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Aeration, effect, degradation

Aeration, effect, degradation In water-soil system, 59t Aerial pesticide applicators, volume and characteristics of wastewater, 154t,196 Aerobic pathway, trlfluralln degradation, 39... [Pg.354]

Table I Summary of the Effect of Ambient Conditions, Aeration at 1 L/min, Peptone Nutrient at 0.1 Wt. %, Concentration, and the Presence of 5 Other Pesticides (Mix) on the Degradation of Six Pesticides and Two Decomposition Products... [Pg.59]

The effects of all combinations of aeration and nutrients are easily discernable on the right hand YES count column. The increase from 10 to 14 degradation units on a scale of 0 to 32 when aeration was incorporated must be weighed carefully against the cost of adding aeration to the containers. Nutrients had an inhibitory, if any, effect on pesticide degradation in general. [Pg.60]

When PCP solution (Id4 M) under continuous air bubbling is subjected to ultrasound effects, the characteristic absorption bands decrease and the treatment leads to a complex mixture of products. Carbon-chlorine bonds are rapidly cleaved, and after a 150-min sonication time, 90% of the chlorine is recovered in the solution as chloride ions. PCP transformation in aerated solution occurs together with nitrite and nitrate formation. Carbon dioxide is a product of PCP degradation, and it has long been recognized as an inhibitor for sonochemical reactions. [Pg.455]

The effect of the halogen substituent (fluoro, chloro, bromo and iodo) on the yield and mechanism of 4-halophenol photolysis was investigated by Durand et al. [24], Transient spectroscopy in aerated aqueous solutions indicated the formation of p-benzoquinone O-oxide from each derivative except 4-iodophenol for which no transients were detected p-benzoquinone and hydroquinone were found as photoproducts for all four compounds. It was concluded that the carbene mechanism was valid for the whole series. Under continuous irradiation, the 4-halophenol degradation quantum yields were determined to be

fluorescence lifetimes decreased in the same order, from 2.1 ns for 4-fluorophenol to 0.4 ns for 4-chlorophenol and < 0.1 ns for 4-bromophenol. [Pg.166]


See other pages where Aeration, effect, degradation is mentioned: [Pg.2]    [Pg.158]    [Pg.29]    [Pg.432]    [Pg.458]    [Pg.458]    [Pg.172]    [Pg.647]    [Pg.275]    [Pg.102]    [Pg.360]    [Pg.26]    [Pg.551]    [Pg.431]    [Pg.56]    [Pg.56]    [Pg.561]    [Pg.172]    [Pg.13]    [Pg.17]    [Pg.29]    [Pg.102]    [Pg.298]    [Pg.78]    [Pg.221]    [Pg.226]    [Pg.228]    [Pg.232]    [Pg.280]    [Pg.1680]    [Pg.29]    [Pg.251]    [Pg.2471]    [Pg.133]    [Pg.611]    [Pg.37]    [Pg.193]    [Pg.813]    [Pg.211]    [Pg.80]    [Pg.330]    [Pg.323]    [Pg.158]    [Pg.2452]    [Pg.435]   


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Aeration

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Degradation effects

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