1 D), 4-chloro-2-15 methylphenoxy)acetic acid (MCPA), 4-(2,4-dichlorophenoxy)butanoic16 acid (2,4-DB),

2 -D) and 2-methyl-4-chlorophenoxyacetic acid (MCPA) were observed in soil.

3 ace and 4-chloro-2-methylphenoxyacetic acid (MCPA) herbicide was studied using density functional the

4 rbicide 4-chloro-2-methylphenoxyacetic acid (MCPA) in response to differently aggregated distribution

5 rbicide 4-chloro-2-methylphenoxyacetic acid (MCPA) was revealed.

6              Different surface OH groups and MCPA proton states were used to mimic the strong effects

7 quantified by the spatial covariance between MCPA and degraders.

8 ron + iodosulfuron + thiencarbazone, 2,4-D + MCPA, and acetochlor, in controlling Amaranthus retrofle

9          Rate constants of 0.1-1.3 h(-1) for MCPA, 2,4-D, mecoprop, atenolol, and diclofenac, corresp

10  the drug carbamazepine, while the herbicide MCPA (2-methyl-4-chloro-phenoxyacetic acid) and the drug

11 e potential for degradation of the herbicide MCPA in three horizons of an agricultural soil.

12 ced macroscopic degradation rates, increased MCPA leaching, and prolonged the persistence of residual

13 entate inner-sphere complex with the neutral MCPA molecule were found to be the most energetically st

14 have negligible consequences for the fate of MCPA, but strong clustering of degraders can delay pesti

15 ) compound-specific isotope fractionation of MCPA (4-chloro-2-methylphenoxyacetic acid) and 2,4-D (2,

16                            The incubation of MCPA in the presence of this material yielded an herbici

17 g, and prolonged the persistence of residual MCPA.

18 e sharing of the carbonyl oxygen between the MCPA carboxylate group and a singly coordinated surface

19    A two-step mechanism was proposed for the MCPA removal, in which a reversible first-order adsorpti

20            The nature of the products of the MCPA catalytic degradation as well as the reaction condi

21 al topsoil, we also tested the effect of the MCPA concentration on the mineralization kinetics.