The effect of landuse on soil organic carbon chemistry and sorption of pesticides and metabolites.
Earlier studies had shown significant differences in sorption of nine pesticides in soils collected from two landuses (native vegetation and market gardens), which could not be explained on the basis of organic carbon content alone. Consequently it was hypothesised that the differences in sorption behaviour between the two landuses may be due to variation in the chemistry of the organic carbon. In this study the relationship between sorption behaviour of the nine chemicals and soil organic carbon chemistry, as determined by solid-state (13)C NMR spectroscopy, was investigated. No significant differences were found between the two landuses in the distribution of the four main spectral regions of the (13)C NMR spectra of soil OC, except for the carbonyl fraction (165-220ppm), which may reflect the low OC content of the soils from both landuses. For all chemicals, except prometryne, the most significant (P<0.01 or P<0.001) relationship between K(d) values and types of OC was found with the aromatic (110-165ppm) or the alkyl (0-45ppm) fraction. A comparison was made of the variability of K(d) values normalized over OC (i.e. K(oc)), alkyl, aromatic and alkyl+aromatic fractions. Expressing K(d) values for all chemicals, except azinphos methyl, in soils under native vegetation as K(alkyl) or K(aromatic) greatly decreased the variability compared with the K(oc) value. However in the cultivated soils only the sorption coefficients for DEA, DIA and fenamiphos showed a decrease in variability when expressed as K(alkyl) or K(aromatic). This reflected the stronger relationship between sorption coefficients and the alkyl and aromatic fraction of soil OC in soils from native vegetation compared with those determined from the market garden soils. The different relationships between sorption coefficients and types of OC of the two landuses also suggests that the type of aromatic and alkyl carbon under the two landuses is different and NMR characterisation of the OC was not sufficient to distinguish these differences.
Oliver
D P
DP
CSIRO Land and Water, PMB No. 2, Glen Osmond, South Australia 5064, Australia. danni.oliver@csiro.au
Baldock
J A
JA
Kookana
R S
RS
Grocke
S
S
D000327:Adsorption; D002244:Carbon / Q000737:chemistry*; D004784:Environmental Monitoring; D007700:Kinetics; D009682:Magnetic Resonance Spectroscopy; D008962:Models, Theoretical; D010575:Pesticides / Q000032:analysis / Q000737:chemistry*; D012989:Soil Pollutants / Q000032:analysis*
D010575:Pesticides; D012989:Soil Pollutants; D002244:Carbon