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. 2016 Apr 20;47(3):563–570. doi: 10.1016/j.bjm.2016.04.009

Table 2.

Kinetic studies of chlorpyrifos degradation in various microbiologically active soils. The initial chlorpyrifos concentration was 200 mg kg−1 soil.

Soil treatment Regression equation Δk (d−1)A ΔV (mg kg−1 d−1)B T1/2 (d)D R2C
SS ln(Ct/C0) = −0.004t − 0.015 0.0053a 0.84a 130.7l 0.983
nSS ln(Ct/C0) = −0.013t + 0.025 0.0111b 2.01b 62.45k 0.985
PS ln(Ct/C0) = −0.016t + 0.042 0.0128a 2.27a 54.15d 0.982



SS + JCp4 ln(Ct/C0) = −0.063t + 0.231 0.0517e 4.57h 12.93e 0.941
nSS + JCp4 ln(Ct/C0) = −0.089t + 0.257 0.0688i 4.76j 10.07a 0.922
PS + JCp4 ln(Ct/C0) = −0.092t + 0.194 0.088c 5.69b 7.86a 0.944



SS + FCp1 ln(Ct/C0) = −0.058t + 0.159 0.0476g 4.40g 14.56f 0.953
nSS + FCp1 ln(Ct/C0) = −0.078t + 0.173 0.064h 4.76j 10.83b 0.972
PS + FCp1 ln(Ct/C0) = −0.076t + 0.141 0.079b 5.69b 8.77c 0.962

SS, sterilized soil; nSS, non-sterilized soil; PS, planted soil; +, inoculated with.

A

Linear equation between ln(Ct/C0) of chemical data and time yielded regression equation and regression coefficient (R2).

B

Degradation rate constant (k) calculated using Ct = C0 × ekt. Ct residual concentration of CP (mg kg−1).

C

Chlorpyrifos disappearance rate.

D

Disappearance time calculated by T1/2 = ln 2/k.