桂芳艳, 刘雨芳, 莫书银, 孙丽川, 孙远东, 刘文海, 戈峰. 转Cry1Ab/Ac基因水稻对稻田底栖动物群落的影响[J]. 中国生态农业学报(中英文), 2015, 23(9): 1178-1184. DOI: 10.13930/j.cnki.cjea.150375
引用本文: 桂芳艳, 刘雨芳, 莫书银, 孙丽川, 孙远东, 刘文海, 戈峰. 转Cry1Ab/Ac基因水稻对稻田底栖动物群落的影响[J]. 中国生态农业学报(中英文), 2015, 23(9): 1178-1184. DOI: 10.13930/j.cnki.cjea.150375
GUI Fangyan, LIU Yufang, MO Shuyin, SUN Lichuan, SUN Yuandong, LIU Wenhai, GE Feng. Effects of transgenic Cry1Ab/Ac rice on zoobenthos communities in paddy fields[J]. Chinese Journal of Eco-Agriculture, 2015, 23(9): 1178-1184. DOI: 10.13930/j.cnki.cjea.150375
Citation: GUI Fangyan, LIU Yufang, MO Shuyin, SUN Lichuan, SUN Yuandong, LIU Wenhai, GE Feng. Effects of transgenic Cry1Ab/Ac rice on zoobenthos communities in paddy fields[J]. Chinese Journal of Eco-Agriculture, 2015, 23(9): 1178-1184. DOI: 10.13930/j.cnki.cjea.150375

Cry1Ab/Ac基因水稻对稻田底栖动物群落的影响

Effects of transgenic Cry1Ab/Ac rice on zoobenthos communities in paddy fields

  • 摘要:Bt基因抗虫水稻的成功研发, 为有效控制鳞翅目害虫对水稻的危害提供了一条最为有效、经济的途径。稻田底栖动物群落是转Bt基因抗虫水稻的重要非靶标生物。为了解转Bt基因水稻对稻田底栖动物群落的安全性, 以转Cry1Ab/Ac基因抗虫水稻‘华恢1号’(简写为HH1)为材料, 以其非转基因亲本‘明恢63’(简写为MH63)为对照, 以稻田底栖动物群落为指示生物, 运用群落学方法, 通过连续2年在江西南昌的大田试验, 研究了转Cry1Ab/Ac基因抗虫水稻对稻田底栖动物群落的影响。结果显示: 2012年在HH1与MH63的稻田中分别采集到底栖动物22种与25种, 其中两生境中相同物种19种, 两群落物种组成相似度为0.808 5, 有7种优势种, 优势种相似度为0.833 3。2013年在HH1与MH63稻田中分别采集到底栖动物26种与28种, 两类稻田相同底栖动物22种, 两群落物种组成相似度为0.814 8, 有6种优势种, 优势种相似度为1.000 0。2012年与2013年群落总体分析与时间动态分析均显示, 两类稻田中底栖动物的物种丰富度、个体数量、多样性指数、均匀性指数及优势集中性指数变化趋势相似, 且均无显著差异。结果表明: 连续种植2年转Cry1Ab/Ac基因水稻HH1对南昌稻田底栖动物群落无明显的负作用。

     

    Abstract: Transgenic Bt rice has been developed successfully and has provided an effective and economical control on lepidopterous pests in rice field. Zoobenthos in paddy fields is an important non-target organism for transgenic Bt rice. To understand the safety of transgenic Bt rice on zoobenthos community in paddy fields, the effects of transgenic Cry1Ab/Ac rice on zoobenthos community were studied in paddy fields using the community method. The experiment was conducted in 2-consecutive-year field of transgenic Cry1Ab/Ac rice ‘Huahui No. 1’ (HH1 for short) in Nanchang, Jiangxi Province. The non-transgenic parent rice ‘Minghui 63’ (MH63 for short) was used as control treatment. Benthic animal community in paddy fields was used as bio-indicator. In 2012, some 22 and 25 species of benthic animals were respectively collected in HH1 and MH63 paddy fields. There were 19 species in common and 7 dominant species in zoobenthos communities in HH1 and MH63 paddy fields. The similarity of all the species and the dominant species of zoobenthos communities in HH1 and MH63 habitats were 0.808 5 and 0.833 3, respectively. In 2013, 26 and 28 species of benthic animals were collected in paddy fields planted respectively with HH1 and MH63, comprising of 22 common and 6 dominant species. The similarity of all the species and the dominant species of zoobenthos communities in HH1 and MH63 paddy fields were respectively 0.814 8 and 1.000 0. Analyses of both total and temporal dynamics of community parameters such as the indexes of species richness, individual number, diversity, evenness and dominance in HH1 and MH63 paddy fields in 2012 and 2013 displayed similar rates and trends and with no observed significant difference. Analysis of HH1 field (with 2 consecutive years of cultivation) in Nanchang suggested that transgenic Cry1Ab/Ac rice had no obvious adverse effect on benthic animal community.

     

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