scholarly journals Influence of pesticide concentration on their heterogeneous atmospheric degradation by ozone

Chemosphere ◽  
2019 ◽  
Vol 228 ◽  
pp. 75-82 ◽  
Author(s):  
Coraline Mattei ◽  
Julien Dupont ◽  
Henri Wortham ◽  
Etienne Quivet
2017 ◽  
Vol 121 (13) ◽  
pp. 2610-2619 ◽  
Author(s):  
Lin Cheng ◽  
Xiaojuan Yu ◽  
Kun Zhao ◽  
Hua Hou ◽  
Baoshan Wang

2000 ◽  
Vol 104 (13) ◽  
pp. 2925-2930 ◽  
Author(s):  
M. Mashino ◽  
M. Kawasaki ◽  
T. J. Wallington ◽  
M. D. Hurley

2019 ◽  
Vol 716 ◽  
pp. 35-41 ◽  
Author(s):  
Nand Kishor Gour ◽  
Nandini Priyam Rajkumari ◽  
Ramesh Chandra Deka ◽  
Subrata Paul ◽  
Ajanta Deka

2010 ◽  
Vol 62 (11) ◽  
pp. 2579-2589 ◽  
Author(s):  
Koji Tani ◽  
Yoshihiko Matsui ◽  
Kentaro Narita ◽  
Koichi Ohno ◽  
Taku Matsushita

We quantitatively evaluated the factors that affect the concentrations of rice-farming pesticides (an herbicide and a fungicide) in river water by a sensitivity analysis using a diffuse pollution hydrologic model. Pesticide degradation and adsorption in paddy soil affected concentrations of the herbicide pretilachlor but did not affect concentrations of the fungicide isoprothiolane. We attributed this difference to the timing of pesticide application in relation to irrigation and drainage of the rice paddy fields. The herbicide was applied more than a month before water drainage of the fields and runoff was gradual over a long period of time, whereas the fungicide was applied shortly before drainage and runoff was rapid. However, the effects of degradability-in-water on the herbicide and fungicide concentrations were similar, with concentrations decreasing only when the rate constant of degradation in water was large. We also evaluated the effects of intermittent irrigation methods (irrigation/artificial drainage or irrigation/percolation) on pesticide concentrations in river water. The runoff of the fungicide, which is applied near or in the period of intermittent irrigation, notably decreased when the method of irrigation/artificial drainage was changed to irrigation/percolation. In a sensitivity analysis evaluating the synergy effect of degradation and adsorbability in soil, the degradation rate constant in soil greatly affected pesticide concentration when the adsorption coefficient was small but did not affect pesticide concentration when the adsorption coefficient was large. The pesticide concentration in the river water substantially decreased when either or both the degradation rate constant in soil and adsorption coefficient was large.


2015 ◽  
Vol 115 (10) ◽  
pp. 3704-3759 ◽  
Author(s):  
James B. Burkholder ◽  
R. A. Cox ◽  
A. R. Ravishankara

2005 ◽  
Vol 109 (48) ◽  
pp. 10903-10909 ◽  
Author(s):  
Elena Jiménez ◽  
Beatriz Lanza ◽  
Andrés Garzón ◽  
Bernabé Ballesteros ◽  
José Albaladejo

Weed Science ◽  
1981 ◽  
Vol 29 (2) ◽  
pp. 147-155 ◽  
Author(s):  
R. G. Nash

Two or more pesticides together may produce a growth response in plants that is not predictable by their individual or independent toxicities. This unpredicted (dependent) response results from an interaction, a concept that usually is not easily interpreted. Dependent responses are further complicated by the fact that they can be either synergistic or antagonistic. Several methods exist for identifying and measuring phytotoxic interactions. Nearly all methods have certain shortcomings, however. Additive and multiplicative models (mathematical expressions) are the two basic approaches to determining pesticide interactions. The two-parameter, isobole, and calculus methods axe additive; whereas, Colby and regression estimate are multiplicative models. Regression estimate analysis considers deviations due to experimental errors, and a statistical significance can be attached to the interaction magnitude, thereby overcoming the deficiencies of the Colby method, but both methods seem to be limited to response data in which the combined pesticide concentration is the sum of the individual pesticide concentrations. The two-parameter method seems to be limited to response data in which the combined concentration is equal to the individual pesticide concentration and to response data in which a pesticide concentration necessary to produce a 50% of control value is interpolated rather than extrapolated. The calculus method is a mathematical expression of the growth response, and interaction is measured by derivation of the equation obtained. The calculus method is difficult to interpret and has a major weakness because it depends upon the multiple regression equation of the observed data. The regression estimate method is recommended as a reasonable approach to interpretation of interaction type data, with a SAS language computer program available from the author.


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