Sorption and desorption kinetics of diuron, fluometuron, prometryn and pyrithiobac sodium in soils

Citation
S. Baskaran et Ir. Kennedy, Sorption and desorption kinetics of diuron, fluometuron, prometryn and pyrithiobac sodium in soils, J ENVIR S B, 34(6), 1999, pp. 943-963
Citations number
41
Categorie Soggetti
Environment/Ecology
Journal title
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART B-PESTICIDES FOOD CONTAMINANTS AND AGRICULTURAL WASTES
ISSN journal
03601234 → ACNP
Volume
34
Issue
6
Year of publication
1999
Pages
943 - 963
Database
ISI
SICI code
0360-1234(1999)34:6<943:SADKOD>2.0.ZU;2-R
Abstract
The sorption and desorption characteristics of four herbicides (diuron, flu ometuron, prometryn and pyrithiobac-sodium) in three different cotton growi ng soils of Australia was investigated. Kinetics and equilibrium sorption a nd desorption isotherms were determined using the batch equilibrium techniq ue. Sorption was rapid (> 80% in 2 h) and sorption equilibrium was achieved within a short period of time (ca 4 h) for all herbicides. Sorption isothe rms of the four herbicides were described by Freundlich equation with an r( 2) value > 0.98. The herbicide sorption as measured by the distribution coe fficient (K-d) values ranged from 3.24 to 5.71 L/kg for diuron, 0.44 to 1.1 3 L/kg for fluometuron, 1.78 to 6.04 L/kg for prometryn and 0.22 to 0.59 L/ kg for pyrithiobac-sodium. Sorption of herbicides was higher in the Mores s oil than in Narrabri and Wee Waa soils. When the K-d values were normalised to organic carbon content of the soils (K-oc), it suggested that the affin ity of the herbicides to the organic carbon increased in the order: pyrithi obac-sodium < fluometuron < prometryn < diuron. The desorption isotherms we re also adequately described by the Freundlich equation. For desorption, al l herbicides exhibited hysteresis and the hysteresis was stronger for highl y sorbed herbicides (diuron and prometryn) than the weakly sorbed herbicide s (fluometuron and pyrithiobac-sodium). Hysteresis was also quantified as t he percentage of sorbed herbicides which is not released during the desorpt ion step (omega = [n(ad)/n(de)-1] x 100). Soil type and initial concentrati on had significant effect on omega. The effect of sorption and desorption p roperties of these four herbicides on the off-site transport to contaminate surface and groundwater are also discussed in this paper.