Production Practices and Quality Assessment of Food Crops. Vol. 1
Production Practices and Quality Assessment of Food Crops. Vol. 1
Production Practices and Quality Assessment of Food Crops. Vol. 1
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196 S. del Valle-Tascon <strong>and</strong> J. L. Carrasco-Rodriguez<br />
aminoethoxyvinyl glycine to inhibit stress ethylene biosynthesis makes plants less<br />
sensitive (Mehlhorn et al., 1991). Ozone may react with volatile compounds emitted<br />
by plants into the protoplast. Interactions <strong>of</strong> O 3 with ethylene or other hydrocarbons<br />
are thought to be part <strong>of</strong> the mechanism leading to injury. Ozone-sensitive<br />
species were found to produce more ethylene during O 3 treatment than ozone-tolerant<br />
plants (Wellburn <strong>and</strong> Wellburn, 1996). In summary, stress ethylene is considered<br />
to be the major cause <strong>of</strong> accelerated senescence <strong>and</strong> leaf abscission (Mehlhorn et<br />
al., 1991).<br />
9. LEAF VISUAL INJURY<br />
Visual injury to crop plants caused by O 3 can range from severe necrosis <strong>and</strong> death<br />
<strong>of</strong> much or all the exposed tissue, to mild chlorosis (Heagle et al., 1973; Deveaou<br />
et al., 1987; Heagle et al., 1987; Mulchi et al.; 1988, Heggestad, 1997). Acute injury<br />
usually involves necrosis, varying from general large die-back areas, to small areas,<br />
stipples or flecks; such injuries occurring as a result <strong>of</strong> fumigation with high doses<br />
<strong>of</strong> O 3. Chronic injury results from exposures to sub-acute dosage. Chlorosis <strong>and</strong><br />
death <strong>of</strong> isolated cells are generally observed in these conditions. However, visible<br />
injury is not dependent upon O 3 concentration or exposure time (Heck et al., 1966).<br />
In the last few decades, the effects <strong>of</strong> O 3 on crops have been made by visual procedures.<br />
The principal drawbacks <strong>of</strong> this procedure are subjectivity, inconsistency,<br />
<strong>and</strong> low specificity.<br />
10. PHYSIOLOGICAL EFFECTS<br />
Elevated atmospheric O 3 frequently has harmful effects on the photosyntheticperformance<br />
<strong>of</strong> agricultural crops (Heck et al., 1983, Amundson et al., 1987; Lehnherr<br />
et al., 1988; Violin, 1998; Donnelly et al., 1998, 2000). Reduction in chlorophyll<br />
content (Köllner <strong>and</strong> Krauss, 2000) <strong>and</strong> carboxylation efficiency (Reid <strong>and</strong> Fiscus,<br />
1988; Farage et al., 1991) contribute to the observed decrease in net photosynthesis<br />
under elevated O 3. The loss <strong>of</strong> Rubisco activity induced by elevated O 3<br />
apparently results from a decrease in the quantity <strong>of</strong> Rubisco present (Pell et al.,<br />
1992; Baker et al., 1994). Moreover, exposure to O 3 typically reduces effective<br />
leaf area, thus decreasing light interception <strong>and</strong> the quantity <strong>of</strong> assimilate available<br />
to support the growth <strong>of</strong> economic yield component. O 3-induced disruption<br />
<strong>of</strong> cellular metabolism may also promote a loss <strong>of</strong> chlorophyll <strong>and</strong> increase<br />
senescence (Gr<strong>and</strong>jean <strong>and</strong> Furher, 1989; Fangmeier et al., 1994; Djanperä et al.,<br />
1998).<br />
11. MECHANISM OF OZONE ACTION<br />
The precise mechanism <strong>of</strong> O 3-induced injury in plants is poorly understood (Pell<br />
et al., 1992; Heath, 1994; Schaudner et al., 1997; Heath <strong>and</strong> Taylor, 1997; Pell et