Toxicological Effects of Technical Xylene Mixtures on the Female Reproductive System: A Systematic Review
Abstract
:1. Introduction
2. Materials and Methods
2.1. PRISMA
2.2. Search Strategy
2.3. Inclusion and Exclusion Criteria
2.4. Data Retrieval and Analysis
3. Results
3.1. In Vitro and In Vivo Studies
3.1.1. Ovarian Cell Toxicity
3.1.2. Maternal Toxicity
3.1.3. Developmental Toxicity
3.2. Human Studies
3.2.1. Menstrual Disturbances
3.2.2. Endocrine Disruption
3.2.3. Adverse Birth Outcomes and Other Potential Reproductive Health Risks
4. Discussion
5. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Database | Search String |
---|---|
Web of Science | TS-((“xylene*” OR “xylol” OR “mixed xylene*” OR “dimethylbenzene” OR “xylene isomer*” OR “xylene toxicit*” OR “xylene exposure” OR “xylene administration” OR “xylene inhalation” OR “xylene treatment”) AND (“reproduct* system” OR ‘female reproduct*” OR “endocrine system” OR “menstrual regulat*” OR “ovar* function” OR “development*”) AND (“animal stud*” OR “human stud*” OR “in vitro stud*” OR “occupation* exposure*)) |
Scopus | TITLE-ABS-KEY((“xylene*” OR “xylol” OR “mixed xylene*” OR “dimethylbenzene” OR “xylene isomer*” OR “xylene toxicit*” OR “xylene exposure” OR “xylene administration” OR “xylene inhalation” OR “xylene treatment”) AND (“reproduct* system” OR ‘female reproduct*” OR “endocrine system” OR “menstrual regulat*” OR “ovar* function” OR “development*”) AND (“animal stud*” OR “human stud*” OR “in vitro stud*’ OR “occupation* exposure*)) |
Variable | Description | ||
---|---|---|---|
Population | Human population studies, animal experiments, and ovarian cells’ in vitro culture. | ||
Human | Animal | In vitro cell culture | |
Exposure | Inhalation. | Inhalation. | Direct exposure to the target cells. |
Comparator | Women of reproductive age with no exposure risks. | Animal receiving vehicle-only treatment. | Ovarian cells cultured without the test compound. |
Outcomes | Menstrual disturbances, endocrine disruption, and adverse birth outcomes. | Decrease in the maternal body weight and food intake. | Increased cellular proliferation and apoptotic signals. |
Criteria | Inclusion | Exclusion |
---|---|---|
Article category | Research articles (journals) | Systematic review journals, books or book chapters, legal documents, conference proceedings. |
Language | English | Non-English |
Duration of publications | From 1990 to 2022 | Before year 1990 |
Geographical selection | Across the world | None |
First Author (Year) | Location | Test Populations | Exposure | Organic Solvents Studied | Findings in Relations to Xylene |
---|---|---|---|---|---|
Sirotkin et al. [16] | Slovakia | Bovine and porcine ovaries’ granulosa cells. | Granulosa cells cultured with or without BTEX (1%). | BTEX. | Addition of 1% BTEX promoted apoptosis and cellular proliferation. Ovarian hormone (progesterone) increased significantly (16.38 ng/106 cells/day vs. 7.64 ng/106 cells/day). |
Tarko et al. [17] | Slovakia | Ovarian cells of Holstein cows. | The ovarian granulosa were incubated with 20 ng/mL of 99% mixture of o-, m-, or p-xylene and chia seed extracts for 48 h. | o-, m-, and p-xylene. | Addition of xylene stimulated ovarian cell proliferation. It suppressed progesterone and testosterone release with or without the chia seed supplement. |
Tarko et al. [18] | Slovakia | Ovarian granulosa cells of the Holstein breed. | The ovarian granulosa were incubated with a 20 µg/mL of 99% mixture of ortho-, meta-, or para-xylene and quercetin extracts (1, 10, or 100 µg/mL) for 48 h. | o-, m-, and p-xylene. | Addition of xylene stimulated ovarian cell proliferation and the release of IGF-1. It suppressed progesterone and testosterone release with or without the quercetin supplement. |
Sirotkin et al. [19] | Slovakia | Porcine ovarian granulosa cells. | Ovarian granulosa cells were cultured with 0.1% xylene, toluene, or benzene for 2 days with and without porcine FSH (1, 10, or 100 ng/mL) | Xylene, toluene, and benzene. | Xylene and benzene (0.1%) stimulated the progesterone release, accumulation of PCNA, and apoptosis, thus reducing the cellular viability. |
Sirotkin et al. [20] | Slovakia | Bovine ovarian cells from cows having different body condition scores. | Ovarian granulosa cells were cultured with 0.1% xylene, toluene, or benzene. | Xylene, benzene, toluene. | Xylene stimulated the expression of apoptosis and proliferation markers in the ovarian cells of cows having a low body condition score. |
Sirotkin et al. [21] | Slovakia | Porcine ovarian granulosa cells. | Ovarian granulosa cells were cultured with 0, 10, 100, or 1000 ng/mL of xylene with 10 µg/mL of buckwheat, rooibos, or vitex plant extracts. | o-, m-, and p-xylene. | Xylene suppressed cell viability, induced apoptosis, and decreased the release of progesterone and estradiol. Addition of the studied plant extracts was able to mitigate the cellular toxicity from xylene. |
First Author (Year) | Location | Test Populations | Exposure | Organic Solvents Studied | Findings in Relations to Xylene |
---|---|---|---|---|---|
Hass and Jakobsen [22] | Denmark | 72 pregnant Wistar rats. divided into two groups of 36 animals. | Inhalation exposure of 200 ppm of xylene or clean air from GD 4 until GD 20. | Technical xylene. | Exposure to 200 ppm of technical xylene from GD 4 until GD 20 did not exert maternal toxicity. However, the incidence of delayed ossification in the skull of the xylene exposed fetuses. |
Saillenfait et al. [9] | France | 572 pregnant female Sprague-Dawley rats, with 20 to 26 animals assigned for each group. | Inhalation exposure of 100, 500, 1000, and 2000 ppm of ethylbenzene, technical xylene, and its isomers from GD 6 until GD 20. | Technical xylene, technical xylene’s individual isomers (o-, m-, and p-xylene), and ethylbenzene. | Inhalational technical xylene exposure of 1000 ppm caused a significant decrease in maternal body weight gain between GD 6 and GD 13. Exposure to 2000 ppm of technical xylene significantly decreased maternal food consumption. |
Saillenfait et al. [23] | France | 156 pregnant female Sprague-Dawley rats, with 19 to 23 animals assigned for each group. | Inhalation exposure of 250 ppm, 1000 ppm of ethylbenzene and 1000 ppm, 3000 ppm of methyl ketone (individual and combined exposure) from GD 6 until GD 20. | Ethylbenzene and methyl ketone. | Co-exposure of ethylbenzene, and methyl ketone (250 ppm ethylbenzene/3000 ppm methyl ketone) resulted in a significant reduction in maternal body weight and food consumption. |
Saillenfait et al. [24] | France | 150 pregnant female Sprague-Dawley rats, with 19 to 21 animals assigned for each group. | Inhalation exposure of ethylbenzene (250 ppm, 1000 ppm), toluene (500 ppm, 1500 ppm), and butyl acetate (500 ppm, 1500 ppm) with single or combined exposure from GD 6 until GD 20. | Ethylbenzene, toluene, and butyl acetate. | Exposure to butyl acetate at high concentrations (2000/3000 ppm) reduced maternal weight significantly, but not in combination with ethylbenzene or toluene. |
Singh et al. [25] | India | Adult flies and 3rd instar larvae of D. melanogaster. | Standard dietary supply for D. melanogaster larvae with or without the test chemicals (1,10, 50, 100 mM of test compounds). | Xylene, toluene, and benzene. | Xylene at concentrations of 50 mM and 100 mM delayed the development of adult flies and reduced the number of eggs laid by female D. melanogaster. |
Malloul et al. [26] | Morocco | 21 pregnant female Swiss mice. | Inhalation exposure to 300 ppm and 600 ppm of paint thinner for 30 min (with 5-min interval after 15-min exposure) twice daily during the gestational period. | Paint thinner with major compositions of toluene, xylene, benzene, and dichloromethylene. | Prenatal exposure to 600 ppm of paint thinner caused a significant decline in the maternal weight. Abortion and preterm birth were induced in pregnant rats exposed to 600 ppm of paint thinner. |
First Author (Year) | Location | Study Design | Test Populations | Exposure | Organic Solvents Studied | Findings in Relations to Xylene |
---|---|---|---|---|---|---|
Cho et al. [27] | China | Cross-sectional human population study | 1408 female petrochemical workers. | Inhalation occupational exposure (<1 ppm/day) of organic solvents. | Xylene, toluene, benzene, and styrene. | 53% increase (OR, 1.53) in oligomenorrhea from 3 or more years work exposure. 7% percent increase in oligomenorrhea (OR, 1.07) from each additional year of work. |
Reutman et al. [28] | United States | Cross-sectional human population study | 170 female personnel of the United States’ Air Force between 18 and 42 years old. | Inhalation occupational exposure of aromatic hydrocarbons (exposure levels between 0.8 and 37.3 ppb). | Aromatic hydrocarbons: BTEX. Aliphatic hydrocarbons: hexane, heptane, octane, nonane, decane, and undecane. | Significant reduction in preovulatory LH levels in women with high breath total BTEX (15.8 vs. 22.0 mIU LH/mg creatinine). BTEX were not significantly associated with changes in midluteal estradiol and progesterone. |
Aguilera et al. [29] | Spain | Human cohort study | 562 pregnant women and their fetuses. | Daily inhalation outdoor exposure to pollutants. | NO2 and BTEX. | Exposure to BTEX during early pregnancy caused smaller biparietal diameters in fetuses. |
Lupo et al. [30] | United States | Case-control human population study | 1108 fetuses of pregnant women delivered with neural tube defects. | Ambient daily exposure of benzene (0.45–7.44 µg/m3), toluene (0.31–14.3 µg/m3), ethylbenzene (0.05–2.74 µg/m3), and xylene 0.36–8.84 µg/m3). | BTEX. | There were strong correlations between BTEX and spina bifida, with a significant relationship with benzene. Measured benzene concentrations were between 0.12 (low) and 7.44 (high) µg/m3. There were relationships with BTEX and anencephaly. |
Ghosh et al. [31] | United States | Human population study | 8181 low-birthweight and 370,922 normal-birth-weight children. | Maternal inhalation of traffic air pollutants (0.4 to 3.0 ppb). | BTEX. | Higher odds of giving birth to low weight neonates when exposed to higher concentrations of traffic contaminants during the third trimester. |
Santiago et al. [32] | Brazil | Case reports | Two female gas station workers with histories of miscarriages. | Occupational exposure to BTEX at the gas station (8 h/week). | BTEX. | Chronic occupational exposure to BTEX induces chromosomal aberrations linked to reproductive hazards and early pregnancy loss. |
Moradi et al. [33] | Iran | Cross-sectional human population study | 36 randomly selected beauty salon workers in Tehran metropolitan. | Occupational indoor inhalation exposure of benzene (4.9 µg/m3), toluene (20.9 µg/m3), ethylbenzene (4.2 µg/m3), and xylene (10.1 µg/m3). | BTEX. | The prevalence of a menstrual disorder was 47% among exposed workers. Urinary pre-shift concentrations of m-xylene and o-xylene were 99.3 ng/L and 57.6 ng/L, respectively. Urinary post-shift concentrations of m-xylene and o-xylene were 276.3 ng/L and 149.2 ng/L, respectively. |
Serrano-Lomelin et al. [34] | Canada | Human population study | 333247 singleton livebirths in Canada based on the postal codes from 2006–2012. | Maternal inhalation exposure to industrial air pollutants (1.3% of total mass of air pollutants measured in tons) | Xylene, toluene, and methyl ethyl ketone. | Xylene containing mixtures of industrial pollutants had a significant association with low birth weight (OR 1.16) |
Cassidy-Bushrow et al. [35] | United States | Human population cohort study | Women with singleton delivery from 2008–2010. | Inhalation exposure to ambient air pollutants (8 µg/m3 BTEX, 18.5 ppb NO2, 14.2 µg/m3 PM10, 10.7 PM2.5). | BTEX, NO2, PM10, PM2.5. | Combined with other maternal factors, e.g., age, poverty, and ethnicity, there was a strong association between BTEX exposure and preterm births. |
Ding et al. [36] | United States | Cross-sectional human population studies | 2432 non-institutionalized women aged 20–49 years on reported use of feminine products. | Exposure to VOCs from feminine products i.e., tampon, sanitary napkin, vaginal douche, feminine spray, powder, and wipes. | Xylene, toluene, ethylbenzene, bromodichloromethane, chloroform, dibromodichloromethane, and dichlorobenzene. | The use of feminine powder was significantly associated with a 35.6% higher whole blood concentration of ethylbenzene (35.6 ng/mL of blood), compared with the never users. The use of feminine powder, vaginal douche, feminine spray, and wipes was significantly higher among non-Hispanic black females. |
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Suaidi, N.A.; Alshawsh, M.A.; Hoe, S.-Z.; Mokhtar, M.H.; Zin, S.R.M. Toxicological Effects of Technical Xylene Mixtures on the Female Reproductive System: A Systematic Review. Toxics 2022, 10, 235. https://doi.org/10.3390/toxics10050235
Suaidi NA, Alshawsh MA, Hoe S-Z, Mokhtar MH, Zin SRM. Toxicological Effects of Technical Xylene Mixtures on the Female Reproductive System: A Systematic Review. Toxics. 2022; 10(5):235. https://doi.org/10.3390/toxics10050235
Chicago/Turabian StyleSuaidi, Noor Asyikin, Mohammed Abdullah Alshawsh, See-Ziau Hoe, Mohd Helmy Mokhtar, and Siti Rosmani Md Zin. 2022. "Toxicological Effects of Technical Xylene Mixtures on the Female Reproductive System: A Systematic Review" Toxics 10, no. 5: 235. https://doi.org/10.3390/toxics10050235
APA StyleSuaidi, N. A., Alshawsh, M. A., Hoe, S. -Z., Mokhtar, M. H., & Zin, S. R. M. (2022). Toxicological Effects of Technical Xylene Mixtures on the Female Reproductive System: A Systematic Review. Toxics, 10(5), 235. https://doi.org/10.3390/toxics10050235