Determination of soil biodegradation half-lives from simulation testing under aerobic laboratory conditions: a kinetic model approach.

A kinetic model approach for determination of biodegradation half-lives from soil simulation testing is presented. The model describes transformation of the parent compound to metabolites and formation of bound (non-extractable) residues as well as mineralization in soil under aerobic laboratory conditions. Experimental data for several pesticide compounds from various soil simulation tests are used for fitting kinetic rate constants. Formation of bound residues, either from parent or metabolites or from both, can be described by first-order kinetics for all examined compounds. Correlation of kinetic rate constants of primary degradation and formation of bound residues from parent compound suggests a common mechanism, presumably co-metabolic microbial activity, for both processes. Inverse modelling allows for estimation of primary degradation half-life DegT50 instead of disappearance time DT50. Application of the DegT50 approach in PBT assessment might result in a different persistent classification for which the developed model delivers an appropriate evaluation tool.

[1]  D. Barraclough,et al.  Bound residues: environmental solution or future problem? , 2005, Environmental pollution.

[2]  Martin Scheringer,et al.  Persistence and Spatial Range as Endpoints of an Exposure-Based Assessment of Organic Chemicals , 1996 .

[3]  O. Richter,et al.  Guidance Document on Estimating Persistence and Degradation Kinetics from Environmental Fate Studies on Pesticides in EU Registration , 2006 .

[4]  P. Schröder,et al.  Formation, characterization and release of non-extractable residues of [14C] -labeled organic xenobiotics in soils , 1998, Environmental science and pollution research international.

[5]  E. Barriuso,et al.  Incorporation of pesticides by soil micro-organisms as a way of bound residues formation , 2004 .

[6]  Hari K. Iyer,et al.  Model Discrimination for Nonlinear Regression Models , 1990 .

[7]  Robert Boethling,et al.  Estimating biodegradation half-lives for use in chemical screening. , 2006, Chemosphere.

[8]  Sac-fry Stages,et al.  OECD GUIDELINE FOR TESTING OF CHEMICALS , 2002 .

[9]  B. Diekkrüger,et al.  Modelling the microbial breakdown of pesticides in soil using a parameter estimation technique , 1994 .

[10]  M. Alexander,et al.  Aging, bioavailability, and overestimation of risk from environmental pollutants , 2000 .

[11]  Frank Wania,et al.  Evaluating environmental persistence , 1998 .

[12]  Colin D. Brown,et al.  Evaluation of methods to derive pesticide degradation parameters for regulatory modelling , 2001, Biology and Fertility of Soils.

[13]  K. Jones,et al.  Bioavailability of persistent organic pollutants in soils and sediments--a perspective on mechanisms, consequences and assessment. , 2000, Environmental pollution.

[14]  M. Matthies,et al.  Mineralization kinetics of chemicals in soils in relation to environmental conditions. , 1996, Ecotoxicology and environmental safety.