|Table of Contents|

Comparision on Accumulation of Heavy Metals in Dominant Arbuscular Mycorrhizal Plants in the Fengfeng Coal Mining Area

《北方园艺》[ISSN:1001-0009/CN:23-1247/S]

Issue:
2020年09
Page:
104-110
Research Field:
Publishing date:

Info

Title:
Comparision on Accumulation of Heavy Metals in Dominant Arbuscular Mycorrhizal Plants in the Fengfeng Coal Mining Area
Author(s):
ZHAO XinWU ZilongSONG GengxinZHANG HaoLI YingJIAO Ziyue
(College of Life Science and Engineering,Handan College/Jinan Taihang Mountain of Wild Plants Resources in Colleges and Universities in Hebei Province Applied Technology Research and Development Center,Handan,Hebei 056005)
Keywords:
coal mining areaarbuscular mycorrhizal fungi (AMF)heavy metal
PACS:
-
DOI:
10.11937/bfyy.20193610
Abstract:
Infection rate of arbuscular mycorrhizal fungi in Setaria viridis and Artemisia scoparia collected from the Fifth,Jiulong and Wutongzhuang of Fengfeng coal mining areas were detected.And the contents of Pb,Cu,Zn,Cr and Mn in plants and soil were studied using flameatomic absorption spectrophotometry,respectively.The absorption and accumulation of two plans with five kinds of heavy metal in the three mining area also were compared by calculating transfer coefficient and enrichment coefficient.In order to provide theoretical support for using plant-arbuscular mycorrhizal fungi to repair soil heavy metal pollution.The results showed that the infection rates of mycorrhiza with S.viridis and A.scoparia were the highest in Wutongzhuang mine,reaching 86.667% and 49.033% respectively.Under natural conditions,they could form a good symbiotic relationship with arbuscular mycorrhizal fungi.The accumulation of Pb and Zn of S.viridis in Wutongzhuang mine were better,the aboveground Pb content,underground Pb content,transfer coefficient and enrichment coefficient of S.viridis were reached 24.157 mg·kg-1,19.139 mg·kg-1,1.262,and 0.156.And Zn content of the aboveground,transfer coefficient and enrichment coefficient were reached 42.295 mg·kg-1,1.127,and 0.259.Not only it was higher than S.viridis in the Fifth and Jiulong mine,but it was also higher than A.scoparia.The accumulation of Cr was higher in both of them than in other mining areas,andthis metricof S.viridis in the same mining area was also higher than that of S.viridis.For the accumulation of Cu and Mn,two kinds of plants in different mining areas showed inconsistent performance,which indicated that the absorption and accumulation of heavy metals by different plants were different.

References:

[1]PEDROSO D F,BARBOSA M V,SANTOS J V,et al.Arbuscular mycorrhizal fungi favor the initial growth of Acacia mangium,Sorghum bicolor,and Urochloa brizantha in soil contaminated with Zn,Cu,Pb,and Cd[J].Bulletin of Environmental Contamination and Toxicology,2018,101(3):386-391.[2]黄明煜,章家恩,全国明,等.土壤重金属的超富集植物研发利用现状及应用入侵植物修复的前景综述[J].生态科学,2018,37(3):194-203.[3]赵仁鑫,郭伟,付瑞英,等.丛枝菌根真菌在不同类型煤矸石山植被恢复中的作用[J].环境科学,2013,34(11):4447-4454.[4]AUDET P,CHAREST C.Dynamics of arbuscular mycorrhizal symbiosis in heavy metal phytoremediation:Meta-analytical and conceptual perspectives[J].Environmental Pollution,2007,147:609-614.[5]LEBEAU T,BRAUD A,JEZEQUEL K.Performance of bioaugmentation-assisted phytoextraction applied to metal contaminated soils:A new[J].Environmental Pollution,2008,153(3):497-522.[6]SMITH S E,READ D J.Mycorrhizal symbiosis[M].Cambridge:Academic Press,2008.[7]REDA E A,RABAB A M.Alleviation of cadmium stress by arbuscular mycorrhizal symbiosis[J].International Journal of Phytoremediation,2019,21:663-671.[8]CABRAL L,SOARES C R,GIACHINI A J,et al.Arbuscular mycorrhizal fungi in phytoremediation of contaminated areas by trace elements:Mechanisms and major benefits of their applications[J].Word Journal of Microbiology & Biotechnology,2015,31(11):1655-1664.[9]曾加会,李元媛,阮迪申,等.植物根际促生菌及丛枝菌根真菌协助植物修复重金属污染土壤的机制[J].微生物学通报,2017,44(5):1214-1221.[10]SALAZAR M J,MENOYO E,FAGGIOLI V,et al.Pb accumulation in spores of arbuscular mycorrhizal fungi[J].Science of the Total Environment,2018,643:238-246.[11]FAGGIOLI V,MENOYO E,GEML J,et al.Soil lead pollution modifies the structure of arbuscular mycorrhizal fungal communities[J].Mycorrhiza,2019,29:363-373.[12]CHEN B,NAYUKI K,KUGA Y,et al.Uptake and intraradical immobilization of cadmium by arbuscular mycorrhizal fungi as revealed by a stable isotope tracer and synchrotron radiation μX-ray fluorescence analysis[J].Microbes Environment,2018,33:257-263.[13]CARNEIRO M A,SIQUEIRA J O,MOREIRA F M.Establishment of herbaceous plants in heavy metal contaminated soils inoculated with arbuscular mycorrhizal fungi[J].Pesquisa Agropecuaria Brasileira,2001,36:1443-1452.[14]CHATURVEDI R,FAVAS P J C,PRATAS J,et al.Effect of Glomus mosseae on accumulation efficiency,hazard index and antioxidant defense mechanisms in tomato under metal (loid) stress[J].International Journal of Phytoremediation,2018,20:885-894.[15]PHILLIPS J M,HAYMAN D S.Improved procedures for clearing and attaining parasitic and vesicular-arbuscular mycorrhizal fungi for rapid assessment of infection[J].Transactions of the British Mycological Society,1970,55:158-161.[16]TROUVELOT A,KOUGH J L,GIANINAZZI-PEARSON V.Mesure du taux de mycorrhization VA d′un systeme radiculaire.Recherche de methods d′estimation ayant une signification fonctionelle[C].Paris,In:Mycorrhizae:Physiology and Genetics Les Mycorrhizaes:Physiologie et Génétique.INRA,1986.[17]李银科,徐祎然,范鹏,等.微波消解火焰原子吸收法测定中草药中痕量铅、铬、镉和镍的研究[J].云南民族大学学报(自然科学版),2010,19(2):116-118.[18]杨剑虹,王成林,代亨林.土壤农化分析与环境监测[M].北京:中国大地出版社,2008.[19]SHARMA P,DUBEY R S.Plumbum toxicity in plants[J].Brazilian Journal of Plant Physiology,2005,17:35-52.[20]高媚娇,金玲,郭晓瑞.土壤中重金属Cu胁迫对植物的危害研究[J].自然科学,2014(2):18-23.[21]颜蒙蒙,王济,胡丰青,等.贵阳郊区菜地土壤重金属Zn、Cd、Pb、Cu污染及潜在生态危害评价[J].四川农业大学学报,2016,34(3):336-341,380.[22]KOV〖AKCˇ〗IK J,BABULA P,HEDBAVNY J,et al.Physiology and methodology of chromium toxicity using alga Scenedesmus quadricauda as model object[J].Chemosphere,2015,120:23-30.[23]畅喜云,范月君,陈志国.重金属Cr6+、Mn2+污染对小麦幼苗生理生化特性及生长的影响研究[J].种子,2012,31(8):39-42,48.[24]RASK K A,JOHANSEN J L,KJΦLLER R,et al.Differences in arbuscular mycorrhizal colonisation influence cadmium uptake in plants[J].Environmental and Experimental Botany,2019,162:223-229.[25]SILVA S,SIQUEIRA J Q,SOARES C R F S.Mycorrhizal fungi influence on brachiaria grass growth and heavy metal extraction in a contaminated soil[J].Pesquisa Agropecuaria Brasileira,2006,41:1749-1757.[26]杜建斌,曾明,谢江辉.杧果VA菌根形态结构观察[J].中国南方果树,2005,34(1):34-35.[27]陈保冬,张莘,伍松林,等.丛枝菌根影响土壤-植物系统中重金属迁移转化和累积过程的机制及其生态应用[J].岩矿测试,2019,38(1):1-25.

Memo

Memo:
-
Last Update: 2020-07-24