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. Author manuscript; available in PMC: 2020 May 1.
Published in final edited form as: Environ Res. 2020 Feb 8;184:109243. doi: 10.1016/j.envres.2020.109243

Table 3.

Description of pesticide concentrations measured in PUF from passive air sampling (PAS) for proximal (n = 40, schools = 10) and non-proximal schools (n = 8, schools = 2) during four periods of, on average, 6.7 weeks (SD = 1.9, range: 3.9–12.1), from June 2010 to October 2011, ISA study, Matina County, Costa Rica.

Pesticides LOD (ng/m3) Overall % > LOD Overall ICC Proximal schools (ng/m3) (n = 40, schools = 10) Non-proximal schools (ng/m3) (n = 8, schools = 2)

% > LOD Mean (SD) Min p10 p25 p50 p75 p90 Max % > LOD Mean (SD) Min p10 p25 p50 p75 p90 max
Insecticides
Chlorpyrifosa 0.5 98% 0.80 100% 18.2 (6.3) 6.1 10.7 13.4 18.4 22.0 25.9 36.1 88% 3.5 (3.8) < 0.5 < 0.5 0.6 2.1 5.4 11.4 11.4
Diazinon 0.3 31% 28% 0.6 (1.0) < 0.3 < 0.3 < 0.3 < 0.3 0.7 2.8 4.0 50% 1.2 (1.3) < 0.3 < 0.3 < 0.3 0.9 2.0 3.8 3.8
Nematicides
Etoprophos 0.5 81% 0.00 85% 5.5 (10.9) < 0.5 < 0.5 0.6 1.6 4.8 18.7 60.9 63% 2.2 (3.0) < 0.5 < 0.5 < 0.5 0.7 4.5 8.2 8.2
Terbufos 3.0 17% 20% 6.2 (13.7) < 3.0 < 3.0 < 3.0 < 3.0 < 3.0 16.0 61.7 0%
Terbufos sulfone 0.5 56% 60% 6.3 (8.0) < 0.5 < 0.5 < 0.5 2.6 10.7 21.3 28.7 38% 1.2 (1.9) < 0.5 < 0.5 < 0.5 < 0.5 1.5 6.1 6.1
Fungicides
Pyrimethanilb 0.5 81% 0.80 90% 5.4 (6.9) < 0.5 < 0.5 1.0 1.7 8.3 19.1 22.2 38% 0.4 (0.2) < 0.5 < 0.5 < 0.5 < 0.5 0.5 0.7 0.7
Chlorothalonilc c 48% 48% - - - - - - - - 50% - - - - - - - -
Fenpropimorphd 1.5 31% 38% 2.3 (3.5) < 1.5 < 1.5 < 1.5 < 1.5 2.2 5.1 21.0 0%
Spiroxamine 3.0 10% 13% 5.5 (12.1) < 3.0 < 3.0 < 3.0 < 3.0 < 3.0 21.4 61.9 0%
Difenoconazole 1.0 6% 8% 1.3 (3.4) < 1.0 < 1.0 < 1.0 < 1.0 < 1.0 0.5 21.3 0%
Epoxiconazole 1.0 27% 33% 3.1 (4.5) 2.5 < 1.0 < 1.0 < 1.0 4.3 10.6 15.9 0%
a

Concentrations of proximal schools were higher and more frequently detected than non-proximal schools: Student’s t-test p<0.0001, Pearson Chi-Square p <0.05.

b

Concentrations of proximal schools higher and more frequently detected than non-proximal schools: Wilcoxon/Kruskal Wallis p<0.0001, Pearson Chi-Square p<0.001.

c

Chlorothalonil concentrations could not be quantified because it was degraded partially by acetone hexane used to extract the sample.

d

Concentrations of proximal schools more frequently detected than non-proximal schools: Pearson Chi-Square p<0.05.