[1]曲木子,谢会成*,李际红.窄冠黑青杨对重金属复合胁迫的生理响应[J].西北林学院学报,2013,28(05):8-12.[doi:10.3969/j.issn.1001-7461.2013.05.02]
 QU Muzi,XIE Huicheng*,LI Jihong.Physiological and Ecological Response of Narrow Crown Black-Cathay Poplar to Stress of Mixed Heavy Metals[J].JOURNAL OF NORTHWEST FORESTRY UNIVERSITY,2013,28(05):8-12.[doi:10.3969/j.issn.1001-7461.2013.05.02]
点击复制

窄冠黑青杨对重金属复合胁迫的生理响应()
分享到:

《西北林学院学报》[ISSN:1001-7461/CN:61-1202/S]

卷:
第28卷
期数:
2013年05期
页码:
8-12
栏目:
出版日期:
2013-09-09

文章信息/Info

Title:
Physiological and Ecological Response of Narrow Crown Black-Cathay Poplar to Stress of Mixed Heavy Metals
文章编号:
1001-7461(2013)-05-0008-05
作者:
曲木子谢会成*李际红
山东农业大学 林学院,山东 泰安 271018
Author(s):
QU Muzi XIE Huicheng* LI Jihong
College of Forestory, Shandeng Argricudlural Universrty, Taian, Shandong 271018, China
关键词:
窄冠黑青杨 复合胁迫 丙二醛含量 脯氨酸含量 光合活性 根系活力
Keywords:
Narrow Crown Black-Cathay Poplar combined stress malondialdehyde proline content photosynthetic activity root activity
分类号:
S792.113.01
DOI:
10.3969/j.issn.1001-7461.2013.05.02
文献标志码:
A
摘要:
采用盆栽试验方法研究了不同浓度Pb2+、Cd2+、Hg2+复合胁迫下黑青杨的相关生理生化指标的变化。结果表明:随着重金属复合胁迫浓度的增加,黑青杨的根系活力、光合活性各指标呈下降的趋势; 叶片游离脯氨酸含量与丙二醛(MDA)呈逐渐增加趋势; 在较低浓度的Pb2+、Cd2+、Hg2+复合胁迫的处理下,黑青杨根系活力稍有增强,说明低浓度的复合胁迫对其有一定的刺激作用; 随着土壤复合胁迫浓度增加,黑青杨的净光合速率(Pn)、胞间二氧化碳浓度(Ci)、气孔导度(Gs)和蒸腾速率(Tr)逐渐下降,且均在最高处理浓度时达到谷值。研究发现,高浓度的Pb2+、Cd2+、Hg2+复合胁迫所导致的Pn下降是由气孔限制因素所致。本研究能为环境监测中评价土壤重金属污染程度提供参考,同时也为受污染地区绿化树种的选择提供科学的理论依据。
Abstract:
Potted seedlings of Narrow Crown Black-Cathay Poplar were treated by the solutions of mixed heavy metals with different concentrations, including Pb2+, Cd2+, and Hg2+ to explore their influences on the physiological and biochemical indices of the poplar. The results showed that the root activity and photosynthetic activity exhibited decreasing tendency while the changes of praline content and the contents of malondialdehyde(MDA)exhibited increasing tendency with the increase of the heavy metal concentrations. Under the low-concentration combined stress treatment, the root activity increased slightly, indicating the stimulation effect of the combined stress at low concentrations. With the increase of the concentration, the net photosynthetic rate(Pn), intercellular CO2 concentration(Ci), stomatal conductance(Gs)and transpiration rate(Tr)decreased. It was discovered that Pn decline caused by the stress at high concentration was because of stomatal limitation. The results of this research could provide a reference to evaluate the degree of soil heavy metals pollution in environmental monitoring and provide a scientific basis to select the greening tree species in the contaminated areas.

参考文献/References:

[1] 陈怀满.土壤植物系统中的重金属污染[M].北京:科学出版社, 1996:1-14.
[2] 杨世勇,王方,谢建春.重金属对植物的毒害及植物的耐性机制[J].环境科学报,2004(1):71-72. YANG S Y,WANG F,XIE J C.Plant toxicity of heavy metals and the tolerant mechanisms of plants[J].Journal of Environmental Sciences,2004(1):71-72.(in Chinese)
[3] KAMBHAMPATI M S,BEGONIA G B, BEGONIA M F T, et al. Phytoremediaton of a lead-contaminated soil using morning Glory(Pomoeo lacttnoso L.):Effects of a synthetic chelate[J]. Environmental Contamination and Toxicology,2003,71: 379-386.
[4] 王宏镔,束文圣,蓝崇钰.重金属污染生态学研究现状与展望[J].生态学报,2005,25(3):596-605. WANG H B,SHU W S,LAN C Y.Ecology for heavy metal pollution: recent advances and future prospects[J].Acta Ecologica Sinica,2005,25(3):596-605.(in Chinese)
[5] 何振立.污染及有益元素的土壤化学平衡[M].北京:中国环境科学出版社,1998:77-86.
[6] 吴燕玉,余国营,王新.Cd,Pb,Cu,Zn,As复合污染对水稻的影响[J].农业环境保护,1998,17(2):49-54. WU Y Y,YU G Y,WANG X.Compound pollution of Cd, Pb, Cu, Zn and As on lowland rice[J].Agriculture Environmental Protection,1998,17(2):49-54.
[7] JOSEM ARGUELLO,ELIFEREN, MANUEL GONZALEZ-GUERRERO. The structure and function of heavy metal transport P1B-ATPases [J]. Biometals,2007,966:233-248.
[8] 马引利.Cd,Hg对小麦幼苗生长的影响及DNA损伤效应研究[D].西安:陕西师范大学,2001.
[9] ANDERSEN M K,RAULUND-RASMUSSEN K,STROBEL B W,et al.The effects of tree species and site on the solubility of Cd,Cu,Ni,Pb and Zn in soils[J].Water Air & Soil Pollution,2004,154:357-370.
[10] 黄化刚,李廷轩,杨肖娥.植物对铅胁迫的耐性及其解毒机制研究进展[J].应用生态学报,2009,20(3):696-704. HUANG H G,LI T X,YANG X E. Research advances in plant lead tolerance and det -oxification mechani sm[J].Chinese Journal of Applied Ecology,2009,20(3):696-704.(in Chinese)
[11] 朱宇林,曹福亮.Cd、Pb胁迫对银杏光合特性的影响[J].西北林学院学报,2006,21(1): 4750. ZHU Y L,CAO F L.Effects of Cd single and combined stress on chlorophyll content and photosynthetic characteristics of ginkgo[J].Journal of Northwest Forestry University, 2006,21(1): 4750.(in Chinese)
[12] 朱宇林,曹福亮.Cd单一及其与Pb 复合胁迫对银杏叶抗氧化保护酶活性的影响[J].西北林学院学报,2007,22(5):711. ZHU Y L,CAO F L.Effects of Cd single and Pb combined stress on the antioxidant enzymes activities of ginkgo leaves[J]. Journal of Northwest Forestry University, 2007,22(5):711.(in Chinese)
[13] 杨金凤,卜玉山,邓红艳.镉、铅及其复合污染对油菜部分生理指标的影响[J]. 生态学杂志,2009,28(7):1284-1287. YANG J F,BO Y S,DENG H Y. Effects of cadmium, lead, and their combined pollution on some physiological indices of Brassia campestris[J].Chinese Journal of Ecology 2009,28(7): 1284-1287.(in Chinese)
[14] 汤章诚.逆境条件下脯氨酸的积累及意义[J].植物生理学通讯,1984,13(1):15-21. TANG Z C.Proline accumulation and significance of stress conditions[J]. Plant Physiology Journal,1984,13(1):15-21.
[15] 杨金凤,卜玉山,邓红艳.镉、铅及其复合污染对油菜部分生理指标的影响[J]. 生态学杂志,2009,28(7):1284-1287.
[16] 蔡囊.5种阔叶落叶树种对土壤Cu污染的耐性评价研究研究[D].北京:北京林业大学,2009:44.
[17] 杨双春,刘玲,潘一,等. Hg2+、Cd2+胁迫对玉米生理生态的影响[J].辽宁石油化工大学学报,2004(9):36-40. YANG S C,LIU L,PAN Y,et al. physiological and Ecological response of maize to Hg2+and Cd2+Stress[J].Journal of Liaoning University of Petroleum & Chemical Technology,2004(9):3640.
[18] 周希琴,李裕红.木麻黄种子萌发对铬胁迫的生理生态响应[J].中国生态农业学报,2004, 12(1): 53-55. ZHOU X Q,LI Y H. The physiological and ecological responses of the seed germination of Casuarina equisetifolia to chromic stress[J].Journal of Chinese Ecological Agriculture,2004,12(1):53-55.(in Chinese)
[19] 徐勤松,施国新,杜开和.镉胁迫对水车前叶片抗氧化酶系统和亚显微结构的影响[J].农村生态环境,2001,17(2):30 -34.
[20] 李裕红,王荣富,应朝阳.桐花树幼苗根系对镉胁迫的抗氧化生理响应[J].福建农业学报,2007,22(2):193196. LI Y H,WANG R F,YING C Y. Antioxidant physiological responses of Aegiceras corniculatum seedling root system to cadmium stress[J].Fujian Journal of Agricultural Scienc,2007,22(2):193196.(in Chinese)
[21] 杨艳华,陈国祥,刘少华,等.Hg2+胁迫下两优培九和武运粳7号水稻幼苗抗性差异的研究[J].农业生态环境,2003,18(3):34-37.
[22] 周朝彬,胡庭兴,胥晓刚,等.铅胁迫对草木樨叶中叶绿素含量和几种光合特性的影响[J].四川农业大学学报,2005,23(4):432-435. ZHOU C B,HU T X,XU X G,et al.Effect of lead stress on chlorophyll content and photosynthetic characters in leaf of melilotus suavena[J]. Journal of Sichuan Agricultural University,2005,23(4):432-435.(in Chinese)
[23] 王新,梁仁禄,周启星.土壤外源汞污染对大豆幼苗生长的影响研究[J].农业环境保护, 2001,20(2):74-77.
[24] 王林,史衍玺. 镉、铅及其复合污染对萝卜生理生化特性的影响[J]. 中国生态农业学报,2008,16(2):411-414. WANG L,SHI Y X. Effects of cadmium, lead and their compound pollution on physiological and biochemical characteristics of radish[J]. Chinese Journalof Eco-Agriculture.2008,16(2):411-414.(in Chinese)
[25] MEDIAVILLA S,SANTIAGO H,ESCUDERO A.Stomatal and mesophyll limitations to photosynthesis in one ever green and one deciduous mediterranean oak species[J]. Photosynthetica,2002,40:553-559.
[26] FARQUHAR G D,SHARKEYU T D.Stomatal conductance and photosynthesis[J].Ann. Rev. Plant Physiol,1982,33:317-345.
[27] SUN G W,ZHU Z J,FANG X Z.Effect of cadmium on photosynthesis and chlorophyll fluorescence of pakchoi[J].Plant Nutrition and Fertilizer Science,2005,11(5):700-703.
[28] POZEHENRIEDER C,GUNSE B,BARCEL J.Influence of cadmium on water relations, stomatal resistance and abscisic acid content in expanding bean leaves[J].Plant Physiol,1989,90:1365-1371.
[29] 杨华庚,陈慧娟.高温胁迫对蝴蝶兰幼苗叶片形态和生理特性的影响[J].中国农学通报,2009,25(11):123-127.
[30] 李艳丽,李永杰.土壤铅胁迫对旱柳生长及相关生理特性的影响[J].北方园艺,2011(13):168-170.

备注/Memo

备注/Memo:
收稿日期:2012-12-19 修回日期:2013-01-21
基金项目:山东农业大学博士基金; 山东农业大学青年创新基金(23622)。
作者简介:曲木子,男,在读硕士,研究方向:恢复生态学。E-mail:qjyuf02008@163.com *通信作者:谢会成,男,副教授,研究方向:城市林业、污染生态。
更新日期/Last Update: 2013-09-30