School of Agriculture, Food and Ecosystem Sciences - Theses
Permanent URI for this collection
Search Results
1 - 2 of 2
-
ItemDevelopment of a technique to overcome the problems associated with high dieldrin concentration in soil( 1995)Degradation of dieldrin in soils was studied in laboratory experiments. Application of powdered zinc in dilute acetic acid, nickel chloride in sodium borohydride and potassium tertiary butoxide in dimethyl sulphoxide to pots containing solonized brown soil, podzol, red brown earth, grey clay, alluvial and krasnozem soils had little effect on the rate of degradation. Application of potassium tertiary butoxide in dimethyl sulphoxide solution to soil samples containing dieldrin achieved a rapid decrease in pesticide concentration in some cases. However, the undesirable effects of these chemicals on soil fauna and flora and on soil physical properties indicate that their use in the field could not be recommended. Adsorption of dieldrin (as illustrated by the Freundlich constant) was greater in red brown earth and grey clay soils than in the solonized brown soil. The rate of dieldrin desorption from these soils was found to be in the order solonized brown soil > red brown earth > grey clay. Dieldrin uptake by plants was determined, with carrots being found to absorb the greatest quantities of dieldrin. All plant species took up considerably more dieldrin when grown on sand than on clay. Lupin translocated very little dieldrin to the plant tops. The amounts of insecticide translocated to the plant tops were not proportional to the amounts of insecticide present in soil. Brown coal was found to be a very good dieldrin adsorbent. Addition of brown coal in the proportion 4:1 soil:brown coal reduced the uptake of dieldrin by carrots from contaminated soil to acceptable levels. Both mice and sheep did not show any obvious symptoms of ill-health after being fed diets containing 10 ?g g-1 dieldrin plus 10% brown coal for 16 weeks. Animals fed diets containing 10% brown coal and 10 ?g g-1 dieldrin had lower concentrations of the insecticide in the internal organs. The concentration of dieldrin in the kidney fat of sheep fed this diet was above the maximum limit suggested to apply to animals raised for human consumption.
-
ItemThe activity of glyphosate and other herbicides in soil( 1989)The effects of herbicides on a legume Rhizobium symbiosis were studied in laboratory experiments. Root applications of all herbicides examined reduced nodulation of legumes grown in aqueous nutrient media. The growth of Rhizobium trifolii TA1 was reduced by 2 - 20 mg ai 1-1 of diquat, 2 mg ai 1-1 of paraquat, 10 mg ai 14 of glyphosate and 2 mg ail-1 of chlorsulfuron. No other herbicide affected rhizobia growth when applied at 2 - 20 mg ai l-1 of nutrient medium. Inoculation with TA1 pre-treated with amitrole, atrazine or glyphosate decreased nodulation of sub-clover plants indicating that these herbicides may affect the nodulation potential of certain strains of Rhizobium. Residues of 2,4-D, amitrole, diquat, trifluralin and glyphosate persisted in a Walpeup sandy loam in sufficient concentration for four months after application to soil to affect growth and symbiotic activity of sub-clover. The behaviour of glyphosate in soil, under various conditions was studied in the laboratory. Adsorption of glyphosate as depicted by Freundlich K constant was greater in an acid soil than in three alkaline soils and values for this constant ranged from 8 - 67.8 at 23.5C and 4.3 - 57.8 at 10C. Rate of decomposition of 14C-glyphosate at 25C decreased slowly over the experimental period in all soils. Two compartments of adsorbed glyphosate in soil were identified as labile glyphosate and non-labile glyphosate and these reflected the strength of adsorption of the chemical. The amount of glyphosate in the labile firm for the soils ranged from 24 - 34.5% of the total and half-life ranged from 6 - 9 days. The amount of glyphosate in the non-labile form for soils ranged from 67 . 75% of the total and half-life ranged from 222 to 835 days. At 10C, the two compartments of glyphosate adsorption were identified for the Walpeup and Rutherglen soils but only one compartment could be identified in the Wimmera and Culgoa soils. Methodology was developed to permit extraction and analysis of glyphosate and AMPA in soil. Recovery of glyphosate from soils where time between fortification and extraction was only 30 sec. was 84.6 - 104%. However where extraction was delayed 13 hours, recoveries were 47.6 - 66.8%. The extractant (0.1 M triethylamine) was shown to be unable to desorb adsorbed glyphosate. Studies revealed that at 25C, the pool of extractable glyphosate was rapidly depleted by decomposition. At this temperature, the pool of extractable glyphosate was supplemented by slow desorption of non-labile glyphosate for each soil. At 10C, depletion of the pool of extractable glyphosate was considerably slower. For the Walpeup and Rutherglen soils, the rate of desorption of glyphosate from the non-labile pool was less than the rate of loss by decomposition of the herbicide. Rate of desorption of non-labile glyphosate in the Wimmera soil was shown to be the same as the rate of loss by decomposition of the herbicide. Loss of extractable glyphosate in the Culgoa soil occurred by decomposition and by slow adsorption of extractable herbicide from the labile to the non-labile form. The effects of residues of glyphosate in the field following an autumn and a summer application were investigated at selected field sites. Following the autumn application, phytotoxic activity of glyphosate was observed in sub-clover plants growing at the Walpeup and Culgoa sites but not at the Wimmera site. Growth and nodulation of plants sown up to 4 weeks after herbicide treatment were reduced at the Walpeup site. Only nodulation of plants sown up to 4 weeks after treatment was reduced at the Culgoa site. Results suggest that residues of glyphosate are only likely to significantly affect the growth of susceptible plants during winter on sandy soils. Following summer application of glyphosate, no phytotoxic activity of the herbicide was observed for sub-clover plants grown in the Walpeup sandy loam. Results suggest that in a hot summer, it is unlikely that residues of glyphosate in any soil would cause significant damage to plant growth.