In recent years, individuals are rampantly exposed to vapours of benzene, through paint, plastic, petroleum industries, fuel exhaust, and tobacco smoke. Hence the present investigation was directed towards determining the effect of benzene metabolites, namely, phenol-hydroquinone and catechol, on the motility, viability, and nuclear integrity of the human spermatozoa. From the results obtained it was clear that exposure to phenol-hydroquinone caused a significant decline in both, sperm motility and viability. Exposure to a phenol-hydroquinone (Phase I) microenvironment may therefore inhibit metabolically active enzymes, thus impeding ATP production, and in turn lowers sperm motility and viability. In addition, the present study also revealed that both metabolites of benzene caused significant denaturation of sperm nuclear DNA. Hence, exposure to phenol-hydroquinone in vitro could have resulted in generation of free radicals and altered membrane function, which is reflected by a decline in the motility, viability, and loss of sperm nuclear DNA integrity. In Phase II, the exposure of human sperm in vitro to varied concentrations of catechol caused only insignificant changes in sperm motility and viability as compared to those observed on exposure to phenol-hydroquinone. Hence, exposure to catechol appeared to have less toxic effects than those of phenol-hydroquinone. 1. Introduction Benzene is an important industrial chemical present in petroleum products that is also omnipresent in the environment due to emissions from gasoline and combustion of hydrocarbons and tobacco [1, 2]. Urban populations throughout the world and cigarette smokers are routinely exposed to air concentrations of benzene in the range of 1–20?ppb [3]. Benzene is both exhaled unchanged in the lungs, as well as metabolized in liver and excreted as metabolites in the urine. The first step in benzene metabolism is the formation of benzene oxide, an epoxide, by cytochrome P-450 dependent mixed function oxidases. The epoxide undergoes hydroxylation to phenol which is then excreted as a glucuronidase or sulphate conjugate or converted to hydroquinone and benzoquinone. Phenol, hydroquinone glucuronide, and hydroquinone sulphate serve as markers for this enzymatic pathway. A second pathway involves conversion of benzene oxide to malondialdehyde through an NADPH mediated process, resulting in catechol production through the intermediate benzene glycol [4]. Significant concentrations of the phenolic compounds (phenol, catechol, and hydroquinone) are observed in human urine even in the absence of
References
[1]
L. Wallace, “Environmental exposure to benzene: an update,” Environmental Health Perspectives, vol. 104, supplement 6, pp. 1129–1136, 1996.
[2]
A. T. S. D. R. Agency for Toxic Substances and Disease Registry, “Toxicological profile for benzene,” US DHHS PB/98/101157/AS, Agency for Toxic Substances and Disease Registry, 1997.
[3]
C. P. Weisel, “Benzene exposure: an overview of monitoring methods and their findings,” Chemico-Biological Interactions, vol. 184, no. 1-2, pp. 58–66, 2010.
[4]
P. J. Sabourin, B. T. Chen, and G. Lucier, “Effect of dose on the absorption and excretion of [14C] benzene administered orally or by inhalation in rats and mice,” Toxicology and Applied Pharmacology, vol. 87, no. 2, pp. 325–336, 1987.
[5]
T. A. McDonald, N. T. Holland, C. Skibola, P. Duramad, and M. T. Smith, “Hypothesis: phenol and hydroquinone derived mainly from diet and gastrointestinal flora activity are causal factors in leukemia,” Leukemia, vol. 15, no. 1, pp. 10–20, 2001.
[6]
M. D. Shelby and K. L. Witt, “Comparison of results from mouse bone marrow chromosome aberration and micronucleus tests,” Environmental and Molecular Mutagenesis, vol. 25, no. 4, pp. 302–313, 1995.
[7]
H. Bulsiewicz, “The influence of phenol on chromosomes of mice (Musimusculus) in the process of spermatogenesis,” Folia Morphologica, vol. 36, no. 1, pp. 3–22, 1977.
[8]
O. J. D'Cruz, A. Vassilev, and F. M. Uckun, “Studies in humans on the mechanism of potent spermicidal and apoptosis- inducing activities of vanadocene complexes,” Biology of Reproduction, vol. 62, no. 4, pp. 939–949, 2000.
[9]
R. J. Aitken and G. N. De Luliis, “On the possible origins of DNA damage in human spermatozoa,” Molecular Human Reproduction, vol. 16, no. 1, pp. 3–13, 2010.
[10]
D. Sakkas and J. G. Alvarez, “Sperm DNA fragmentation: mechanisms of origin, impact on reproductive outcome, and analysis,” Fertility and Sterility, vol. 93, no. 4, pp. 1027–1036, 2010.
[11]
D. P. Evenson, K. L. Larson, and L. K. Jost, “Sperm chromatin structure assay: its clinical use for detecting sperm DNA fragmentation in male infertility and comparisons with other techniques,” Journal of Andrology, vol. 23, no. 1, pp. 25–43, 2002.
[12]
WHO, Laboratory Manual for the Examination and Processing of Human Semen, Cambridge University Press, Cambridge, UK, 5th edition, 2010.
[13]
P. Talbot and R. S. Chacon, “A triple-stain technique for evaluating normal acrosome reactions of human sperm,” Journal of Experimental Zoology, vol. 215, no. 2, pp. 201–208, 1981.
[14]
R. I. Tejada, J. C. Mitchell, and A. Norman, “A test for the practical evaluation of male fertility by acridine orange (AO) fluorescence,” Fertility and Sterility, vol. 42, no. 1, pp. 87–91, 1984.
[15]
D. Sammett, E. W. Lee, J. J. Kocsis, and R. Snyder, “Partial hepatectomy reduces both metabolism and toxicity of benzene: chapter 1,” Journal of Toxicology and Environmental Health, vol. 5, no. 5, pp. 785–792, 1979.
[16]
R. K. Singh and F. W. Bansode, “Benzene-induced histopathological changes and germ cell population dynamics in testes of Sprague Dawley rats,” Journal of Environmental Biology, vol. 32, no. 6, pp. 687–694, 2011.
[17]
H. J. Badham and L. M. Winn, “In utero exposure to benzene disrupts fetal hematopoietic progenitor cell growth via reactive oxygen species,” Toxicological Sciences, vol. 113, no. 1, pp. 207–215, 2009.
[18]
A. Turhan and E. Dere, “The effect of benzene on the activity of adenosine deaminase in tissues of rats,” Journal of Biochemistry and Molecular Biology, vol. 40, no. 3, pp. 295–301, 2007.
[19]
S. Aiso, H. Arito, T. Nishizawa, K. Nagano, S. Yamamoto, and T. Matsushima, “Thirteen-week inhalation toxicity of p-dichlorobenzene in mice and rats,” Journal of Occupational Health, vol. 47, no. 3, pp. 249–260, 2005.
[20]
A. Steiber, J. Kerner, and C. L. Hoppel, “Carnitine: a nutritional, biosynthetic, and functional perspective,” Molecular Aspects of Medicine, vol. 25, no. 5-6, pp. 455–473, 2004.
[21]
K. Inaba, “Molecular architecture of the sperm flagella: molecules for motility and signaling,” Zoological Science, vol. 20, no. 9, pp. 1043–1056, 2003.
[22]
C. B. Lindemann, “Structural-functional relationships of the dynein, spokes, and central-pair projections predicted from an analysis of the forces acting within a flagellum,” Biophysical Journal, vol. 84, no. 6, pp. 4115–4126, 2003.
[23]
C. Eberhard, M. B. Hermann, and N. M. A. Susan, Andrology: Male Reproductive Health and Dysfunction, completely revised and updated edition, Springer, New York, NY, USA, 3rd edition, 2010.
[24]
D. E. Chapman, M. J. Namkung, and M. R. Juchau, “Benzene and benzene metabolites as embryotoxic agents: effects on cultured rat embryos,” Toxicology and Applied Pharmacology, vol. 128, no. 1, pp. 129–137, 1994.
[25]
H. Chen and D. A. Eastmond, “Synergistic increase in chromosomal breakage within the euchromatin induced by an interaction of the benzene metabolites phenol and hydroquinone in mice,” Carcinogenesis, vol. 16, no. 8, pp. 1963–1969, 1995.
[26]
T. J. Atkinson, “A review of the role of benzene metabolites and mechanisms in malignant transformation: summative evidence for a lack of research in nonmyelogenous cancer types,” International Journal of Hygiene and Environmental Health, vol. 212, no. 1, pp. 1–10, 2009.