigeria. Pakistian Jour. Of Nutrition. (2011). 10 (10): 959-964.
In article      View Article
 
[38]  Nwoko C. O., E. N. Emenyonu and C. E. Umejuru, Trace Metal Contamination of Selected vegetables grown around Owerri Municipality, Nigeria. Journal of Agriculture and Ecology Research International. (2014) 1(1): 18-29.
In article      View Article
 
[39]  Nwoko, C.O and J.K Egunjobi. Lead Contamination of Soil and Vegetation in an abandoned battery factory site in Ibadan, Nigeria. Journal of Sustainable Agriculture and Environment. 2002. Vol. 4(1). 91-96.
In article      
 
[40]  Demirbas A.. Metal ion uptake by mushrooms from natural and artificially enriched soils. Food Chem. 2002. 78: 89-93.
In article      View Article
 

Published with license by Science and Education Publishing, Copyright © 2018 Uloma A. Ihugba, Chris O. Nwoko, Feechi R. Tony-Njoku, Adaeze A. Ojiaku and Lucy Izunobi

Creative CommonsThis work is licensed under a Creative Commons Attribution 4.0 International License. To view a copy of this license, visit https://creativecommons.org/licenses/by/4.0/

Cite this article:

Normal Style
Uloma A. Ihugba, Chris O. Nwoko, Feechi R. Tony-Njoku, Adaeze A. Ojiaku, Lucy Izunobi. Heavy Metal Determination and Health Risk Assessment of Oyster Mushroom Pleurotus tuberregium (Fr.) Singer, Collected from Selected Markets in Imo State. NIGERIA. American Journal of Environmental Protection. Vol. 6, No. 1, 2018, pp 22-27. https://pubs.sciepub.com/env/6/1/4
MLA Style
Ihugba, Uloma A., et al. "Heavy Metal Determination and Health Risk Assessment of Oyster Mushroom Pleurotus tuberregium (Fr.) Singer, Collected from Selected Markets in Imo State. NIGERIA." American Journal of Environmental Protection 6.1 (2018): 22-27.
APA Style
Ihugba, U. A. , Nwoko, C. O. , Tony-Njoku, F. R. , Ojiaku, A. A. , & Izunobi, L. (2018). Heavy Metal Determination and Health Risk Assessment of Oyster Mushroom Pleurotus tuberregium (Fr.) Singer, Collected from Selected Markets in Imo State. NIGERIA. American Journal of Environmental Protection, 6(1), 22-27.
Chicago Style
Ihugba, Uloma A., Chris O. Nwoko, Feechi R. Tony-Njoku, Adaeze A. Ojiaku, and Lucy Izunobi. "Heavy Metal Determination and Health Risk Assessment of Oyster Mushroom Pleurotus tuberregium (Fr.) Singer, Collected from Selected Markets in Imo State. NIGERIA." American Journal of Environmental Protection 6, no. 1 (2018): 22-27.
Share
  • Table 2. Comparison of Weekly intake of Zn, Pb, Ni and Cu by consuming Oyster mushroom (P.tuberregium) to provisional tolerable weekly intake (PTWI)
[1]  Falandysz, J., Kawano, M., Swieczkowski, A., Brzostowski, A., & Dadej, M. Total mercury in wild-grown higher mushrooms and underlying soil from Wdzydze Landscape Park, Northern Poland. Food Chemistry, 2003. 81, 21-26.
In article      View Article
 
[2]  Petkovšek, S. A. S., Pokorny, B.. Lead and cadmium in mushrooms from the vicinity of two large emission sources in Slovenia. Science of the Total Environment, 2013.vol. 443, p. 944-954.
In article      View Article  PubMed
 
[3]  Kalač, P.. A review of chemical composition and nutritional value of wild growing and cultivated mushrooms. Journal of science food and Agriculture in Nitra. 2013, vol. 93,
In article      PubMed
 
[4]  Kalač, P.. Chemical composition and nutritional value of European species of wild growing mushrooms: a review. Food Chemistry, 2009.vol. 113, p. 9-16.
In article      View Article
 
[5]  Wang, X. M., Zhang, J., Wu, L. H., Zhao, Y. L., Li, T., Li, J. Q., et al.. A mini-review of chemical composition and nutritional value of edible wild-grown mushroom from China. Food Chemistry, 2014.vol. 151, p. 279-285.
In article      View Article  PubMed
 
[6]  Falandysz, J., Borovička, J.. Macro and trace mineral constituents and radionuclides in mushrooms: Health benefits and risks. Applied Microbiology and Biotechnology, 2013.vol. 97, no. 2, p. 477-501.
In article      View Article  PubMed
 
[7]  Zhang, D., Gao, T., Ma, P., Luo, Y., Su, P. Bioaccumulation of heavy metal in wild growing mushrooms from Liagshan Yi nationality autonomous prefecture, China. Journal of Natural Science, 2008. vol. 13, no. 3, p. 267-272.
In article      View Article
 
[8]  Radulescu, C., Stihi, C., Busuioc, G., Gheboianu, A. I., Popescu, I. V. Studies concerning heavy metals bioaccumulation of wild edible mushrooms from industrial area by using spectrometric techniques. Bulletin of Environmental Contamination and Toxicology, 2010. vol. 84, p. 641-646.
In article      View Article  PubMed
 
[9]  Ostos, C., Pérez-Rodríguez, F., Arroyo, B. M., Moreno-Rojas, R.. Study of mercury content in wild edible mushrooms and its contribution to the Provisional Tolerable Weekly Intake in Spain. Journal of Food Composition and Analysis, 2015.vol. 37, p. 136-142.
In article      View Article
 
[10]  Árvay, J., Záhorcová, Z., Tomáš, J., Hauptvogl, M., Stanovič, R., Harangozo, Ľ.. Mercury in edible wild-grown mushrooms from historical mining area-Slovakia: bioaccumulation and risk assessment. J. Microbiol. Biotech. Food Sci., 2015.vol. 4, special issue 3, p. 1-4.
In article      View Article
 
[11]  Krasińska, G., Falandysz, J.. Mercury in Orange Birch Bolete Leccinum versipelle and soil substratum: bioconcentration by mushroom and probable dietary intake by cosumers. Environmental Science and Pollution Research (in press). 2015
In article      PubMed  PubMed
 
[12]  Jonathan, S.G. and Fasidi, I.O. Antimicrobial activities of two Nigeria edible macro-fungi: Lycoperdon pusilum (Bat. Ex) and Lycoperdon giganteum (Pers.), African Journal of Biomedical Research, 2003. 6: 85 – 90
In article      View Article
 
[13]  Garcia, M. A., Alonso, J., Fernandez, M. I., & Melgar, M. J. Lead content in edible wild mushrooms in Northwest Spain as indicator of environmental contamination. Archives Environmental Contaminatian and Toxicology, 1998. 34, 330-335.
In article      View Article  PubMed
 
[14]  Onweremadu, E.U. and Duruigbo, C.I. Assessment of Cd concentration of crude oil polluted arable soil. International Journal of Environmental Science and Technology, 2007. 4(3), 409-412.
In article      View Article
 
[15]  Nwachukwu, A.M., Feng, H., and Achilike, K. Integrated study for automobile wastes management and environmentally friendly mechanic villages in the Imo River Basin, Nigeria. African Journal of Environmental Science and Technology, 2010. 4(4), 234-294.
In article      View Article
 
[16]  Nnorom I. C. , J. E. Alagbaoso U. H. Amaechi, C. Kanu and U. Ewuzie Determination of Beneficial and Toxic Metals in Fresh Palm Oil (Elaeis guineensis Jacq.) from South-Eastern Nigeria: Estimation of Dietary Intake Benefits and Risks. Journal of Scientific Research & Reports. 2014. 3(16): 2216-2226.
In article      View Article  PubMed
 
[17]  Usero, J., E. Gonza-Regalado and I. Gracia, Trace metal in the bivalve molluscs Ruditapes decussates and Ruditapes philippinarum from the Atlantic Coast of Southern Spain. Environ. Int., 1997. 23: 291-298.
In article      View Article
 
[18]  Svoboda L, Zimmermannov´a K, Kalaˇc P. Concentrations of mercury, cadmium, lead, and copper in fruiting bodies of edible mushrooms in an emission area of a copper smelter and a mercury smelter. Sci Total Environ. 2000. 246(1): 61-7.
In article      View Article
 
[19]  US EPA (Environmental Protection Agency). A review of the reference dose and reference concentration processes. Risk Assessment Forum, Washington, DC; EPA/630/P-02/002F, 2002. Available online at https://www.epa.gov/ncea/raf.
In article      View Article
 
[20]  FAO/WHO, Joint Expert Committee on Food Additives, Fifty-ninth meeting, 2002, (2004). p (www.fao.org/es/ESN/Jecfa/59corr.pdf) accessed 20th June, 2017.
In article      View Article
 
[21]  Chien LC, Hung TC, Choang KY, Choang KY, Yeh CY, Meng PJ, Shieh MJ, Han BC Daily intake of TBT, Cu, Zn, Cd and As for fishermen in Taiwan. Sci Total Environ .2002. 285:177-185.
In article      View Article
 
[22]  Bennett DH, Kastenberg WE, McKone TE A multimedia, multiple pathway risk assessment of atrazine: the impact of age differentiated exposure including joint uncertainty and variability. Reliability Eng Sys Saf. 1999. 63:185-198.
In article      View Article
 
[23]  Naughton DP, Petróczi A. Heavy metal ions in wines: meta-analysis of target hazard quotients reveals health risks. Chem Cent J, 2008: 2:22.
In article      View Article  PubMed
 
[24]  Quarcoo A, Adotey G. Determination of heavy metals in Pleurotus ostreatus (Oyster mushroom) and Termitomyces clypeatus (Termite mushroom) sold on selected markets in Accra, Ghana. Mycosph. 2013. 4(5): 960-967.
In article      View Article
 
[25]  Daniel-Umeri R. A., K. Emumejaye and C.K Ojebah. Assessment of Heavy Metals in Some Wild Edible Mushrooms Collected from Ozoro and its Environs, Delta State, Nigeria. International Journal of Science and Technology. 2015. Vol. 5(10): 1-9.
In article      View Article
 
[26]  Udochukwu U, Nekpen B.O, Udinyiwe O.C, Omeje FI. Bioaccumulation of Heavy metals and pollutants by edible mushroom collected from Iselu market Benin-city. Int Jour. Current Microbiol App Sci. 2014. 3(10): 52-7.
In article      View Article
 
[27]  Akyuz M, Kirbag S. Nutritive value of wild edible and cultured mushrooms. Turkish Jour. Bio. 2010. 34: 97-102.
In article      View Article
 
[28]  Gebrelibanos, M Negussie Megersa2 and Abi M. Taddesse3. Levels of essential and non-essential metals in edible mushrooms cultivated in Haramaya, Ethiopia. International Journal of Food Contamination .2016. 3:2. 1-12.
In article      View Article
 
[29]  Huang Q, Y. Jia, Y. Wan, H. Li, and R. Jiang Market Survey and Risk Assessment for Trace Metals in Edible Fungi and the Substrate Role in Accumulation of Heavy Metals. Journal of Food. 2015. Vol. 80(7): 1612-1618.
In article      View Article  PubMed
 
[30]  Zhu F., Li Q, Wenxiu F, Meiying Q, Hailing H, XuejingW. .Assessment of heavy metals in some wild edible mushrooms collected from Yunnan Province, China Environ Monit Assess. 2010. 3 : 1-9.
In article      View Article
 
[31]  Okwulehie IC, Ogoke JABioactive, nutritional and heavy metal constituents of some edible mushrooms found in Abia State of Nigeria. Int J App Microbio Biotech Res.2013. .1:7–15.
In article      View Article
 
[32]  Isıloglu M, Yılmaz F, Merdivan M.. Concentrations of trace elements in wild edible mushrooms. Food Chem. 2001. 73(2): 169-75.
In article      View Article
 
[33]  Nnorom IC, Jarzyñska G, Drewnowska M, Kojta AK, Pankavec S, Falandysz J Trace elements in sclerotium of Pleurotus tuber-regium (Ósu) mushroom-dietary intake and risk in Southeastern Nigeria. J Food Comp Anal. 2013. 29:73-81.
In article      View Article
 
[34]  Silvestre MD, Lagarda MJ, Farra R, Martineze-Costa C, Brines J. Copper, iron and zinc determination in human milk using FAAS with microwave digestion.Food Chem. 2000. 68:95-9.
In article      View Article
 
[35]  Uzun Y, Genccelep H, Kaya A, Akcay ME. The mineral contents of some wild edible mushrooms. Eko. 2011; 20(80): 6-12.
In article      View Article
 
[36]  George P.L, Ranatunga T.D, Reddy S.S, Sharma G.C.. A comparative analysis of mineral elements in the mycelia and the fruiting bodies of Shiitake mushrooms. Am J Food Tech. 2014; 9(7): 360-9.
In article      View Article
 
[37]  Nwoko C.O and L.O Mgbeahuruike Heavy metal Contamination of ready-to-use herbal remedies in South eastern Nigeria. Pakistian Jour. Of Nutrition. (2011). 10 (10): 959-964.
In article      View Article
 
[38]  Nwoko C. O., E. N. Emenyonu and C. E. Umejuru, Trace Metal Contamination of Selected vegetables grown around Owerri Municipality, Nigeria. Journal of Agriculture and Ecology Research International. (2014) 1(1): 18-29.
In article      View Article
 
[39]  Nwoko, C.O and J.K Egunjobi. Lead Contamination of Soil and Vegetation in an abandoned battery factory site in Ibadan, Nigeria. Journal of Sustainable Agriculture and Environment. 2002. Vol. 4(1). 91-96.
In article      
 
[40]  Demirbas A.. Metal ion uptake by mushrooms from natural and artificially enriched soils. Food Chem. 2002. 78: 89-93.
In article      View Article