Mutation Research
Year 1997; Volume 393; Pages 283-288.
Chromosomal aberrations and micronuclei
in lymphocytes of workers at a phosphate fertilizer factory
Ziqiang Meng, Bo Zhang
Division of Environmental Biological Toxicology,
Department of Life Sciences, Shanxi University, Taiyuan 030006,
China
Abstract
The frequencies of chromosomal aberrations (CA)
and micronuclei (MN) in peripheral blood lymphocytes of 40 workers
at a phosphate fertilizer factory in North China, were studied.
HF and SiF4 are the main air pollutants and small amounts of dust
containing fluoride, NH3 and S02 were also present in the factory.
It was shown that the chemicals caused an increase in both CA and
MN. The mean frequencies per 100 metaphase of major CA type (chromosome
rings, translocations, and dicentrics) of the workers and the non-exposed
controls were 0.91 and 0.24 (p < 0.01), respectively. The average
percentages of lymphocytes with MN of the workers and the controls
were 1.55 ± 0.71 and 0.62 + 0.54 (p < 0.01), respectively.
Both CA frequency and MN frequency of the workers increased with
length of the chemical exposure period up to 10 years.
Keywords: Fluoride; Chromosomal aberration; Micronuclei;
Human lymphocyte
1. Introduction
Fluoride is a ubiquitous substance found naturally
in food and water, and it is also a common air pollutant in some
industrial productions. A number of studies of the genotoxic effects
of fluoride have been conducted in a variety of systems, including
plants, bacteria, fruit flies, animals, and also human cells. However,
the results on this topic have been conflicting. Some studies have
reported that fluoride is a mutagenic
agent and causes chromosomal damage, but other investigations have
showed fluoride does not produce genotoxic effects [1- 14].
To examine possible damage to the genetic apparatus
at chromosomal level caused by exposure of workers to air pollution
in a phosphate fertilizer factory, in which HF and SiF4 are the
main air pollutants, we analyzed the peripheral blood lymphocytes
of the workers for chromosomal aberrations (CA) and micronuclei
(MN). The present studies provide evidence that chronic exposure
of workers to the air pollutants in the factory is associated with
increased CA and MN in their blood lymphocytes.
2. Materials and methods
2. 1. Chemical pollutants
In the air of the workplace of the phosphate fertilizer
factory, fluorine (F), sulfur dioxide (S02), ammonia (NH3), and
floating dust (particle diameter: < 10 um) were analyzed with
the selecting electrode method of fluorine ions, pararosaniline
hydrochloride spectrophotometry, sodium hypochlorate-salicylate
spectrophotometry, and the weight method, respectively [15]. The
concentrations of these chemicals varied irregularly over one year
in this workplace, the range for F concentrations was from 0.50
to 0.80 mg/m3 air at the time of investigation, for S02 was from
0.02 to 0.07 mg/m3, for NH3 was from 0.01 to 0.05 mg/m3, for the
floating dust was from 0.05 to 0.20 mg/m3. These data indicated
that the air pollutant in the workplace was mainly fluorine (HF
and SiF4).
2.2. Subjects
The subjects were 40 workers exposed mainly to
fluoride (HF, and SiF4) within the same workplace of the phosphate
fertilizer factory, and 40 controls, working and studying in Shanxi
University, situated in the same city as the factory, matched according
to sex, age and smoking habits. It was difficult to find enough
people in the factory who were not exposed to fluoride or other
chemicals as a control population, so university staff in the same
city were chosen as controls. The income levels of the workers and
the university staff controls were generally similar at the time
of investigation, but data on the socio-economical levels and nutritional
status of the subjects were not collected and analyzed. All subjects
were interviewed about recent viral infections, vaccinations, previous
occupational exposure to chemicals, drug intake and alcohol consumption.
No difference in these respects could be found between the worker
and the control group. Occupational exposure to the chemicals had
not caused clinical symptoms in workers and all controls were also
healthy.
2.3. Cell culture
Venous blood was drawn into heparinized tubes and
the samples coded and cultures established the same day according
to the technique of Hungerford [16] with minor modifications. To
culture lymphocytes whole blood (0.2 ml) was added to 4.8 ml of
RPMI1640 medium containing 20% new calf serum, 100 units/ml penicillin,
100 ug/ml streptomycin and 2% phytohemagglutinin M (PHA). The blood
was cultured at 37'C in 5% C02. For CA analysis, the cells were
cultured for 48 h. For the MN assay, the cells were cultured for
72 h, and the cytochalasin B (Sigma Chemical Co., final concentration
3 ug/ml) was added to the cultures 24 h prior to harvesting, according
to the method described by Fenech and Morley [17].
2.4. Analysis for CA and MN
For measuring MN frequency, cultures were centrifuged
at 80-100 X g for 6-8 min after an incubation period of 72 h. The
pelleted cells were treated to preserve the cytoplasm by gently
resuspending in 5 ml hypotonic solution of 0.075 M KCI/saline (2:8
v/v) for 3-5 min and then resuspending twice in 5 ml cold Carnoy's
fixative (methanol/glacial acetic acid, 3:1 v/v) for 20 min at room
temperature. After the final centrifugation (at 100 X g for 8 min)
cells were thoroughly mixed using the tip of a Pasteur pipette and
were dropped from a height of 3-4 cm onto wet, clean slides. For
each culture at least two slides were prepared. The slides were
air-dried and stained with 10% Giemsa for approximately 10 min.
For CA analysis, the cultures were processed in
the same way except that 0.1 ml of colcemid (final concentration:
2.7 x 10-5 M) was added to each culture for mitotic arrest 4 h before
harvest and the hypotonic treatment was performed with prewarmed
0.075 M KCI for 15 min at 37'C. The air-dried slides were stained
with 10% Giemsa.
2.5. Slide scoring
For cytogenetic analysis, preparations were coded
and scored blind. Scoring of MN was limited to binucleate lymphocytes
only with preserved cytoplasm [17], according to the criteria proposed
by Countryman and Heddle [18]. Identification of binucleate cells
in cell groups required careful visual examination of the individual
cell boundaries. The results are expressed as the average percentage
of micronucleated cells per 2000 binucleate cells on the two different
slides from the same culture.
CA were analyzed in 200 metaphase cells for each
person. Only cells with 46 chromosomes were included in the analysis.
Cells analyzed for chromatid and isochromatid breaks and other types
of aberrations [19].
2.6. Statistical analysis
The x2-test was used for the CA and the MN frequencies.
3. Results
The average percentages of chromosome-type, chromatid-type
aberrations and their total were all significantly higher (p <
0.01) in workers than in controls (Table 1). Dicentrics, centric
rings, acentric fragments and chromatid breaks were the types of
aberrations that showed a significant increase (Table 2).
Table 2 also indicates that the frequencies of
major chromosomal aberrations (including rings, translocations,
and dicentrics) in workers and in controls were 0.91% and 0.24%,
respectively. The difference between them was statistically significant
(P < 0.01).
| TABLE
1.
Frequencies of lymphocytes with chromosomal aberrations |
| Group |
Control |
Worker |
| Number of persons |
42 |
40 |
| Number of metaphases |
8400 |
8000 |
| Aberrant cells with chromosome-type aberrations
(frequency, %) |
27 (0.32 + 0.08) a |
104 (1.30 + 0.18) b |
| Aberrant cells with chromatid-type aberrations
(frequency, %) |
28 (0.33 + 0.07) |
77 (0.96 + 0.08) b |
| Total number of aberrant cells |
55 (0.65 + 0.09) |
181 (2.26 + 0.27) b |
(a) Mean frequency per
100 metaphase, %
(b) Significantly different from control by x2-test at
p < 0.01 |
| TABLE
2.
Types of chromosomal aberrations of lymphocytes |
| Group |
Control |
Worker |
| Number of subjects |
42 |
40 |
| Number of cells |
8400 |
8000 |
| Chromosome-type aberrations |
|
|
| Dicentrics |
3 (0.0357) a |
11 (0.1375) b |
| Acentric rings |
1 (0.0119) |
2 (0.0250) |
| Centric rings |
13 (0.1548) |
52 (0.6500) c |
| Acentric fragments |
2 (0.0238) |
24 (0.3000) c |
| Translocations |
3 (0.0357) |
8 (0.1000) |
| Minutes |
5 (0.0595) |
8 (0.1000) |
| Gaps |
6 (0.0714) |
85 (1.0625) c |
| Total |
27 (0.3214) |
105 (1.3125) c |
| Chromatid-type aberrations |
|
|
| Breaks |
28 (0.3333) |
73 (0.9125) c |
| Interchanges |
0 (0.0000) |
4 (0.0500) |
| Total |
28 (0.3333) |
77 (0.9625) c |
| Total chromosomal aberrations |
55 (0.6707) |
182 (2.2750) c |
(a) Mean frequency per
100 metaphase, %.
(b) Significantly different from control group by x2-test
at p < 0.05
(c) Significantly different from control group by x2-test
at p < 0.01 |
Table 3 shows the frequencies of cells with MN in peripheral blood
lymphocytes of workers were statistically significantly higher than
controls (p < 0.01). Fig. 1 shows the
frequency distribution of lymphocytes with MN among the workers;
31.0% of the controls were found not to have lymphocytes with MN.
Frequencies of cells with MN in 52.4% controls were in the range
0.10 to 1.00%, only 16.6% of the controls were in the range 1.00
to 2.00%, and none was over 2.00%. However, all subjects in the
worker group had cells carrying MN; 75% of workers were over 1.00%
and 17.50% were higher than 2.00%, these differences between the
workers and the controls were statistically significant (p <
0.01).
Analysis of the correlation between the individual
results for the micronucleus index and cells with aberrations indicated
that the correlation factor, R, was 0.426 (p < 0.01). It implies
that there is a positive correlation between MN and CA in the worker
group.
There was correlation between the mean frequency
of lymphocytes with CA or the mean frequency of lymphocytes with
MN and length of service for which workers were exposed to the air
pollutants at the factory (Table 4). Both the frequency of the cells
with CA and the frequency of the cells with MN increased with length
of pollutant exposure period up to 10 years. However, both frequencies
begin to decrease after about 10 years of pollutant exposure period.
| TABLE
3.
Frequencies of lymphocytes with micronuclei (MN) |
| Group |
Control |
Worker |
| Number of persons |
42 |
40 |
| Number of binucleate cells observed |
84 000 |
80 000 |
| Number of binucleate cells with MN |
520 |
1240 |
| Frequencies of binucleate cells with MN (X
+ SE a, %) |
0.62 + 0.54 |
1.55 + 0.71 b |
(a) Standard error of the
means from all persons of each group.
(b) Significantly different from control by x2-test at
p < 0.01 |
| TABLE
4.
Chromosomal aberrations (CA) or micronuclei (MN) and length
of service in workers at the phosphate fertilizer factory |
| Group (years) |
No. of persons |
Chromosomal aberrations |
Micronuclei |
| No. of cells observed |
No. of cells with CA |
% (X + SE) |
No. of cells observed |
No. of cells with CA |
% (X + SE) |
| < 5 |
24 |
4800 |
87 |
1.81 + 0.26 |
48 000 |
600 |
1.25 + 0.61 |
| 5-10 |
10 |
2000 |
72 |
3.60 + 0.41 a |
20 000 |
470 |
2.35 + 0.12 a |
| > 10 |
6 |
1200 |
22 |
1.83 + 0.51 |
12 000 |
170 |
1.42 + 0.53 |
| (a) p < 0.01 versus
< 5 group by x2-test |
4. Discussion
Fluorine is a necessary biological trace element
for human health [12]. However, some animal experiments have indicated
that fluoride is tumorigenic, that it increases tumor growth rate
and interferes with DNA repair in vitro and in vivo [14,20]. Yiamouyiannis
and Burk [20] reported an increase in human cancer death rate in
fluoridated areas. Studies of the relationship of non-waterborne
fluorides and cancer have reported positive correlations between
food fluoride levels and stomach cancer [21] and a possible correlation
between airborne fluorides and lung cancer [22,23]. Some studies
indicate that NaF induces chromosome aberrations in cultured human
blood lymphocytes in vitro, and in bone marrow cells of mice [4,24].
Our study here provides evidence that the air pollutants at the
phosphate fertilizer factory, in which HF and SiF4 are the main
chemicals, could induce both CA and MN in human blood lymphocytes
in vivo. Our earlier observation on sister-chromatid exchanges (SCE)
of peripheral blood lymphocytes from this same population showed
that the mean SCEs/cell of the workers was significantly higher
than that of the controls (p < 0.01) [13]. The results of our
studies imply that even if the concentration of the chemical pollutants
in the air is low (e.g. F 0.50-0.80 mg/m 3), it may cause damage
to genetic material at the chromosomal level, although the general
health of workers in the phosphate fertilizer factory was found
to be satisfactory. There is, therefore, a need to improve safety,
sanitary conditions, and health surveillance for the high risk group,
which had an increased frequency of major CA, SCE, and MN induced
by the chemical pollutants. However, in this study data on the socio-economic
and nutritional status were not collected. Although the income levels
of the factory workers and the university staff controls were generally
similar at the time of investigation, the potential impact of these
factors were not studied, but one cannot exclude that these factors
may have had some impact on the results obtained.
It has been found that fluoride affects enzymatic
activities, and this effect could delay mitotic and meiotic cycles
causing chromosomal breakages [25]. Such chromosomal aberrations
may eventually lead to the formation of structural changes and fragmentation
as observed in the present studies. Since it has been shown that
fluoride can inhibit nucleic acid synthesis [26], it is suggested
that chromosomal abnormalities induced by fluoride could be the
results from interaction with the enzymes responsible for DNA synthesis
or repair, rather than directly with DNA.
The evidence presented here showed the chromosome
damage rate declines in those who have worked for more than 10 years
in the factory. This might be due to an adaptation mechanism being
produced to the chemical pollutants, or due to an equilibrium being
reached between chromosome damages, lymphocyte death, and lymphocyte
renewal, and/or DNA damage and repair in the cells.
In the phosphate fertilizer factory, HF and SiF4
are the main air pollutants. However, dust containing fluoride,
ammonia (NH3), and sulfur dioxide (S02) were also released in small
amounts into the air in the fertilizer production, as mentioned
in our earlier paper [13]. These pollutants may also contribute
to the cytogenetic damage observed [27]. Hence, health studies of
workers exposed chronically to HF and SiF4 are needed to understand
the meaning of the observed cytogenetic damage in their lymphocytes.
References
[1] World Health Organization, Fluorine and Fluorides,
Environmental Health Criteria 36, WHO, Geneva, 1984, pp. 1-136.
[2] G. Obe, R. Slacik-Erben, Suppressive activity
by fluoride on the induction of chromosome aberrations in human
cells with alkylating agents in vitro, Mutat. Res. 19 (1973) 369-371.
[3] G. Jagiello, J. Lin, Sodium fluoride as potential
mutagen in mammalian eggs, Arch. Environ. Health 29 (1974) 230-235.
[4] D. Jachimczak, B. Skotarczak, The effect of
fluoride and lead ions on the chromosomes of human leucocytes in
vitro, Genet. Polon. 19 (1978) 353-357.
[5] D. Kram, E.L. Schneider, L. Singer, G.R. Martin,
The effects of high and low fluoride diets on the frequencies of
sister chromatid exchanges, Mutat. Res. 57 (1978) 51-55.
[6] G.R. Martin, K.S. Brown, D.W. Matheson, H.
Lebowitz, L. Singer, R. Ophoug, Lack of cytogenctic effects in mice
or mutations in Salmonella receiving sodium fluoride, Mutat. Res.
66 (1979) 159-167.
[7] G.E. Smith, A surfeit of fluoride?, Sci. Prog.
Oxf. 69 (1985) 429-442.
[8] T. Tsutsui, N. Suzuki, M. Ohmori, H. Maizumi,
Cytotoxicity, chromosome aberrations and unscheduled DNA synthesis
in cultured human diploid fibroblasts induced by sodium fluoride,
Mutat. Res. 139 (1984) 193-198.
[9] Y. Li, A.J. Dunipace, G.K. Stookey, Genotoxic
effects of fluoride: a controversial issue, Mutat. Res. 195 (1988)
127136.
[10] C.L. Crespi, G.M. Seixas, T. Turner, B.M.
Penman, Sodium fluoride is a less efficient human cell mutagen at
low concentration, Environ. Mol. Mutagen. 15 (1990) 71-77.
[11] D. Slamenova, A. Gabelova, K. Ruppova, Cytotoxicity
and genotoxicity testing of sodium fluoride on Chinese hamster V79
cells and human EUE cells, Mutat. Res. 279 (1992) 109-115.
[12] E. Zeiger, M.D. Shelby, K.L. Witt, Genetic
toxicity of fluoride, Environ. Mol. Mutagen. 21 (1993) 309-318.
[13] Z.Q. Meng, H.Q. Meng, X.L. Cao, Sister-chromatid
exchanges in lymphocytes of workers at a phosphate fertilizer factory,
Mutat. Res. 334 (1995) 243-246.
[14] M. Mihashi, T. Tsutsui, Clastogenetic activity
of sodium fluoride to rat vertebral body-derived cells in culture,
Mutat. Res. 368 (1996) 7-13.
[15] D.L. Xi, Y.S. Sun, X.I. Liu (Eds.), Methods
in Environmental Monitoring, Higher Education Press, Beijing, 1995,
pp. 381-411.
[16] D.A. Hungerford, Leukocytes cultured from
small inocula of whole blood and the preparation of metaphase chromosomes
by treatment with hypotonic KCI, Stain Technol. 40 (1965) 333-337.
[17] M. Fenech, A.A. Morley, Measurement of micronuclei
in lymphocytes, Mutat. Res. 147 (1985) 29-36.
[18] P.I. Countryman, J.A. Heddle, The production
of micronuclei from chromosome aberrations in irradiated cultures
of human lymphocytes, Mutat. Res. 41 (1976) 321-332.
[19] K.E. Buckton, H.J. Evans (Eds.), Methods for
the Analysis of Human Chromosome Aberrations, WHO, Geneva, 1973,
pp. 1-51.
[20] J. Yiamouyiannis, D. Burk, Fluoridation and
cancer age-dependence of cancer mortality related to artificial
fluoridation, Fluoride 10 (1977) 102-124.
[21] T. Okamura, T. Matsuhisa, Studies on fluoride
and other related material in rice. I. The fluoride content of lowland
nonglutinous unpolished rice and its geographical correlation with
mortality from gastric cancer, Nippon Sakumotsu Gakkai Kiji 32 (1963)
132-138.
[22] N.N. Litvinov, M.S. Goldberg, S.M. Kimina,
Morbidity and mortality in man caused by pulmonary cancer and its
relation to the pollution of the atmosphere in the areas of aluminum
plants, Acta Union. Intern. Contra Cancrum. 19 (1963) 742745.
[23] V.A. Cecilioni, Observations on cancer in
a steel city, Fluoride 7 (1974) 153-165.
[24] A.H. Mohamed, M.E. Chandler, Cytological effects
of sodium
fluoride on mice, Fluoride 15 (1982) 110-118.
[25] E.M. Bogin, M. Abrams, Y. Avidar, B. Isreali,
Effect of fluoride on enzymes from serum, liver, kidney, skeletal
and heart muscles of mice, Fluoride 9 (1976) 42-56.
[26] M.A. Bempong, E.C. Tower, Sensitivity of rat
testis to inhibitors of nucleic acid synthesis. II. Mutagenic action
of mitomycin C, J. Heredity 64 (1970) 324-331.
[27] Z.Q. Meng, L.Z. Zhang, Cytogenetic damage
induced in human lymphocytes by sodium bisulfite, Mutat. Res. 298
(1992) 63-69.
To learn more about fluoride pollution,
see www.fluoridealert.org/f-pollution.htm
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