10
H. AKSOY
ET AL.
JOURNAL
OF APPLIED
TOXICOLOGY
J. Appl. Toxicol. 2006; 26: 10–15
Published online 12 September 2005 in Wiley InterScience (www.interscience.wiley.com). DOI: 10.1002/jat.1098
Genotoxicity study in lymphocytes of offset printing
workers
Hüseyin Aksoy,1 Serkan Yılmaz,1 Mustafa Çelik,2 Deniz Yüzba6ıoglu1* and Fatma Ünal1
1
2
Gazi Üniversitesi, Fen-Edebiyat Fakültesi, Biyoloji Bölümü, 06500 Teknikokullar, Ankara, Turkey
Sütçü Imam Üniversitesi, Fen-Edebiyat Fakültesi, Biyoloji Bölümü, Kahramanmara6, Turkey
Received 18 April 2004; Revised 20 June 2005; Accepted 20 June 2005
ABSTRACT: The potential cytogenetic damage in offset printing workers was evaluated using sister chromatid exchanges (SCEs), chromosome aberrations (CAs) and micronuclei (MN) as biomarkers in peripheral lymphocytes of 26 volunteers (14 workers, 12 controls). The CA, SCE and MN frequency of offset printing workers was significantly higher
than in their controls. The replication index (RI) was not affected while the mitotic index (MI) was affected most in the
workers. It can be concluded from this study that chronic occupational exposure to printing dyes and thinner may lead
to a slightly increased risk of genetic damage among offset printing workers. Copyright © 2005 John Wiley & Sons, Ltd.
KEY WORDS: offset printing workers; occupational exposure; sister chromatid exchanges (SCEs); chromosome aberrations
(CAs); micronuclei (MN)
Introduction
In recent years, there has been an increased problem
of human exposure to potentially toxic chemicals in
the work place. A large volume of epidemiological data
deals with potential cancer risks in printing processes.
Svensson et al. (1990) reported that a significant increase
in cancers of the respiratory tract was observed among
rotogravure printers. Aerosols from high speed rotary
printing machines consist of ink mists, which are believed
to induce lung cancer (Leon et al., 1994). In addition
some studies reported that kidney cancer, urinary bladder
cancer and leukemia were shown among printing workers
(IARC, 1996).
Offset printing workers are exposed to offset printing
dyes and thinner. Offset printing dyes contain cobalt and
hydroquinone. Cobalt is a heavy metallic chemical element. It is a member of group VIII of the periodic table.
It is used for cancer therapy and in industry for detecting
flaws in metal parts. The overall genetic evaluation was
that cobalt and its compounds are possibly carcinogenic
to humans (group 2B) (IARC, 1991). In the same evaluation, cobalt (II) compounds were reported to induce
DNA damage, DNA protein cross links, gene mutations,
sister chromatid exchanges and aneuploidy in in vitro
studies on animal and human cells. There was some
evidence that cobalt (II) compounds could also induce
aneuploidy in vivo in Syrian hamster bone marrow and
testes (IARC, 1991). Another chemical used in printing,
* Correspondence to: Deniz Yuzbasıoglu, Gazi Üniversitesi, Fen-Edebiyat
Fakultesi, Biyologi Bölümü, 06500 Teknikokullar, Ankara, Turkey.
E-mail: deniz@gazi.edu.tr
Copyright © 2005 John Wiley & Sons, Ltd.
hydroquinone, is extensively used as a reducing agent
and as a photographic developer. It is a skin-lightening
agent and is used in cosmetics, hair dyes and medical
preparations (WHO, 1996). Knadle (1985) reported
that hydroquinone induced sister chromatid exchanges
(SCEs) at relatively high concentrations in human
lymphocytes. Stillman et al. (1999) reported that hydroquinone induced hypoploidy in a human lymphoblastoid
cell line GM09948. Offset printing workers also use
widely an industrial thinner containing toluene (about
65%) for the cleaning of the offset machines. Bauchinger
et al. (1982) and Schmid et al. (1985) reported an increased incidence of SCEs in individuals occupationally
exposed to toluene. A high incidence of chromosomal
aberrations (CA) and sister chromatid exchanges in the
lymphocytes of rotogravure printing workers has been
reported. The CA and SCE frequencies were higher in
workers than in the control groups (Pelclova et al., 1990;
Hammer et al., 1998). However, some studies in the literature showed that there was no relationship between
chronic occupational exposure to toluene and increased
incidence of chromosomal aberration (Haglung et al.,
1980; Maki-Paakkanen et al., 1980; Richer et al., 1993).
Genotoxicity biomarkers have received considerable
interest as tools for detecting human genotoxic exposure and effects. The largest databases are available
for CA; a high CA level has been associated with an
increased cancer risk while the frequencies of SCEs and
micronucleus (MN) were not associated with cancer risk
(Hagmar et al., 1998a,b; Bonassi et al., 2000). The induction of SCEs has been described as a rapid and sensitive
end-point for testing mutagenicity. An increase of
SCE frequency can be an indicator of persistent DNA
J. Appl. Toxicol. 2006; 26: 10–15
GENOTOXICITY STUDY IN OFFSET PRINTING WORKERS 11
damage (Palitti et al., 1982; Cardoso et al., 2001). The
cytokinesis-blocked micronucleus assay is used to detect
acentric chromosome fragments or whole chromosomes
left upon nucleus division and visible as small additional
nuclei in the cytoplasm. Hence, the appearance of micronuclei should point to clastogenic and/or aneugenic
effects (Giri et al., 2002).
This paper analysed cytogenetic damage in peripheral
blood lymphocytes of offset printing workers by using
CAs, SCEs and micronucleus assay (MN). Changes in
cell proliferation kinetics through the replication index
(RI) and cytotoxic effect by means of the mitotic index
(MI) were also evaluated.
dried at room temperature and mounted with depex. For
the SCE study, the slides were stained with Giemsa
according to the method of Speit and Houpter (1985)
with some modifications.
The mitotic index (MI) was determined by scoring
1000 cells from each donor. Chromosomal abnormalities
were scored from 100 well-spread metaphases per donor.
For the occurrence of the number of SCEs, a total of
25 cells from each donor under second metaphases was
scored. In addition, 100 cells from each donor were
scored for the determination of the replication index (RI).
The RI, calculated according to the following formula
[1 × M1] + [2 × M2] + [3 × M3]/N
Material and Methods
Twenty six volunteers (14 exposed, 12 controls) were
studied in this work. The volunteers were selected
according to their ages and smoking habit. Three age
groups were selected: 16–25, 26–35 and 36–45. None
of the volunteers had any problems relating to health,
alcohol and drug consumption. Six of the exposed
workers were smokers, the others were nonsmokers.
Their ages were in the range 18–45 years and averaged
27.64 years. The mean duration of employment was
10.36 years (min. 1 year, max. 30 years). The working
period was 45 h per week. A total of 12 male blood
donors from the Gazi University of Ankara were used as
a control group. This group consisted of six smokers and
six nonsmokers, aged 22–38 years (average 28.70 years).
The preparations of cells were made by the following
procedures.
SCE and CA Analysis
Human peripheral blood cells were used as the test systems. Heparinized blood (1/10: 2 ml venous blood containing 0.2 ml heparin) was collected and stored at +4 °C
for 30 min. The whole blood was added to 2.5 ml
chromosome medium B (Biochrom) supplemented with
10 µg ml−1 bromodeoxyuridine. The cultures were incubated at 37 °C for 72 h. 0.06 µg ml−1 colchicine was
added 2 h prior to the harvesting of the culture. Then,
the cells were harvested by centrifugation (1200 rpm,
10 min), and the pellet was resuspended in a hypotonic
solution of 0.075 M KCl for 30 min at 37 °C. Following
this process, the cells were centrifuged again and fixed
in a cold methanol:acetic acid (3:1) mixture for 35 min
at +4 °C. At the end of this procedure, the cells were
treated with fixative two times. Then slides were made by
dropping and air drying.
For chromosome aberrations, slides were stained with
5% Giemsa (pH = 6.8) prepared in Sorensen buffer solution, for 20–25 min, and then washed in distilled water,
Copyright © 2005 John Wiley & Sons, Ltd.
where N represents the number of observed cells, M1, M2
and M3 represent the number of cells undergoing first,
second and third mitosis (Lin et al., 1987).
MN Analysis
In this analysis the blood samples were added to 2.5 ml
chromosome medium B (Biochrom). The cultures were
incubated at 37 °C for 72 h. At 44 h after beginning the
culture, cytocalasin-B (5.2 µg ml−1) was added to each
culture. Then, the cells were harvested by centrifugation
(1000 rpm, 10 min), and the pellets were resuspended in
a hypotonic solution of 0.075 M KCl for 5 min at +4 °C.
The cells were again centrifuged and fixed in the cold
methanol:acetic acid (3:1) mixture for 15 min. The
fixation procedure was applied three times. Into the last
fixative, 1% formaldehyde was added to preserve the
cytoplasm. The slides were made by dropping and air
drying. For the MN analysis, the slides were stained with
5% Giemsa (pH = 6.8), prepared in Sorensen buffer
solution, for 20–25 min, washed in distilled water,
dried at room temperature and mounted with depex.
Micronuclei were scored from 1000 binucleated cells
per donor.
Statistical Analysis
The significance between the percentage of abnormal
cells, CA/cell, RI, MI and MN in cultures and their controls were determined using the z-test. The significance
between mean SCE in treated cultures and their controls
were determined using the t-test.
Results
In this study, 26 volunteers were studied. Of these, 14
were offset printing workers and 12 were controls. As
shown in the Fig. 1 and Table 1, the abnormal cell ratio
J. Appl. Toxicol. 2006; 26: 10–15
12
H. AKSOY ET AL.
Table 1. Types and distribution of chromosome aberrations in offset printing workers according to smoking habit
and age
Group
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Age
16–25
16–25
26–35
26–35
36–45
36–45
Smoking
habit
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
No. of
subjects
2
3
2
3
2
1
2
3
2
2
2
2
No. of cells
scored
200
300
200
300
200
100
200
300
200
200
200
200
Aberrations
Abnormal
cell ± SE (%)
B′
B″
SU
DC
ER
F
P
CE
6
23
—
29
8
10
1
27
6
13
2
15
—
6
—
3
—
1
—
3
—
6
—
3
—
16
3
12
—
2
3
3
—
17
1
2
—
9
—
15
—
1
—
4
2
9
1
2
—
1
—
2
—
1
—
—
—
—
—
—
—
1
—
1
—
—
—
4
—
4
1
2
—
—
—
—
—
—
—
1
—
4
—
—
—
—
—
1
2
—
—
—
—
—
—
—
3.00
16.00
1.50
18.33
2.50
13.33
2.00
14.00
2.00
26.00
2.50
11.00
±
±
±
±
±
±
±
±
±
±
±
±
1.21
2.12a
0.86
2.24a
1.10
3.40a
0.98
2.00a
0.99
3.10a
1.00
2.21a
CA/cell ± SE
0.030
0.190
0.015
0.210
0.050
0.150
0.020
0.140
0.040
0.270
0.025
0.120
±
±
±
±
±
±
±
±
±
±
±
±
0.01
0.02a
0.01
0.02a
0.01
0.04a
0.01
0.06a
0.01
0.03a
0.01
0.02a
B′, chromatid break; B″, chromosome break; SU, sister chromatid union; DC, dicentric chromosome; ER, endoreduplication; F, fragment; P, polyploidy;
CE, chromatid exchange.
a
Significant from the control P < 0.001 (z-test).
Figure 1. Chromosome aberrations in peripheral
blood lymphocytes of smoker and nonsmoker offset
printing workers and their controls
was significantly increased compared with their controls.
In the smoker workers the increase of abnormal cells was
higher than in the nonsmokers. The CA/cell ratio significantly increased in exposed groups when compared with
the controls. Also the increase of CA/cell was higher
in the smoker groups than in the nonsmoker groups
in the 26–35 and 36–45 age groups (Table 1). The
eight types of abnormalities recorded were chromatid and
chromosome breaks, sister chromatid union, dicentric
chromosomes, endoreduplication, fragment, polyploidy
and chromatid exchange. Chromatid breaks and sister
chromatid union were observed as the most common
aberrations (Fig. 2).
The replication index (RI) was not affected in the
worker groups but the mitotic index was decreased
significantly in all the age groups of nonsmokers
(Table 2). The SCE frequency was significantly increased
in exposed groups when compared with their controls
(Table 2, Fig. 3). In all exposed groups, the SCE
frequency was higher in the smoker workers than in the
nonsmoker workers.
The micronuclei frequency was significantly increased
in all exposed groups except in the smoker workers
Copyright © 2005 John Wiley & Sons, Ltd.
Figure 2. Most common aberrations observed in
offset printing workers, (a) chromatid break (b) sister
chromatid union
of the 16–25 age group (Table 3). The frequency of
micronuclei was significantly higher in exposed groups
compared with their controls in total (Fig. 4). In all
J. Appl. Toxicol. 2006; 26: 10–15
GENOTOXICITY STUDY IN OFFSET PRINTING WORKERS 13
Table 2. Distribution of SCE, RI and MI in peripheral blood lymphocytes of offset printing workers according to
smoking habit and age
Groups
Ages
Smoking
habit
No. of
subjects
No. of cells
scored (SCE)
Min-max
SCE
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
16–25
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
2
3
2
3
2
1
2
3
2
2
2
2
50
75
50
75
50
25
50
75
50
50
50
50
2–12
5–20
2–9
5–15
1–14
5–20
1–19
4–17
5–23
5–20
2–8
6–15
a
b
c
d
Significant
Significant
Significant
Significant
16–25
26–35
26–35
36–45
36–45
from
from
from
from
the
the
the
the
control
control
control
control
P
P
P
P
<
<
<
<
SCE/cell
± SE
6.28
9.97
4.68
8.75
5.68
9.48
4.70
8.51
8.20
9.80
5.12
9.20
±
±
±
±
±
±
±
±
±
±
±
±
0.41
0.35b
0.23
0.29b
0.45
0.74b
0.46
0.29b
0.61
0.47a
0.29
0.32b
M1
M2
M3
38
48
40
46
10
16
42
54
30
69
44
29
50
108
57
93
50
25
81
105
52
66
70
62
112
144
103
161
140
59
77
141
118
65
86
109
RI ± SE
2.37
2.32
2.32
2.38
2.75
2.43
2.18
2.29
2.44
1.98
2.21
2.40
±
±
±
±
±
±
±
±
±
±
±
±
0.05
0.04
0.05
0.04
0.04
0.08
0.05
0.04
0.05
0.06
0.06
0.06
MI ± SE (%)
3.20
3.90
5.50
3.83
4.20
4.60
7.60
3.57
4.50
3.85
6.25
4.05
±
±
±
±
±
±
±
±
±
±
±
±
0.39
0.35
0.51
0.35c
0.44
0.66
0.59
0.34d
0.46
0.43
0.54
0.44c
0.05 (t-test)
0.01 (t-test)
0.01 (z-test)
0.001 (z-test)
Table 3. Distribution of MN in peripheral blood lymphocytes of offset printing workers according to smoking
habit and age
Groups
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
Controls
Workers
a
b
Ages
16–25
16–25
26–35
26–35
36–45
36–45
Smoking
habit
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
Smoker
Smoker
Nonsmoker
Nonsmoker
No. of
subjects
BN cells
scored
2
3
2
3
2
1
2
3
2
2
2
2
2000
3000
2000
3000
2000
1000
2000
3000
2000
2000
2000
2000
Distribution of BN cells
according to the no. of MN
(1)
(2)
(3)
(4)
8
16
4
15
10
11
2
20
4
19
8
18
0
2
0
1
0
1
0
4
0
2
2
1
0
0
0
1
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
MN/cell (%)
0.40
0.67
0.20
0.67
0.50
1.30
0.10
0.93
0.20
1.15
0.60
1.00
±
±
±
±
±
±
±
±
±
±
±
±
0.138
0.148
0.094
0.148a
0.154
0.357b
0.063
0.173b
0.094
0.236b
0.170
0.221a
Significant from the control P < 0.05 (z-test)
Significant from the control P < 0.001 (z-test)
Figure 3. Sister chromatid exchanges in peripheral
blood of offset printing workers according to smoking
habit and their controls
Figure 4. MN in peripheral blood of offset printing
workers according to smoking habit and their controls
exposed groups (except the 16–25 age group), the MN
frequency was higher in the smoker workers than in the
nonsmoker workers but this result was not statistically
significant.
Discussion
Copyright © 2005 John Wiley & Sons, Ltd.
In this study the CA, SCE and MN (except smokers
of the 16–25 age group) frequency of exposed workers
J. Appl. Toxicol. 2006; 26: 10–15
14
H. AKSOY ET AL.
significantly increased in all the age groups compared
with their controls. The MI value was significantly
decreased only in the nonsmoker groups. However, the
RI value was not affected in workers when compared
with the controls.
In this investigation, eight types of chromosomal
aberrations were observed and it was found that the
most common aberrations were chromatid breaks and
sister chromatid union. Pelclova et al. (1990) reported
that chromatid and chromosome breaks, gaps, chromatid
and chromosome exchanges were observed in rotogravure
printing workers. Genotoxicity of toluene was investigated in rotogravure printing plant workers and a
significant increase was observed only in chromatid
breaks (Pelclova et al., 2000).
Printing dyes used by offset printing workers contain
cobalt and hydroquinone. Some researchers have shown
that cobalt was possibly carcinogenic to humans (IARC,
1991) and that hydroquinone was positive for cytogenetic
effects, which included induction of micronuclei (Yager
et al., 1990; Robertson et al., 1991; Vian et al., 1995)
and sister chromatid exchanges (Erexson et al., 1985;
Knadle, 1985). However, Roza et al. (2003) reported that
hydroquinone was cytotoxic, but did not induce chromosomal aberrations in human lymphocytes culture in vitro.
Offset printing workers also use thinner for machine
cleaning processes. Thinner contains a high amount of
toluene and some researchers have reported that occupational exposure to toluene increased the incidence of
SCEs (Bauchinger et al., 1982; Schmid et al., 1985;
Pelclova et al., 2000). In contrast, some studies showed
that there was no relationship between chronic occupational exposure to toluene and increased incidence of
chromosomal aberration and sister chromatid exchanges
(Haglung et al., 1980; Maki-Paakkanen et al., 1980;
Richer et al., 1993). Pelclova et al. (1990) reported that
CA frequency was increased in rotogravure printing
workers compared with controls. In another study Hammer et al. (1998) reported that the SCE frequency was
significant at a high confidence level in rotogravure printing workers. The authors pointed out a strong relationship
between individual toluene burden and the genotoxic risk
of the exposed workers.
Many studies have been carried out to evaluate the
cytogenetic effects of occupational exposure to various
health hazard chemicals in different field workers. Sardas
et al. (1994) reported that the frequency of SCE was
higher in workers employed in car-painting workshops.
The genotoxicity study carried out by Topaktas et al.
(2002) in workers of an iron and steel factory showed
that the frequency of CA was higher, while the frequency
of the SCE was not in all the smoker-nonsmoker workers,
than in the smoker-nonsmoker control groups. In addition, the authors observed that there was no significant
decrease in the RI, but the MI was significantly lower
in exposed groups than in the controls. Bogadi-Sare
Copyright © 2005 John Wiley & Sons, Ltd.
et al. (1997) reported that exposure to benzene and
toluene increased the CA frequency in the lymphocytes
of workers. The genotoxicity study of Swedish paint
industry workers showed that there was no significant
increase in the frequency of CA and SCE (Haglung et al.,
1980). Pastor et al. (2001) reported that a comparison between workers and controls did not reveal any
statistical significant difference in the MN frequency for
either lymphocytes or buccal cells in Greek farmers.
Genotoxicity research in wooden furniture workers has
shown that micronuclei and SCE frequency in exposed
groups was higher than in the controls (Elavarasi et al.,
2002). Iravathy Goud et al. (2004) reported that there is
a significant increase in the frequency of MN in buccal
epithelial cells and peripheral blood lymphocytes as well
as chromosomal aberrations in individuals working with
photocopying machines. A significant increase in the formation of SCE, CA and MN frequencies were reported in
Pb-Zn miners exposed to heavy metals (Bilban, 1998).
In the literature, several studies demonstrated that CA,
SCE and MN frequencies generally increased in workers
occupationally exposed to the environmental contaminants discussed above. Some of these investigations
revealed that there is a relationship between age, smoking and increase in abnormalities (Maki-Paakkanen et al.,
1980; Topaktas et al., 2002). Whereas, some investigators
reported that there was no relationship between age,
smoking and increasing abnormalities (Khalil et al.,
1994; Surrales et al., 1997).
Data obtained in this study showed that the CA, SCE
and MN frequency of the exposed workers were higher
than the controls. The CA frequency and CA/cell was
almost equal in smoker and nonsmoker workers in the
16–25 and 26–35 age groups but higher only in smokers
of the 36– 45 age group than in the nonsmokers. A strong
relationship between CA and smoking habit, age and
exposure to pollutants was observed. In all exposed
groups, the SCE and MN (except the 16–25 age group)
frequency was higher in smokers than in nonsmokers.
However, the increase of SCE and MN frequency was
not associated with age. As a result, the present study
showed that the CA analysis was more sensitive to environmental contaminants than other cytogenetic end-points.
It can be concluded from this study that chronic occupational exposure to printing dyes and toluene leads to an
increased risk of genetic damage among offset printing
workers. The genotoxic and potential carcinogenic risks
of printing dyes and toluene should be taken into account
in the process of offset printing.
References
Bauchinger M, Schmid E, Dresp J, Kolin-Gerresheim J, Hauf R,
Suhr E. 1982. Chromosome changes in lymphocytes after occupational exposure to toluene. Mutat. Res. 102: 439– 445.
J. Appl. Toxicol. 2006; 26: 10–15
GENOTOXICITY STUDY IN OFFSET PRINTING WORKERS 15
Bilban M. 1998. Influence of the work environment in a Pb-Zn mine on
the incidence of cytogenetic damage in miners. Am. J. Ind. Med. 34:
455–463.
Bogadi-Sare A, Brumen V, Turk R, Karacic V, Zavalic M. 1997.
Genotoxic effects in workers exposed to benzene: with special
reference to exposure biomarkers and confounding factors. Ind.
Health 35: 367–373.
Bonassi S, Hagmar L, Stromberg U, Montagud AH, Tinnerberg H,
Forni A, Heikkila P, Wanders S, Wilhardt P, Hansteen IL,
Knudsen LE, Norppa H. 2000. Chromosomal aberrations in
lymphocytes predict human cancer independently of exposure to
carcinogens. European Study Group on Cytogenetic Biomarkers
and Health. Cancer Res. 60: 1619–1625.
Cardoso RS, Takahashi-Hyodo S, Peitl Jr P, Ghilardi-Neto T,
Sakamoto-Hojo ET. 2001. Evaluation of chromosomal aberrations,
micronuclei, and sister chromatid exchanges in hospital workers
chronically exposed to ionizing radiation. Teratog. Carcinog.
Mutagen. 21: 431–439.
Elavarasi D, Ramakrishnan V, Subramoniam T, Ramesh A,
Cherian KM, Emmanuel C. 2002. Genotoxicity study in lymphocytes
of workers in wooden furniture industry. Current Sci. 82: 869–873.
Erexson GL, Wilmer JL, Kligerman AD. 1985. Sister chromatid
exchange induction in human lymphocytes exposed to benzene and
its metabolites in vitro. Cancer Res. 45: 2471–2477.
Giri S, Giri A, Sharma GD, Prasad SB. 2002. Mutagenic effects of
carbosulfan, a carbamate pesticide. Mutat. Res. 519: 75–82.
Haglung U, Lundberg I, Zech L. 1980. Chromosome aberrations and
sister chromatid exchanges in Swedish paint industry workers. Scand.
J. Work Environ. Health 6: 291–298.
Hagmar L, Bonassi S, Stromberg U, Brogger A, Knudsen LE,
Norppa H, Reuterwall C. 1998a. Chromosomal aberrations in
lymphocytes predict human cancer: a report from the European Study
Group on Cytogenetic Biomarkers and Health (ESCH). Cancer Res.
58: 4117– 4121.
Hagmar L, Bonassi S, Stromberg U, Mikoczy Z, Lando C, Hansteen IL,
Montagud AH, Knudsen L, Norppa H, Reuterwall C, Tinnerberg H,
Brogger A, Forni A, Hogstedt B, Lambert B, Mitelman F,
Nordenson I, Salomaa S, Skerfving S. 1998b. Cancer predictive value
of cytogenetic markers used in occupational health surveillance programs: a report from an ongoing study by the European Study Group
on Cytogenetic Biomarkers and Health. Mutat. Res. 405: 171–178.
Hammer KD, Mayer N, Pfeifer EH. 1998. Sister chromatid exchanges
in rotogravure printing plant workers Int. Arch. Occup. Environ.
Health 71: 138–142.
IARC 1991. Cobalt and cobalt compounds. Monogr. Eval. Carcinog.
Risks Hum. 52: 363–472.
IARC. 1996. Printing processes (Occupational exposure Group 2B) and
printing inks (Group 3). Monogr. Eval. Carcinog. Risks Hum. 65:
33–149.
Iravathy Goud K, Hasan Q, Balakrishna N, Prabhakar Rao K, Ahuja
YR. 2004. Genotoxicity evaluation of individuals working with
photocopying machines. Mutat. Res. 563: 151–158.
Khalil AM, Qassem W, Kamal OM. 1994. No significant increase
in sister chromatid exchanges in cultured blood lymphocytes from
workers in a large oil refinery. Mutat. Res. 312: 187–191.
Knadle S. 1985. Synergistic interaction between hydroquinone and
acetaldehyde in the induction of sister chromatid exchange in human
lymphocytes in vitro. Cancer Res. 45: 4853– 4857.
Leon DA, Thomas P, Hutchings S. 1994. Lung cancer among newspapers printers exposed to ink mist: a study of trade union members
of Manchester, England. Occup. Environ. Med. 51: 87–94.
Lin MF, Wu CL, Wang TC. 1987. Pesticide clastogenicity in Chinese
hamster ovary cells. Mutat. Res. 188: 241–250.
Copyright © 2005 John Wiley & Sons, Ltd.
Maki-Paakkanen J, Husgafvel-Pursiainen K, Kalliomaki PL, Tuominen
J, Sorsa M. 1980. Toluene-exposed workers and chromosome aberrations. J. Toxicol. Environ. Health 6: 775–781.
Palitti FC, Tanzarella R, Cozzi R, Ricondy E, Vitagliana A, Fiori M.
1982. Comparison of frequencies of SCEs induced by chemical
mutagens in bone-marrow spleen and spermatogoneal cells of mice.
Mutat. Res. 103: 191–195.
Pastor S, Gutiérrez S, Creus A, Xamena N, Piperakis S, Marcos R.
2001. Cytogenetic analysis of Greek farmers using the micronucleus
assay in peripheral lymphocytes and buccal cells. Mutagenesis 16:
539–545.
Pelclova D, Cerna M, Pastorkova A, Vrbikova V, Prochazka B,
Hurychova D, Dlaskova Z, Hornychova M. 2000. Study of the
genotoxicity of toluene. Arch. Environ. Health 55: 268–273.
Pelclova D, Rössner P, Pickova J. 1990. Chromosome aberrations
in rotogravure printing plant workers. Mutat. Res. 245: 299–
303.
Richer CL, Chakrabarti S, Senecal-Quevillon M, Duhr MA, Zhang XX,
Tardif R. 1993. Cytogenetic effects of low level exposure to toluene,
xylene and their mixture on human blood lymphocytes. Int. Arch.
Occup. Environ. Health 64: 581–585.
Robertson ML, Eastmond DA, Smith MT. 1991. Two benzene
metabolites, catechol and hydroquinone, produce a synergistic induction of micronuclei and toxicity in cultured human lymphocytes.
Mutat. Res. 249: 201–209.
Roza L, De Vogel N, Van Delft JHM. 2003. Lack of clastogenic effects
in cultured human lymphocytes treated with hydroquinone. Food
Chem. Toxicol. 41: 1299–1305.
Sardas S, Karakaya AE, Furtun Y. 1994. Sister chromatid exchange
in workers employed in car-painting workshops. Int. Arch. Occup.
Environ. Health 66: 33–35.
Schmid E, Bauchinger M, Hauf R. 1985. Chromosome changes with
time in lymphocytes after occupational exposure to toluene. Mutat.
Res. 142: 37–39.
Speit G, Houpter S. 1985. On the mechanisms of differential giemsa
staining of bromodeoxyuridine-substituted chromosomes. II. Differences between the demonstration of sister chromatid differentiation
and replication patterns. Hum. Genet. 70: 126–129.
Stillman WS, Varella-Garcia M, Irons RD. 1999. The benzene
metabolites hydroquinone and catechol act in synergy to induce dosedependent hypoploidy and −5q31 in a human cell line. Leuk. Lymph.
35: 269–281.
Surrales J, Autio K, Nylund L, Jarventaus H, Norppa H, Veidebaum T,
Sorsa M, Peltonen K. 1997. Molecular cytogenetic analysis of
buccal cells and lymphocytes from benzene-exposed workers.
Carcinogenesis 381: 163–170.
Svensson BG, Nise G, Englander V, Attewell R, Skerfing S, Möller T.
1990. Dead and tumors among rotogravure printers exposed to
toluene. Br. J. Ind. Med. 47: 372–379.
Topaktas M, Rencüzogulları E, Ila HB, Kayraldiz A. 2002. Chromosome aberration and sister chromatid exchange in workers of the iron
and steel factory of Iskenderun Turkey. Teratog. Carcinog. Mutagen.
22: 411– 423.
Vian L, Van Hummelen P, Bichet N, Gouy D, Kirsch-Volders M. 1995.
Evaluation of hydroquinone and chloral hydrate on the in vitro
micronucleus test on isolated lymphocytes. Mutat. Res. 334: 1–7.
WHO. 1996. IPCS International Programme On Chemical Safety.
Health and Safety Guide No. 101. Hydroquinone Health and Safety
Guide. United Nations Environment Programme International Labour
Organisation. WHO: Geneva.
Yager JW, Eastmond DA, Robertson ML, Paradisin WM, Smith MT.
1990. Characterization of micronuclei induced in human lymphocytes
by benzene metabolites. Cancer Res. 50: 393–399.
J. Appl. Toxicol. 2006; 26: 10–15