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优质稻品种硒镉富集特性研究初报
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Abstract:
为筛选适合株洲市种植的优质、富硒、低镉的优质稻品种,引进15个优质稻品种进行随机区组试验,在灌浆初期施用生物纳米硒肥1次,硒肥用量(以Se计) 1.25 g/667m2,测定精米镉、总硒、有机硒含量。结果表明:1) 在重度镉污染土壤条件下(1.17 mg/kg),15个优质稻品种对镉的吸收积累能力存在一定的差异,但未达到显著水平(P = 0.05);其中,精米镉含量最低的是拾两优1817,说明该品种具有低镉积累特性。与不施硒肥相比,施用硒肥品种的精米镉含量平均降低3.05%,降镉效果不明显。2) 15个优质稻品种籽粒硒富集能力存在极显著差异(P = 0.01),精米硒含量品种间变幅在18.3~121.6 μg/100g,平均为67.5 μg/100g,说明通过施用含量硒叶面肥,完全可以在低硒或缺硒区生产出高含量的富硒大米。其中:玉针香、泰丰优农39、泰优农39、巴斯马蒂等品种的硒富集能力较强,在富硒大米生产中具有较好的优势。3) 15个优质稻品种精米的有机硒占比(%)有极显著差异(P = 0.01),品种间变幅在76%~100%,平均为92%,其中:香优52、悦两优美香新占、美香占2号、农香42的有机硒占比达到99%,说明这些品种的硒生物转化率高。4) 以精米总硒含量或富硒效率(权重系数0.4)和有机硒占比(权重系数0.6)为指标进行灰色关联度分析表明,15个优质稻品种中,富硒综合性状优良的常规稻品种是玉针香和巴斯马蒂、三系杂交稻品种是泰优农39、两系杂交稻品种是泰丰优农39和又香优浓39。玉针香和巴斯马蒂为1等优质米,香味浓郁,食味好;且垩白粒率和垩白度低,透明度1级,外观品质高;667 m2产量400 kg左右,又符合当地气候生产条件对品种的特征要求,在高档富硒香米开发中具有良好的推广应用前景。
In order to select high-quality rice varieties with high quality, low cadmium and rich selenium suitable for planting in Zhuzhou, 15 high-quality rice varieties were introduced to carry out a randomized block test. At the early stage of grain filling, biological nano selenium fertilizer was applied once, and the amount of selenium fertilizer (calculated as Se) was 1.25 g/667m2. The contents of cadmium, total selenium and organic selenium in milled rice were determined. The results showed that: 1) under the condition of heavy cadmium pollution (1.17 mg/kg), there was a certain difference in the ability of cadmium absorption and accumulation among 15 high-quality rice varieties, but it did not reach a significant level (p = 0.05); Among them, the lowest cadmium content in milled rice is shiliangyou 1817, which indicates that this variety has the characteristics of low cadmium accumulation. Compared with no selenium fertilizer, the content of cadmium in milled rice with selenium fertilizer decreased by an average of 3.05%, and the effect of reducing cadmium was not obvious. 2) There was a very significant difference in grain selenium enrichment among 15 high-quality rice varieties (p = 0.01), and the selenium content in milled rice varied from 18.3 to 121.6 μG/100g, average 67.5 μG/100g, indicating that high selenium rich rice can be produced in low selenium or selenium deficient areas by applying selenium rich leaf fertilizer. Among them, Yu-zhen-xiang, Tai-feng-you-nong 39, Tai-you-nong 39, Basmati and other varieties have strong se-lenium enrichment ability, and have good advantages in the production of selenium rich rice. 3) The percentage of organic
[1] | El-Shora, H.E. and Ali, A.S. (2011) Changes in Activities of Nitrogen Metabolism Enzymes in Cadmium Stressed Mar-row Seedlings. Asian Journal of Plant Sciences, 10, 117-124. https://doi.org/10.3923/ajps.2011.117.124 |
[2] | 喻华, 冯文强, 秦鱼生, 等. 镉胁迫对不同基因型水稻生长和镉吸收的影响[J]. 西南农业学报, 2013, 26(3): 878-883. |
[3] | 宗良纲, 徐晓炎. 水稻对土壤中镉的吸收及其调控措施[J]. 生态学杂志, 2004, 23(3): 120-123. |
[4] | 邓波儿, 刘同仇, 郑文娟. 黄棕壤性水稻土镉临界浓度的研究[J]. 华中农业大学学报, 1991, 10(4): 374-377. |
[5] | 朱亮, 邵孝侯. 耕作层中重金属Cd形态分布规律及植物有效性研究[J]. 河海大学学报, 1997, 25(3): 50-56. |
[6] | 陈涛, 吴燕玉, 张学询, 等. 张士灌区镉土改良和水稻镉污染防治研究[J]. 环境科学, 1980, 1(5): 7-11. |
[7] | 曹仁林, 贾晓葵, 张建顺. 镉污染水稻土防治研究[J]. 天津农林科技, 1999(6): 12-17. |
[8] | Lenz, M. and Lens, P.N.L. (2009) The Essential Toxin: The Changing Perception of Selenium in Environmental Sciences. Sciences of the Total En-vironment, 407, 3620-3633. https://doi.org/10.1016/j.scitotenv.2008.07.056 |
[9] | Gavin, E. and Helmut, S. (2001) The Biochemistry of Selenium and the Glutathione System. Environmental Toxicology and Pharmacology, 10, 153-158. https://doi.org/10.1016/S1382-6689(01)00078-3 |
[10] | Combs, G.F. (2001) Selenium in Global Food Systems. British Journal of Nutrition, 85, 517-547.
https://doi.org/10.1079/BJN2000280 |
[11] | Rayman, M.P. (2000) The Importance of Seleniurn to Human Health. The Lancet, 356, 233-241.
https://doi.org/10.1016/S0140-6736(00)02490-9 |
[12] | 张艳嫣, 陈丹, 谭艳玲, 等. 外源硒对低温胁迫下铁皮石斛幼苗的缓解效应及其抗氧化生理特征变化[J]. 西北植物学报, 2013, 33(4): 747-754. |
[13] | Hu, Q.H., Yang, F.M., Pan, G.X., et al. (2001) Effect of Selenium on the Quality and Selenium Levels in Soybean. Chinese Journal of Oil Crop Science, 23, 42-44. |
[14] | Birringer, M., Pilawa, S. and Flohe, I. (2002) Trends in Selenium Biochemistry. Natural Prod-uct Reports, 19, 693-718.
https://doi.org/10.1039/B205802M |
[15] | 谭周磁, 陈嘉勤, 薛海霞. 硒(Se)对降低水稻重金属Pb, Cd, Cr污染的研究[J]. 湖南师范大学自然科学学报, 2000, 23(3): 80-83. |
[16] | 张海英, 韩涛, 田磊, 等. 草莓叶面施硒对其重金属镉和铅积累的影响[J]. 园艺学报, 2011, 38(3): 409-416. |
[17] | 崔剑波. 生态环境中的生命元素硒与健康的研宄生态学进展[J]. 生态学报, 2010, 6(4): 243-251. |
[18] | 廖自基. 微量元素的环境化学及生物效应[M]. 北京: 中国环境科学出版社, 1992: 102-106. |
[19] | 池忠志, 杨洋, 杨福明, 姜心禄, 郑家国. 生产富硒稻谷的硒肥施用技术研究[J]. 西南农业学报, 2011, 24(6): 2289-2292. |
[20] | 黄太庆, 江泽普, 黄雁飞, 廖青, 邢颖, 梁潘霞. 不同配方含硒叶面肥对水稻富硒降镉的影响[J]. 南方农业学报, 2017, 48(7): 1185-1189. |
[21] | 阳静, 龚建华, 欧立军, 邓建红, 杨永红, 邓雅文, 粟文俊. COVID防治与硒营养关系研究与探讨[J]. 农业科学, 2020, 10(5): 263-272. |
[22] | Wang, Z. and Gao, Y. (2001) Biogeochemical Cycling of Selenium in Chinese Environments. Applied Geochemistry, 16, 1345-1351. https://doi.org/10.1016/S0883-2927(01)00046-4 |
[23] | 湖南省农业厅科教处与老科协. 硒与人体健康知识[M]. 武汉: 湖北省农业厅, 2007. |
[24] | 王宗爽, 段小丽, 刘平, 等. 环境健康风险评价中我国居民暴露参数探讨[J]. 环境科学研究, 2009, 22(10): 1164-1170. |
[25] | Premarathna, L., Mclaughlin, M.J., Kirby, J.K., et al. (2012) Selenate-Enriched Urea Granules Are Highly Effective Fertilizer for Selenium Biofortification of Paddy Rice Grain. Journal of Agricultural and Food Chemistry, 60, 6037-6044. https://doi.org/10.1021/jf3005788 |
[26] | 崔朝解, 周琴, 胡小琪, 等. 中国居民谷类及薯类消费现状分析[J]. 中国食物与营养, 2008(3): 33-36. |
[27] | 唐华俊, 李暂敏. 基于中国居民平衡膳食模式的人均粮食需求量研究[J]. 中国农业科学, 2012, 45(11): 2315-2327. |