Literature DB >> 29556524

Cytogenetics data in adult men involved in the recycling of electronic wastes.

Yanan Du1, Yan Wang1, Liqing Du1, Chang Xu1, Kaihua Ji1, Jinhan Wang1, Qiang Liu1.   

Abstract

In this data article, 146 villagers (exposed group) were randomly selected from the workers who involved in the e-wastes recycling directly as a daily job in Tianjin. Control group, including 121 villagers, came from another town without e-waste disposal sites. Chromosomal aberrations (CA) and cytokinesis blocking micronucleus (CBMN) were performed to detect the cytogenetic effect for each subject. DNA damage was detected using comet assay; the DNA percentage in the comet tail (TDNA%), tail moment (TM), and Olive tail moment (OTM) were recorded to describe DNA damage to lymphocytes and spermatozoa. Routine semen analysis, spermatozoa motility and morphology were analyzed. The RT2Profiler PCR array was used to measure levels of expression of 84 genes related to quality of DNA. It showed significant relationships between CA, CBMN, DNA damage and exposure time in exposure subjects. The alteration of sperm motility rate, abnormality rate and total sperm counts had association with exposure time and age.

Entities:  

Year:  2018        PMID: 29556524      PMCID: PMC5854875          DOI: 10.1016/j.dib.2018.02.051

Source DB:  PubMed          Journal:  Data Brief        ISSN: 2352-3409


Specifications table Value of the data. The data were helpful to understand the positive associations between both CA and CBMN and the duration of working with e-wastes. When stratified for age, for each of the age sub-groups, a statistically significant difference was observed between the group exposed to e-waste and the reference group. Semen quality was worse in the workers who recycled e-wastes than that of reference subjects.

Data

A largest electronic waste disposal centers in northern China had been found recently years. Components of e-wastes such as electronic circuit boards or microchips were illegally burned or heated for reclaimable materials (Fig. 1).
Fig. 1

Recycling of e-wastes without any protection. Heat the circuit boards to get metals.

Recycling of e-wastes without any protection. Heat the circuit boards to get metals. The exposure and reference group were both divided by age into three sub-groups (20–29, 30–39 and >40 years old). For each age sub-group, significant differences were found between exposure and reference groups (Fig. 2A-F). No significant difference was observed among age-groups in either the exposure or reference group (Fig. 2A-F).
Fig. 2

DNA damage detected by comet assay in lymphocytes and spermatozoa for different age sub-groups. The group of workers recycling e-wastes and reference group were both divided into three sub-groups by age (20–29, 30–39 and >40 years old). A-C: TDNA%, TM and OTM in lymphocytes between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. D-F: TDNA%, TM and OTM in spermatozoa between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. **: P < 0.01. Two way ANOVA was also used to test the interactions between age and DNA damage in lymphocytes and spermatozoa, respectively. (lymphocytes: F = 2.13, P = 0.15; spermatozoa: F = 1.67, P = 0.21).

DNA damage detected by comet assay in lymphocytes and spermatozoa for different age sub-groups. The group of workers recycling e-wastes and reference group were both divided into three sub-groups by age (20–29, 30–39 and >40 years old). A-C: TDNA%, TM and OTM in lymphocytes between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. D-F: TDNA%, TM and OTM in spermatozoa between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. **: P < 0.01. Two way ANOVA was also used to test the interactions between age and DNA damage in lymphocytes and spermatozoa, respectively. (lymphocytes: F = 2.13, P = 0.15; spermatozoa: F = 1.67, P = 0.21). The exposure group was stratified into three sub-groups according to their exposure time (≤ 3, 3–6 and > 6-year groups). The statistical significant relationships between DNA damage (TDNA%, TM) and duration of exposure for DNA damage were found in both lymphocytes and spermatozoa (Fig. 3A and B).
Fig. 3

Relationship between exposure duration and DNA damage of lymphocytes (A) and spermatozoa (B) in the exposed group. It showed significant relationship between TDNA%, TM and exposure duration for not only lymphocytes but also spermatozoa. *: P < 0.05.

Relationship between exposure duration and DNA damage of lymphocytes (A) and spermatozoa (B) in the exposed group. It showed significant relationship between TDNA%, TM and exposure duration for not only lymphocytes but also spermatozoa. *: P < 0.05. For each of the sub-groups divided by age, there was significantly higher of CA and CBMN in the e-waste workers compared to the reference group (Fig. 4A and B). No significant difference was found among sub-groups in either the exposure or reference group (Fig. 4A and B).
Fig. 4

CA (A) and CBMN (B) in lymphocytes of workers recycling e-wastes and in reference group for different age sub-groups. A-B: CA and CBMN in lymphocytes between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. There is no difference of CA and CBMN among the age sub-groups. **: P < 0.01. Two way ANOVA was also used to test the interactions between age and CA, CBMN in lymphocytes, respectively. (CA: F = 2.03, P = 0.18; CBMN: F = 1.07, P = 0.39).

CA (A) and CBMN (B) in lymphocytes of workers recycling e-wastes and in reference group for different age sub-groups. A-B: CA and CBMN in lymphocytes between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. There is no difference of CA and CBMN among the age sub-groups. **: P < 0.01. Two way ANOVA was also used to test the interactions between age and CA, CBMN in lymphocytes, respectively. (CA: F = 2.03, P = 0.18; CBMN: F = 1.07, P = 0.39). Statistically significant was found between CA, CBMN and exposure time (Fig. 5A). A classical micronucleus in a binucleated lymphocyte, a dicentric chromosome and an acentric fragment are shown in Fig. 5B and C.
Fig. 5

Relationship between exposure duration and frequency of CA and CBMN in lymphocytes of exposed subjects. A: It shows significant relationships between CA, CBMN and exposure duration in lymphocytes. B: One micronucleus in a binucleated lymphocyte of the group of workers recycling e-wastes. C: A metaphase lymphocyte of the group of workers recycling e-wastes. The red arrow directs a dicentric chromosome; the blue arrow directs an acentric fragment. **: P < 0.01, *: P < 0.05.

Relationship between exposure duration and frequency of CA and CBMN in lymphocytes of exposed subjects. A: It shows significant relationships between CA, CBMN and exposure duration in lymphocytes. B: One micronucleus in a binucleated lymphocyte of the group of workers recycling e-wastes. C: A metaphase lymphocyte of the group of workers recycling e-wastes. The red arrow directs a dicentric chromosome; the blue arrow directs an acentric fragment. **: P < 0.01, *: P < 0.05. Sperm motility rate, abnormality rate and total sperm counts were analyzed in the three sub-groups divided by age for exposure and reference groups. For the same age sub-groups, significant difference was found between exposure and reference group (Fig. 6A, B and C). The sperm parameters above also showed significant difference among different sub-groups in exposure or reference group respectively (Fig. 6A1, B1 and C1).
Fig. 6

Sperm motility rate, abnormality rate and total sperm counts for different age sub-groups. A-C: Sperm motility rate, abnormality rate and total sperm counts between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. There is significant difference of sperm motility rate, abnormality rate and total sperm counts between the group of workers recycling e-wastes and reference group in the age sub-groups, respectively. A1-C1: Line chart showed the change of sperm motility rate, abnormality rate and total sperm counts along with age. There is significant difference of sperm motility rate, abnormality rate and total sperm counts among the age sub-groups in exposure or reference group respectively. **: P < 0.01, *: P < 0.05. Two way ANOVA was also used to test the interactions between age and sperm motility rate, abnormality rate and total sperm counts, respectively. (sperm motility rate: F = 3.24, P = 0.07; abnormality rate: F = 3.13, P = 0.08; total counts: F = 2.89, P = 0.12).

Sperm motility rate, abnormality rate and total sperm counts for different age sub-groups. A-C: Sperm motility rate, abnormality rate and total sperm counts between the group of workers recycling e-wastes and reference group for the sub-groups divided by age. There is significant difference of sperm motility rate, abnormality rate and total sperm counts between the group of workers recycling e-wastes and reference group in the age sub-groups, respectively. A1-C1: Line chart showed the change of sperm motility rate, abnormality rate and total sperm counts along with age. There is significant difference of sperm motility rate, abnormality rate and total sperm counts among the age sub-groups in exposure or reference group respectively. **: P < 0.01, *: P < 0.05. Two way ANOVA was also used to test the interactions between age and sperm motility rate, abnormality rate and total sperm counts, respectively. (sperm motility rate: F = 3.24, P = 0.07; abnormality rate: F = 3.13, P = 0.08; total counts: F = 2.89, P = 0.12). Relationship between semen alteration and exposure time of e-wastes was analyzed in exposure group. For the three sub-groups divided by exposure time (≤ 3, 3–6 and >6years groups), semen parameters were analyzed for every two sub-groups by Wilcoxon rank-sum test. Sperm motility rate, semen volume, sperm concentration and total sperm count decreased significantly with exposure time, however, sperm abnormality rate increased significantly with e-wastes exposure time (Fig. 7).
Fig. 7

Relationship among semen parameters and exposure duration. A: Sperm motility rate and semen volume decreased but sperm abnormality rate increased significantly with e-wastes exposure duration. B: Sperm concentration and total sperm count both decreased significantly with exposure duration. *: P < 0.05.

Relationship among semen parameters and exposure duration. A: Sperm motility rate and semen volume decreased but sperm abnormality rate increased significantly with e-wastes exposure duration. B: Sperm concentration and total sperm count both decreased significantly with exposure duration. *: P < 0.05. RNA of peripheral blood cells was isolated by use of the RNeasy Mini kit (Qiagen, Hilden, Germany) as instructed by the manufacturer. Integrity of RNA was assessed by means of the Bioanalyzer 2100 (Agilent Technologies, Palo Alto, CA). 84 key genes (Table 1) from Human DNA Damage Signaling Pathway were simultaneously assayed by use of the RT2Profiler PCR array plate (SuperArray Bioscience Corporation, Frederick, MD) according to the manufacturer's protocol. The detail of gene expression analysis was shown in Ref. [1].
Table 1

Gene table of the 84 genes assayed with Human DNA Damage Signaling pathway PCR array RT2Profiler.

No.UnigeneGeneBankSymbolDescriptionGene Name
1Hs.431048NM_005157ABL1C-abl oncogene 1, receptor tyrosine kinaseABL/JTK7
2Hs.601206NM_198889ANKRD17Ankyrin repeat domain 17GTAR/NY-BR-16
3Hs.73722NM_080649APEX1APEX nuclease (multifunctional DNA repair enzyme) 1APE/APE-1
4Hs.367437NM_000051ATMAtaxia telangiectasia mutatedAT1/ATA
5Hs.271791NM_001184ATRAtaxia telangiectasia and Rad3 relatedFRP1/MEC1
6Hs.533526NM_000489ATRXAlpha thalassemia/mental retardation syndrome X-linked (RAD54 homolog, S. cerevisiae)ATR2/MRXHF1
7Hs.194143NM_007294BRCA1Breast cancer 1, early onsetBRCAI/BRCC1
8Hs.519162NM_006763BTG2BTG family, member 2PC3/TIS21
9Hs.292524NM_001239CCNHCyclin HCAK/p34
10Hs.184298NM_001799CDK7Cyclin-dependent kinase 7CAK1/CDKN7
11Hs.24529NM_001274CHEK1CHK1 checkpoint homolog (S. pombe)CHK1
12Hs.291363NM_007194CHEK2CHK2 checkpoint homolog (S. pombe)CDS1/CHK2
13Hs.135471NM_006384CIB1Calcium and integrin binding 1 (calmyrin)CIB/KIP
14Hs.249129NM_001279CIDEACell death-inducing DFFA-like effector aCIDE-A
15Hs.151573NM_004075CRY1Cryptochrome 1 (photolyase-like)PHLL1
16Hs.290758NM_001923DDB1Damage-specific DNA binding protein 1, 127 kDaDDBA/UV-DDB1
17Hs.505777NM_004083DDIT3DNA-damage-inducible transcript 3CEBPZ/CHOP
18Hs.339396NM_007068DMC1DMC1 dosage suppressor of mck1 homolog, meiosis-specific homologous recombination (yeast)DMC1H/HsLim15
19Hs.435981NM_001983ERCC1Excision repair cross-complementing rodent repair deficiency, complementation group 1 (includes overlapping antisense sequence)COFS4/UV20
20Hs.487294NM_000400ERCC2Excision repair cross-complementing rodent repair deficiency, complementation group 2 (xeroderma pigmentosum D)COFS2/EM9
21Hs.498248NM_130398EXO1Exonuclease 1HEX1/hExoI
22Hs.591084NM_004629FANCGFanconi anemia, complementation group GFAG/XRCC9
23Hs.409065NM_004111FEN1Flap structure-specific endonuclease 1FEN-1/MF1
24Hs.292493NM_001469XRCC6X-ray repair complementing defective repair in Chinese hamster cells 6 (Ku autoantigen, 70 kDa)CTC75/CTCBF
25Hs.80409NM_001924GADD45AGrowth arrest and DNA-damage-inducible, alphaDDIT1/GADD45
26Hs.9701NM_006705GADD45GGrowth arrest and DNA-damage-inducible, gammaCR6/DDIT2
27Hs.661218NM_002066GMLGlycosylphosphatidylinositol anchored molecule like proteinLY6DL
28Hs.577202NM_005316GTF2H1General transcription factor IIH, polypeptide 1, 62 kDaBTF2/TFIIH
29Hs.191356NM_001515GTF2H2General transcription factor IIH, polypeptide 2, 44 kDaBTF2/BTF2P44
30Hs.386189NM_016426GTSE1G-2 and S-phase expressed 1B99
31Hs.152983NM_004507HUS1HUS1 checkpoint homolog (S. pombe)Hus1
32Hs.503048NM_002180IGHMBP2Immunoglobulin mu binding protein 2CATF1/HCSA
33Hs.17253NM_054111IHPK3Inositol hexaphosphate kinase 3INSP6K3/IP6K3
34Hs.61188NM_033276XRCC6BP1XRCC6 binding protein 1KUB3
35Hs.1770NM_000234LIG1Ligase I, DNA, ATP-dependentMGC117397
36Hs.463978NM_002758MAP2K6Mitogen-activated protein kinase kinase 6MAPKK6/MEK6
37Hs.432642NM_002969MAPK12Mitogen-activated protein kinase 12ERK3/ERK6
38Hs.35947NM_003925MBD4Methyl-CpG binding domain protein 4MED1
39Hs.195364NM_000249MLH1MutL homolog 1, colon cancer, nonpolyposis type 2 (E. coli)COCA2/FCC2
40Hs.436650NM_014381MLH3MutL homolog 3 (E. coli)HNPCC7
41Hs.509523NM_002431MNAT1Menage a trois homolog 1, cyclin H assembly factor (Xenopus laevis)MAT1/RNF66
42Hs.459596NM_002434MPGN-methylpurine-DNA glycosylaseAAG/APNG
43Hs.192649NM_005590MRE11AMRE11 meiotic recombination 11 homolog A (S. cerevisiae)ATLD/HNGS1
44Hs.597656NM_000251MSH2MutS homolog 2, colon cancer, nonpolyposis type 1 (E. coli)COCA1/FCC1
45Hs.280987NM_002439MSH3MutS homolog 3 (E. coli)DUP/MRP1
46Hs.271353NM_012222MUTYHMutY homolog (E. coli)MYH
47Hs.396494NM_018177N4BP2Nedd4 binding protein 2B3BP
48Hs.492208NM_002485NBNNibrinAT-V1/AT-V2
49Hs.66196NM_002528NTHL1Nth endonuclease III-like 1 (E. coli)NTH1/OCTS3
50Hs.380271NM_002542OGG18-oxoguanine DNA glycosylaseHMMH/HOGG1
51Hs.20930NM_020418PCBP4Poly(rC) binding protein 4LIP4/MCG10
52Hs.147433NM_182649PCNAProliferating cell nuclear antigenMGC8367
53Hs.424932NM_004208AIFM1Apoptosis-inducing factor, mitochondrion-associated, 1AIF/PDCD8
54Hs.111749NM_000534PMS1PMS1 postmeiotic segregation increased 1 (S. cerevisiae)DKFZp781M0253/HNPCC3
55Hs.632637NM_000535PMS2PMS2 postmeiotic segregation increased 2 (S. cerevisiae)HNPCC4/PMS2CL
56Hs.225784NM_005395PMS2L3Postmeiotic segregation increased 2-like 3PMS2L9/PMS5
57Hs.78016NM_007254PNKPPolynucleotide kinase 3'-phosphatasePNK
58Hs.631593NM_014330PPP1R15AProtein phosphatase 1, regulatory (inhibitor) subunit 15AGADD34
59Hs.700597NM_006904PRKDCProtein kinase, DNA-activated, catalytic polypeptideDNAPK/DNPK1
60Hs.531879NM_002853RAD1RAD1 homolog (S. pombe)HRAD1/REC1
61Hs.16184NM_002873RAD17RAD17 homolog (S. pombe)CCYC/HRAD17
62Hs.375684NM_020165RAD18RAD18 homolog (S. cerevisiae)RNF73
63Hs.81848NM_006265RAD21RAD21 homolog (S. pombe)HR21/HRAD21
64Hs.655835NM_005732RAD50RAD50 homolog (S. cerevisiae)RAD50-2/hRad50
65Hs.631709NM_002875RAD51RAD51 homolog (RecA homolog, E. coli) (S. cerevisiae)BRCC5/HRAD51
66Hs.172587NM_133509RAD51L1RAD51-like 1 (S. cerevisiae)R51H2/RAD51B
67Hs.655354NM_004584RAD9ARAD9 homolog A (S. pombe)RAD9
68Hs.546282NM_002894RBBP8Retinoblastoma binding protein 8CTIP/RIM
69Hs.443077NM_016316REV1REV1 homolog (S. cerevisiae)REV1L
70Hs.461925NM_002945RPA1Replication protein A1, 70 kDaHSSB/REPA1
71Hs.408846NM_022367SEMA4ASema domain, immunoglobulin domain (Ig), transmembrane domain (TM) and short cytoplasmic domain, (semaphorin) 4ACORD10/RP35
72Hs.591336NM_014454SESN1Sestrin 1PA26/SEST1
73Hs.211602NM_006306SMC1AStructural maintenance of chromosomes 1ACDLS2/DKFZp686L19178
74Hs.81424NM_003352SUMO1SMT3 suppressor of mif two 3 homolog 1 (S. cerevisiae)DAP-1/GMP1
75Hs.654481NM_000546TP53Tumor protein p53LFS1/TRP53
76Hs.697294NM_005427TP73Tumor protein p73P73
77Hs.694840NM_016381TREX1Three prime repair exonuclease 1AGS1/AGS5
78Hs.191334NM_003362UNGUracil-DNA glycosylaseDGU/DKFZp781L1143
79Hs.654364NM_000380XPAXeroderma pigmentosum, complementation group AXP1/XPAC
80Hs.475538NM_004628XPCXeroderma pigmentosum, complementation group CXP3/XPCC
81Hs.98493NM_006297XRCC1X-ray repair complementing defective repair in Chinese hamster cells 1RCC
82Hs.647093NM_005431XRCC2X-ray repair complementing defective repair in Chinese hamster cells 2DKFZp781P0919
83Hs.592325NM_005432XRCC3X-ray repair complementing defective repair in Chinese hamster cells 3XRCC3
84Hs.444451NM_016653ZAKSterile alpha motif and leucine zipper containing kinase AZKAZK/MLK7
Gene table of the 84 genes assayed with Human DNA Damage Signaling pathway PCR array RT2Profiler.

Experimental design, materials and methods

Instruments and reagents

Agarose gels with normal and low melting points were purchased from the Biowest Company (Miami, FL, USA). TrisHCl, DMSO, NaHCO3, formaldehyde (A.P.), trypan blue and TritonX-100 were purchased from Sigma (St. Louis, MO, USA). The electrophoresis apparatus was purchased from BIO-RAD (Hercules, CA, USA), and the Nikon90i fluorescence microscope was purchased from NIKON (Tokyo, Japan). The comet slides were purchased from Trevigen. Inc. (Gaithersburg, MD, USA).

Routine semen analysis

The procedure of routine semen analysis was performed according to the standard methods in the WHO manual [2]. Briefly, the semen samples were examined immediately after liquefaction or within one hour of ejaculation. All the semen samples were ensured to be homogeneous by mixing thoroughly. A fixed volume of 10 μl semen was delivered onto a clean glass slide and covered with a coverslip. Scanning the slide and estimating the number of spermatozoa per 400× magnification field gives an approximate sperm concentration in 106/ml. This estimate is used to decide the dilution (1:5, 1:10, 1:20, 1:50) for determining the sperm concentration by hemocytometry. The spermatozoa concentration was determined using the hemocytometer method on two separate preparations of the semen sample. The diluted semen sample was dropped onto the hemocytometer and covered with a coverslip, and was placed in a humid chamber for about five minutes to prevent drying out. The cells sedimented during this time and were then counted. The count only included complete spermatozoa (heads with tails). Any sperm lying on the line dividing two adjacent squares was counted only if it was on the upper or the left side of the square being assessed.

Alkaline Comet assay

Spermatozoa or lymphocytes were suspended in PBS at a concentration of 1 × 105/ml. The comet assay, also called single cell gel electrophoresis, was performed as previously reported [3]. Briefly, comet slides were coated with 100 μl of 0.75% (w/v) normal-melting-point agarose. Once the first agarose layer was coagulated, a mixture of 75 µl of low-melting-point agarose and 25 µl of spermatozoa suspension was applied as the second layer. The comet slides were immersed in cold lysis buffer (2.5 M NaCl, 0.5 M EDTA, 10 mM Tris HCl pH 10.0 containing 1% Triton X-100, 40 mM dithiothreitol and 100 μg/ml proteinase K) for 2 h at room temperature to remove any DNA-associated proteins. After lysis, double-distilled water was used to rinse away excess salt. All the comet slides were then placed in buffer for 20 min in a horizontal electrophoresis tank that was pre-filled with cold alkaline buffer (1 mM Na2EDTA and 0.3 M NaOH, pH 13.0) to loosen the tight double-helical structure of DNA for electrophoresis. Electrophoresis was then performed at 25 V and 10 mA for 20 min in electrophoresis buffer at room temperature. The slides were then rinsed twice with distilled water and stained with ethidium bromide (2 µg/ml). All of the above procedures were carried out in the dark to avoid additional DNA damage. The comets were viewed using a Nikon 90i fluorescence microscope, and images of 100 comets were collected for each subject using a digital imaging system. Cells that overlapped were not counted. All the comet images were analyzed using Comet Assay Software Project (CASP, Wroclaw University, Poland) [4] and the DNA percentage in the comet tail (TDNA%), the tail moment (TM) and the Olive tail moment (OTM) were recorded to describe the DNA damage to the spermatozoa or lymphocytes.
Subject areaEnvironment and health
More specific subject areaEnvironmental pollution, cytogenetic alteration
Type of dataTable and figure
How data was acquiredCA and CBMN were acquired using ZEISS MetaSystems (Germany). DNA damage was detected by comet assay.
Data formatAnalyzed
Experimental factorsSemen and blood were sampled from the two groups in our lab.
Experimental featuresLymphocytes were cultured in RPMI 1640 medium for CA and CBMN assay. Spermatozoa or lymphocytes were suspended in PBS for comet assay.
Data source locationInstitute of Radiation Medicine, Chinese Academy of Medical Sciences & Peking Union Medical College
Data accessibilityAll the data are in this data article.
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