TABLE 3.
Research progress on the effects of Se on accumulation of heavy metals in higher plants.
| Added Se form | Amounts | Heavy metal species | Crop species | Test results | Heavy metal availability | References |
| Se(IV) | 0, 0.5, 1 mg kg–1 | As | Rice | The addition of Se (IV) reduced total As content in soil solution, but increased As content in rice grain by 43.7–74.6%. | Decrease | Wan et al., 2018 |
| Se(IV) | 0, 1, 5, 10 mg kg–1 | As | Rice | Se (IV) application significantly reduced rice grain As content by 8.6, 31.4, and 33.7% with the Se content of 1, 5, and 10 mg kg–1, respectively. | – | Zhou et al., 2017b |
| Se(IV) | 0, 1, 5 mg kg–1 | As | Rice | Se (IV) application reduced As availability in rhizosphere soil. Se (IV) application significantly reduced the grain As content. | Decrease | Lv et al., 2020 |
| Se(IV) | 0, 0.5, 3, 6 mg kg–1 | Hg | Rice | Se(IV) addition forms IHg-Se complexes, resulting reduction of effectiveness of Hg in soil. As content in rice grain reduced with the increase of Se (IV) concentration. | Decrease | Tang et al., 2017 |
| Se(IV) | 0, 20, 40, 60, 100, 300, 500 mg kg–1 | Hg | Rice | Se (IV) application decreased inorganic Hg and MeHg concentration in grain and root. | Decrease | Xu et al., 2019 |
| Se(IV) | 0, 3 mg kg–1 | Hg | Rice | Se(IV) application reduced MeHg content in soil and in rice root, straw and grain. | Decrease | Wang et al., 2016 |
| Se(IV) | 1 mg kg–1 | Cd | Rice | Se(IV) reduced exchangeable Cd content but increased the Cd content combined with carbonate and iron-manganese oxides. Se(IV) addition reduced rice Cd content by 36.5% | Decrease | Huang et al., 2018 |
| Se(IV) | 0, 0.5, 1, 2, 4, 8 mg kg–1 | Cd | Wheat | Se(IV) reduced Cd content in wheat shoot from 25 to 35%. | – | Atarodi et al., 2018 |
| Se(IV) | 0, 1, 5, 10, 15, 20 mg kg–1 | Cd | Rape | Se(IV) markedly reduced Cd concentration in both root and shoot. | – | Wu et al., 2016b |
| Se(IV) | 0, 1, 5 mg kg–1 | Cd | Rice | Se (IV) application reduced Cd availability in rhizosphere soil. Se (IV) application significantly reduced the grain Cd content. | Decrease | Lv et al., 2020 |
| Se(VI) | 0, 0.1, 1, 5 mg kg–1 | As | Rice | Se(VI) addition reduced As content in rice root, shoot and grain. | – | Liao et al., 2016 |
| Se(VI) | 0, 0.5, 3, 6 mg kg–1 | Hg | Rice | Se(VI) addition forms IHg-Se complexes, resulting reduction of effectiveness of Hg in soil. Hg content in rice grain reduced with the increase of Se (VI) concentration. | Decrease | Tang et al., 2017 |
| Se(VI) | 0, 0.1, 1, 5 mg kg–1 | Cd | Rice | Se(VI) addition reduced Cd content in rice root, shoot and grain. | – | Liao et al., 2016 |
| Se(VI) | 0, 3 mg kg–1 | Hg | Rice | Se(VI) application reduced MeHg content in soil and in rice root, straw and grain. | Decrease | Wang et al., 2016 |
| Undefined | 0, 0.003, 0.03, 0.15, 0.3, 1.5 mg kg–1 | Hg | Rice | Low Se concentration reduced Hg and MeHg content in rice grains, but high Se concentration increased it. | – | Li et al., 2019a |