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Vergara - 1976 - Physiological and morphological adaptability of ri

Vergara - 1976 - Physiological and morphological adaptability of ri

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ciuziaon DIOXIDE AND RICE ‘new 215<br />

Under field conditions, the soil supplies some CO, to crop photosynthesis.<br />

The cont<strong>ri</strong>bution <strong>of</strong> soil CO2 to net or gross photosynthesis has been estimated<br />

for upl<strong>and</strong> crops <strong>and</strong> under va<strong>ri</strong>ed weather conditions (Moss et 211.. 1961; Monteith<br />

et al.. 1964). Upl<strong>and</strong> soils supply‘ CO, from 1.5 to 52.8 g - m"! - days‘. depending<br />

on soils. temperature, soil moisture, <strong>and</strong> presence or absence <strong>of</strong> crops<br />

(Lundegardh, 1964; Monteith et a1., 1964). Flooded paddy soils may supply less<br />

CO, due to the insulation effect <strong>of</strong> st<strong>and</strong>ing ivater on CO, diffusion into the air.<br />

Tanaka et a1., (1966) reported that where all straw from the previous crop had<br />

been removed. any CO, released from a submerged soil was undetectable.<br />

Murata et a1., (1957) also reported that only small amounts <strong>of</strong> CO, came out <strong>of</strong><br />

flooded paddy soils, ranging from —0.2 ' g - m4 - day" when 7.5 tfha <strong>of</strong> compost<br />

ivas applied. to 2.2 g - m4 - day-M when 56.3 t/ha tvas applied.<br />

Recently, Yoshida et al. (1974) found that much larger amounts <strong>of</strong> soil CO1<br />

came out <strong>of</strong> paddy soils even when no compost was applied. It ranged from 3.9<br />

to 5.’? g - m = - day l under flooded conditions <strong>and</strong> from 6.0 to 8.6 g - 111': - day‘<br />

under drained conditions. This apparent discrepancy‘ among three reports is<br />

perhaps due to measurement techniques rather than to environmental conditions.<br />

Since severe CO, deficits occur around crop surfaces <strong>of</strong> <strong>ri</strong>ce it would be<br />

reasonable to assume that soil CO; moving to crop surfaces could be efficiently’<br />

used for photosyrnlhesis.<br />

As shown in Table 2. the estimated cont<strong>ri</strong>bution <strong>of</strong> soil CO, to gross photosynthesis<br />

was 6% for the flooded soil <strong>and</strong> 7% for the drained soil‘. its cont<strong>ri</strong>bution<br />

to net dry matter production tvas 9% for the flooded soil <strong>and</strong> 12% for the<br />

drained soil. The estimated cont<strong>ri</strong>butions <strong>of</strong> soil CO, flux to <strong>ri</strong>ce photosynthesis<br />

are about the same as those reported for upl<strong>and</strong> crops (Moss et a1., 1961; Monteith<br />

et a1. 1964;). Less than 10% cont<strong>ri</strong>bution <strong>of</strong> soil CO, flux to gross photosynthesis<br />

is expected for a good <strong>ri</strong>ce crop under sunny day's.<br />

In wann areas <strong>of</strong> Japan some farmers drain paddy fields for 5 to 10 days about<br />

the maximum tiller number stage. sometimes earlier or later depending on soil<br />

conditions. This practice is known as “nakabosh? (midsummer drainage) <strong>and</strong><br />

is believed to increase <strong>ri</strong>ce yields. The reasons for the beneficial effect <strong>of</strong> “midsummer<br />

drainage" are given elsewhere (Nojima, 1963). Conside<strong>ri</strong>ng that soil<br />

CO1 flux is increased by drainage, the beneficial effect <strong>of</strong> midsummer drainage<br />

Table 2. Carbon balance between <strong>ri</strong>ce photosynthesis <strong>and</strong> soil<br />

CO, flux.<br />

Flooded<br />

Drained<br />

Net dry matter production 22 26<br />

(g CHsO- rn= day)<br />

Gross photosynthesis 35 44<br />

(g CH9 m1 day‘)<br />

$0" CO; flux du<strong>ri</strong>ng daytime 2 0<br />

(g CH;Oi m-l day-‘J<br />

3.2<br />

Estimated cont<strong>ri</strong>bution <strong>of</strong> soil CO; to.<br />

Net dry matter production ($6) 9 12<br />

Gross photosynthesis ($6) 6 7

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