Phytoextraction by high-Cd-accumulating rice to reduce Cd in wheat grains grown in Cd-polluted fields
Open Access
- 4 March 2014
- journal article
- research article
- Published by Taylor & Francis in Soil Science and Plant Nutrition
- Vol. 60 (2) , 266-275
Abstract
Phytoextraction using indica rice plants (Indian Rice Oryza ssp.) is a promising technique for remediating cadmium (Cd)-polluted paddy fields. Because this technique has only been established for paddy fields, we decided to examine phytoextraction in upland fields that have been converted from paddy fields. Although “CHOKOUKOKU” shows a shattering habit and lodging, its Cd uptake was significantly higher than that of other indica rice varieties. On the other hand, “IR8”, which was able to accumulate only moderate levels of Cd in its shoots, has a lodging tolerance, making it an optimal variety for southwest Japan, which experiences several typhoons each year. Therefore, both “CHOKOUKOKU” and “IR8” were useful in estimating practical phytoextraction in upland fields. A practical phytoextraction examination showed that the total Cd uptake of “CHOKOUKOKU” and “IR8” was 822 and 545 g ha−1, respectively, after a 4-year period. After phytoextraction by planting high Cd-accumulating rice plants, the Cd concentration of the plot soil decreased by approximately 35%, compared to the initial Cd concentration. To evaluate phytoextraction efficiency in the upland field, wheat (Triticum aestivum) was subsequently grown in the remediation field. The Cd concentration in the grains of “SHIROGANEKOMUGI” grown in the phytoextraction plot was lower than that grown in a non-phytoextraction plot; regrettably, it exceeded the Codex Alimentarius Commission standard, whereas the grain Cd concentrations of “CHUGOKU165” planted in phytoextraction plots complied with the Codex standard for wheat grain. These results suggest that phytoextraction using high Cd-accumulating rice varieties is a practical remediation system for low Cd-polluted upland fields. Moreover, we determined the end point of the phytoextraction process, which occurs when the soil Cd concentration of the phytoextraction fields is less than 0.6 mg kg−1 if “CHUGOKU165” is cultivated in this area.Keywords
This publication has 13 references indexed in Scilit:
- Effects of Water Management on Cadmium and Arsenic Accumulation and Dimethylarsinic Acid Concentrations in Japanese RiceEnvironmental Science & Technology, 2009
- Practical phytoextraction in cadmium-polluted paddy fields using a high cadmium accumulating rice plant cultured by early drainage of irrigation waterSoil Science and Plant Nutrition, 2009
- Cadmium Concentration in Grains of Japanese Wheat Cultivars : Genotypic Difference and Relationship with Agronomic CharacteristicsPlant Production Science, 2008
- Remediation of cadmium-contaminated paddy soils by washing with calcium chloride: Verification of on-site washingEnvironmental Pollution, 2007
- Phytoextraction of cadmium by rice (Oryza sativa L.), soybean (Glycine max (L.) Merr.), and maize (Zea mays L.)Environmental Pollution, 2007
- IsBrassica junceaa suitable plant for phytoremediation of cadmium in soils with moderately low cadmium contamination? – Possibility of using other plant species for Cd-phytoextractionSoil Science and Plant Nutrition, 2006
- Potential ofThlaspi caerulescensfor Cadmium Phytoremediation: Comparison of Two Representative Soil Types in Japan under Different Planting FrequenciesSoil Science and Plant Nutrition, 2005
- Genotypic variations in cadmium levels of rice grainSoil Science and Plant Nutrition, 2003
- Phytoextraction of Cd and Zn with Thlaspi caerulescens in field trialsSoil Use and Management, 2003
- Phytoextraction of Cadmium and Zinc from a Contaminated SoilJournal of Environmental Quality, 1997