| Literature DB >> 23937118 |
Kim de Jong1, H Marike Boezen, Nick H T ten Hacken, Dirkje S Postma, Judith M Vonk.
Abstract
BACKGROUND: Lung growth in utero and lung function loss during adulthood can be affected by exposure to environmental tobacco smoke (ETS). The underlying mechanisms have not been fully elucidated. Both ETS exposure and single nucleotide polymorphisms (SNPs) in Glutathione S-Transferase (GST) Omega genes have been associated with the level of lung function. This study aimed to assess if GSTO SNPs interact with ETS exposure in utero and during adulthood on the level of lung function during adulthood.Entities:
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Year: 2013 PMID: 23937118 PMCID: PMC3751364 DOI: 10.1186/1465-9921-14-83
Source DB: PubMed Journal: Respir Res ISSN: 1465-9921
Characteristics participants included in sample 1 and sample 2
| 8128 | 5308 | |
| 3483 (43) | 2133 (40) | |
| 47 (18–89) | 48 (21–90) | |
| | | |
| Never, n (%) | 3277 (40) | 2154 (41) |
| Ex, n (%) [median (min-max)] | 2882 (36) [8 (0–86)] | 2014 (39) [7 (0–100)] |
| Current, n (%) [median (min-max)] | 1936 (24) [15 (0–100)] | 1065 (20) [16 (0–81)] |
| | | |
| | 867 (13) | 559 (13) |
| ≥ 1 hour/day | 1788 (24) | 1029 (21) |
| At the workplace | 565 (7) | 303 (6) |
| | | |
| FEV1 (ml) | 3412 (831) | 3331 (840) |
| FEV1pp (%)1 | 102 (14) | 102 (14) |
| FEV1/FVC (%) | 77 (7) | 76 (7) |
| 7635 | 5070 |
The second sample (sample 2) was used to verify the initial findings from sample 1, both samples are part of the LifeLines population-based cohort study.
1 FEV1pp = FEV1 as percentage predicted based on reference equations constructed by Quanjer et al. [28].
Figure 1Mean FEV(liters) for non-exposed and exposed subjects stratified by smoking status (never/ever smoker). The analysis was adjusted for sex, current smoking, packyears smoked, and centered for group specific (never/ever smokers) means for age, height and weight. A: In utero ETS (no/yes). B: daily ETS exposure (≥1 hr). C: ETS exposure at the workplace (no/yes).
Figure 2Mean FEV(liters) for non-exposed and ETS exposed subjects stratified by genotype for the two genotyped SNPs rs1147611 and rs156699.GSTO1 SNP rs1147611 (upper row) and GSTO2 SNP rs156699 (lower row). The analysis was adjusted for sex, current, ex-smoking, packyears smoked, and centered for mean age, height and weight. A: In utero ETS (no/yes). B: daily ETS exposure (≥1 hr). C: ETS exposure at the workplace (no/yes).
Effects for ETS exposure (no/yes), the SNPs, and the interaction of SNPs (recessive model) with ETS exposure on FEV
| | | |||
|---|---|---|---|---|
| | N, in analysis | 6003 | 2576 | 3427 |
| −33 (−69 ; 4) | −25 (−81 ; 32) | −43 (91 ; 5) | ||
| | rs4925 | −33 (−77 ; 10) | −1 (65 ; 63) | −58 (−117 ; 1) |
| | ETS*rs4925 | $ | 161 (−18 ; 340) | |
| − | −32 (−89 ; 26) | − | ||
| | rs1147611 | −22 (−58 ; 14) | 6 (−46 ; 58) | −46 (−96 ; 3) |
| | ETS*rs1147611 | $ | $ | |
| − | −28 (−85 ; 30) | − | ||
| | rs156697 | −28 (−64 ; 9) | 9 (−44 ; 62) | − |
| | ETS*rs156697 | $ | $ | |
| −33 (−70 ; 3) | −24 (−81 ; 32) | −45 (−93 ; 4) | ||
| | rs156699 | −30 (−70 ; 10) | −9 (−66 ; 49) | −48 (−104 ; 7) |
| ETS*rs156699 | $ | 143 (−15 ; 300) | ||
The linear regression model for the whole group was adjusted for sex, age, height, weight, current, ex-smoking and packyears smoked. Consequently we stratified by smoking status (never/ever) and adjusted for the other possible confounders.
*p-value<0.05 **p-value<0.01 *** p-value<0.001.
$significant after FDR correction for multiple testing.
Effects for daily ETS exposure (≥1 hr), the SNPs, and the interaction of SNPs (recessive model) with daily ETS exposure on FEV
| | | |||
|---|---|---|---|---|
| | 6822 | 2901 | 3921 | |
| Daily ETS | −27 (−56;3) | −31 (−79 ; 16) | −28 (−66 ; 10) | |
| | rs4925 | 61 (−37;49) | −46 (−106 ; 15) | |
| | ETS*rs4925 | − | −153 (−306 ; 0) | −72 (−192 ; 47) |
| Daily ETS | −25 (−55;5) | −28 (−77 ; 22) | −28 (−67 ; 11) | |
| | rs1147611 | 15 (−22;51) | −24 (−75 ; 28) | |
| | ETS*rs1147611 | − | −122 (−247 ; 3) | −45 (−147 ; 52) |
| Daily ETS | −29 (−59;1) | −28 (−77 ; 22) | −34 (−73 ; 5) | |
| | rs156697 | 6 (−31;43) | −40 (−93 ; 12) | |
| | ETS*rs156697 | −59 (−137;19) | − | −2 (−104 ; 99) |
| Daily ETS | −26 (−56;3) | −29 (−78 ; 19) | −28 (−66 ; 10) | |
| | rs156699 | 6 (−35;46) | 44 (−12 ; 100) | −29 (−86 ; 28) |
| ETS*rs156699 | − | −133 (−268 ; 2) | −56 (−165 ; 54) | |
The linear regression model for the whole group was adjusted for sex, age, height, weight, current, ex-smoking and packyears smoked. Consequently we stratified by smoking status (never/ever) and adjusted for the other possible confounders.
*p-value<0.05.
There were no significant effects after FDR correction for multiple testing.
Effects for workplace ETS exposure (n/y), the SNPs, and the interaction of SNPs (recessive model) with workplace ETS exposure on FEV
| | 7149 | 3051 | 4098 | |
| Workplace ETS | −26 (−71 ; 20) | −51 (−126 ; 25) | −17 (−73 ; 40) | |
| | rs4925 | 8 (−34 ; 50) | 78 (17 ; 138) | −48 (−105 ; 9) |
| | ETS*rs4925 | $- | $- | −84 (−268 ; 100) |
| Workplace ETS | −22 (−68 ; 25) | −41 (−117 ; 36) | −15 (−73 ; 43) | |
| | rs1147611 | 8 (−27 ; 42) | 49 (0 ; 99)# | −29 (−78 ; 19) |
| | ETS*rs1147611 | $- | $- | −65 (−218 ; 87) |
| Workplace ETS | −21 (−67 ; 25) | −41 (−118 ; 36) | −14 (−72 ; 44) | |
| | rs156697 | 8 (−28 ; 44) | 50 (−1 ; 100) | −29 (−79 ; 20) |
| | ETS*rs156697 | $- | $- | −84 (−245 ; 77) |
| Workplace ETS | −17 (−63 ; 28) | −41 (−117 ; 35) | −9 (−66 ; 48) | |
| | rs156699 | 6 (−32 ; 45) | 43 (−12 ; 98) | −26 (−79 ; 28) |
| ETS*rs156699 | $- | $- | −140 (−311 ; 30) | |
The linear regression model for the whole group was adjusted for sex, age, height, weight, current, ex-smoking and packyears smoked. Consequently we stratified by smoking status (never/ever) and adjusted for the other possible confounders.
*p-value<0.05 **p-value<0.01.
$significant after FDR correction for multiple testing.
Verification of the interaction of SNPs (recessive model) with different types of ETS exposure on FEVin sample 2
| | 3914 | 4527 | 4702 | |
| ETS | −45 (−91 ; 1) | − | −40 (−98 ; 18) | |
| | rs4925 | 11 (−43 ; 65) | 15 (−36 ; 66) | 33 (−17 ; 83) |
| | ETS*rs4925 | 111 (−32 ; 253) | 25 (−93 ; 142) | −163 (−390 ; 65) |
| ETS | − | − | −40 (−100 ; 20) | |
| | rs1147611 | 4 (−40 ; 47) | 21 (−21 ; 63) | 26 (−15 ; 67) |
| | ETS*rs1147611 | 94 (−22 ; 211) | 5 (−89 ; 98) | −87 (−254 ; 81) |
| ETS | − | − | −38 (−98 ; 21) | |
| | rs156697 | 2 (−42 ; 46) | 17 (−25 ; 59) | 28 (−13 ; 69) |
| | ETS*rs156697 | 17 (−79 ; 113) | −99 (−269 ; 70) | |
| ETS | −46 (−92 ; 1) | − | −42 (−101 ; 17) | |
| | rs156699 | −9 (−58 ; 39) | 0 (−46 ; 47) | 10 (−35 ; 56) |
| ETS*rs156699 | 106 (−29 ; 241) | 9 (−97 ; 115) | −101 (−292 ; 91) | |
Effects for in utero ETS exposure (no/yes), daily ETS exposure (≥1 hr), workplace ETS exposure (no/yes), the SNPs, and the interaction of GSTO SNPs (recessive model) with different types of ETS exposure on FEV1 in sample 2 (verification). The linear regression model for the whole group was adjusted for sex, age, height, weight, current, ex-smoking and packyears smoked.
*p-value<0.05.