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Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK

Received: 24 October 2016    Accepted: 28 November 2016    Published: 30 December 2016
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Abstract

Soil-plant-animal and soil-animal pathways are the principal routes through which trace element e.g fluorine (F) enters the animal body systems. It is believed that soils and herbage contaminated with such trace elements may, eventually, reflect in the bones and other animal tissues. However, the correlationship between soil F and Bone F among grazing animals has not been substantially, established. This study aimed at investigating the association between F concentration in soil to those found in the bones of sheep and cattle reared in metalliferous mining areas of the United Kingdom. The study area included Derbyshire, a site of fluorite (CaF2) mineralization; Ceredigion and Mendips, sites of mostly galena (PbS) mineralization, the latter two sites used as control sites for this study. The analytical approach involved alkali fusion, perchloric acid digestion and sequential extraction procedures in determining total soil F, total bone F and soil bioavailable F, respectively. The spectrophotometric technique was then used to determine soil F from solution extracts. The results showed mean total soil F concentrations of 302.3 mg/kg, 175.4 mg/kg and 70.8 mg/kg in Derbyshire, Mendips and Ceredigion respectively. The same order was observed for bone F with as high as 218.3 mg/kg, 118.1 mg/kg and 88.9 mg/kg found in Derbsyhire, Mendips and Ceredigion respectively. Analysis of Spearman rank coefficients established that there is a moderate association between soil bioavailable F and bone F (rs=0.571), significant at p < 0.1; a conclusion suggesting possible high risk from F on animals grazing within heavily contaminated areas affected by historical F mining.

Published in Journal of Health and Environmental Research (Volume 2, Issue 5)
DOI 10.11648/j.jher.20160205.11
Page(s) 27-33
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Metalliferous, Contamination, Bioavailable, Ingestion, Association

References
[1] N. D. Grace, P. Loganathan, and M. J. Hedley, “The effect of age on the fluoride concentration in the metacarpus of grazing sheep in New Zealand”, in New Zealand Veterinary Journal, 56 (3), pp. 115-119, 2008.
[2] N. D. Grace, P. Loganathan, and M. J. Hedley, “The effect of a temporal change in ingestion rates of fluorine (F) in soil on the concentration of F in serum and bone of young sheep”, in New Zealand Veterinary Journal, 55 (2), pp. 77-80, 2007.
[3] K. Krishna, and P. K. Govil, “Soil contamination due to heavy metals from an industrial area of Surat, Gujarat, Western India”, in Environment Monitoring Assessment, pp. 124: 263–275, DOI 10.1007/s10661-006-9224-7, 2007.
[4] P. W. Abrahams, and N. B. Blackwell, “The importance of ingested soils in supplying fluorine and lead to sheep grazing contaminated pastures in the Peak District mining area of Derbyshire, UK”, in Environmental Science and Pollution Research, Springer-Verlag, 11356-013-1826-3, 2013.
[5] R. Fuge, “The automated colorimetric determination of fluorine and chlorine in geological samples”, in Chemical Geology, vol.17, pp. 37-43, 1976.
[6] D. T. Waugh, W. Potter, H. Limeback, and M. Godfrey, “Risk Assessment of Fluoride Intake from Tea in the Republic of Ireland and its Implications for Public Health and Water Fluoridation”, in International Journal of Environmental Research and Public Health, 13 (3), pp.259, 2016. Available online, http://doi.org/10.3390/ijerph13030259.
[7] L. Xu, K. Luo, F. Feng, and J. Tan, “Studies on the chemical mobility of fluorine in rocks”, in Research report Fluoride, 39 (2)145, China, 2006.
[8] M. Smith, P. W. Abrahams, M. P. Dagleish and J. Steigmajer, “The intake of lead and associated metals by sheep grazing mining-contaminated floodplain pastures in Mid-Wales, UK: Soil ingestion, soil -metal partitioning and potential availability to pasture herbage and livestock”, in Science of the Total Environment 407 (5), pp. 3731–3739, 2009.
[9] N. D. Grace, P. Loganathan, M. W. Deighton, G. Molano, and M. J. Hedley, “Ingestion of soil fluorine: its impact on the fluorine metabolism of dairy cows”, in New Zealand Journal of Agricultural Research, vol. 48: pp. 23-27, 2005.
[10] C. Zhua, J. Chen, H. Zheng, Y. Wu, and J. W. Xu, “A colorimetric method for fluoride determination in aqueous samples based on the hydroxyl deprotection reaction of a cyanine dye”.
[11] P. Quevauviller, A. Ure, H. Muntau, and B. Griepink, “Improvement of analytical measurements within the BCR-programme: single and sequential extraction procedures applied to soil and sediment analysis”, International Journal of Environmental Analytical Chemistry, vol. 51, pp. 129-134, 1993.
[12] M. Ure, P. Quevauviller, H. Muntau, and B. Griepink, "Speciation of heavy metals in soils and sediments: An account of the improvement and harmonization of extraction techniques undertaken under the auspices of the BCR of the Commission of the European Communities", International Journal of Environmental Analytical Chemistry, Vol. 51, pp. 135-151, 1993.
[13] P. Loganathan, C. W. Gray, M. J. Hedley and H. C. Roberts, “Total and soluble fluorine concentrations in relation to properties of soils in New Zealand”, European Journal of Soil Science, vol.57, pp. 411-421, 2006.
[14] N. L. Blackwell, “The chemical partitioning of fluorine, lead and associated metals in soils of the historic metalliferous mining area of Derbyshire, UK: implications of involuntary soil ingestion to sheep”, A Thesis Submitted in partial fulfilment of the Requirements of Aberystwyth University for the Degree of Master in Environmental Monitoring and Analysis. Aberystwyth University, UK, 2010.
[15] N. A. Geeson, P. W. Abrahams, M. P. Murphy, and I. Thornton, "Fluorine and metal enrichment of soils and pasture herbage in the old mining areas of Derbyshire, UK", Agriculture, Ecosystems and Environment, 68 (3), pp. 217-231, 1998.
[16] B. E. Davies, “Heavy metal contamination from base metal mining and smelting: implications for man and his environment”, Applied Environmental Geochemistry. I. Thornton, London: Academic Press, 1983.
[17] D. Johnston, “A metal mines strategy for Wales”, Environment Agency Wales, United Kingdom, 2004.
[18] [ICRCL] Interdepartmental Committee on the Redevelopment of Contaminated Land, “Notes on the restoration and aftercare of metalliferous mining sites for pasture and grazing”, Guidance Note 70/90, Department of the Environment, 1990.
[19] [ATSDR] Agency for Toxic Substances and Disease Registry. Toxicological profile for Lead, Department of Health and Human Services, Public Health Service, Atlanta, U. S., 2007.
[20] T. A. O' Donnell, “The chemistry of Fluorine”, Inorganic Chemistry, vol. 5, Pergamon Press. 1975.
[21] S. L. Choubisa, V. Modasiya, C. K. Bahura, and Z. Sheikh, “Toxicity of fluoride in cattle of the Indian thar desert, Rajasthan, India”, Research report. Fluoride vol.45 (4), pp.371–376, 2012.
[22] T. B Colman and D. C. Cooper, Exploration for Metalliferous and Related Minerals in Britain: A Guide, 2nd Ed. DTI mineral Program. Publication No. 1, 2000.
[23] Kabata-Pendias and H Pendias, Trace elements in soils and plants. London: CRC Press, 2001.
[24] G. J. Zagury, C. Bedeaux, and B. Welfringer, "Influence of mercury speciation and fractionation on bioaccessibility in soils", Archives of Environmental Contamination and Toxicology, vol.56, pp. 371-379, 2009.
[25] R. Raiswe, J. R. Hawkings, L. G. Benning, A. R. Baker, R. Death, S. Albani, N. Mahowald, M. D. Krom, S. W. Poulton, J. Wadham, and M. Tranter, “Potentially bioavailable iron delivery by iceberg-hosted sediments and atmospheric dust to the polar oceans” Biogeosciences, vol. 13, pp. 3887–3900, doi: 10.5194/bg-13-3887-2016, 2016.
[26] A. K. Tiwari, A. K. Singh and M. K. Mahato, “GIS based evaluation of fluoride contamination and assessment of fluoride exposure dose in groundwater of a district in Uttar Pradesh, India”, Human And Ecological Risk Assessment, vol. 0, No. 0, 1–11, availableonline, http://dx.doi.org/10.1080/10807039.2016.1220824, 2016.
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    Othoo Calvince Ouko, Abrahams William Peter. (2016). Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK. Journal of Health and Environmental Research, 2(5), 27-33. https://doi.org/10.11648/j.jher.20160205.11

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    ACS Style

    Othoo Calvince Ouko; Abrahams William Peter. Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK. J. Health Environ. Res. 2016, 2(5), 27-33. doi: 10.11648/j.jher.20160205.11

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    AMA Style

    Othoo Calvince Ouko, Abrahams William Peter. Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK. J Health Environ Res. 2016;2(5):27-33. doi: 10.11648/j.jher.20160205.11

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  • @article{10.11648/j.jher.20160205.11,
      author = {Othoo Calvince Ouko and Abrahams William Peter},
      title = {Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK},
      journal = {Journal of Health and Environmental Research},
      volume = {2},
      number = {5},
      pages = {27-33},
      doi = {10.11648/j.jher.20160205.11},
      url = {https://doi.org/10.11648/j.jher.20160205.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jher.20160205.11},
      abstract = {Soil-plant-animal and soil-animal pathways are the principal routes through which trace element e.g fluorine (F) enters the animal body systems. It is believed that soils and herbage contaminated with such trace elements may, eventually, reflect in the bones and other animal tissues. However, the correlationship between soil F and Bone F among grazing animals has not been substantially, established. This study aimed at investigating the association between F concentration in soil to those found in the bones of sheep and cattle reared in metalliferous mining areas of the United Kingdom. The study area included Derbyshire, a site of fluorite (CaF2) mineralization; Ceredigion and Mendips, sites of mostly galena (PbS) mineralization, the latter two sites used as control sites for this study. The analytical approach involved alkali fusion, perchloric acid digestion and sequential extraction procedures in determining total soil F, total bone F and soil bioavailable F, respectively. The spectrophotometric technique was then used to determine soil F from solution extracts. The results showed mean total soil F concentrations of 302.3 mg/kg, 175.4 mg/kg and 70.8 mg/kg in Derbyshire, Mendips and Ceredigion respectively. The same order was observed for bone F with as high as 218.3 mg/kg, 118.1 mg/kg and 88.9 mg/kg found in Derbsyhire, Mendips and Ceredigion respectively. Analysis of Spearman rank coefficients established that there is a moderate association between soil bioavailable F and bone F (rs=0.571), significant at p < 0.1; a conclusion suggesting possible high risk from F on animals grazing within heavily contaminated areas affected by historical F mining.},
     year = {2016}
    }
    

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  • TY  - JOUR
    T1  - Importance of Contaminated Soils in Supplying Bioaccessible Fluoride to Grazing Animals From the Historic Metalliferous Mining Areas of the UK
    AU  - Othoo Calvince Ouko
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    Y1  - 2016/12/30
    PY  - 2016
    N1  - https://doi.org/10.11648/j.jher.20160205.11
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    AB  - Soil-plant-animal and soil-animal pathways are the principal routes through which trace element e.g fluorine (F) enters the animal body systems. It is believed that soils and herbage contaminated with such trace elements may, eventually, reflect in the bones and other animal tissues. However, the correlationship between soil F and Bone F among grazing animals has not been substantially, established. This study aimed at investigating the association between F concentration in soil to those found in the bones of sheep and cattle reared in metalliferous mining areas of the United Kingdom. The study area included Derbyshire, a site of fluorite (CaF2) mineralization; Ceredigion and Mendips, sites of mostly galena (PbS) mineralization, the latter two sites used as control sites for this study. The analytical approach involved alkali fusion, perchloric acid digestion and sequential extraction procedures in determining total soil F, total bone F and soil bioavailable F, respectively. The spectrophotometric technique was then used to determine soil F from solution extracts. The results showed mean total soil F concentrations of 302.3 mg/kg, 175.4 mg/kg and 70.8 mg/kg in Derbyshire, Mendips and Ceredigion respectively. The same order was observed for bone F with as high as 218.3 mg/kg, 118.1 mg/kg and 88.9 mg/kg found in Derbsyhire, Mendips and Ceredigion respectively. Analysis of Spearman rank coefficients established that there is a moderate association between soil bioavailable F and bone F (rs=0.571), significant at p < 0.1; a conclusion suggesting possible high risk from F on animals grazing within heavily contaminated areas affected by historical F mining.
    VL  - 2
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Author Information
  • School of Cooperatives and Community Development, Cooperative University of Kenya, Nairobi, Kenya

  • Institute of Geography and Earth Sciences, Aberystwyth University, Wales, UK

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