Journal of Drug Metabolism & Toxicology

Journal of Drug Metabolism & Toxicology
Open Access

ISSN: 2157-7609

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Short Communication - (2021)Volume 12, Issue 3

Implications and Significance of Methyl Mercury Toxicity and Exposure in Rice and Fish

James R. Palmieri*, Tracee Guthrie, Gurleen Kaur, Erin Collins and Brooke Benjamin
 
*Correspondence: Dr. James R. Palmieri, Department of Microbiology and Immunology, Edward College of Osteopathic Medicine, Blacksburg, Virginia, USA, Tel: 540-676-5830, Email:

Author info »

Abstract

Rice and fish are staple food items in many cultures and are particularly vulnerable to the accumulation of heavy metals, specifically mercury, when exposed to agricultural contamination via agricultural soils and water sources. These contaminated foods are then consumed by higher organisms up in the food chain, leading to further accumulation of the mercury, a process known as bio-amplification. Mercury is considered to be the most toxic heavy metal due to the fact that it causes significant systemic toxic effects. This commentary discusses the implications and significance of mercury in rice and fish and illustrates the necessity for further research to demonstrate the importance for public awareness and education for prevention of exposure to mercury via fish and rice ingestion.

Keywords

Bio amplification; Methyl mercury; Toxicity; Neurotoxicity; Breast milk

Description

Mercury (Hg), exists in two forms, organic and inorganic, which when consumed in quantities more than our body can eliminate, the excess is mainly accumulated in the kidney, causing kidney damage and toxicity to surrounding organs and tissues [1]. Due to no established biological function, organic and inorganic forms of mercury are considered systemic toxins since they can cause multiple organ damage [2,3]. The inorganic form of mercury is already found readily within the environment, allowing it to directly enter the crop or organism when mixed with fresh or seawater [4]. When inorganic mercury combines with carbo via microorganisms, methyl mercury (MeHG) is formed; this is then incorporated into the food source of rice and fish.

Once ingested MeHg gets absorbed by the gastrointestinal tract, where most of it binds to either hemoglobin within erythrocytes or to cysteine residues on various proteins to form covalent bonds [5,6]. Once MeHg is bound to cysteine residues, it forms a methylmercury-cysteinyl compound which can cross the blood brain barrier and enter the central nervous system. Within the central nervous system, the methyl mercury becomes demethylated forming inorganic mercury, which accumulates and acts as a neurotoxin disrupting the production of neurotransmitters leading to paresthesia, ataxia, and dysarthria or even death. MeHg acts as a neurotoxin through the disruption of the oxidant/antioxidant balance via inhibition of thioredoxin reductase and glutathione peroxidase, leading to an increase in oxidative stress. The current mainstay of treatment for symptomatic mercury toxicity is chelating agents, plasma exchange, plasmapheresis, and hemodialysis [7].

The neurotoxic effects elicited by MeHG are especially important when concerning developing fetuses and infants, who are more vulnerable to smaller amounts of MeHg due to having underdeveloped metabolic pathways and decreased body weight [8-10]. Due to the widespread and increased use of rice in many commonly consumed items, such as baby food, infants are at an even greater risk for exposure [11].

Other at risk groups include, pregnant women, mothers who breastfeed their neonates and infants, low income populations and cultures which consume rice in large quantities [12-14]. Therefore, when a diet already composed largely of rice is combined with a diet rich in fish, risk for toxic methyl mercury levels is greatly increased, a process known as bio amplification.

When rice and fish are grown in an environment rich in mercury, it increases the exposure and risk of acquisition, furthering the bio amplification. The most prominent atmospheric source of industrial mercury (Hg) emissions is artisanal mining and smelting Hg emissions [15].The increased amounts of methyl mercury in rice come from sources such as mining that are done in nearby rice fields and from the farming practices that are implemented [16]. Inorganic mercury (IHg) released by industrial emissions is absorbed into the pore water of rice paddies. Anaerobic mercury-ethylating bacteria that reside in the soil of rice paddies methylate dissolved IHg into MeHg. MeHg is taken up and trapped by the roots of the rice plant [17]. The roots become a major bio accumulator for MeHg, not IHg [18]. When the farming fields or mining facility is near a water source runoff can occur leading to increased levels of inorganic mercury in the water, which is then transformed into methyl mercury by microorganisms [19].

The methyl mercury is then consumed by small aquatic organisms, such as fish [19].There is a lack of data on the recommended provisional tolerable weekly intake, PWTI, of mercury supplied by the FDA, thus it is difficult to educate and inform the at-risk populations on the tolerable mercury consumption levels [20].

Conclusion

More research is needed on Hg content in commercially available rice and rice-based foods, so that the FDA can monitor MeHg content and advise the aforementioned vulnerable populations accordingly, as is done with Hg content in fish. Additionally, there needs to be increased public education and regulations on mercury in rice and fish-based products in order to improve consumer knowledge regarding mercury presence in rice, breast milk, rice-based and fish-based products in order to mitigate the amount of exposure.

References

  1. Park JD, Zheng W. Human Exposure and Health Effects of Inorganic and Elemental Mercury. J Prev Med Public Health. 2012;45(6): 344-352.
  2. Zeng F, Wei W, Li M, Huang R, Yang F, Daun Y. Heavy Metal Contamination in Rice-Producing Soils of Hunan Province, China and Potential Health Risks. Int J Environ Res Public Health. 2015;12(12): 15584-15593.
  3. Palmieri JR, Guthrie T, Kaur G, Collins E, Benjamin B, Brunette J, et al. Research Article: Implications and Significance of Mercury in Rice. Nutr Metab. 2020;3(2): 1-5.
  4. Diez S. Human Health Effects of Methylmercury Exposure. Rev Environ Contam Toxicol. 198: 111-132.
  5. Jan AT, Azam M, Siddiqui K, Ali A, Choi I, Mohd Q, et al. Heavy Metals and Human Health: Mechanistic Insight into Toxicity and Counter Defense System of Antioxidants. Int J Mol Sci. 2015;16(12): 29592-29630.
  6. Bernhoft RA. Mercury toxicity and treatment: a review of the literature. J Environ Public Health. 2012;2012: 460508.
  7. Ye BJ, Kim BG, Jeon MJ, Kim SY, Kim HC, Jang TW, et al. Evaluation of mercury exposure level, clinical diagnosis and treatment for mercury intoxication. Ann Occup Environ Med. 2016;28(1): 1-8.
  8. Choi AL, Grandjean P. Methylmercury exposure and health effects in humans. Environment Chem. 2008;5: 112-120.
  9. Rothenberg SE, Myers LW, Creswell JE. Rice methylmercury exposure and mitigation: a comprehensive review. Environ Res. 2014;133: 407-423.
  10. Zhang H, Feng X, Larssen T, Qiu G, Vogt RD. In inland China, rice, rather than fish, is the major pathway for methylmercury exposure. Environ Health Perspect. 2010;118(9): 1183-1188.
  11. Brombach CC, Manorut P, Dona PPPK, Ezzeldin MF, Chen B, chorns WT, et al. Methylmercury varies more than one order of magnitude in commercial European rice. Food Chem. 2016;214(5): 360-365.
  12. Bradley MA, Barst BD, Basu N. A review of mercury bioavailability in humans and fish. Int J Environ Res Public Health. 2017;14(2): 169.
  13. Clarkson TW, Vyas JB, Ballatori N. Mechanisms of mercury disposition in the body. Am J Ind Med. 2007;50(10):757-764.
  14. Bo M, Feng X, Qiu G, Liang P, Li P, Chen C, et al. The process of methylmercury accumulation in rice (Oryza sativa L.). Environ Sci Technol. 2011;45(7): 2711-2717.
  15. Li R, Wu H, Ding J, Fu W, Gan L. Mercury pollution in vegetables, grains and soils from areas surrounding coal-fired power plants. Scientific reports. 2017;7(3): 46545.
  16. Rothenberg SE, Myers LW, Creswell JE. Rice methylmercury exposure and mitigation: a comprehensive review. Environ Res. 2014;133: 407-423.
  17. Zhang H, Feng X, Larssen T, Shang L, Li P. Bioaccumulation of methylmercury versus inorganic mercury in rice (Oryza sativa L.) grain. Environ Sci Technol. 2010;44(12): 4499-4504.
  18. Palmieri JR, Council-Troche M, Fraim J, McCabe A, Rzigalinski BA. Chronic Methyl Mercury Toxicity in a 72 Year-Old Athletic Male from Southwestern Virginia. J Clin Toxicol. 2020;10(6): 454.
  19. Joint FAO. Seventy-second meeting, Rome, 16-25 February 2010: summary and conclusions. Rome: Joint FAO/WHO Expert Committee on Food Additives, 16 p. JECFA/72/SC.

Author Info

James R. Palmieri*, Tracee Guthrie, Gurleen Kaur, Erin Collins and Brooke Benjamin
 
Department of Microbiology and Immunology, Edward College of Osteopathic Medicine, Blacksburg, Virginia, USA
 

Citation: Palmieri JR, Guthrie T, Kaur G, Collins E, Benjamin B (2021) Implications and Significance of Methyl mercury Toxicity and Exposure in Rice and Fish. J Drug Metab Toxicol. 12:258.

Received: 02-Jul-2021 Accepted: 16-Jul-2021 Published: 23-Jul-2021 , DOI: 10.35248/2157-7609.21.12.258

Copyright: © 2021 Palmieri JR, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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