Shield
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This page is a study.
The page identifier is Op_en4434 |
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Moderator:Jouni (see all) |
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Scope
SHIELD study: Home indoor, school indoor, school outdoor and personal exposure to VOCs with 113 children age of 7 to 13 years in 2000. [1]
Definition
- id: study1
- Abbreviation: SHIELD
Data
VOC_P_1 | study1 | Chloroform concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Benzene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Ethylbenzene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Styrene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | 1,4-dichlorobenzene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Toluene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Tetrachloroethylene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Carbon tetrachloride concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | D-limonene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Methylene chloride concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | A-pinene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | B-pinene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
VOC_P_1 | study1 | Tichloroethene concentration (ug/m3) distributions for personal exposure for 113 children in Minneapolis in winter and spring 2000 | Samples (2-day average) collected concurrently for a single child in each household (winter, n=93; spring, n=88). Quantiles were calculated using weights to adjust for nonselection and nonresponse. | MP |
Result
{{#opasnet_base_link:Op_en4434}}
CAS | location | Season | N | % > DL | Median | 10th | 90th |
67-66-3 | MP | Winter | 113 | 100 | 0.7 | 0.3 | 2.1 |
67-66-3 | MP | Spring | 113 | 98.9 | 1.2 | 0.5 | 2.9 |
71-43-2 | MP | Winter | 113 | 100 | 2.1 | 0.7 | 6.5 |
71-43-2 | MP | Spring | 113 | 100 | 1.5 | 0.7 | 4.2 |
100-41-4 | MP | Winter | 113 | 100 | 1 | 0.6 | 2.4 |
100-41-4 | MP | Spring | 113 | 100 | 0.9 | 0.5 | 2 |
100-42-5 | MP | Winter | 113 | 93.5 | 0.5 | 0.2 | 1.2 |
100-42-5 | MP | Spring | 113 | 85.2 | 0.5 | 0.1 | 1.2 |
106-46-7 | MP | Winter | 113 | 92.5 | 1 | 0.2 | 167.2 |
106-46-7 | MP | Spring | 113 | 93.2 | 1.3 | 0.2 | 87.2 |
108-88-3 | MP | Winter | 113 | 100 | 7.7 | 3.4 | 17.7 |
108-88-3 | MP | Spring | 113 | 100 | 7.7 | 3.1 | 18 |
127-18-4 | MP | Winter | 113 | 100 | 0.4 | 0.2 | 1.3 |
127-18-4 | MP | Spring | 113 | 96.6 | 0.4 | 0.2 | 0.9 |
56-23-5 | MP | Winter | 113 | 100 | 0.5 | 0.4 | 0.6 |
56-23-5 | MP | Spring | 113 | 100 | 0.5 | 0.4 | 0.6 |
138-86-3 | MP | Winter | 113 | 100 | 24.7 | 7.5 | 159.5 |
138-86-3 | MP | Spring | 113 | 100 | 22.2 | 8.3 | 110 |
75-09-2 | MP | Winter | 113 | 19.4 | 0.4 | 0.2 | 1.3 |
75-09-2 | MP | Spring | 113 | 17 | 0.3 | 0.2 | 1.3 |
80-56-8 | MP | Winter | 113 | 100 | 1.9 | 0.7 | 5.1 |
80-56-8 | MP | Spring | 113 | 100 | 1.8 | 0.6 | 5.4 |
127-91-3 | MP | Winter | 113 | 93.5 | 1.7 | 0.4 | 11.5 |
127-91-3 | MP | Spring | 113 | 87.5 | 1.1 | 0.1 | 5.3 |
79-01-6 | MP | Winter | 113 | 90.3 | 0.3 | 0.1 | 0.8 |
79-01-6 | MP | Spring | 113 | 72.7 | 0.2 | 0.1 | 0.8 |
See also
References
- ↑ Adgate et al., Environ. Health Perspect. 112 (2004), 1386-1392
Related files
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