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. 2011 Mar 22;55(6):620–633. doi: 10.1093/annhyg/mer008

Table 7.

Correlation of urinary THPI measures with the original AHS pesticide exposure intensity algorithm and with the adjusted algorithm

THPI exposure measurea n %>LOD Original algorithm
Adjusted algorithm
βb P-value βb P-value
24-h conc., μg l−1 130 NAc 0.0001 1.0 0.0307 0.08
24-h mass, μg 130 NAc −0.0035 0.84 0.0284 0.14
Mass, first-morning, Day 1, μg 140 61.4 −0.011 0.63 0.0411 0.12
Conc., first-morning, Day 1, μg g−1 creatinine 140 61.4 0.0016 0.94 0.0498 0.04
Excretion rate, overnight (Day 0 to Day 1), μg h−1 117 59.8 −0.015 0.56 0.0367 0.15

Conc., concentration; LOD, limit of detection; NA, not applicable.

a

Urinary THPI levels previously reported in Hines et al. (2008).

b

The estimated regression coefficient and P-value were computed using MLE via PROC NLMIXED with person treated as a random effect. The data were left-censored at the LOD. The log-normal distribution was specified in the model. Use of MLE for treating censored data was not feasible for the 24-h urine measurements because several samples had been summed to create the 24-h value; instead, values below the LOD were replaced with LOD/2, the samples summed, and the β and P-value estimated via the PROC MIXED procedure with person treated as a random effect.

c

The percentage of days where all samples comprising the summed 24-h total had THPI levels below the LOD was 24% for airblast and 55% for hand spray.