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Frequencies of trisomy 1, 5 and 7 in the peripheral blood lymphocytes of workers exposed to benzene, and unexposed controls. Individual values for each study subject are presented and the median is shown as a horizontal bar. The three exposure categories are: controls ( s ), workers exposed to ഛ 31 p.p.m. ( d ) and to Ͼ 31 p.p.m. ( m ) benzene. A natural log transformation was used to normalize each outcome and a test for trend was performed by linear regression, controlling for age and gender, the original matching variables. A statistically significant increasing trend was seen for trisomy of all three chromosomes (1, P trend Ͻ 0.001; 5, P trend Ͻ 0.01; 7, P trend Ͻ 0.0001). 

Frequencies of trisomy 1, 5 and 7 in the peripheral blood lymphocytes of workers exposed to benzene, and unexposed controls. Individual values for each study subject are presented and the median is shown as a horizontal bar. The three exposure categories are: controls ( s ), workers exposed to ഛ 31 p.p.m. ( d ) and to Ͼ 31 p.p.m. ( m ) benzene. A natural log transformation was used to normalize each outcome and a test for trend was performed by linear regression, controlling for age and gender, the original matching variables. A statistically significant increasing trend was seen for trisomy of all three chromosomes (1, P trend Ͻ 0.001; 5, P trend Ͻ 0.01; 7, P trend Ͻ 0.0001). 

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Two of the most common cytogenetic changes in therapy- and chemical-related leukemia are the loss and long (q) arm deletion of chromosomes 5 and 7. The detection of these aberrations in lymphocytes of individuals exposed to potential leukemogens may serve as useful biomarkers of increased leukemia risk. We have used a novel fluorescence in situ hyb...

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... with controls (n 44), the mean frequency of trisomy 1 in all exposed workers (n 43) was increased from 0.27 to 0.53 (P 0.01), of trisomy 5 from 0.51 to 0.88 (P 0.05) and of trisomy 7 from 0.87 to 1.66 (P 0.001). These increases in trisomy were detected especially in the 31 p.p.m. group (Figure 2). In the 31 p.p.m. group, frequencies of trisomy 1 and 5 were not significantly increased, whereas trisomy 7 showed an increase of borderline signific- ance (P 0.05). ...
Context 2
... trends were observed for chromosomes 1, 5 and 7 (P 0.05). Interestingly, all three chromosomes have very similar tetra- somy frequency levels in each category (controls, lower exposure and higher exposure) (Table II), whereas trisomy rates are quite different from one chromosome to another (Figure 2). In fact, most of the tetrasomies we detected (93%) were tetraploidy rather than real tetrasomies, which means that four copies of each chromosome were present in the same cell. ...

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... 10,139 Numerous studies have reported that benzene exposure induced leukemia-related chromosomal changes that are commonly observed in AML can be detected in the peripheral blood lymphocytes of workers who have been heavily exposed to benzene. 11,12,140,141 The presence of monosomy 5 and monosomy 7 has been observed in the human lymphocytes from healthy workers exposed to benzene. 140 Benzene metabolites also produce AML-related chromosomal changes in human CD34 þ progenitor cells, providing evidence that chromosomal aberrations, such as aneuploidy and translocations, may be the genetic pathway for induction of AML by benzene. ...
... 11,12,140,141 The presence of monosomy 5 and monosomy 7 has been observed in the human lymphocytes from healthy workers exposed to benzene. 140 Benzene metabolites also produce AML-related chromosomal changes in human CD34 þ progenitor cells, providing evidence that chromosomal aberrations, such as aneuploidy and translocations, may be the genetic pathway for induction of AML by benzene. 141,142 Furthermore, a study using OctoChrome fluorescent in situ hybridization and the micronucleus-centromere assay reported that benzene exposure causes monosomy of chromosomes 5, 6, 7, and 10 and trisomy of chromosomes 8, 9, 17, 21, and 22. 143 Chromosomal aberrations such as translocation t (14;18) and dose-dependent induction of long-arm deletion of chromosome 6 [del(6q)] have been reported in workers who have been exposed to benzene. ...
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... In turn, pBQ, as with chemotherapeutic alkylating agents, acts as an electrophile on DNA within the target cell inducing myelotoxicity (Irons 1985a;Irons et al. 1992). Additional support for this hypothesis was evidenced by abnormalities in chromosome 5 and 7 in lymphocytes of healthy benzene-exposed workers, and in reports of abnormalities in chromosome 5 and 7 human CD34þ hematopoietic progenitor cells following in vitro exposure to benzene metabolites (Irons and Stillman 1996;Zhang et al. 1998;Stillman et al. 1999Stillman et al. , 2000Smith et al. 2000). However, abnormalities in chromosomes 5 and 7 have not been directly correlated concurrently in the bone marrow (e.g. the target organ of toxicity) of diseased workers following exposure to benzene. ...
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Benzene and formaldehyde (FA) are important industrial chemicals and environmental pollutants that cause leukemia by inducing DNA damage and chromosome aberrations in hematopoietic stem cells (HSC), the target cells for leukemia. Our previous studies showed that workers exposed to benzene and FA exhibit increased levels of aneuploidy in their blood cells. As centrosome amplification is a common phenomenon in human cancers, including leukemia, and is associated with aneuploidy in carcinogenesis, we hypothesized that benzene and FA would induce centrosome amplification in vitro. We treated human lymphoblastoid TK6 cells with a range of concentrations of hydroquinone (HQ, a benzene metabolite) or FA for 24 h, allowed the cells to recover in fresh medium for 24 h, and examined centrosome amplification; chromosomal gain, loss, and breakage; and cytotoxicity. We included melphalan and etoposide, chemotherapeutic drugs that cause therapy-related acute myeloid leukemia and that have been shown to induce centrosome amplification as well as chromosomal aneuploidy and breakage, as positive controls. Melphalan and etoposide induced centrosome amplification and chromosome gain and breakage in a dose-dependent manner, at cytotoxic concentrations. HQ, though cytotoxic, did not induce centrosome amplification or any chromosomal aberration. FA-induced centrosome amplification and cytotoxicity, but did not induce chromosomal aberrations. Our data suggest, for the first time, that centrosome amplification is a potential mechanism underlying FA-induced leukemogenesis, but not benzene-induced leukemogenesis, as mediated through HQ. Future studies are needed to delineate the mechanisms of centrosome amplification and its association with DNA damage, chromosomal aneuploidy and carcinogenesis, following exposure to FA. Environ. Mol. Mutagen., 2015. © 2015 Wiley Periodicals, Inc. © 2015 Wiley Periodicals, Inc.
... Regarding the position of chromosome breakage, it was mostly found in chromosome number 3 and 6, while the study by Zhang, et al 18,19 reported that anomaly were more frequent in chromosome number 5, 7, and 9, while Sasiadek and Jagielski 20 found anomaly in chromosome number 2, 4, 6, and 9. From the gene cards of the Institute of Gene International, it is known that some diseases are related to the number of chromosome damage. 21 It is mentioned that abnormalities/diseases might occur if there is damage to the chromosome numbers 3, 6, 7, and 9. Damage to chromosomes number 3 is associated with metabolism disorders, and anomaly in chromosome 3 is more closely related to triglycerides/HDL ratio, especially for the Caucasian families in USA, 22 and increasing of the heart problems and metabolic syndrome. ...
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Background: Benzene has been used in industry since long time and its level in environment should be controled. Although environmental benzene level has been controlled to less than 1 ppm, negative effect of benzene exposure is still observed, such as chromosome breakage. This study aimed to know the prevalence of lymphocyte chromosome breakage and the influencing factors among workers in low level benzene exposure.Methods: This was a cross sectional study in oil & gas industry T, conducted between September 2007 and April 2010. The study subjects consisted of 115 workers from production section and head office. Data on type of work, duration of benzene exposure, and antioxidant consumption were collected by interview as well as observation of working process. Lymphocyte chromosome breakage was examined by banding method. Analysis of relationship between chromosome breakage and risk factors was performed by chi-square and odd ratio, whereas the role of determinant risk factors was analyzed by multivariate forward stepwise.Results: Overall lymphocyte chromosome breakage was experieced by 72 out of 115 subjects (62.61%). The prevalence among workers at production section was 68.9%, while among administration workers was 40% (p > 0.05). Low antioxidant intake increases the risk of chromosome breakage (p = 0.035; ORadjusted = 2.90; 95%CI 1.08-7.78). Other influencing factors are: type of work (p = 0,10; ORcrude = 3.32; 95% CI 1.33-8.3) and chronic benzene exposure at workplace (p = 0.014; ORcrude = 2.61; 95% CI 1.2-5.67), while the work practice-behavior decreases the lymphocyte chromosome breakage (p = 0.007; ORadjusted = 0.30; 95% CI 0.15-0.76).Conclusion: The prevalence of lymphocyte chromosome breakage in the environment with low benzene exposure is quite high especially in production workers. Chronic benzene exposure in the workplace, type of work, and low antioxidant consumption is related to lymphocyte chromosome breakage. Thus, benzene in the workplace should be controlled to less than 1 ppm, and the habit of high antioxidant consumption is recommended.