Journal of Agricultural Science and Technology ›› 2023, Vol. 25 ›› Issue (8): 10-21.DOI: 10.13304/j.nykjdb.2022.0580
• BIOTECHNOLOGY & LIFE SCIENCE • Previous Articles
Liying YANG(), Mengya TAI, Yeyu ZHAI, Zicheng XU, Wuxing HUANG(
)
Received:
2022-07-11
Accepted:
2022-09-03
Online:
2023-08-20
Published:
2023-09-07
Contact:
Wuxing HUANG
通讯作者:
黄五星
作者简介:
杨丽莹 E-mail: yanglying@126.com;
基金资助:
CLC Number:
Liying YANG, Mengya TAI, Yeyu ZHAI, Zicheng XU, Wuxing HUANG. Progress of Research on the Effect of Sulfur on Cadmium Uptake and Accumulation by Plants and Its Mechanism[J]. Journal of Agricultural Science and Technology, 2023, 25(8): 10-21.
杨丽莹, 邰孟雅, 翟夜雨, 许自成, 黄五星. 硫对植物吸收积累镉的影响及其作用机制研究进展[J]. 中国农业科技导报, 2023, 25(8): 10-21.
植物 Plant | 硫形态 Sulfur form | 硫处理水平 Sulfur treatment level | 镉处理水平 Cadmium treatment level | 处理时间 Treatment time | 结果 Result | 参考 文献 Reference |
---|---|---|---|---|---|---|
水稻 Oryza sativa | 元素硫/Na2SO4/ 巯基有机黏土 S(S0)/Na2SO4/ MP | 0、50、100 mg∙kg-1 | 1.14、1.99 mg∙kg-1 | 整个生育期 Whole growth period | 根Cd↓;地上部Cd,Cd向籽粒转移系数↑ Cd in roots↓; Cd in shoots,TF to grains↑ | |
Na2S | 500 mg∙L-1 | 0.67 mg∙kg-1/0.0、0.2、0.5、1.0、2.0、 5.0 mg∙L-1 | 整个生育期 Whole growth period | 籽粒Cd,Cd向籽粒转移系数↓ Cd in grains, TF to grains↓ | ||
K2SO4 | 0、10、40、80、 160 mg∙kg-1 | 0.79 mg∙kg-1 | 整个生育期 Whole growth period | 从根到茎以及从茎到籽粒的Cd转移系数↓ TF from roots to stems and TF from stems to grains↓ | ||
S0/石膏 S0/ gypsum | 0、150、300 mg∙kg-1 | 0、5 mg∙kg-1 | 整个生育期Whole growth period | 籽粒Cd,从根部到地上部的Cd转移系数↓ Cd in grains, TF from roots to shoots↓ | ||
Na2SO4 | 0.00、1.75、3.50、 7.00 mmol∙ L-1 | 0.0、1.0 μmol∙L-1 | 7 d | 根Cd,叶Cd,从根部到地上部的Cd转移系数↓ Cd in roots, Cd in leaves, TF from roots to shoots↓ | ||
Na2SO4 | 2、6、12 mmol∙L-1 | 0、10、100 μmol∙L-1 | 7 d | 叶Cd,Cd向叶转移系数↑ Cd in leaves, TF to leaves↑ | ||
小麦 Triticum aestivum | MgSO4+Na2SO4 | 2、6、9 mmol∙L-1 | 0.0、0.2、20.0、 40.0 μmol∙L-1 | 14 d | 地上部Cd,从根部到地上部的Cd转移系数↑ Cd in shoots, TF from roots to shoots↑ | |
Na2SO4 | 0、30、60 mg∙kg-1 | 0.35、10.35 mg∙kg-1 | 整个生育期 Whole growth period | 籽粒Cd↑ Cd in grains↑ | ||
MnSO4 | 0、500、1 000、 2 000 mg∙kg-1 | 1.98 mg∙kg-1 | 整个生育期Whole growth period | 根Cd,籽粒Cd,Cd向籽粒转移系数↓ Cd in roots, Cd in grains, TF to grains↓ | ||
S0/石膏 S0/ gypsum | 0、2 000、4 000、 8 000 mg∙kg-1 | 3.02 mg∙kg-1 | 整个生育期Whole growth period | 石膏处理各组织Cd↓, S0处理↑ Gypsum treatment Cd↓, S0 treatment Cd↑ | ||
Na2SO4 | 0、60、120 mg∙kg-1 | 3.0 mg∙kg-1 | 整个生育期Whole growth period | 根Cd↑;籽粒Cd,Cd向籽粒转移系数↓ Cd in roots ↑;Cd in grains, TF to grains↓ | ||
小白菜 Brassica chinensis | Na2SO4 | -2、0、2 mmol∙L-1 (-2为缺S处理 -2 represents sulphur deficiency treatment) | 0、50 μmol∙L-1 | 7 d | 叶Cd↓ Cd in leaves ↓ | |
Na2SO4/CaSO4 | 0、5 mmol∙L-1 | 0、20 μmol∙L-1 | 8 d | 叶Cd↓ Cdin leaves ↓ |
Table 1 Effect of different forms and content levels of sulfur on cadmium uptake and accumulation by plants
植物 Plant | 硫形态 Sulfur form | 硫处理水平 Sulfur treatment level | 镉处理水平 Cadmium treatment level | 处理时间 Treatment time | 结果 Result | 参考 文献 Reference |
---|---|---|---|---|---|---|
水稻 Oryza sativa | 元素硫/Na2SO4/ 巯基有机黏土 S(S0)/Na2SO4/ MP | 0、50、100 mg∙kg-1 | 1.14、1.99 mg∙kg-1 | 整个生育期 Whole growth period | 根Cd↓;地上部Cd,Cd向籽粒转移系数↑ Cd in roots↓; Cd in shoots,TF to grains↑ | |
Na2S | 500 mg∙L-1 | 0.67 mg∙kg-1/0.0、0.2、0.5、1.0、2.0、 5.0 mg∙L-1 | 整个生育期 Whole growth period | 籽粒Cd,Cd向籽粒转移系数↓ Cd in grains, TF to grains↓ | ||
K2SO4 | 0、10、40、80、 160 mg∙kg-1 | 0.79 mg∙kg-1 | 整个生育期 Whole growth period | 从根到茎以及从茎到籽粒的Cd转移系数↓ TF from roots to stems and TF from stems to grains↓ | ||
S0/石膏 S0/ gypsum | 0、150、300 mg∙kg-1 | 0、5 mg∙kg-1 | 整个生育期Whole growth period | 籽粒Cd,从根部到地上部的Cd转移系数↓ Cd in grains, TF from roots to shoots↓ | ||
Na2SO4 | 0.00、1.75、3.50、 7.00 mmol∙ L-1 | 0.0、1.0 μmol∙L-1 | 7 d | 根Cd,叶Cd,从根部到地上部的Cd转移系数↓ Cd in roots, Cd in leaves, TF from roots to shoots↓ | ||
Na2SO4 | 2、6、12 mmol∙L-1 | 0、10、100 μmol∙L-1 | 7 d | 叶Cd,Cd向叶转移系数↑ Cd in leaves, TF to leaves↑ | ||
小麦 Triticum aestivum | MgSO4+Na2SO4 | 2、6、9 mmol∙L-1 | 0.0、0.2、20.0、 40.0 μmol∙L-1 | 14 d | 地上部Cd,从根部到地上部的Cd转移系数↑ Cd in shoots, TF from roots to shoots↑ | |
Na2SO4 | 0、30、60 mg∙kg-1 | 0.35、10.35 mg∙kg-1 | 整个生育期 Whole growth period | 籽粒Cd↑ Cd in grains↑ | ||
MnSO4 | 0、500、1 000、 2 000 mg∙kg-1 | 1.98 mg∙kg-1 | 整个生育期Whole growth period | 根Cd,籽粒Cd,Cd向籽粒转移系数↓ Cd in roots, Cd in grains, TF to grains↓ | ||
S0/石膏 S0/ gypsum | 0、2 000、4 000、 8 000 mg∙kg-1 | 3.02 mg∙kg-1 | 整个生育期Whole growth period | 石膏处理各组织Cd↓, S0处理↑ Gypsum treatment Cd↓, S0 treatment Cd↑ | ||
Na2SO4 | 0、60、120 mg∙kg-1 | 3.0 mg∙kg-1 | 整个生育期Whole growth period | 根Cd↑;籽粒Cd,Cd向籽粒转移系数↓ Cd in roots ↑;Cd in grains, TF to grains↓ | ||
小白菜 Brassica chinensis | Na2SO4 | -2、0、2 mmol∙L-1 (-2为缺S处理 -2 represents sulphur deficiency treatment) | 0、50 μmol∙L-1 | 7 d | 叶Cd↓ Cd in leaves ↓ | |
Na2SO4/CaSO4 | 0、5 mmol∙L-1 | 0、20 μmol∙L-1 | 8 d | 叶Cd↓ Cdin leaves ↓ |
植物 Plant | 硫形态 Sulfur form | 硫处理水平 Sulfur treatment level | 镉处理水平 Cadmium treatment level | 处理时间 Treatment time | 结果 Result | 参考 文献 Reference |
---|---|---|---|---|---|---|
小白菜 Brassica chinensis | Na2SO4 | 0、50 mg∙kg-1 | 0、1、5、25、50、 100 mg∙kg-1 | 30~35 d | 根Cd↑;叶Cd,Cd向叶片转移系数↓ Cd in roots ↑; Cd in leaves, TF to leaves↓ | |
菠菜 Ipomoea aquatica | Na2SO4 | 100、200 mg∙kg-1 | 0.24、2.50 mg∙kg-1 | 14 d | 根Cd↑;叶Cd↓,Cd向叶片转移系数↓ Cd in roots ↑; Cd in leaves, TF to leaves↓ | |
苋菜 Amaranshus mangostanus | S0/(NH4)2SO4/CaSO4 | 0、50 mg∙kg-1 | 15 mg∙kg-1 | 45 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
大白菜 Brassica campestris | S0/Na2SO4/Na2SO3 | 200 mg∙kg-1 | 2.3 mg∙kg-1 | 40 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
烟草 Nicotiana tabacum | K2SO4 | 0、130、105 mg∙kg-1 | 0、1、5 mg∙kg-1 | 20 d | 根Cd,叶Cd↓ Cd in roots, Cd in leaves↓ | |
K2SO4 | 0、510、1 020 mg∙kg-1 | 9.4 mg∙kg-1 | 60 d | 根Cd,叶Cd,Cd向叶片转移系数↑ Cd in roots, Cd in leaves, TF to leaves↑ | ||
伴矿景天 Sedum plumbizincicola | S0 | 0~4 000 mg∙kg-1 | 1.33、4.44 mg∙kg-1 | 90 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
S0/FeSO4 | 0~1 500 mg∙plant-1/0~ 1 200 mg∙plant-1 | 0.65 mg∙kg-1 | 60 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | ||
S0 | 0、180、360、 720 g∙m-2 | 1.33 mg∙kg-1 | 150 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | ||
超积累型东南景天 Sedum alfredii Hance | K2SO4 | 0.00、0.75、1.50、 2.25 mmol∙L-1 | 0、10、100 μmol∙L-1 | 30 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
龙葵 Solanum nigrum | S0/石膏 S0/ gypsum | 0、100、50+ 50 mg∙kg-1 | 0、25、50 mg∙kg-1 | 70 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ |
Table 1 Effect of different forms and content levels of sulfur on cadmium uptake and accumulation by plants
植物 Plant | 硫形态 Sulfur form | 硫处理水平 Sulfur treatment level | 镉处理水平 Cadmium treatment level | 处理时间 Treatment time | 结果 Result | 参考 文献 Reference |
---|---|---|---|---|---|---|
小白菜 Brassica chinensis | Na2SO4 | 0、50 mg∙kg-1 | 0、1、5、25、50、 100 mg∙kg-1 | 30~35 d | 根Cd↑;叶Cd,Cd向叶片转移系数↓ Cd in roots ↑; Cd in leaves, TF to leaves↓ | |
菠菜 Ipomoea aquatica | Na2SO4 | 100、200 mg∙kg-1 | 0.24、2.50 mg∙kg-1 | 14 d | 根Cd↑;叶Cd↓,Cd向叶片转移系数↓ Cd in roots ↑; Cd in leaves, TF to leaves↓ | |
苋菜 Amaranshus mangostanus | S0/(NH4)2SO4/CaSO4 | 0、50 mg∙kg-1 | 15 mg∙kg-1 | 45 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
大白菜 Brassica campestris | S0/Na2SO4/Na2SO3 | 200 mg∙kg-1 | 2.3 mg∙kg-1 | 40 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
烟草 Nicotiana tabacum | K2SO4 | 0、130、105 mg∙kg-1 | 0、1、5 mg∙kg-1 | 20 d | 根Cd,叶Cd↓ Cd in roots, Cd in leaves↓ | |
K2SO4 | 0、510、1 020 mg∙kg-1 | 9.4 mg∙kg-1 | 60 d | 根Cd,叶Cd,Cd向叶片转移系数↑ Cd in roots, Cd in leaves, TF to leaves↑ | ||
伴矿景天 Sedum plumbizincicola | S0 | 0~4 000 mg∙kg-1 | 1.33、4.44 mg∙kg-1 | 90 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
S0/FeSO4 | 0~1 500 mg∙plant-1/0~ 1 200 mg∙plant-1 | 0.65 mg∙kg-1 | 60 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | ||
S0 | 0、180、360、 720 g∙m-2 | 1.33 mg∙kg-1 | 150 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | ||
超积累型东南景天 Sedum alfredii Hance | K2SO4 | 0.00、0.75、1.50、 2.25 mmol∙L-1 | 0、10、100 μmol∙L-1 | 30 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ | |
龙葵 Solanum nigrum | S0/石膏 S0/ gypsum | 0、100、50+ 50 mg∙kg-1 | 0、25、50 mg∙kg-1 | 70 d | 根Cd,叶Cd↑ Cd in roots, Cd in leaves↑ |
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