

浏览全部资源
扫码关注微信
1. 湖南农业大学农学院,长沙,410128
2. 郴州市农作物种子储备和技术推广站,湖南,郴州,423000
3. 湖南农业大学化学与材料科学学院,长沙,410128
Published:2023
移动端阅览
TIAN Qinqin, ZHANG Feiting, CHEN Nana, et al. Effect of Calcium Magnesium Hydrotalcite on Yield and Cadmium Accumulation of Double Cropping Rice[J]. 2023, 37(3): 353-361.
TIAN Qinqin, ZHANG Feiting, CHEN Nana, et al. Effect of Calcium Magnesium Hydrotalcite on Yield and Cadmium Accumulation of Double Cropping Rice[J]. 2023, 37(3): 353-361. DOI: 10.13870/j.cnki.stbcxb.2023.03.045.
为研究不同用量钙镁水滑石对镉污染稻田土壤特性、双季稻产量与稻米镉积累的影响
探讨镉污染双季稻田钙镁水滑石的最佳施用方式。2021年
以早稻品种"湘早籼45号"和"陆两优996"
晚稻品种"创两优669"和"玉针香"为试验材料
在湖南省郴州市良田镇重度镉污染稻田(全镉含量1.16 mg/kg)开展大田试验
比较研究钙镁水滑石(0
CK;早稻基施3 000 kg/hm2
T1;早稻基施1 500 kg/hm2
T2;早稻基施750 kg/hm2+晚稻基施750 kg/hm2
T3)4个处理下土壤特性、双季稻产量构成与植株镉积累情况。结果表明:(1)钙镁水滑石可提高土壤pH与碱解氮、速效钾、速效磷含量
早稻成熟期分别提高0~3.06%
4.30%~13.80%
6.67%~40.00%
25.53%~30.47%;晚稻成熟期分别提高1.56%~4.07%
11.79%~14.50%
15.79%~31.58%
3.73%~17.17%;增幅表现为T1>T2>T3。(2)施用钙镁水滑石可降低土壤有效镉含量
早、晚稻成熟期各降低5.26%~42.86%
18.19%~36.84%;降幅表现为T1>T2>T3。(3)糙米镉含量和成熟期植株地上部镉积累量以T1最低
T2、T3次之
CK最高
"湘早籼45号"分别降 低33.33%~44.44%
4.89%~20.76%;"陆两优996"分别降低30.00%~60.00%
6.00%~30.98%;"玉针香"分别降低27.78%~50.00%
15.93%~34.07%;"创两优669"分别降低26.67%~60.00%
12.58%~28.56%。(4)钙镁水滑石使早、晚稻产量分别提高4.11%~10.79%
1.69%~11.29%。"湘早籼45号"、"创两优669"和"玉针香"产量以T1处理最高
陆两优996产量以T2处理最高
除玉针香外
各品种T1和T2处理产量差异不显著。可见
较大的钙镁水滑石施用量对水稻的增产、降镉效果较好
但综合考虑处理间水稻产量与镉含量差异的显著性及钙镁水滑石成本
以钙镁水滑石1 500 kg/hm2较为适宜。
In order to study the effects of different amounts of calcium and magnesium hydrotalcite on the soil characteristics of cadmium-contaminated rice fields
the yield of double cropping rice and the cadmium accumulation in rice
and to explore the best application mode of calcium and magnesium hydrotalcite in cadmium contaminated double cropping rice fields
in 2021
field experiments were conducted in the heavy cadmium contaminated rice fields (total cadmium content 1.16 mg/kg) in Liangtian Town
Chenzhou City
Hunan Province
using early rice varieties Xiangzaoxian 45 and Luliangyou 996
late rice varieties Chuang Liangyou 669 and Yuzhenxiang as experimental materials
The soil characteristics
yield components and cadmium accumulation of double cropping rice under four treatments of calcium magnesium hydrotalcite (0
CK; early rice basal application of 3 000 kg/hm2
T1; early rice basal application of 1 500 kg/hm2
T2; early rice basal application of 750 kg/hm2; late rice basal application of 750 kg/hm2
T3) were compared. The results showed that: (1) The application of calcium magnesium hydrotalcite could increase the soil pH and the contents of alkali hydrolyzable nitrogen
available potassium
and available phosphorus
respectively by 0~3.06%
4.30%~13.80%
6.67%~40.00%
and 25.53%~30.47% at the maturity of early rice
respectively
and 1.56%~4.07%
11.79%~14.50%
15.79%~31.58%
3.73%~17.17% at the maturity of late rice
showing a trend of T1 > T2 > T3. (2) Application of calcium and magnesium hydrotalcite could reduce the content of available cadmium in soil. The content of available cadmium in early and late rice ripening stages was reduced by 5.26%~42.86% and 18.19%~36.84% respectively
with a trend of T1 > T2 > T3. (3) The content of cadmium in brown rice and the accumulation of cadmium in the upper part of plant at maturity were the lowest in T1
the second in T2 and T3
and the highest in CK. The content of cadmium in Xiangzaoxian 45 decreased by 33.33%~44.44% and 4.89%~20.76% respectively
that in Luliangyou 996 decreased by 30.00%~60.00% and 6.00%~30.98% respectively
that in Yuzhixiang decreased by 27.78%~50.00% and 15.93%~34.07% respectively
and that in Chuang Liangyou 669 decreased by 26.67%~60.00% and 12.58%~28.56% respectively. (4) The yield of double cropping rice Xiangzaoxian 45
Chuang Liang You 669 and Yuzhen Xiang was the highest in T1
followed by T2 and T3
and the lowest was in CK; The yield of Luliangyou 996 was the highest in T2 treatment
the second in T1 and T3 treatment
and the lowest in CK treatment. Calcium magnesium hydrotalcite increased the yield of early and late rice by 4.11%~10.79% and 1.69%~11.29%
respectively. This experiment shows that the larger application amount of calcium magnesium hydrotalcite has a better effect on rice yield increase and cadmium reduction
but considering the significance of rice yield and cadmium content difference between treatments and the cost of calcium magnesium hydrotalcite
1 500 kg/hm2 calcium magnesium hydrotalcite is more appropriate under this experiment condition.
环境保护部,国土资源部.全国土壤污染状况调查公报[J].中国环保产业,2014(5):10-11.
Liu X J, Tian G J, Jiang D, et al. Cadmium (Cd) distribution and contamination in Chinese paddy soils on national scale[J].Environmental Science and Pollution Research International,2016,23(18):1-12.
董克,赵颖.污染农田土壤-作物体系复合污染及人体健康风险研究[J].环境与可持续发展,2018,43(5):91-93.
Luo Q H, Bai B, Xie Y H, et al. Effects of Cd uptake, translocation and redistribution in different hybrid rice varieties on grain Cd concentration[J].Ecotoxicology and Environmental Safety,2022,240:e113683.
曹胜,周卫军,周雨舟,等.硅钙镁土壤调理剂对酸性镉污染土壤及稻米的降镉效果[J].河南农业科学,2017,46(12):54-58.
He L Z, Meng J, Wang Y, et al. Attapulgite and processed oyster shell powder effectively reduce cadmium accumulation in grains of rice growing in a contaminated acidic paddy field[J].Ecotoxicology and Environmental Safety,2021,209:e111840.
Liu C, Wang L, Yin J, et al. Combined amendments of nano-hydroxyapatite immobilized cadmium in contaminated soil-potato (
Solanum tuberosum
L.) system[J].Bulletin of Environmental Contamination and Toxicology,2018,100(4):581-587.
黄卫,庄荣浩,喻鹏,等.农田土壤镉污染现状与治理方法研究进展[J].湖南师范大学自然科学学报,2022,45(1):49-56.
LI P, Wang X X, Zhang T L, et al. Effects of several amendments on rice growth and uptake of copper and cadmium from a contaminated soil[J].Journal of Environmental Sciences,2008,20(4):449-455.
石刚,庞巧莲,李文燕,等.土壤调理剂的应用现状及前景[J].现代农业科技,2021(24):138-139.
帅泽宇,谷子寒,陈基旺,等.土壤耕作方式对双季稻产量构成与穗镉积累的影响[J].水土保持学报,2019,33(3):348-357.
国家标准化管理委员会,国家质量监督检验检疫总局.GBT 23739-2009,土壤质量-有效态铅和镉的测定-原子吸收法[S].北京:中国标准出版社,2019.
李强,赵秀兰,胡彩荣,等.ISO 10390:2005土壤质量pH的测定[J].污染防治技术,2006(1):19.
鲍士旦.土壤农化分析[M].北京:中国农业出版社,2000.
江棋.土壤调理剂对镉污染稻田土壤质量和稻米品质的影响[D].武汉:华中农业大学,2020.
林小兵,武琳,王惠明,等.不同用量土壤调理剂对镉污染农田土壤环境的影响[J].长江流域资源与环境,2021,30(7):1734-1745.
解秋,吴锡林,李小燕,等.硅钙钾镁土壤调理剂对五常水稻长势及产量的影响[J].北方水稻,2020,50(1):18-21.
Hong C O, Lee D K, Chung D Y, et al. Liming effects on cadmium stabilization in upland soil affected by gold mining activity[J].Archives of Environmental Contamination Toxicology,2007,52:496-502.
丁凌云,蓝崇钰,林建平,等.不同改良剂对重金属污染农田水稻产量和重金属吸收的影响[J].生态环境,2006(6):1204-1208.
He Y B, Huang D Y, Zhu Q H, et al. A three-season field study on the in-situ remediation of Cd-contaminated paddy soil using lime, two industrial by-products, and a low-Cd-accumulation rice cultivar[J].Ecotoxicology and Environmental Safety,2017,136:135-141.
辜娇峰,周航,杨文弢,等.复合改良剂对镉砷化学形态及在水稻中累积转运的调控[J].土壤学报,2016,53(6):1576-1585.
李欣阳.土壤-水稻系统Cd形态变化、活化特征与Cd迁移阻控研究[D].长沙:中南林业科技大学,2019.
严勋,唐杰,李冰,等.不同水稻品种对镉积累的差异及其与镉亚细胞分布的关系[J].生态毒理学报,2019,14(5):244-256.
沙乐乐.水稻镉污染防控钝化剂和叶面阻控剂的研究与应用[D].武汉:华中农业大学,2015.
李耀奇,谷雨,李明德,等.4种土壤调理剂对镉污染稻田修复效果[J].湖南农业科学,2019(11):65-68.
0
Views
909
下载量
1
CSCD
Publicity Resources
Related Articles
Related Author
Related Institution
京公网安备11010802024621