Anthropometric Characteristics and Mineral Distribution and Contamination in Artisanal Small-scale Gold Mining Site of Ciguha in Gunung Pongkor, Bogor

Authors

  • Haryoto Kusnoputranto
  • Jonatan Oktoris Simanjuntak
  • Nila Puspita Sari
  • Bambang Wispriyono
  • Abdur Rahman Department of Environmental Health, Faculty of Public Health, Universitas Indonesia

DOI:

https://doi.org/10.24203/ajas.v5i2.4659

Keywords:

Artisanal and small-scale gold mining (ASGM), contamination level, mineral, ciguha

Abstract

Ciguha in Gunung Pongkor, Bogor, had been an artisanal and small-scale gold mining site (ASGM) since 1998 where amalgamations were used intensively leading to pollution in water, soil, and foodstuffs. The present study assessed distribution and contamination level (CL) of minerals in a total of 69 environmental samples consisting of drinking water (n = 12), rice (n = 13), vegetable (n = 15), fruits (n = 5), fish (n = 14), and soil (n = 10). Chromium, iron, and manganese representing trace essential elements but toxic at high level, mercury representing heavy metal, arsenic representing toxic metalloid, and selenium representing essential metalloid which toxic at high level, were analyzed as mineral contaminants. Meanwhile, a total of 101 Ciguha residents consisting of 60 adults, 15 teenagers, and 26 school aged children were involved to charaterize athropometric exposure factors. The results shows that mercury has polluted soil, kangkung, thai squash, cassava leaves, and rice with contamination level (CL) of 604.43, 8.15, 6.01, 4.14, and 2.76 folds, respectively, while chromium has only polluted thai squash with CL of 1.18 folds. Amazingly, mercury distribution was only in the third position after iron and manganese, while the most distributed mineral was iron and the least was selenium. In overall environmental matrices, the detection frequencies of iron, manganese, mercury, chromium, arsenic, and selenium were 94.2, 56.2, 52.2, 47.8, 21.7, and 15.9 %, respectively. In conclusion, mercury was the most critical contaminant in ASGM site of Ciguha that has heavily polluted soil and grown vegetables, but the most distributed mineral was iron. Toxicologically, only mercury and chromium are important while arsenic, iron, manganese, and selenium are of less concern since the CL<1.

References

Antam, Annual Report, 2012: Daya Tahan Finansial Mengatasi Tantangan/Financial Endurance Beyond Challenges, in Reportal, P.T. Aneka Tambang TBK (available at www. antam.com), Jakarta, 2012.

Irawan, I., C.E.F. Mumbunan, and A. Ardianto, Community development in the urban area of a developing country – a case study of the Antam-Pongkor gold mine, Java Island. Indonesia Mining Engineering, 57(2), pp. 37-41, 2005.

Tim Konservasi Pongkor, Laporan Akhir Pendataan Penyebaran Merkuri pada Wilayah Pertambangan di Daerah Pongkor Kabupaten Bogor, Provinsi Jawa Barat, Daftar Isian Pelaksanaan Anggaran (DIPA) No. 0164.0.L/0.20-13.0/XII/2006, Pusat Sumber Daya Geologi, Badan Geologi, Departemen Energi dan Sumber Daya Mineral, Bandung, 2006.

Yasuda, M., et al., Metal Concentrations of River Water and Sediments in West Java, Indonesia. Bulletin of Environmental Contamination and Toxicology, 87(6), pp. 669-73, 2011.

Rahman, A., et al. Health risk estimates from exposure to minerals in artisanal gold mining site in Gunung Pongkor, Bogor, Indonesia. in Full Paper Proceeding of International Trend in Multidisciplinary Academic Research 2014, vol 1, pp 467-490, ISBN 978-969-9948-24-4 (electronic version avaialable at http://www.globalilluminators.org/wp-content/uploads/2014/ 12/ITMAR-14-390.pdf), 2014.

Lwanga, S.K. and S. Lemeshow, Sample size determination in health studies: A practical manual (software version by K C Lun and Peter Chiem, National University of Singapore), World Health Organization, Geneva, 1997.

Foucher, E., Modelling Trace Element Uptake by Plants Grown in Contaminated Soils, (Master of Science Thesis) McGill University, Ottawa, Canada, 2010.

Watanabe, C., et al., Water intake in an Asian population living in arsenic-contaminated area, Toxicology and Applied Pharmacology, 198, pp. 272-282, 2004.

Indonesia, Pedoman Konversi Berat Matang-Mentah, Berat Dapat Dimakan (BDD), dan Resep Makanan Siap Saji dan Jajanan, Badan Penelitian dan Pengembangan Kesehatan, Kementerian Kesehatan RI, Jakarta, 2014.

US-EPA, Seminar Publication: Risk Assessment, Management and Communication of Drinking Water Contamination, Office of Drinking Water, US Environmental Protection Agency, Cincinnati OH, 1990.

IRIS, Arsenic, inorganic (CASRN 7440-38-2) (electronic version available at http://www.epa. gov/iris/subst/0278.htm), Integrated Risk Information System, US Environmental Protection Agency, 1998.

IRIS, Chromium (VI) (CASRN 18540-29-9) (electronic version available at http://www.epa. gov/iris/subst/0144.htm), Integrated Risk Information System, US Environmental Protection Agency, 1998.

PPRTV, Provisional Peer Reviewed Toxicity Values for Superfund, Derivation Support Documents (electronic version available at http://hhpprtv.ornl.gov/quickview/pprtv_papers.php), Integrated Risk Information System, US Environmental Protection Agency, 2014.

IRIS, Manganese (CASRN 7439-96-5) (electronic version available at http://www.epa.gov/ iris/subst/0373.htm), Integrated Risk Information System, US Environmental Protection Agency, 2001.

IRIS, Methylmercury (MeHg) (CASRN 22967-92-6) (electronic version available at http://www. epa.gov/iris/subst/0073.htm), Integrated Risk Information System, US Environmental Protection Agency, 1987.

IRIS, Selenium and Compounds (CASRN 7782-49-2) (electronic article retrieved on 29 June 2015 from http://www.epa.gov/iris/subst/0472.htm), Integrated Risk Information System, US Environmental Protection Agency, 1991.

Ferguson, J.E., The Heavy Elements: Chemistry, Environmental Impact and Health Effect, Oxford, Pergamon Press, 1990.

Soarea, M.E., E. Vieira, and M.d.L. Bastos, Chromium Speciation Analysis in Bread Samples. J. Agric. Food Chem., 58, pp. 1366-1370, 2010.

Hubner, R., K.B. Astin, and R.J.H. Herbert, Comparison of sediment quality guidelines (SQGs) for the assessment of metal contamination in marine and estuarine environments, J. Environ. Monit., 11, pp. 713-722, 2009.

Suhariyono, G. and Y. Menry. Analisis karakteristik unsur-unsur dalam tanah di berbagai lokasi dengan menggunakan XRF, in Prosiding PPI-PDIPTN 2005, Puslitbang Teknologi Maju-BATAN, Yogyakarta, 2005.

Hajeb, P., S. Jinap, and I. Ahmad, Biomagnifications of mercury and methylmercury in tuna and mackerel, J. Environ. Monit. Assess., 171, pp. 205-217, 2010.

US-EPA, Exposure Factors Handbook: 2009 Update. External Review Draft July 2009, EPA/600/R-09/052A, Office of Research and Development, National Center for Environmental Assessment, US Environmental Protection Agency, Washington DC, 2009.

Suryaman, U.S. and A. Rahman, Safe Area for Residential Population to Reside Near Limestone Mining: A Risk Management Approach, J. Ekolog. Kesehatan, 10(4), pp. 256-265, 2011.

Rahman, A., et al., Health risk estimates from exposure to pulp and paper mills contaminants, in Proceeding of the International Federation of International Health 12th World Congress ISBN 978-88-7587-664-7, Medimon S. R. L., Bologna, Italy, 2012.

Rahman, A., et al., Analisis Risiko Kesehatan Lingkungan Pertambangan Kapur di Sukabumi, Cirebon, Tegal, Jepara dan Tulung Agung (Environmental Health Risk Assessment of Limestone Mining in Sukabumi, Cirebon, Tegal, Jepara, and Tulung Agung), J. Ekolog. Kesehatan, 7(1), pp. 665-677, 2008.

Nukman, A., et al., Analisis dan Manajemen Risiko Kesehatan Pencemaran Udara: Studi Kasus di Sembilan Kota Besar Padat Transportasi, J. Ekolog. Kesehatan, 4(2), pp. 270-289, 2005.

Trihono, et al., eds. Buku Survei Konsumsi Makanan Individual dalam Studi Diet Total 2014, Lembaga Penerbitan, Badan Penelitian dan Pengembangan Kesehatan, Kementerian Kesehatan RI, Jakarta, 2014.

WHO, Promoting fruit and vegetable consumption around the world. Global Strategy on Diet, Physical Activity and Health (electronic article retrieved on 3 January 2017 from http://www. who.int/dietphysicalactivity/fruit/en/), 2017.

Department of Ecology State of Washington, Fish Consumption Rates, Technical Support Document: A Review of Data and Information about Fish Consumption in Washington, Version 2.0 Final, ed. P.N. 12-09-058, Toxics Cleanup Program, Washington State Department of Ecology, Olympia WA, 2013.

Ambreen, F., M. Javed, and B. Ummara, Tissue Specific Heavy Metals Uptake in Economically Important Fish Cyprinus carpio at Acute Exposure of Metals Mixtures. Pakistan Journal of Zoology, 47(2), 2015.

Rahman, A., et al., Kandungan logam, metaloida, dan nonlogam dan profil kesehatan masayrakat di wilayah peruntukan pertambangan emas Gunung Pongkor dan wilayah pembanding di Pamijahan, Kapupaten Bogor, Pusat Teknologi Intervensi Kesehatan Masayarakat, Badan Penelitian dan Pengembangan Kesehatan, Kementerian Kesehatan RI (unpublished work), Jakarta, 2013.

Haider, S.Z., et al. in Proceeding of International Conference on Water Hyacinth, United Nation Environment Programme, Nairobi, Kenya, 1984.

Guo, L. and T.J. Cutright, Remediation of acid mine drainage (AMD)-contaminated soil by Phragmites australis and rhizosphere bacteria, Environmental Science and Pollution Research International, 21(12), pp. 7350-60, 2014.

National Academy of Sciences, Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc (electronic version retrieved on 1 September 2015 from http://www.nap.edu/ catalog/10026.htm), 2001.

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Published

2017-04-27

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How to Cite

Anthropometric Characteristics and Mineral Distribution and Contamination in Artisanal Small-scale Gold Mining Site of Ciguha in Gunung Pongkor, Bogor. (2017). Asian Journal of Applied Sciences, 5(2). https://doi.org/10.24203/ajas.v5i2.4659

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