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. 2017 Jul 24;16:78. doi: 10.1186/s12940-017-0280-y

Associations of genetic variation in CASP3 gene with noise-induced hearing loss in a Chinese population: a case–control study

Yinyin Wu 1,#, Juntao Ni 1,#, Mingjian Qi 1, Chengjian Cao 2, Yuxian Shao 2, Liangwen Xu 1, Haiyan Ma 1,, Lei Yang 1,
PMCID: PMC5525200  PMID: 28738811

Abstract

Background

Noise-induced hearing loss (NIHL) is a complex disease caused by environmental and genetic risk factors. This study explored the relationship between the genetic variations in the CASP gene and the risk of developing NIHL among Chinese workers exposed to occupational noise.

Methods

A case–control study of 272 NIHL workers and 272 normal-hearing workers matched for age, sex and years of noise exposure was conducted. Fifteen single-nucleotide polymorphisms (SNP) in the CASP1, CASP3, CASP4, CASP5, CASP6, CASP8, CASP9, CASP10 and CASP14 genes were genotyped using the polymerase chain reaction–ligase detection reaction method. Using conditional logistic regression models, the adjusted odds ratios (ORs) and 95% confidence intervals (CIs) of genetic variations associated with NIHL risk were calculated.

Results

Two SNPs in the CASP3 gene were associated with NIHL risk. For rs1049216, TT genotype was associated with a decreased risk of NIHL (OR = 0.246, 95% CI = 0.069–0.886) when compared with the CC genotype. For rs6948, the AC and CC genotype were associated with a decreased NIHL risk (OR = 0.568, 95% CI = 0.352–0.916) compared with AA genotype. There were joint effects of working time and CASP3 polymorphisms on NIHL risk (P < 0.05).

Conclusions

Genetic variations in the CASP3 gene and the joint effects of working time and CASP3 polymorphisms may modify the risk of developing NIHL.

Electronic supplementary material

The online version of this article (doi:10.1186/s12940-017-0280-y) contains supplementary material, which is available to authorized users.

Keywords: Genetic susceptibility, CASP3, Single-nucleotide polymorphism/SNP, Noise-induced hearing loss/NIHL

Background

Long-term and high-intensity noise directly affects hearing and leads to noise-induced hearing loss (NIHL) [1]. Hearing loss is the most prevalent sensory organ disability worldwide. The World Health Organization (WHO) has estimated that the number of people with hearing disability was 42,000 in 1985, 120 million in 1995,250 million in 2001, and up to 360 million in 2011 [2]. In the United States, 10 million people have NIHL, and in China, the number of workers with NIHL has increased by 77.8% from 2010 to 2012 [3].

Besides noise exposure, there are many other risk factors of NIHL such as smoking, alcohol consumption, organic solvent exposure, high blood pressure, cholesterol, and sleeping problems [4, 5]. Genetic factors and gene-environment interactions might also play an important role in the development of NIHL. Researchers have observed that individuals have different outcomes of hearing damage, even exposed to similar levels of noise [6, 7].

The occurrence of NIHL is based on cochlear hair cell damage and death [8]. Apoptosis is one of the ways to cause hair cell death, which is a cell-independent and orderly death controlled by a specific gene [9, 10]. Caspase activation is the central link in apoptosis. Caspases are activated by stepwise hydrolysis under the influence of an apoptotic signal, and cleavage of cell structural and functional proteins causes apoptosis [11]. Many species of caspase have been founded, and can be divided into three categories, according to difference of cascade reaction in the upstream and downstream position and function. The first class is the apoptotic promoters, including caspase-8, −9 and −10, which are located upstream of the cascade reaction, and can self-activate and activate downstream caspases. The second class is the apoptotic effectors, including caspase-3 and -6, which are located downstream of the cascade reaction, and can be activated by the upstream promoter. Caspases that have been activated can act on the specific substrate to cause biochemical and morphological changes in cells, leading to apoptosis. The third class is associated with inflammation and plays a supporting role in death-receptor-mediated apoptosis, and includes caspase-1, −4, −5 and −14.

Given the important roles of caspases in apoptosis, we assumed that variants of these genes might be associated with the risk of NIHL in the Chinese population. To examine this hypothesis, we genotyped 15 single-nucleotide polymorphisms (SNP) in the CASP1, CASP3, CASP4, CASP5, CASP6, CASP8, CASP9, CASP10 and CASP14 genes in 272 NIHL workers and 272 normal-hearing workers, and analyzed the associations of these SNPs with NIHL. We also explored the interactions among these SNPs and noise exposure.

Methods

Participants

This study involved 272 NIHL workers and 272 normal-hearing workers who were recruited from a cross-sectional study of 1549 occupational noise-exposed workers, which was conducted between March 1 and December 31, 2014. These workers were exposed to continuous and steady occupational noise in 16 factories, such as machinery manufacturing and a thermal power plant of Hangzhou City, Zhejiang Province. None of the workers was exposed to other occupational hazards. The inclusion criteria for participants were as follows: (1) cumulative time of occupational noise exposure [noise exposure time  8 h/day or 40 h/week, and noise intensity ≥80 dB(A)] >1 year, and (2) Han ethnicity. Participants with a history of exposure to explosives, head injury, family history of hearing loss, other otological diseases, otitis, fever or common infections (e.g., influenza, diarrhea and hepatitis), or with ototoxic drug administration within 1 month before the physical examination were all excluded.

Participants were selected and divided into cases and controls according to the following criteria. The definitions of the cases were: (1) participants with normal hearing before exposure; (2) >1 year of occupational noise exposure; and (3) hearing threshold worse than 25 dB at high frequency. The definitions of the controls were: (1) participants >1 year of occupational noise exposure; and (2) hearing thresholds < 25 dB at each frequency. The controls were matched with sex, age (±5 years), and years of noise exposure one for each case.

The study was approved by the Research Ethics Committees of Hangzhou Institute for Occupational Health with informed consent obtained from each participant.

Physical examination and epidemiological investigation

Trained physicians performed a physical examination following a standard protocol for each participant, and parameters including body weight and height, pulse rate, and blood pressure were collected. Trained professional physicians conducted a face-to-face interview by using a structured questionnaire to collect information from each participant, including demographic characteristics, lifestyle habits, history of disease and drug use, family history of deafness, history of noise exposure in the workplace, and use of ear protection for noise.

Audiological status assessment and environmental noise measurement

Before audiometry, all participants stopped noise exposure for >48 h. Audiometry was carried out by trained physicians using standard procedures for each participant in a sound-attenuating chamber with a background noise level < 25 dB(A). According to the Chinese Diagnostic Criteria of Occupational NIHL (GBZ49–2014), hearing thresholds of both ears were determined with the ascending method in 5-dB steps at frequencies of 500, 1000, 2000, 3000, 4000 and 6000 Hz. The results were polished for age and gender according to GB/T7582–2004. The hearing threshold at high frequency by PTA was defined as the average at 3000, 4000 and 6000 Hz for each ear. The hearing threshold at speech frequency was defined as the average at 500, 1000 and 2000 Hz for each ear.

A noise statistical analyzer (AWA6218; Westernization Instrument Technology Co. Ltd., Beijing, China) was used to evaluate the intensity of noise in the workplace. Noise exposure was evaluated with continuous dB(A)-weighted sound pressure levels (Lex.8 h) according to the National Criteria of Measurement of Noise in the Workplace (GBZ/T189.8–2007) (China, 2007). Cumulative noise exposure (CNE) was calculated as CNE = Lex.8 h + 10logT, where T means years of noise exposure.

SNP selection and genotyping

Candidate SNPs in the CASP1, CASP3, CASP4, CASP5, CASP6, CASP8, CASP9, CASP10 and CASP14 genes were selected based on HapMap database (http://hapmap.ncbi.nlm.nih.gov), dBSNP (http://www.ncbi.nlm.nih.gov/snp/), and 1000 genomes dataset (http://www.1000genomes.org/). SNP function prediction software was also adopted such as Variant Effect Predictor (http://asia.ensembl.org/info/docs/tools/vep/index.html) and SNP Function Prediction (http://snpinfo.niehs.nih.gov/snpinfo/snpfunc.htm). Inclusion criteria were as follows: (1) located in the coding region, promoter region, 3′-untranslated region (UTR), or 5′-UTR; (2) minor allele frequency (MAF) of Chinese Han living in Beijing (CHB) >0.10; (3) linkage disequilibrium value of r2 > 0.80; and (4) reported in previous studies [1215]. Fifteen SNPs were selected according to those criteria: rs1977989 in CASP1, rs1049216 and rs6948 in CASP3, rs630003 in CASP4, rs507879 and rs523104 in CASP5, rs1042891 in CASP6, rs1045494 and rs3769823 in CASP8, rs1052576 and rs4645978 in CASP9, rs13006529 and rs3900115 in CASP10, and rs3181312 and rs3181309 in CASP14.

Genomic DNA was isolated from peripheral blood samples using TIANamp Blood DNA Kits (Tiangen Biotech, Beijing, China) and was stored at −80 °C. Genotyping of the SNPs was carried out using the polymerase chain reaction–ligase detection reactions (PCR-LDR) method (Shanghai Generay Biotech Company). The primer and probe sequences are shown in Table 1.

Table 1.

Basic information, primer and probe sequences of selected SNPs

No. Gene rs No. location allele MAF
(CHB)
Primers for PCR Probes for detecting variations P HWE
1 CASP1 rs1977989 11:105,026,117 A/G 0.232 F:TGAATATCATGTGGGCGCTC
R:TTTCTACCTCTTCCCAGGAC
TA:GGATTTTAGAGCATTTCAAAATTCA
TG:TTTGGATTTTAGAGCATTTCAAAATTCG
TR:AATTTTTGGATTAAGGATTCTCAGC
0.325
2 CASP3 rs1049216 4:184,628,935 C/T 0.2 F:GTGCAGTCATTATGAGAGGC
R:TTTGAGCCTTTGACCATGCC
TC:TTTTTTTTTGAAAAAGTTAAACATTGAAGTAAC
TT:TTTTTTTTTTTTGAAAAAGTTAAACATTGAAGTAAT
TR:GAATTTTTATGATATTCCCCCCACTTTTTTT
0.279
3 CASP3 rs6948 4:184,627,976 A/C 0.16 F:TGTTCTAAAGGTGGTGAGGC
R:TGAGACTTGGTGCAGTGACG
TA:TTTTTTTTTTTTTCCAGCCGGAGGCCAGAGCTGAGCA
TC:TTTTTTTTTTTTTTTTCCAGCCGGAGGCCAGAGCTGAGCC
TR:CTCAGCCCGGGAGGCAGGCTCCAGGTTTTTTTTT
0.264
4 CASP4 rs630003 11:104,970,269 G/C 0.25 F:CTTCTGCCTGGTTGATTTGG
R:GCTGAGATGGATGAACTGAC
TC:TTTTGATACTTGTGTTTGAATCATGAAGC
TG:TTTTTTTGATACTTGTGTTTGAATCATGAAGG
TR:TCTCACGCTGTGTTTCTCAGCTCCATTT
0.911
5 CASP5 rs507879 11:105,007,200 A/G 0.329 F:GTTAAGATGTTGGAATACCTG
R:GATCTTTTGGTCCATATTGAG
TA:TTTTTTTTGAGGAAAAGAAAAAATATTATGATA
TG:TTTTTTTTTTTGAGGAAAAGAAAAAATATTATGATG
TR:CCAAAATTGAAGACAAGGCCCTGATTTTTTT
0.522
6 CASP5 rs523104 11:104,998,981 G/C 0.211 F:GCCTATCTTGATTTCATAGAA
R:AGAAAAACATGGGGAACTCTG
TC:TTTTTTTTTTTTTCTCAGATGACTGTGAAGAGATGAC
TG:TTTTTTTTTTTTTTTTCTCAGATGACTGTGAAGAGATGAG
TR:TGCCAAGGATGCTGGAGAGTCTCTGTTTTTTTTT
0.623
7 CASP6 rs1042891 4:109,688,930 C/T 0.483 F:AATCCCAGCTACTTGGAAGG
R:TAAGGCAGTTCTCTGCTAGG
TC:TCGTTAGGGTGAAGCATTATGGTCC
TT:TTTTCGTTAGGGTGAAGCATTATGGTCT
TR:AATGATTCAAATGTTTTAAAGTTTA
0.581
8 CASP8 rs1045494 2:201,287,058 T/C 0.183 F:CTGGCCGATGGTACTATTTAG
R:TAAGCCCTCTATATTCATAGC
TC:TTTTTTTTTTTTTTTTAATAACACTGTCTCCTTTCTCTTAC
TT:TTTTTTTTTTTTTTTTTTTAATAACACTGTCTCCTTTCTCTTAT
TR:GCTTAAGGCTTTGGGAATGTTTTTAGCTGGTTTTTTT
0.522
9 CASP8 rs3769823 2:201,258,272 C/T 0.366 F: ATATTGTGGTTTCCTGTTGAAG
R: TAGTCAACTCAACAGGAAGTG
TC:AAGGCTCCCAGGAAGAAGTTTCTTC
TT:TTTAAGGCTCCCAGGAAGAAGTTTCTTT
TR:TACTTTCAATAACCACCCTGGCTCT
<0.001
10 CASP9 rs1052576 1:15,506,048 G/A 0.366 F:TGCTTCTGGCTCACCTGCAGC
R:TTGGACACAAGAAGGGACATG
TA:TTTTTGCTGGCTTTGCTGGAGCTGGCGCA
TG:TTTTTTTTGCTGGCTTTGCTGGAGCTGGCGCG
TR:GCAGGACCACGGTGCTCTGGACTGCTTT
0.802
11 CASP9 rs4645978 1:15,525,539 A/G 0.392 F:GAAAAGTGGCTAGCACGATG
R:CTGTTCCAAACTCGAGTGTC
TA:GTGTGGGAGGTGTTAGGGTGGGAGA
TG:TTTGTGTGGGAGGTGTTAGGGTGGGAGG
TR:GAGGGAAGAGGGAATGGAAGACTGT
0.324
12 CASP10 rs13006529 2:201,217,736 A/T 0.2 F:CTGCTGTCAACGATGATGTG
R:CTAGAATGACAGGTGGAGAC
TA:CCTGTGCCCCTGGATGCACTTTCAA
TT:TTTCCTGTGCCCCTGGATGCACTTTCAT
TR:TATAGCAGAGAGTTTTTGTTGGTTC
0.452
13 CASP10 rs3900115 2:201,185,954 A/G 0.22 F:GCTGGCCATGAAATCTCAAG
R:AAAGGGTCTTCCTCACTCAG
TA:TTTTGCTGGAGAAGTCCAGCTCAGCCTCA
TG:TTTTTTTGCTGGAGAAGTCCAGCTCAGCCTCG
TR:GATGTTTTTGAACATCTCTTGGCAGTTT
0.341
14 CASP14 rs3181312 19:15,057,642 A/C 0.466 F:CCTCAGCTTCTCATATCTGC
R:TTAACTCCTGGCCTCAAGTG
TA:TTTTAGTGGCTCACACCTGTATTCCCGAA
TC:TTTTTTTAGTGGCTCACACCTGTATTCCCGAC
TR:TTTGAGAGTCTGAAGCGGGAGGATCTTT
0.272
15 CASP14 rs3181309 19:15,056,984 T/C 0.279 F:ATTCCCTGTTGTCACCTTGC
R:AGCTCCTACCTTGGAGATAG
TC:CTCTTTTCCACAACCTGCTAAATCC
TT:TTTCTCTTTTCCACAACCTGCTAAATCT
TR:TGATCCATCTGAAAACTTTTCTAAT
0.136

The PCR was performed in an ABI Prism 7000 Sequence Detection System in a total volume of 15 μl, including 1 μl genomic DNA, 1.5 μl 10× PCR buffer, 1.5 μl MgCl2, 0.3 μl dNTPs, 0.15 μl each primer, and 0.2 μl Taq DNA polymerase. The PCR was performed as follows: an initial melting step of 3 min at 94 °C, 35 cycles of denaturation for 15 s at 94 °C, annealing for 15 s at 55 °C and extension for 30 s at 72 °C, followed by a 3 min final extension at 72 °C. The ligation reaction for each PCR product was carried out with a total volume of 10 μl, including 3 μl PCR product, 1 μl 10× Taq DNA ligase buffer, 5 U Taq DNA ligase, and 0.01 μl each discriminating probe. The LDR was performed as follows: 30 cycles at 94 °C for 30 s and 56 °C for 3 min. After the LDR reaction, 1 μl LDR product was mixed with 8 μl loading buffer, and was melted for 3 min at 95 °C. The mixture was then analyzed on the ABI3730xl platform. Ten percent of the samples were randomly selected and genotyped repeatedly for the quality control, and the concordance was 100%.

Statistical analysis

Continuous variables in accordance with normal distribution were expressed as mean ± standard deviation (SD) and were analyzed by Student’s t-test. Continuous variables for skewed distribution were expressed as median (P25, P75) and were analyzed by Wilcoxon rank test. Categorical variables were expressed as frequencies (%) and were analyzed by Person’s χ2 test. Hardy–Weinberg equilibrium tests were conducted using Pearson’s χ2 test for each SNP among the controls. The associations between the SNPs and NIHL risk were evaluated using conditional logistic regression for adjusted odds ratio (OR) with 95% confidence interval (CI). Potential gene–environment interaction was explored by stratified and crossover analysis. Multifactor dimensionality reduction (MDR) analysis was conducted to explore gene-gene interaction using MDR version 1.0.0 (Computational Genetics Laboratory of the University of Pennsylvania, Philadelphia, PA, USA). All the statistical analyses were performed using SAS version 9.1 (SAS Institute, Cary, NC, USA). P < 0.05 was considered statistically significant. Bonferroni correction was applied for multiple hypothesis testing.

Results

The basic characteristics of the participants are shown in Table 2. There were 272 cases and 272 controls with an average age of 32.5 and 31.7 years, respectively. There were no significant differences between the cases and controls in the distribution of demographic characteristics, smoking habit, weekly working time, years of noise exposure, noise intensity exposure, and CNE (P > 0.05). Significant differences were observed for several lifestyle factors including music listening time, telephone use time, and time to go to sleep between the cases and controls (P < 0.05). Compared with the controls, more cases listened to music for >2 h/day, used the telephone for >16 min/day, and went to sleep later than 23:00 h.

Table 2.

Basic characteristics of the study participants

Controls(n = 272) Cases(n = 272) χ 2 P
Age (years, mean ± SD) 31.70 ± 7.67 32.48 ± 7.58 −1.192a 0.234
Sex, n (%) 0 1
 Male 241(88.6) 241(88.6)
 Female 31(11.4) 31(11.4)
Marriage status, n (%) 0.427 0.808
 Single 69(25.4) 64(23.5)
 Married 201(73.9) 205(75.4)
 Divorce 2(0.7) 3(1.1)
Education, n (%) 1.890 0.389
 Primary school and below 96(35.3) 110(40.4)
 Junior middle school 123(45.2) 118(43.4)
 High school and above 53(19.5) 44(16.2)
Income [yuan/month, n (%)] 2.488 0.288
 < 2500 104(38.2) 118(43.4)
 2500- 79(29.0) 81(29.8)
 ≧3500 89(32.7) 73(26.8)
Smoking, n (%) 1.843 0.175
 No 187(68.8) 172(63.2)
 Yes 85(31.2) 100(36.8)
Music listening time (h/day) 17.770 <0.001
 0 174(64.0) 130(47.8)
 < 2 88(32.4) 115(42.3)
 ≧2 10(3.7) 27(9.9)
Telephone using time (min/day) 27.224 <0.001
 0 51(18.8) 20(7.7)
 < 16 142(52.2) 120(44.1)
 ≧16 79(29.0) 131(48.2)
Time go to sleep 48.818 <0.001
 Early than 22:00 128(47.1) 56(20.6)
 22:00~ 77(28.3) 86(31.6)
 Later than 23:00 67(24.6) 130(47.8)
Working time (h/week)b 48.00(40.00–60.00) 50.00(40.00–60.00) −1.370c 0.171
Noise exposure time (years)b 5.13(3.02–8.96) 5.04(3.00–8.50) −0.046c 0.963
Noise intensity exposure, dB(A)b 83.20(80.00–87.40) 83.65(80.00–87.40) −0.744c 0.457
CNEb 90.86(85.48–95.49) 91.13(86.59–96.15) −0.665c 0.506

aIndependent t-test

bData was presented as median (P25, P75)

cWilcoxon rank test

As shown in Table 1, 14 SNPs were in Hardy–Weinberg equilibrium (P > 0.05), except for rs3769823 of CASP8. This SNP was therefore excluded from the following analysis (Table 3). Associations were only found between rs1049216 and rs6948 and NIHL risk. For rs1049216, TT genotype was associated with a decreased NIHL risk (OR = 0.246, 95% CI = 0.069–0.886) when compared with the CC genotype. Similar results were found for the dominant and recessive genetic models. For rs6948, AC/CC genotypes were associated with a decreased NIHL risk (OR = 0.568, 95% CI = 0.352–0.916) when compared with the AA genotype. We classified rs1049216 CC and rs6948 AA genotypes as the high-risk genotypes. By computing the numbers of the two genotypes within the combined genotypes, we found that those carrying two risk genotypes were at higher risk of NIHL when compared with those carrying no risk genotype (OR = 1.787, 95%CI = 1.104–2.892). However, none of the associations remained significant after Bonferroni correction.

Table 3.

Association between SNPs and NIHL risk

SNP Genetic model Genotype Controls, n (%) Cases, n (%) P OR(95%CI)a
rs1049216 Additive CC 173(64.3) 195(72.5) 1.0
CT 82(30.5) 68(25.3) 0.050 0.609(0.372–1.000)
TT 14(5.2) 6(2.2) 0.032 0.246(0.069–0.886)
Dominant CC 173(64.3) 195(72.5) 1.0
CT + TT 96(35.7) 72(27.5) 0.014 0.551(0.343–0.885)
Recessive CC + CT 258(94.8) 266(97.8) 1.0
TT 14(5.2) 6(2.2) 0.047 0.277(0.078–0.986)
rs6948 Additive AA 177(65.8) 198(73.6) 1.0
AC 79(29.4) 65(24.2) 0.050 0.607(0.369–1.000)
CC 13(4.8) 6(2.2) 0.089 0.328(0.091–1.185)
Dominant AA 177(65.8) 198(73.6) 1.0
AC + CC 92(34.2) 71(26.4) 0.020 0.568(0.352–0.916)
Recessive AA + AC 256(95.2) 263(97.8) 1.0
CC 13(4.8) 6(2.2) 0.128 0.373(0.105–1.327)
Risk genotypeb 0 91(33.8) 71(26.4) 1.0
1 6(2.2) 3(1.1) 0.701 0.684(0.098–4.779)
2 172(63.9) 195(72.5) 0.018 1.787(1.104–2.892)

aadjusted for age, sex, education, marriage status, income, working time, noise exposure time, noise intensity exposure, CNE, telephone using time, music listening time, and time go to sleep

brs1049216 CC and rs6948 AA genotypes were classified as high-risk genotypes; the number represents the numbers of the two genotypes within the combined genotypes

We also conducted stratified analysis by noise intensity and CNE, and found that when noise intensity was <85 dB(A) or CNE <90 dB(A), rs1049216 CC and rs6948 AA genotypes could be defined as high risk. When noise intensity was <85 dB(A), CT/TT genotypes of rs1049216 was associated with a decreased NIHL risk (OR = 0.425, 95% CI = 0.207–0.871) when compared with the CC genotype, and AC/CC genotypes of rs6948 were associated with a decreased NIHL risk (OR = 0.458, 95% CI = 0.227–0.926) when compared with the AA genotype. The risk of NIHL in those carrying two risk genotypes was 2.307-fold higher than in those carrying no risk genotype (OR = 2.307, 95%CI = 1.123–4.740). Similar results were found when CNE was <90 dB(A). However, none of the results reach statistical significance after Bonferroni correction (see Additional file 1: Table S1 and S2).

To explore further the potential gene–environment interaction in NIHL risk, we conducted a crossover analysis between the SNPs and nongenetic factors including working time, noise exposure time, noise intensity exposure, CNE, telephone use time, music listening time, and time to go to sleep. Associations were found between rs1049216 and rs6948 and working time. Individuals carrying rs1049216CC genotype and working >48 h/week were associated with a significantly higher risk of NIHL (OR = 3.989, 95% CI = 1.787–8.907) when compared with those carrying rs1049216 CT/TT genotype and working ≤48 h/week (Table 4). We found similar results for those carrying the CC genotype and not working >48 h/week (OR = 1.870, 95% CI = 1.012–3.457). Similar results were found for rs6948 and working time, as well as risk genotype and working time. When an individual carried the rs6948 AA genotype or had two risk genotypes, working time > 48 h/week showed a significant association with NIHL risk. We also conducted MDR analysis to explore the interaction between SNPs, but found no positive results (see Additional file 1: Table S3).

Table 4.

Crossover analysis of interaction between SNPs and working time on NIHL risk

SNP Genotype Working time(h/week) Controls, n (%) Cases, n (%) P OR(95%CI)a
rs1049216 CT + TT ≤ 48 59(21.9) 43(16.0) 1.0
CC ≤ 48 95(35.3) 91(33.8) 0.046 1.870(1.012–3.457)
CT + TT > 48 37(13.8) 31(11.5) 0.083 2.263(0.900–5.689)
CC > 48 78(29.0) 104(38.7) 0.001b 3.989(1.787–8.907)
rs6948 AC + CC ≤ 48 56(20.8) 42(15.6) 1.0
AA ≤ 48 98(36.4) 92(34.2) 0.087 1.716(0.925–3.184)
AC + CC > 48 36(13.4) 29(10.8) 0.123 2.076(0.821–5.251)
AA > 48 79(29.4) 106(39.4) 0.001b 3.817(1.710–8.522)
Risk genotype < 2 ≤ 48 60(22.3) 43(16.0) 1.0
2 ≤ 48 94(34.9) 91(33.8) 0.045 1.875(1.014–3.467)
< 2 > 48 37(13.8) 31(11.5) 0.082 2.267(0.902–5.699)
2 > 48 78(29.0) 104(38.7) 0.001b 3.995(1.790-8.919)

aadjusted for age, sex, education, marriage status, income, noise exposure time, noise intensity exposure, CNE, telephone using time, music listening time, and time to go to sleep

bthe P-value remained significant after Bonferroni adjustment for multiple comparisons

Discussion

We investigated the association between caspase polymorphisms and NIHL in Chinese of Han nationality. We found significant differences between NIHL cases and controls for genotypic distributions of SNPs rs1049216 and rs6948 in CASP3. In rs1049216, compared with the participants carrying CC genotypes, the carriers with TT genotype had a decreased risk of NIHL (OR = 0.246, 95% CI = 0.069–0.886). In rs6948, the AC and CC carriers had decreased NIHL risk (OR = 0.568, 95% CI = 0.352–0.916) compared with the participants with AA genotype.

Caspase-3 is the most important effector in the process of apoptosis, and it is the converging point of many apoptotic stimulating signals. Its activation is a sign of apoptosis entering an irreversible stage [16, 17]. Many studies have investigated caspase-3 polymorphism and the risk of some diseases, including mainly Kawasaki disease and cancer, but few studies have related to NIHL [18, 19].

In our study, we defined rs1049216 CC and rs6948 AA genotypes as the high-risk genotypes. By calculating the numbers of the high-risk genotype, we found that the risk of NIHL in those carrying two risk genotypes was 1.787-fold higher than in those carrying no risk genotype (OR = 1.787, 95%CI = 1.104–2.892). This is similar to the results of Yan et al. [20]. By the stratified analysis, positive results were only founded when noise intensity was <85 dB(A) or CNE < 90 dB(A), and the effects of high-risk genotype were not observed when noise intensity was ≥85 dB(A) or CNE ≥90 dB(A). This result suggests that both SNPs are NIHL susceptibility sites and high-intensity noise is still a major NIHL risk factor. To address the question of whether there is a potential interaction between gene and environment, we conducted a crossover analysis between the SNPs and nongenetic factors. Associations were found between rs1049216 and rs6948 and working time. The risk of NIHL in individuals carrying the rs1049216CC genotype and working >48 h/week was 3.989-fold higher than in those carrying rs1049216 CT/TT genotype and working ≤48 h/week (OR = 3.989, 95% CI = 1.787–8.907). Similar results were found for those carrying the CC genotype and not working >48 h/week (OR = 1.870, 95% CI = 1.012–3.457), Similar results were found for rs6948 and working time, as well as risk genotype and working time. When individuals carried rs6948 AA genotype or two high-risk genotypes, working time > 48 h/week showed a significant association with NIHL risk. The results suggested that individuals with rs1049216 and rs6948 mutant alleles in the general population should pay more attention to controlling working time in order to achieve individualized control.

A previous study has shown that there was a strong linkage disequilibrium (D’0.98) between rs6948 and rs1049216, which was in agreement with our results (D’0.993) [21]. SNP’s located in the 3’UTR region play an important role in regulating the stability of mRNAs, mediating mRNA localization, assisting in identifying special codons, and controlling the level of mRNA translation [22, 23]. Both rs6948 and rs1049216 are located in the 3′UTR [24]. It has been suggested that mutant C allele of rs6948 in the binding site of miRNA-24 (binding site: CASP3 3’UTR1290–1296) may downregulate the expression of miRNA-24 and affect expression of caspase-3 [25]. Similarly, rs1049216 may also influence the expression of CASP3 by controlling mRNA translation levels.

Our study had some limitations that should be acknowledged when interpreting our results. First, although this study adopted 1:1 matched case–control design, the sample size was small, and some positive results that could only have been revealed by large samples may not have been found. Second, all of the workers who had been diagnosed with occupational NIHL had been transferred from the original workplace. This study failed to incorporate them, which may have led to selection bias. Finally, due to limited conditions, we use factory, fixed-point measurement of noise level for individual noise exposure values, which may have affected the accuracy of the results.

Conclusion

In conclusion, our findings suggest that genetic variations in the CASP3 gene and their interactions with working time may modify the risk of developing NIHL. The TT genotype of rs1049216 and the AC and CC genotype of rs6948 may be less susceptible to NIHL. In subsequent studies, we will refine the experimental design, and supplement the collection of ambient noise exposure in a larger population to verify the results of the present study.

Acknowledgements

Not applicable.

Funding

This study was supported by the Program for Zhejiang Leading Team of Science and Technology Innovation (No. 2011R50021), the Zhejiang Provincial Natural Science Foundation of China (No. LQ16H260002), and the Science Program for Hangzhou Social Development (20160533B02).

Availability of data and materials

Please contact author for data requests.

Abbreviations

CHB

Han Chinese individuals from Beijing

CI

Confidence interval

CNE

Cumulative noise exposure

MAF

Minor allele frequency

MDR

Multifactor dimensionality reduction

NIHL

Noise-induced hearing loss

OR

Odds ratio

PCR-LDR

Polymerase chain reaction–ligase detection reactions

PTA

Pure tone audiometry

SD

Standard deviation

SNP

Single-nucleotide polymorphism

UTR

Untranslated region

WHO

World Health Organization

Additional file

Additional file 1: Table S1. (21.4KB, docx)

Stratified analysis by noise intensity. Table S2. Stratified analysis by CNE. Table S3. The best combination models identified by MDR. (DOCX 21 kb)

Authors’ contributions

YW and NJ performed the statistical analysis for this study and wrote the manuscript. HM and LY designed the study and revised the manuscript. LX was responsible for quality control of the project. MQ and CC conducted the study design, carried out the experiment. YS was responsible for data collection. All authors approved the final manuscript.

Ethics approval and consent to participate

The study was approved by the Research Ethics Committees of Hangzhou Institute for Occupational Health, Zhejiang, P.R.China. Written informed consent was obtained from each participant.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Footnotes

Electronic supplementary material

The online version of this article (doi:10.1186/s12940-017-0280-y) contains supplementary material, which is available to authorized users.

Contributor Information

Yinyin Wu, Email: 48037663@qq.com.

Juntao Ni, Email: 674457518@qq.com.

Mingjian Qi, Email: 1007990279@qq.com.

Chengjian Cao, Email: 2504493086@qq.com.

Yuxian Shao, Email: hyde.hishi@163.com.

Liangwen Xu, Email: 13588118965@163.com.

Haiyan Ma, Email: mhynym@163.com.

Lei Yang, Email: yanglei62@hznu.edu.cn.

References

  • 1.Adelman C, Weinberger JM, Kriksunov L, Sohmer H. Effects of furosemide on the hearing loss induced by impulse noise. J Occup Med Toxicol. 2011;6:1–7. doi: 10.1186/1745-6673-6-14. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Olusanya BO, Neumann KJ, Saunders JE. The global burden of disabling hearingimpairment: a call to action. Bull World Health Organ. 2014;92:367–373. doi: 10.2471/BLT.13.128728. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Nelson DI, Nelson RY, Concha-Barrientos M, Fingerhut M. The global burden of occupational noise-induced hearing loss. Am J Ind Med. 2005;48:446–458. doi: 10.1002/ajim.20223. [DOI] [PubMed] [Google Scholar]
  • 4.Rabinowitz PM, Galusha D, Slade MD, Dixon-Ernst C, O'Neill A, Fiellin M, et al. Organic solvent exposure and hearing loss in a cohort of aluminium workers. Occup Environ Med. 2008;65:230–235. doi: 10.1136/oem.2006.031047. [DOI] [PubMed] [Google Scholar]
  • 5.Fechter LD. Promotion of noise-induced hearing loss by chemical contaminants. J Toxicol Environ Health A. 2004;67:727–740. doi: 10.1080/15287390490428206. [DOI] [PubMed] [Google Scholar]
  • 6.Konings A, Van LL, Van CG. Genetic studies on noise-induced hearing loss: a review. Ear Hear. 2009;30:151–159. doi: 10.1097/AUD.0b013e3181987080. [DOI] [PubMed] [Google Scholar]
  • 7.Henderson D, Subramaniam M, Boettcher FA. Individual susceptibility to noise-induced hearing loss: an old topic revisited. Ear Hear. 1993;14:152–168. doi: 10.1097/00003446-199306000-00002. [DOI] [PubMed] [Google Scholar]
  • 8.Harding GW, Bohne BA, Vos JD. The effect of an age-related hearing loss gene (Ahl) on noise-induced hearing loss and cochlear damage from low-frequency noise. Hear Res. 2005;204:90–100. doi: 10.1016/j.heares.2005.01.004. [DOI] [PubMed] [Google Scholar]
  • 9.Op de Beeck K, Schacht J, Van CG. Apoptosis in acquired and genetic hearing impairment: the programmed death of the hair cell. Hear Res. 2011;281:18–27. doi: 10.1016/j.heares.2011.07.002. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Fetoni AR, De BP, Eramo SL, Rolesi R, Paciello F, Bergamini C, et al. Noise-induced hearing loss (NIHL) as a target of oxidative stress-mediated damage: cochlear and cortical responses after an increase in antioxidant defense. J Neurosci. 2013;33:4011–4023. doi: 10.1523/JNEUROSCI.2282-12.2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Joseph EK, Levine JD. Caspase signalling in neuropathic and inflammatory pain in the rat. Eur J Neurosci. 2004;20:2896–2902. doi: 10.1111/j.1460-9568.2004.03750.x. [DOI] [PubMed] [Google Scholar]
  • 12.Jeon S, Han S, Lee K, Choi J, Park SK, Park AK, et al. Genetic variants of AICDA/CASP14 associated with childhood brain tumor. Genet Mol Res. 2013;12:2024–2031. doi: 10.4238/2013.January.30.1. [DOI] [PubMed] [Google Scholar]
  • 13.Choi JY, Kim JG, Lee YJ, Chae YS, Sohn SK, Moon JH, et al. Prognostic impact of polymorphisms in the CASPASE genes on survival of patients with colorectal cancer. Cancer Res Treat. 2012;44:32–36. doi: 10.4143/crt.2012.44.1.32. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Yoo SS, Choi JE, Lee WK, Choi YY, Kam S, Kim MJ, et al. Polymorphisms in the CASPASE genes and survival in patients with early-stage non-small-cell lung cancer. J Clin Oncol. 2009;27:5823–5829. doi: 10.1200/JCO.2009.23.1738. [DOI] [PubMed] [Google Scholar]
  • 15.Lan Q, Morton LM, Armstrong B, Hartge P, Menashe I, Zheng T, et al. Genetic variation in caspase genes and risk of non-Hodgkin lymphoma: a pooled analysis of 3 population-based case-control studies. Blood. 2009;114:264–267. doi: 10.1182/blood-2009-01-198697. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Moser T, Predoehl F, Starr A. Review of hair cell synapse defects in sensorineural hearing impairment. Otol Neurotol. 2013;34:995–1004. doi: 10.1097/MAO.0b013e3182814d4a. [DOI] [PubMed] [Google Scholar]
  • 17.Henderson D, Bielefeld EC, Harris KC, Hu BH. The role of oxidative stress in noise-induced hearing loss. Ear Hear. 2006;27:1–19. doi: 10.1097/01.aud.0000191942.36672.f3. [DOI] [PubMed] [Google Scholar]
  • 18.Xing Y, Wang H, Liu X, Yu X, Chen R, Wang C, et al. Retraction note to: meta-analysis of the relationship between single nucleotide polymorphism rs72689236 of caspase-3 and Kawasaki disease. Mol Biol Rep. 2015;42:6377–6381. doi: 10.1007/s11033-015-3905-7. [DOI] [PubMed] [Google Scholar]
  • 19.Wang M, Zhu M, He J, Shi T, Li Q, Wei Q, et al. Potentially functional polymorphisms in the CASP7 Gene contribute to gastric Adenocarcinoma susceptibility in an eastern Chinese population. PLoS One. 2013;8:e74041. doi: 10.1371/journal.pone.0074041. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Yan S, Li YZ, Zhu XW, Liu CL, Wang P, Liu YL. HuGE systematic review and meta-analysis demonstrate association of CASP-3 and CASP-7 genetic polymorphisms with cancer risk. Genet Mol Res. 2013;12:1561–1573. doi: 10.4238/2013.May.13.10. [DOI] [PubMed] [Google Scholar]
  • 21.Iii HDH, Baris D, Zhang Y, Zhu Y, Zheng T, Yeager M, et al. Caspase polymorphisms and genetic susceptibility to multiple myeloma. Hematol Oncol. 2008;26:148–151. doi: 10.1002/hon.852. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Vella MC, Choi EY, Lin SY, Reinert K, Slack FJ. The C. Elegans microRNA let-7 binds to imperfect let-7 complementary sites from the lin-41 3’UTR. Genes Dev. 2004;18:132–137. doi: 10.1101/gad.1165404. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Alvarez DE, Al DLE, Fucito S, Gamarnik AV. Role of RNA structures present at the 3’UTR of dengue virus on translation, RNA synthesis, and viral replication. Virology. 2005;339:200–212. doi: 10.1016/j.virol.2005.06.009. [DOI] [PubMed] [Google Scholar]
  • 24.Chen K, Zhao H, Hu Z, Wang L, Zhang W, Sturgis EM, et al. CASP3 polymorphisms and risk of squamous cell carcinoma of the head and neck. Clin Cancer Res. 2008;14:6343–6349. doi: 10.1158/1078-0432.CCR-08-1198. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Gu S, Wu Q, Zhao X, Wu W, Gao Z, Tan X, et al. Association of CASP3 polymorphism with hematologic toxicity in patients with advanced non-small-cell lung carcinoma treated with platinum-based chemotherapy. Cancer Sci. 2012;103:1451–1459. doi: 10.1111/j.1349-7006.2012.02323.x. [DOI] [PMC free article] [PubMed] [Google Scholar]

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Data Availability Statement

Please contact author for data requests.


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