Yoshida - 1981 - Fundamentals of Rice Crop Science
Yoshida - 1981 - Fundamentals of Rice Crop Science
Yoshida - 1981 - Fundamentals of Rice Crop Science
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162 FUNDAMENTALS OF RICE CROP SCIENCE<br />
deficiency is unlikely but toxicity may occur. There are several reasons, however,<br />
why manganese toxicity in lowland rice is uncommon (Tadano and <strong>Yoshida</strong><br />
1978):<br />
• <strong>Rice</strong> roots have a high degree <strong>of</strong> manganese-excluding power. In solution<br />
culture, the tissue manganese content increases only four fold with rice plants<br />
grown at 300 ppm Mn compared with those grown at 0.1 ppm Mn. It is 109<br />
times for barley and 700 times for radish (Tanaka et al 1975).<br />
• <strong>Rice</strong> tolerates a high manganese content. The critical tissue content for<br />
manganese toxicity is 700 ppm for beans, 1,200 ppm for barley, and 7,000<br />
ppm for rice (Cheng and Quallette 1971).<br />
• Compared with nitrate, ammonia has a retarding effect on manganese uptake<br />
(See Table 3.18).<br />
• A high level <strong>of</strong> iron in submerged soils may counteract an excessive manganese<br />
uptake (Ishizuka et al 1961).<br />
In many cases, a high manganese content in rice tissues is frequently associated<br />
with high yields, possibly indicating that a high manganese content in the soil is<br />
associated with various favorable soil conditions.<br />
3.13. SULFUR<br />
3.13.1. Occurrence <strong>of</strong> deficiency<br />
Sulfur deficiency is a common nutritional disorder in upland crops but it rarely<br />
occurs in lowland rice. Sulfur deficiency <strong>of</strong> lowland rice has been reported from<br />
Mandalay, Burma (Aiyar 1945); the Lower Amazon Basin, Brazil (Wang et al<br />
1976a, b); and South Sulawesi, Indonesia (Mamaril et al 1979). A recent trend in<br />
the fertilizer industry to shift from ammonium sulfate to urea and from superphosphate<br />
to nonsulfur phosphatic fertilizer may induce more widespread sulfur deficiency<br />
in lowland rice.<br />
3.13.2. Sulfate in soil solution<br />
Sulfate is reduced to sulfide in flooded soils. As a consequence, the soil sulfate<br />
concentration declines rapidly and is associated with a sulfide accumulation (Fig.<br />
3.28). Thus, the availability <strong>of</strong> soil sulfur decreases as soil reduction proceeds<br />
(Nearpass and Clark 1960).<br />
The rate <strong>of</strong> sulfate reduction in submerged soils depends on soil properties.<br />
Concentrations as high as 1,500 ppm SO 4<br />
2-<br />
in neutral and alkaline soils may be<br />
reduced to zero within 6 weeks <strong>of</strong> submergence (Ponnamperuma 1972).<br />
3.13.3. Natural supply <strong>of</strong> sulfur<br />
Sources <strong>of</strong> natural sulfur are soil, irrigation water, and atmospheric precipitation.<br />
a. Soil. Soil contains sulfur in organic and inorganic forms. The A value, to<br />
assess the available sulfur in submerged soils, is highly correlated with the soil<br />
sulfur extractable with Ca (H 2 PO 4 ) 2 or KH 2 PO 4 solution (Suzuki 1978). Hence,