通过水培试验,研究比较了不同浓度(10~60 mg/L)的Cr3+、Cr6+胁迫对茶树叶片一些生理生化指标的影响。结果表明:随Cr3+、Cr6+胁迫浓度的增加,茶树受害程度加深,中毒症状明显;叶绿素含量以及叶绿素a/b比值极显著降低,并对净光合速率、胞间CO2浓度、蒸腾速率及气孔导度产生显著负面影响。Cr3+胁迫下,SOD、POD、CAT活性随Cr3+浓度增加呈先升高后降低趋势;而Cr6+胁迫下,SOD、POD活性也出现先升后降趋势,但CAT活性则持续下降。丙二醛含量、细胞膜透性和脯氨酸含量也随Cr3+、Cr6+浓度增加显著增加,表明Cr3+、Cr6+胁迫对茶树细胞质膜系统及主要细胞器的结构与功能都具有较强的破坏作用,Cr6+的毒害作用强于Cr3+。
The toxic effects of different concentrations of Cr3+ and Cr6+ on the physiological and biochemical characteristics of tea plant were studied in Hoagland solution culture. The results indicated that: with the increasing of Cr3+, Cr6+ concentrations, the symptoms of tea plant became obviously; the contents of chlorophyll and the ratio of chlorophyll a and chlorophyll b reduced obviously, and there were obviously negative effects to net photosynthesis rate, intercellular CO2 concentration, transpiration rate and stoma conductivity. Under the Cr3+ stress, the activities of SOD, POD and CAT increased at first and then decreased, under the Cr6+ stress, the activities of SOD and POD increased at first and then decreased too, but the activity of CAT decreased all the time. At the same time, the contents of MDA and proline (Pro), cytomembrane permeability increased obviously with the increasing of Cr3+, Cr6+ concentrations. Therefore, it highlighted that the Cr3+ and Cr6+ stresses could mangle the cytomembrane system, the structures and functions of the major organelles of tea plant, and the toxic effects of Cr6+ on tea plant was stronger than that of Cr3+.
[1] 顾公望, 张宏伟. 微量元素与恶性肿瘤[M]. 上海: 上海科学技术出版社, 1993: 56~567.
[2] 张义贤. 三价铬和六价铬对大麦的毒害效应的研究[J]. 中国环境科学, 1997, 17(6): 555~568.
[3] 周希琴, 吉前华. 铬胁迫下不同品种玉米种子和幼苗的反应及其与铬积累的关系[J]. 生态学杂志, 2005, 24(9): 1048~1052.
[4] 周红卫, 施国新, 徐勤松, 等. Cr6+和Cr3+对水花生几种生理生化指标的影响比较[J]. 农村生态环境, 2002, 18(4): 35~40.
[5] 胡韧, 林秋奇, 张小兰. Cr3+, Cr6+及其复合污染对狐尾藻的毒害作用[J]. 生态科学, 2003, 22(4): 327~331.
[6] 马广岳, 施国新, 徐勤松, 等. Cr6+,Cr3+胁迫对黑藻生理生化影响的比较研究[J]. 广西植物, 2004, 24(2): 161~165.
[7] 童启庆. 茶树栽培学[M]. 北京: 中国农业出版社, 2000.
[8] 徐华. 混合液法测定茶树叶片叶绿素含量[J]. 龙岩师专学报(自然科学版), 1995, 13(3): 94~95.
[9] 熊庆娥. 植物生理学实验教程[M]. 成都: 四川科学技术出版社, 2003.
[10] 王晶英. 植物生理生化实验技术与原理[M]. 哈尔滨: 东北林业大学出版社, 2003: 82~83.
[11] 赵世杰, 许长成, 邹琦, 等. 植物组织中丙二醛测定方法的改进[J]. 植物生理学通讯, 1994, 26(4): 62~65.
[12] 朱广廉, 邓兴旺, 左广能. 植物体内游离脯氨酸的测定[J]. 植物生理学通讯, 1983, 19(1): 35~37.
[13] 周启星. 复合污染生态学[M]. 北京: 中国环境科学出版社, 1995, 162~178 .
[14] 郑爱珍. 重金属Cr6+污染对辣椒幼苗生理生化特性的影响[J].农业环境科学学报,2007,26(4):1343~1346
[15] 徐勤松, 施国新, 杜开和. 六价铬污染对水车前叶片生理生化及细胞超微结构的影响[J]. 广西植物, 2002, 22(1): 92~96.
[16] Raviv M, Wallach R, Silber A, et al.Substrates and their analysis[A]. In: Hydroponic production of vegetables and ornamentals[C]. Sawas D, Passam H(Eds). Athens, Greece: Embryo Publications, 2002: 25~101.
[17] 苏金为, 王湘平. 镉离子对茶叶光合机构及性能的影响[J]. 茶叶科学, 2004, 24(1): 65~69
[18] Panls K P, Thompson J E.Evidence for the accumulation of peroxidized lipids in membranes of senescing cotyledons[J]. Plant Physiol, 1984, 75: 1152~1157.
[19] 徐勤松, 施国新, 周红卫, 等. Cd、Zn复合污染对水车前叶绿素含量和活性氧清除系统的影响[J]. 生态学杂志, 2003, 22(1): 5~8.
[20] 赵福庚, 刘友良. 胁迫条件下高等植物体内脯氨酸代谢及调节的研究进展[J]. 植物学通报, 1999, 16(5): 540~546.
[21] 夏建国, 兰海霞. 镉胁迫对蒙山茶树生长及叶片生理指标的影响[J]. 茶叶科学, 2008, 28(1): 56~61.
[22] 周希琴, 李裕红. 木麻黄种子萌发对铬胁迫的生理生态响应研究[J]. 中国生态农业学报, 2004, 12(1): 53~55.
[23] 王启明. 重金属Cr6+胁迫对玉米幼苗生理生化特性的影响[J]. 河南农业科学, 2006(8): 37~40.