Allelochemicals Biologica... - Name
Allelochemicals Biologica... - Name
Allelochemicals Biologica... - Name
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ALLELOPATHY FOR WEED CONTROL 115<br />
and to detect the sensitivity of the target weed to minute quantities of allelopathic<br />
substances, incised plant parts of aquatic weeds would serve better than whole plants.<br />
For screening of different allelopathic substances for inhibition of water hyacinth, a<br />
specific bio-assay method was designed with cut leaves of water hyacinth (Kathiresan,<br />
2000; Kannan, 2002). This bioassay involved exposure of cut leaves of water hyacinth<br />
to graded doses of plant materials to be tested (dissolved in water). The leaves of<br />
water hyacinth plants (with healthy leaves submerged in water) were detached by<br />
cutting the petiole with a razor blade with care to retain the incision point below<br />
water level. The detached portions of leaf with a part of petiole intact was kept<br />
submerged in water for 90 seconds to ensure that no air was trapped internally. Then<br />
these leaves were transferred to scintillation vials with water where in different plant<br />
products were dissolved and individually compared with an untreated control. The<br />
percent fresh weight reduction of the cut leaves was calculated using the formula<br />
Initial weight of the cut leaves – weight after 24 hr of treatment<br />
X 100<br />
Initial weight of cut leaves<br />
5.2. Dose Response Studies<br />
Even if a plant product proves appreciably allelopathic on aquatic weeds in bio-assay,<br />
tracing the pattern of allelopathic inhibition with graded doses of the plant product<br />
becomes vital as aquatic systems requires enormous quantities of plant product due to<br />
the quantum of water body (dilution), which in many cases is not practically feasible.<br />
Furthermore, this dose response has to be plotted for differing morpho-physiological<br />
states of the weed that occurs in common, as the quantity of allelochemical required<br />
for a knock down effect is less with a small statured weed compared to that of larger<br />
sized weed. For this purpose, before screening of allelopathic plant products on water<br />
hyacinth, the latter was classified in to different morphological stages (large, medium<br />
and small) prevalent in the state of Tamilnadu, India using discriminant analysis<br />
(Kannan and Kathiresan, 1998). Both whole plant and cut leaf bio-assays were done<br />
on each of the three stages of water hyacinth. Higher (10 to 30 g L -1 ) doses were used<br />
in whole plants to impart a near lethal effect on the whole plant and lower doses were<br />
used in cut leaf bio-assays to cause some allelopathic injury, if not lethal. The doses<br />
used for water hyacinth cut leaf bio-assay were 30, 25, 20, 15 10, 5 2.5, 1, 0.5, 0.25,<br />
and 0.1 g L -1 . The dose response data revealed that cut leaf-bioassay was superior to<br />
whole plant assay. For example, C. amboinicus at as low as 0.1 g L -1 dose caused 24%<br />
fresh weight reduction in water hyacinth within a week of exposure (Kathiresan,<br />
2000). Therefore, cut leaf bio-assay could be useful to detect allelopathic potential of<br />
plant products which otherwise may have been missed if whole plant assay was used.<br />
In contrast, the dose response study data revealed that lethal doses for large, medium,<br />
and small plants of water hyacinth were relatively closer. C. amboinicus at low (10 g<br />
L -1 ) dose caused death of the water hyacinth after 20 days whereas at high (25 g L -1 )<br />
dose caused death within one week.