为了防止重金属毒害的发生和在环境监测中对重金属的评价,以小麦为试验对象,采用室内培养方法,研究了不同浓度镉胁迫对小麦种子萌发和幼苗生长、丙二醛及抗氧化酶系统的影响,结果表明,较低浓度镉胁迫对种子发芽率、发芽势、芽生长的抑制效应较小。随着镉胁迫浓度的提高,发芽指数、活力指数及根生长明显受抑制,且镉胁迫浓度越大,抑制作用越大。随着镉浓度的增加,幼苗根、芽中的MDA含量、G-POD明显增加,SOD活性呈现先增加后降低的趋势,其中根的SOD活性在1000μmol/L Cd胁迫下略低于对照,而CAT、APX活性总体呈下降趋势,且浓度越高下降幅度越大,表明遭受了氧化胁迫和膜脂过氧化损伤,这可能是镉胁迫下小麦幼苗根生长受阻的重要原因。
关键词:
镉; 小麦; 萌发; 幼苗生长; 抗氧化酶
Cadmium (Cd)was a highly toxic and persistent environmental poison,its increasing level in soil environment exerted a wild range of adverse effects on plants and even the healthy of human beings by food chains.In the study,the effects of Cd at different concentrations on wheat seeds germination,seedlings growth and the activities of antioxidant enzymes were studied.The results showed the germination percentage,germination potential and shoot growth were not significantly inhibited by cadmium,especially at low Cd concentrations.However,germination index,vigor index,root growth were restrained evidently with the increase of Cd stress.The content of MDA and activities of G-POD in root and shoot increased significantly with the increasing of Cd concentration.The activities of SOD first increased and then decreased as the Cd concentration increased and it was slight lower than that of control in root under 1000μmol/ L Cd stress.However,the activities of CAT and APX were decreased with concentration-dependent manner,ie,the higher concentration of cadmium,the greater changes the enzyme activities,suggesting oxidative damage and membrane lipid peroxidation occurred in seedlings,and it might be the important reason for the growth inhibition of roots subjected to cadmium stress.
[1] 顾继光,林秋奇,胡韧,等.土壤-植物系统中重金属污染的治理途径及其研究展望[J].土壤通报,2005,36 (1):128-133.
[2] 王树会,黄成江.烤烟对不同土壤类型中的镉的吸收及其分配[J].内蒙古农业科技,2008(3):40-42,108.
[3] Wang K R.Tolerance of cultivated plants to cadmium and their utilization in polluted farmland soils[J].Acta Biotechnologica,2002,21:189-198.
[4] He J Y,Zhu C,Ren Y F,et al.Genotypic variation in grain cadmium concentration of lowland rice[J].J Plant Nutri Soil Sci,2006,169:711-716.
[5] 张磊,于燕玲,张磊.外源镉胁迫对玉米幼苗光合特性的影响[J].华北农学报,2008,23(1):101-104.
[6] Hall J L.Cellular mechanisms for heavy metal detoxification and tolerance[J].J Exp Bot,2002,53(366):1-11.
[7] 郑世英,王丽燕,张海英.镉胁迫对两个大豆品种抗氧化酶活性及丙二醛含量的影响[J].江苏农业科学,2007,34(5):53-55.
[8] 何俊瑜,任艳芳.镉胁迫对水稻种子萌发、幼苗生长和淀粉酶活性的影响[J].华北农学报,2008,23(增刊):131-134.
[9] 任安芝,高玉葆.铅、镉、铬单一和复合污染对青菜种子萌发的生物学效应[J].生态学杂志,2000,19(1):19-22.
[10] 宋玉芳,许华夏,任丽萍,等.土壤重金属对白菜种子发芽与根伸长抑制的生态毒性效应[J].环境科学,2002,23(1):103-107.
[11] 张志良,瞿伟.植物生理学实验指导[M].北京:高等教育出版社,2003.
[12] Klapheck S,Zimmer I,Cossse H.Scavenging peroxide in the endosperm of Ricinus communis peroxidase[J].Plant Cell Physiol,1990,31:1005-1013.
[13] Nakano Y,Asada K.Hydrogen peroxide is scavenged by ascorbate-specific peroxidase in spinach chloroplasts[J].Plant Cell Physiol,1981,22:867-880.
[14] Aebi H.Catalase in vitro[J].Method Enzymol,1984,105:121-126.
[15] 黄玉山,罗广华.Cd诱导植物的自由基过氧化损伤[J].植物学报,1997,39(6):522-526.
[16] 张春荣,李红,夏立江,等.镉、锌对紫花苜蓿种子萌发及幼苗的影响[J].华北农学报,2005,20(1):96-99.
[17] 何俊瑜,任艳芳,朱诚,等.镉胁迫对不同水稻品种种子萌发、幼苗生长和淀粉酶活性的影响[J].中国水稻科学,2008,22(4):409-414.
[18] Eun S,Young H S,Lee Y.Cadmium disturbs microtubule organization in the root meristem of Zea mays[J].Physiol Plantarum,2000,110:357-365.
[19] Mikami B,Adachi M,Kage T,et al.Structure of raw starch-digesting Bacillus cereus beta-amylase complexed with maltose[J].Biochemistry,1999,38(22):7050-7061.
[20] 罗立新,孙铁珩,靳月华.镉胁迫下小麦叶中超氧阴离子自由基的积累[J].环境科学学报,1998,18(5):495-499.
[21] Shah K,Kumar R G,Verma A,et al.Effect of cadmium on lipid peroxidation,superoxide anion generation and activities of antioxidant enzymes in growing rice seedlings[J].Plant Science,2001,161:1135-1144.
[22] 吴旭红.三个苜蓿品种对镉污染的生理生态反应及抗性比较[J].生态环境,2005,14(5):658-661.
[23] 李元,王焕校,吴玉树.Cd、Fe 及其复合污染对烟草叶片几项生理指标的影响[J].生态学报,1992,12(2):147-154.