1971
DOI: 10.1007/bf01372649
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Influence of continuous submergence on pH, exchange acidity and pH-dependent acidity in rice soils

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Cited by 5 publications
(3 citation statements)
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“…After 23 DAT, pH dropped from initially 6.8 to 6.0–6.5 at the redoximorphic root–soil matrix interface (Figure S8), potentially caused by protons generated during the precipitation of Fe­(III) (oxyhydr)­oxides and acidification by the release of plant exudates, chelating agents, or plant-derived organic acid molecules (found to decrease soil pH by up to 2 pH units). , The acidification of the unbuffered artificial rhizosphere proceeded until the end of the growth experiment after 45 DAT (pH 5.0–5.5; Figure S8) and significantly correlated to areas with the highest extent in Fe­(III) mineral formation (Figure C and D). The observed pH decrease induced by ROL in our setup has been observed in a similar manner in various wetland soils and was hypothesized to be attributed to ROL-driven Fe­(II) oxidation. These observed changes in soil pH will not only positively affect Fe­(III) solubility but also increase Fe­(II) half-life times and bioavailability for microbial Fe­(II) turnover. However, in natural rice paddy soils, the soil pH buffer capacity would potentially decrease extensive changes in soil pH related to Fe­(II) oxidation.…”
Section: Resultssupporting
confidence: 77%
“…After 23 DAT, pH dropped from initially 6.8 to 6.0–6.5 at the redoximorphic root–soil matrix interface (Figure S8), potentially caused by protons generated during the precipitation of Fe­(III) (oxyhydr)­oxides and acidification by the release of plant exudates, chelating agents, or plant-derived organic acid molecules (found to decrease soil pH by up to 2 pH units). , The acidification of the unbuffered artificial rhizosphere proceeded until the end of the growth experiment after 45 DAT (pH 5.0–5.5; Figure S8) and significantly correlated to areas with the highest extent in Fe­(III) mineral formation (Figure C and D). The observed pH decrease induced by ROL in our setup has been observed in a similar manner in various wetland soils and was hypothesized to be attributed to ROL-driven Fe­(II) oxidation. These observed changes in soil pH will not only positively affect Fe­(III) solubility but also increase Fe­(II) half-life times and bioavailability for microbial Fe­(II) turnover. However, in natural rice paddy soils, the soil pH buffer capacity would potentially decrease extensive changes in soil pH related to Fe­(II) oxidation.…”
Section: Resultssupporting
confidence: 77%
“…The exchange acidity and total acidity of soil increased significantly due to incorporation of rice stubble, irrespective of treatment with yogurt. Increase in exchange acidity but decrease in total potential acidity during three months submergence was reported (Savant and Kibe, 1971). The bottom layer of the soil in the present work remained near saturation throughout the incubation which might have contributed to the observed change in exchange acidity.…”
Section: Forms Of Acidity In Soil At Different Days After Incubationsupporting
confidence: 67%
“…Chemical degradation in water bodies seemed to be pH dependent (http://nepis.epa.gov/Exe/ZyPDF.cgi?Dockey=P1008R8C.pdf). In the soil, flooding irrigation resulted in gradual stabilization of pH around the neutral range . Therefore, differences in soil pH among soils would be minimized in the saturation treatments.…”
Section: Resultsmentioning
confidence: 99%