Skip to main content
. Author manuscript; available in PMC: 2013 Oct 15.
Published in final edited form as: Environ Int. 2012 Jun 23;47:28–36. doi: 10.1016/j.envint.2012.06.002

Table 4.

Logistic regression (GEE) model of the variable sum of dimethyl-substituted metabolites (DMAP) below vs. above the limit of detection in the urine of schoolchildren in Talca Province Chile in December 2010 (summer) and May 2011 (fall).

DMAP* Coef. Std. Error Odds Ratio [95% Conf. Interval] p-value
Phosmet (a) 4.12 0.59 60.61 19.19 191.37 <0.0001
Distance from farms (b) 0.9 0.29 2.48 1.38 4.45 0.002
Pesticide at home(c) 1.44 0.48 3.48 1.37 8.85 0.009
Empedrado (d) 0.87 0.42 2.37 1.04 5.39 0.04
Talca (d) −0.38 0.37 0.66 0.31 1.36 0.26
San Clemente (d) −0.45 0.41 0.64 0.29 1.41 0.27
Time (e) −2.16 0.43 0.12 0.05 0.27 <0.0001
Constant 0.74 0.59

n of observations=369; n of groups=190

**

Sum of Dimethyl-substituted metabolites (DMAP) in the urine of schoolchildren dichotomized as below vs. above the Limit of Detection.

(a)

Variable related with exposure/not exposure to eating of vegetables/fruits with phosmet residues,

(b)

Distance of housing to farms that apply pesticides (Less or equal to 500m).

(c)

Use of OP pesticide fenitrothion at home.

(d)

County (reference=Maule).

(e)

Summer =1 (December 2010) or fall=0 (May 2011)