Phytoremediation of Mine Tailings Using Lolium Multiflorum
详细信息 查看官网全文
- 英文论文题名：Phytoremediation of Mine Tailings Using Lolium Multiflorum
- 论文作者：Violeta Mugica-Alvarez ; Verónica Cortés-Jiménez ; Mabel Vaca-Mier ; Victor Domínguez-Soria
- 英文论文作者：Violeta Mugica-Alvarez ; Verónica Cortés-Jiménez ; Mabel Vaca-Mier ; Victor Domínguez-Soria ; Department of Basic Sciences ; Universidad Autónoma Metropolitana-Azcapotzalco ; Universidad Autónoma Metropolitana-Azcapotzalco ; Department of Energy ; Universidad Autónoma Metropolitana-Azcapotzalco
- 年：2015
- 作者机构：Department of Basic Sciences,Universidad Autónoma Metropolitana-Azcapotzalco;Universidad Autónoma Metropolitana-Azcapotzalco;Department of Energy,Universidad Autónoma Metropolitana-Azcapotzalco;
- 英文论文关键词：La Concha ; México ; phytoremediation ; ryegrass ; heavy metals
- 会议召开时间：2015-04-01
- 会议录名称：International Journal of Environmental Science and Development Vol.6 No.4
- 语种：英文
- 分类号：X173;X751
- 学会代码：CDYA
- 学会名称：成都亚昂教育咨询有限公司
- 页数：6
- 文件大小：1190k
- 原文格式：D
摘要
In this research we studied the feasibility of applying phytoremediation in the mine tailings at La Concha site. The extraction efficiency of heavy metals was studied, as well as the tolerance to high pollution and biomass generation of Lolium multiflorum, known as Italian ryegrass, in the aggressive soils composed almost entirely by mine wastes. Ryegrass seeds were grown in mine tailings containing Cu, Mn, Zn, and Pb concentrations of around 800, 4600, 3200, and 5400 ppm respectively. Triplicate analyses of soils without treatment and with treatments consisting in organic matter(OM) additions were carried out during 90 days. Italian ryegrass has a high tolerance to polluted mine tailings, although the addition of small quantities of organic matter improves the extraction of metals. The highest metals uptake from tailings was achieved through treatment with 20 % OM additions, with varying efficiencies of around 50% for Zn and Pb in 90 days, although for Cu and Mn these were smaller, namely of 28 and 14% respectively. These results show that phytoremediation of mine tailings is possible through grass planting that was able to remove the heavy metals.
In this research we studied the feasibility of applying phytoremediation in the mine tailings at La Concha site. The extraction efficiency of heavy metals was studied, as well as the tolerance to high pollution and biomass generation of Lolium multiflorum, known as Italian ryegrass, in the aggressive soils composed almost entirely by mine wastes. Ryegrass seeds were grown in mine tailings containing Cu, Mn, Zn, and Pb concentrations of around 800, 4600, 3200, and 5400 ppm respectively. Triplicate analyses of soils without treatment and with treatments consisting in organic matter(OM) additions were carried out during 90 days. Italian ryegrass has a high tolerance to polluted mine tailings, although the addition of small quantities of organic matter improves the extraction of metals. The highest metals uptake from tailings was achieved through treatment with 20 % OM additions, with varying efficiencies of around 50% for Zn and Pb in 90 days, although for Cu and Mn these were smaller, namely of 28 and 14% respectively. These results show that phytoremediation of mine tailings is possible through grass planting that was able to remove the heavy metals.
In this research we studied the feasibility of applying phytoremediation in the mine tailings at La Concha site. The extraction efficiency of heavy metals was studied, as well as the tolerance to high pollution and biomass generation of Lolium multiflorum, known as Italian ryegrass, in the aggressive soils composed almost entirely by mine wastes. Ryegrass seeds were grown in mine tailings containing Cu, Mn, Zn, and Pb concentrations of around 800, 4600, 3200, and 5400 ppm respectively. Triplicate analyses of soils without treatment and with treatments consisting in organic matter(OM) additions were carried out during 90 days. Italian ryegrass has a high tolerance to polluted mine tailings, although the addition of small quantities of organic matter improves the extraction of metals. The highest metals uptake from tailings was achieved through treatment with 20 % OM additions, with varying efficiencies of around 50% for Zn and Pb in 90 days, although for Cu and Mn these were smaller, namely of 28 and 14% respectively. These results show that phytoremediation of mine tailings is possible through grass planting that was able to remove the heavy metals.
引文
[1]Economy Secretariat 2013.Statistics of Mining Sector.[Online].Available:http://www.economia.gob.mx/comunidadnegocios/mineria/estadisticas-y-estudios-del-sector
[2]M.H.Wong,“Ecological restoration of mine degraded soils,with emphasis on metal contaminated soils,”Chemosphere,vol.50,pp.775-780,2003.
[3]K.P.Prabha and L.Y.Li,“Phytoremediation technology:Hyperaccumulation metals in plants,”Water and Air Soil Pollution,vol.184no.1,pp.105-126,2007.
[4]O.T.Mendoza,M.Yta,R.M.Tovar,A.D.Almazán,N.F.Mundo,and C.D.Gutiérrez,“Mineralogy and geochemistry of sulfide-bearing tailings from silver mines in Taxco,México area to evaluate their potential environmental impact,”Geofisica Internacional,vol.44,pp.49-64,2005.
[5]D.Mains,D.Craw,and C.G.Rufaut,“Phytostabilization of gold mine tailings,New Zealand.Part 1:Plant establishment in alkaline saline substrate,”International Journal of Phytoremediation,vol.8,pp.131-147,2006.
[6]G.Sarret,J.Vangronsveld,A.Manceau,M.Musso,J.D?Haen,J.J.Mentones,and J.L.Hazemann,“Accumulation forms of Zn and Pb in Phaseolus vulgaris in the presence and absence of EDTA,”Environmental Science&Technology,vol.35,no.13,pp.2854-2859,2001.
[7]U.Kukier and R.L.Chaney,“In situ remediation of nickel phytotoxicity for different plant species,”Journal of Plant Nutrition,vol.27,pp.465-495,2004.
[8]J.Yoon,X.Cao,Q.Zhou,and L.Q.Ma,“Accumulation of Pb,Cu,and Zn in native plants growing on contaminate Florida site,”Science of the Total Environmental,vol.368,pp.456-464,2006.
[9]O.Barrutia,U.Artetxw,A.Hernandez,J.M.Olano,J.I.GarcíaPlazaola,C.Garbisu,and J.M.Becerril,“Native plant communities in an Abandoned Pb-Zn miningárea of northern spain:Implications for phytoremediation and germplasm preservation,”International Journal of Phytoremediation,vol.13,pp.256-270,2011.
[10]Y.G.Liu,H.Z.Zhang,G.M.Zeng,B.R.Huang,and X.Li,“Heavy metal accumulation in plants on Mn mine tailings,”Pedosphere,vol.16,pp.131-136,2006.
[11]Y.Chen,Z.Shen,and X.Li,“The use of vetiver grass,Vetiveria zizanioides in the phytoremediation of soils contaminated with heavy metals,”Applied Geochemistry,vol.19,no.10,pp.1553-1565,2004.
[12]N.Merkl,R.Schultze-Kraft,and C.Infante,“Assessment of tropical grasses and legumes for phytoremediation of petroleum-contaminated soils,”Water,Air,and Soil Pollution,vol.165,no.1-4,pp.195-209,2005.
[13]G.Garc?a,A.Faz,and M.Cunha,“Performance of Piptatherum miliaceum,(Smilo grass)in edaphic Pb and Zn phytoremediation over a short growth period,International Biodeterioration&Biodegradation,vol.54,no.2,pp.245-250,2004.
[14]L.Zhang,H.X.Li,W.F.Ma,and X.H.Zhao,“Phytoremediation of complex contaminations in dredged sewage river sediment by Lolium multiflorum Lam,”Journal of Agro-Environment Science,vol.25,no.1,pp.107-112,2006.
[15]D.L.Johnson,D.R.Anderson,and S.P.Mc Grath,“Soil microbial response during the phytoremediation of a PAH contaminated soil,”Soil Biology and Biochemistry,vol.37,no.12,pp.2334-2336,2005.
[16]E.V.Cortés-Jiménez,V.Mugica-álvarez,M.C.A.GonzálezChávez,R.Carrillo-González,M.Martínez Gordillo,and M.Vaca Mier,“Natural revegetation of alkaline tailing heaps at Taxco,Guerrero,México,”International Journal of Phytoremediation,vol.15,no.2,pp.127-141,2012.
[17]D.J.Rowell,Soil Science:Methods and Applications,2nd ed.Longman,Essex,England,1996.
[18]D.W.Nelson and L.E.Sommers,“Total carbon,organic matter,”in Methods of Soil Analysis,Part 2,Agronomy 9,A.L.Page et al.,Eds.American Society of Agronomy,Madison,1982,pp.539-279.
[19]S.R.Olsen and L.A.Dean,“Phosphurus,”in Methods of Soil Analysis,Part 2,Agronomy 9,C.A.Black Ed.American Society of Agronomy,Madison,Wisconsin,1965,pp.1035-1049.
[20]M.Islam and N.Bhuiyan,“Evaluation of various extractants for available sulfur in wetland rice(Oryza sativa)soils of Bangladesh,”Indian Journal of Agriculture Science,vol.58,pp.603-606,1998.
[21]EPA(Environmental Protection Agency)Acid Digestion of Sediments,Sludge,and Soils,Método 3050A,1992.
[22]W.L.Lindsay and W.A.Norvell,“Development of a DTPA soil zinc,iron,manganese and copper,”Soil Science Society of America Journal,vol.42,pp.421-428,1978.
[23]S.P.Mc Grath and F.J.Zhao,?Phytoextraction of metals and metalloids from contaminatedsoils,”Curr.Opin.Biotechnol,vol.14,pp.277-282,2003.
[2]M.H.Wong,“Ecological restoration of mine degraded soils,with emphasis on metal contaminated soils,”Chemosphere,vol.50,pp.775-780,2003.
[3]K.P.Prabha and L.Y.Li,“Phytoremediation technology:Hyperaccumulation metals in plants,”Water and Air Soil Pollution,vol.184no.1,pp.105-126,2007.
[4]O.T.Mendoza,M.Yta,R.M.Tovar,A.D.Almazán,N.F.Mundo,and C.D.Gutiérrez,“Mineralogy and geochemistry of sulfide-bearing tailings from silver mines in Taxco,México area to evaluate their potential environmental impact,”Geofisica Internacional,vol.44,pp.49-64,2005.
[5]D.Mains,D.Craw,and C.G.Rufaut,“Phytostabilization of gold mine tailings,New Zealand.Part 1:Plant establishment in alkaline saline substrate,”International Journal of Phytoremediation,vol.8,pp.131-147,2006.
[6]G.Sarret,J.Vangronsveld,A.Manceau,M.Musso,J.D?Haen,J.J.Mentones,and J.L.Hazemann,“Accumulation forms of Zn and Pb in Phaseolus vulgaris in the presence and absence of EDTA,”Environmental Science&Technology,vol.35,no.13,pp.2854-2859,2001.
[7]U.Kukier and R.L.Chaney,“In situ remediation of nickel phytotoxicity for different plant species,”Journal of Plant Nutrition,vol.27,pp.465-495,2004.
[8]J.Yoon,X.Cao,Q.Zhou,and L.Q.Ma,“Accumulation of Pb,Cu,and Zn in native plants growing on contaminate Florida site,”Science of the Total Environmental,vol.368,pp.456-464,2006.
[9]O.Barrutia,U.Artetxw,A.Hernandez,J.M.Olano,J.I.GarcíaPlazaola,C.Garbisu,and J.M.Becerril,“Native plant communities in an Abandoned Pb-Zn miningárea of northern spain:Implications for phytoremediation and germplasm preservation,”International Journal of Phytoremediation,vol.13,pp.256-270,2011.
[10]Y.G.Liu,H.Z.Zhang,G.M.Zeng,B.R.Huang,and X.Li,“Heavy metal accumulation in plants on Mn mine tailings,”Pedosphere,vol.16,pp.131-136,2006.
[11]Y.Chen,Z.Shen,and X.Li,“The use of vetiver grass,Vetiveria zizanioides in the phytoremediation of soils contaminated with heavy metals,”Applied Geochemistry,vol.19,no.10,pp.1553-1565,2004.
[12]N.Merkl,R.Schultze-Kraft,and C.Infante,“Assessment of tropical grasses and legumes for phytoremediation of petroleum-contaminated soils,”Water,Air,and Soil Pollution,vol.165,no.1-4,pp.195-209,2005.
[13]G.Garc?a,A.Faz,and M.Cunha,“Performance of Piptatherum miliaceum,(Smilo grass)in edaphic Pb and Zn phytoremediation over a short growth period,International Biodeterioration&Biodegradation,vol.54,no.2,pp.245-250,2004.
[14]L.Zhang,H.X.Li,W.F.Ma,and X.H.Zhao,“Phytoremediation of complex contaminations in dredged sewage river sediment by Lolium multiflorum Lam,”Journal of Agro-Environment Science,vol.25,no.1,pp.107-112,2006.
[15]D.L.Johnson,D.R.Anderson,and S.P.Mc Grath,“Soil microbial response during the phytoremediation of a PAH contaminated soil,”Soil Biology and Biochemistry,vol.37,no.12,pp.2334-2336,2005.
[16]E.V.Cortés-Jiménez,V.Mugica-álvarez,M.C.A.GonzálezChávez,R.Carrillo-González,M.Martínez Gordillo,and M.Vaca Mier,“Natural revegetation of alkaline tailing heaps at Taxco,Guerrero,México,”International Journal of Phytoremediation,vol.15,no.2,pp.127-141,2012.
[17]D.J.Rowell,Soil Science:Methods and Applications,2nd ed.Longman,Essex,England,1996.
[18]D.W.Nelson and L.E.Sommers,“Total carbon,organic matter,”in Methods of Soil Analysis,Part 2,Agronomy 9,A.L.Page et al.,Eds.American Society of Agronomy,Madison,1982,pp.539-279.
[19]S.R.Olsen and L.A.Dean,“Phosphurus,”in Methods of Soil Analysis,Part 2,Agronomy 9,C.A.Black Ed.American Society of Agronomy,Madison,Wisconsin,1965,pp.1035-1049.
[20]M.Islam and N.Bhuiyan,“Evaluation of various extractants for available sulfur in wetland rice(Oryza sativa)soils of Bangladesh,”Indian Journal of Agriculture Science,vol.58,pp.603-606,1998.
[21]EPA(Environmental Protection Agency)Acid Digestion of Sediments,Sludge,and Soils,Método 3050A,1992.
[22]W.L.Lindsay and W.A.Norvell,“Development of a DTPA soil zinc,iron,manganese and copper,”Soil Science Society of America Journal,vol.42,pp.421-428,1978.
[23]S.P.Mc Grath and F.J.Zhao,?Phytoextraction of metals and metalloids from contaminatedsoils,”Curr.Opin.Biotechnol,vol.14,pp.277-282,2003.