Table 3.
Reported ways for reducing the uptake of As by rice plants.
Decreasing of As Uptake | Method | Remarks | Reference |
---|---|---|---|
43% to 70% | Using Anabaena azotica (Microalgae) | (i) Decreasing translocation of As from root to grains; (ii) decreasing DMA in grains and roots and (iii) enhancing nutrient uptake and rice growth | [102] |
40% | Using Chlorella vulgaris and Nannochloropsis sp. (Microalgae) | (i) Increasing root and shoot length and biomass and (ii) reduction in cellular toxicity and antioxidant enzyme | [103] |
48.1% to 77.7% | Using Chlorella vulgaris (Microalgae) and Pseudomonas putida (Bacteria) | (i) Reducing As accessibility; (ii) modulating the As uptake and (iii) enhancing detoxification mechanism. | [95] |
3.5% to 26.0% | Using rhizobacteria (PGPR) | (i) Improving rice growth and (ii) decreasing As accumulation | [104] |
79% (in shoots) | Using Pantoea sp (Bacteria; EA106) | (i) improving Fe uptake by root; (ii) decreasing As accumulation | [105] |
52.3% to 64.5% | Using Rhodopseudomonas palustris C1 and Rubrivivax benzoatilyticus C31(Nonsulfur bacteria) | (i) Improving the rice growth; (ii) increasing chlorophyll a and b and (iii) reducing As accumulation | [106] |
31% (in grains; just leonardite); | Using leonardite + Bacillus pumilus, Pseudomonas sp and Bacillus thuringiensis | (i) High efficiency of leonardite in adsorption of arsenic and (ii) increasing productivity and reducing arsenic in grains | [107] |
92 % (in grains; leonardite + Bacillus pumilus) | |||
91% (in grains; leonardite + Pseudomonas sp) | |||
91% (in grains; leonardite + Bacillus thuringiensis) | |||
17% to 82% (in straw) | Using Pteris vittata (Plant) | (i) Decreasing phosphate extractable; (ii) decreasing methylated As in grains more than inorganic As | [108] |
22% to 58% (in grains) | |||
179% (in root) | Using selenium amendments | (i) Enhancing the essential amino acids; and (ii) increasing non-protein thiols and phytochelatins in rice | [109] |
144% (in shoot) | |||
46% (in straw) | Using Si-rich amendments | (i) Decreasing As accumulation and (ii) reducing CH4 emissions from soil | [97] |
27.5 (in grains) | Using selenite fertilization | (i) Decreasing the soil solution As in flooded condition; (ii) decreasing As uptake by rice in aerobic and (iii) decreasing the proportion of As in rice shoots. | [110] |
50% (straw, flag leaf and husk) | Using silicon | (i) Increasing the Si, Fe and P in soil solution | [111] |
68.9% to 78.3% (in grains) | Using ferromanganese oxide and biochar | (i) increasing the Fe and Mn plaque content and (ii) improving the biomass weight of the rice | [112] |
32% (in grains under low water) | Using zero valent iron | (i) Increasing percentage productive tillers and grain yield and (ii) reducing the cadmium bioaccumulation in rice grains | [113] |