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Di-(2-ethylhexyl) phthalate (DEHP) is currently one of the most widely used plasticizers, widely found in all kinds of items, such as children’s toys and food packaging materials, but also added to wallpaper, cable protective agents and other building decoration materials. DEHP is toxic and absorbed by the human body through respiratory tract, digestive tract and skin contact, which can cause damage to multiple systems, especially the male reproductive system, and testis is an important target organ. Oxidative stress injury is the core mechanism of spermatogenesis disorder caused by DEHP. DEHP exposure can cause oxidative stress or reactive oxygen species (ROS) increase in germ cells, and on this basis, promote cell apoptosis or cause excessive autophagy. The toxicity of DEHP to Leydig cells is mainly to interfere with the synthesis of steroid hormones. For Sertoli cells, ferroptosis and destruction of the blood-testis barrier are common injury mechanisms. In addition, gene methylation caused by DEHP not only affects the spermatogenic process, but also has epigenetic effects on offspring. In this paper, we reviewed the pathological damage, germ cell toxicity and epigenetic effects of DEHP on testis, and focused on the damage and molecular mechanism on testicular spermatogenic cells, Leydig cells and Sertoli cells. Future research is required to elucidate the body’s clearance mechanism and treatment plan after exposure to DEHP and whether DEHP will damage the function of myoid cells. It is hoped that this can provide new ideas for prevention and treatment of male reproductive disorders resulting from long-term exposure to plastic products.
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OBJECTIVE To study the effect of fluoropezil on embryo-fetal developmental toxicity and toxicokinetics in rabbits,and provide reference for clinical medication.METHODS According to the sequence of pregnancy,pregnant rabbits were divided into five groups:vehicle control group(1%hydroxy-propyl methylcellulose+1.5%polyethylene glycol 400 aqueous solution),positive control group(cyclo-phosphamide 18 mg·kg-1),and fluoropezil(3.6,9.0 and 22.5 mg·kg-1)groups.The vehicle control group and the fluoropezil groups were ig administrated on the 6th to 18th day of gestation(GD6-18)while the positive control group was ig given cyclophosphamide on GD6-20.The pregnant rabbits were sacri-ficed on GD28,and the embryo-fetal development was detected.Sex hormone levels of pregnant rabbits on GD5,GD18 and GD28 were detected by ELISA method.Blood samples with toxokinetics were collected for concomitant toxic generation at the first and last administration,and drug concentrations in fetal,placenta and amniotic fluid were detected with liquid chromatography tandem mass spectrometry(LC-MS/MS).RESULTS Fluoropezil 3.6,9.0 and 22.5 mg·kg-1 had no significant effect on body mass,mass gain,food consumption,pregnancy outcomes,fetal appearance,viscera,skeletal and physical growth and development of pregnant rabbits.Only on GD18 or GD28,the levels of follicle stimulating hormone,estra-diol and progesterone in each dose group fluctuated to some extent.The combined toxokinetics results indicated that fluoropezil could cross the placental barrier of the rabbits,but did not accumulate in preg-nant rabbits or fetuses.Fetal mass,crown-rump length and uterus mass in the cyclophosphamide group were lower than those in the vehicle control group.The appearance and bone of the cyclophos-phamide group were positive.CONCLUSION The no observed adverse effect level(NOAEL)of fluoro-pezil toxicity on rabbit embryo-fetal development is 22.5 mg·kg-1,which is 125 times of the effective dose.At the dosage level of 22.5 mg·kg-1,Cmax is 1093 μg·L-1,and AUC(0-24 h)6650 μg·h·L-1 on GD18.
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Tripterygium wilfordii is widely used in the treatment of autoimmune system diseases, but its obvious reproductive toxicity limits the clinical application and promotion of the drug. At present, there is no clear solution to the reproductive injury of Tripterygium wilfordii. TCM believes that its reproductive toxicity lies in its properties of pungent, bitter, and cold. Long-term use can dry liver and blood, hurt liver and yang, consume kidney essence, damage kidney and yang, destroy the balance of qi and blood, yin and yang in the internal organs, and cause infertility. Based on the relationship between liver and kidney and human reproductive function, this article proposed to understand the reproductive toxicity of Tripterygium wilfordii from the perspective of "Yi and Gui homology", and explored the method of reducing the reproductive toxicity of Tripterygium wilfordii according to the thought of "treating liver and kidney together", in order to expand the theoretical thinking of TCM for the safe clinical application of this drug.
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Endocrine disrupting chemicals (EDCs) are a class of chemical substances widely present in daily-life environment, and can enter human body through various pathways, posing a threat to reproductive development and health. Oxidative stress (OS) is one of the most important fundamental mechanisms underlying the reproductive toxicity of EDCs. Numerous studies have found that exposure to EDCs can increase the levels of reactive oxygen species (ROS) in human reproductive system and reduce the activity and quantity of multiple enzymatic antioxidants, leading to oxidative stress and inducing damage to the reproductive system at various levels such as DNA and cells. Many research results have shown that supplementing food-derived non-enzymatic antioxidants can reduce ROS levels and increase the activity of enzymatic antioxidants, thereby reduce OS levels, and further repair EDCs-induced reproductive damage. In addition, many food-derived antioxidants are important elements involved in reproductive physiological activities and have protective effects on reproductive health. This paper summarized the reproductive toxicity of EDCs, including damage to reproductive cells, interference with hormone action, and influence on reproductive-related epigenetic regulation, elaborated the relationship between OS and reproductive toxicity of EDCs, and further summarized the alleviating effects and related mechanisms of food-derived antioxidants such as vitamins, trace elements, and plant polyphenols and pigments against reproductive toxicity of EDCs, aiming to provide a theoretical and scientific basis for prevention and treatment against reproductive toxicity of EDCs.
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Aim: Factory workers, pesticide applicators and farmers are the most susceptible group to reproductive problems due to continuous exposure to pesticides. Farmers now increasingly deploy pesticides in their agronomic practices. This research aimed to assess the impact on reproductive markers and stress markers of acute exposure to chlorview, an organophosphate pesticide, through oral and inhalation routes using animal model. Study Design: A total of 64 male wistar rats were used for the experiment. The animals were divided into two groups for oral (36 rats) and inhalation (28 rats) routes of exposure. Acute toxicity studies and the median lethal dose were carried out using a modified method. Methodology: Standard methods were used to determine oxidative stress markers of lipid peroxides, catalase activity and glutathione peroxidase activity. Immunoassay test kit was used to determine the reproductive toxicity studies. Results: The results from the 24 hour acute toxicity studies revealed that oral exposure to pesticide gave a median lethal dose (LD50) of 155 mg/kg b.w. while inhalation exposure gave a median lethal concentration (LC50) of 1414 mg/kg b.w. for 60 min. Oxidative stress markers [glutathione (GSH), Malondialdehyde (MDA), catalase (CAT) and glutathione peroxidase (GPx)] show that the pesticide induced appreciable oxidative imbalance in the system. In oral exposure, there was a significant (p<0.05) increase in the activity when compared to control. The reproductive marker toxicity studies revealed that oral exposure to pesticide led to a significant (p<0.05) increase in the Cholesterol (which has a correlation with estradiol) and a significantly (p<0.05) decreased in testosterone and sperm count when compared to control. This research concludes that exposure to pesticides can pose a reasonable risk to reproductive and stress markers through oral and inhalation routes of exposure which affect many biochemical processes.
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Background: Metal toxicity is of major concern to human health. The metals may modulate molecular mechanisms of various pathways. Rasashastra, the branch of Ayurveda, narrates the properties, unique preparation, processing techniques, and therapeutic uses of minerals. The use of herbal metallic prep- arations has evoked concern for their potential to produce toxicity, interest in efficacy as therapeutic agents and safety related issues. Abhraka Bhasma, is one such incinerated herbo-metallic preparation of mica, widely used by traditional medicine practitioners. Although there are reports of Abhraka Bhasma on beneficial effects, clear evidence is lacking on the effect of Abhraka Bhasma on genotoxicity and DNA repair. Objective: The present study aims to understand the effects of Abhraka Bhasma on geno toxicity, DNA repair, and other mechanisms in the mice test model. Material and methods: The experiments were conducted in in vivo Swiss albino mice. The acute oral toxicity was performed as per the OECD guidelines. The mice were treated with Abhraka Bhasma (120 or 360 mg/kg body weight) for 7 days. They were then challenged with ethyl methanesulfonate and the DNA repair was analyzed. Results: The data obtained indicated that the Abhraka Bhasma is not a genotoxic and reproductive toxic formulation. The selected higher concentration of Abhraka Bhasma showed a protective role against ethyl methanesulfonate induced chromosomal damages and enhanced constitutive DNA base excision repair in mice. Conclusion: The anti-oxidant, potentiation of DNA repair and hematinic properties of Abhraka Bhasma may be attributed to the synergistic actions of its bioactive components.
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Objective To observe the metabolomic changes of amniotic fluid in control group and administration group,and to explore the toxicity of aqueous extract of rhubarb on reproduction and embryonic development of pregnant rats.Methods Pregnant rats in teratogenic sensitive period were given rhubarb aqueous extract by gavage for 10 days.The toxicity of rhubarb to maternal rats and the abnormal conditions of dead fetus and absorbed fetus were observed.The amniotic fluid samples were detected by liquid chromatography-mass spectrometry(LC-MS),the amniotic fluid metabolic profiles were compared by principal component analysis(PCA)and partial least squares(OPLS-DA),and the differential lipids were analyzed by metaboanalyst 5.0.Results Rhubarb administration in the teratogenic sensitive period can significantly reduce the number of live fetuses,and lead to adverse phenomena such as absorption of fetuses and premature death of fetuses.The preliminary results of lipomics showed that rhubarb could cause the metabolic disorder of amniotic fluid in pregnant rats,and there were metabolic abnormalities in lipids in amniotic fluid such as PI,PC and LPC.Conclusion Under the equivalent dose of the maximum dose recommended by the clinic,the aqueous extract of rhubarb has certain reproductive and embryonic toxicity to rats;Rhubarb may affect the normal development of rat embryos by causing the disorder of lipid metabolism in amniotic fluid.
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With the widespread use of mobile phones, laptops, and WIFI, the effects of radio frequency radiation (RFR) on human health are of increasing concern, and there are particular concerns about its reproductive toxicity. Studies have shown that the reproductive system is a sensitive target for RFR. In males, RFR is associated with decreased sperm quality and serum testosterone levels, but there are few studies on the biological effects of RFR by altering physical parameters on the male reproductive system. This paper introduced common sources of RFR, reviewed the toxic effects and mechanisms of RFR targeting male reproductive system from the aspects of spermatogenic cells, sperm structure, blood-testicular barrier, and testicular function, and analyzed male reproductive system related toxic effects of RFR by varying physical parameters including frequency, treatment duration, and specific absorption rate, so as to provide a theoretical basis and scientific basis for the safe and reasonable use of radio frequency electromagnetic field by humans and subsequent in-depth research.
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Background Tricresyl phosphate (TCP) is mainly used as a flame retardant. Studies have confirmed that it has cytotoxicity and neurotoxicity, but its reproductive toxicity is not clear. Objective To investigate the reproductive toxicity and potential mechanism of TCP subacute exposure on Caenorhabditis elegans. Methods Caenorhabditis elegans were exposed to solvent control and 0.1, 1, 10, 100, and 1000 μg·L−1 TCP respectively for 72 h. Brood size and number of fertilized eggs in the uterus were detected to evaluate reproductive ability. The number of total germline cells and the relative area of gonad arm were measured to evaluate the development of gonads. The body length and body width of Caenorhabditis elegans were detected to evaluate growth and development. The activities of reactive oxygen species (ROS) and superoxide dismutase (SOD) in Caenorhabditis elegans, and the mitochondrial active oxygen metabolism genes (mev-1 and gas-1) of N2 nematodes were detected by real-time fluorescence quantitative polymerase chain reaction (qRT-PCR) to evaluate oxidative stress. WS1433 transgenic nematodes and wild-type nematodes N2 were exposed to solvent control or TCP (0.1, 1, 10, 100, and 1000 μg·L−1) respectively. DNA damage in germ cells of WS1433 transgenic nematodes was detected, the relative expressions of DNA damage-related genes (hus-1, clk-2, cep-1, and egl-1) in N2 nematodes were detected by qRT-PCR to evaluate the effect of TCP exposure on genetic damage. Results Compared with the solvent control group (217.00 ± 12.20), the brood size of N2 nematodes in the 100 μg·L−1 and 1000 μg·L−1 TCP groups decreased (170.80 ± 11.51, 169.60 ± 10.52, P < 0.05). Compared with the solvent control group (18.43 ± 1.69), the number of fertilized eggs of N2 nematodes in the 100 μg·L−1 and 1000 μg·L−1 TCP groups decreased (13.47 ± 0.81, 11.95 ± 0.90, P < 0.05). Compared with the solvent control group (312.46 ± 77.4), the number of total germline cells of N2 nematodes in the 100 μg·L−1 and 1000 μg·L−1 TCP groups decreased (281.80 ± 12.98, 273.50 ± 8.53, P < 0.05). Compared with the solvent control group, the relative area of gonads of N2 nematodes in the 100 μg·L−1 and 1000 μg·L−1 TCP groups decreased by 13.83% and 17.25% respectively (P<0.05). Compared with the solvent control group [(1058.10±80.12) μm, (78.21±14.69) μm], the body length and body width of N2 nematodes in the 100 μg·L−1 and 1000 μg·L−1 TCP groups decreased (P<0.05). Compared with the solvent control group, the relative fluorescence intensity of ROS in nematodes in the 10, 100, and 1000 μg·L−1 TCP groups increased significantly (107.60%±1.02%, 105.90%±1.40%, and 106.40%±1.85%, respectively, P<0.05), and the activities of SOD were reduced (by 20.66%, 15.88%, and 16.44%, respectively, P<0.05). Compared with the solvent control group (1.3±1.3), the number of DNA-damaged germ cells of WS1433 nematodes in the 100 and 1000 μg·L−1 TCP groups increased significantly (2.4±0.3, 2.7±0.3, P<0.05); the expressions of mev-1 and gas-1 genes in N2 nematodes in the 10, 100 and 1000 μg·L−1 TCP groups decreased significantly (P<0.05); the expressions of hus-1 in the 0.1-1000 μg·L−1 TCP groups significantly increased (P<0.05); the expressions of clk-2 and egl-1 in the 100 and 1000 μg·L−1 TCP groups increased significantly (P<0.05); the expressions of cep-1 in the 1, 10, and 100 μg·L−1 TCP groups increased significantly (P<0.05). Conclusion TCP may cause reproductive damage to nematodes through oxidative stress and germ cell DNA damage.
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Environmental endocrine disrupting chemicals are a kind of exogenous chemicals that generally exist in the environment, and can disturb the endocrine homeostasis and adversely affect reproductive, immune, neurological, and other functions after entering the body, among which the damage to the reproductive system is the most significant one. Studies have confirmed that the long-term exposure to environmental endocrine disrupting chemicals have irreversible and harmful effects on primordial germ cell growth, reproductive organ development, and reproductive endocrine regulation, and also have obvious correlations with the occurrence and development of various reproductive system tumors. This paper reviewed various reproductive toxicities induced by common environmental endocrine disrupting chemicals in the developmental and reproductive stages, and associated mechanisms involved in the occurrence and development of reproductive system tumors.
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Global plastics production has been increasing year by year. Due to the large quantity of plastics and the difficulty of their degradation, plastics are continuously accumulated in the environment. Therefore, plastic waste has become one of the most serious threats to the global environment. Microplastics can be absorbed into organisms through the mouth, respiratory tract and skin, causing organ(intestine, liver) toxicity, reproductive and developmental toxicity, and neurotoxicity. Moreover, microplastics can also take up other pollutants distributed in the surrounding environment, such as heavy metals and organic pollutants, jointly exerting combined toxic effects. The extracts of microplastics, including microplastics unstable polymers and additives, also have toxic effects. The molecular mechanisms involved in the toxic effects induced by microplastics include oxidative stress, inflammation, disturbance of intestinal flora, disturbance of gene expression, and others.
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Background 2,4-Dichlorophenoxyacetic acid (2,4-D) is widely used as a broad-leaved herbicide and plant growth regulator. Related studies have shown that 2,4-D has neurotoxicity, ability to disrupt endocrine function, genotoxicity, carcinogenicity, and reproductive toxicity. Objective This experiment is conducted to investigate the effect of 2,4-D exposure on reproductive system of female rats, and to preliminarily explore the potential ameliorative effect of Lycium barbarum polysaccharide (LBP) and its possible mechanism. Methods Twenty-four SPF female SD rats with six rats in each group were randomly divided into a blank control group (deionized water 1 mL·d−1), an exposure group (75 mg·kg−1 2,4-D), an LBP control group (50 mg·kg−1 LBP), and an LBP intervention group (75 mg·kg−1 2,4-D + 50 mg·kg−1 LBP). The rats were given intragastric administration once a day for 28 consecutive days. Body weight was measured every two days. After exposure, ovary and uterus were weighed and organ coefficients were calculated; the pathological changes of ovary and uterus were detected by hematoxylin-eosin staining (HE); the level of estradiol (E2) in serum was detected by ELISA; the levels of superoxide dismutase (SOD), glutathione peroxidase (GSH-Px), and malondialdehyde (MDA) in serum were measured by corresponding kits; the apoptosis of ovarian and uterine cells was detected by TUNEL fluorescence staining; and the protein expression levels of Fas, FasL, FADD, Pro-Caspase-8, Cleaved-Caspase-8, Pro-Caspase-3, and Cleaved-Caspase-3 in ovarian tissues were detected by Western blotting. Results Compared with the blank control group, the ovarian structure of the exposure group was abnormal, the number of follicles at different developmental stages decreased, morphological changes were observed, and the number of atretic follicles increased; the endometrium was incomplete, with different degrees of nuclear pseudostratification and decreased number of glands in lamina propria. Compared with the exposure group, the ovarian structure of the LBP intervention group was complete, and the follicles at different developmental stages increased in amount, remained intact, and were arranged closely; the uterine structure was relatively intact, showing decreased endometrial loss and nuclear pseudostratification. There were significant differences in the levels of SOD, GSH-Px, E2, and MDA among the four groups (F=86.1, 26.2, 43.3, and 22.3, all P<0.01). Compared with the blank control group, the levels of serum SOD, GSH-Px, and E2 decreased in the exposure group (P<0.01), while the concentration of MDA increased (P<0.01). Compared with the exposure group, the levels of serum SOD, GSH-Px, and E2 in the LBP intervention group increased (P<0.01), and the concentration of MDA decreased (P<0.01). There were significant differences in the apoptosis rates of ovarian and uterine cells among the four groups (F=64.8, 55.5, both P<0.01). Compared with the blank control group, the apoptosis rates of ovarian and uterine cells increased in the exposure group (P<0.01). Compared with the exposure group, the apoptosis rates of ovarian and uterine cells decreased in the LBP intervention group (P<0.01). There were significant differences in the expression levels of death receptor pathway-related proteins in ovarian tissues among the four groups (all P<0.05). Compared with the blank control group, the expression levels of Fas, FasL, FADD, Pro-Caspase-8, Cleaved-Caspase-8, Pro-caspase-3, and Cleaved-Caspase-3 were increased in the exposure group (P<0.05 or 0.01). Compared with the exposure group, the expression levels of above proteins were decreased in the LBP intervention group (P<0.05 or 0.01). Conclusion The study findings reveal that 2,4-D can induce oxidative stress and further mediate Fas-FasL pathway to induce apoptosis, resulting in reproductive system damage in female rats. LBP can reduce the oxidative stress level, down-regulate the expression of Fas-FasL pathway-related proteins, and reduce the apoptosis of germ cells, therefore protecting reproductive system of female rats.
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Spermatogenic dysfunction caused by cyclophosphamide (CP) chemotherapy has seriously influenced the life quality of patients. Unfortunately, treatments for CP-induced testicular spermatogenic dysfunction are limited, and the molecular mechanisms are not fully understood. For the first time, here, we explored the effects of bone marrow mesenchymal stem cell-derived exosomes (BMSC-exos) on CP-induced testicular spermatogenic dysfunction in vitro and in vivo. BMSC-exos could be taken up by spermatogonia (GC1-spg cells). CP-injured GC1-spg cells and BMSC-exos were cocultured at various doses, and then, cell proliferation was measured using 3-[4,5-dimethylthiazol-2-yl]-2,5 diphenyl tetrazolium bromide (MTT) assay. In addition, photophosphorylation of extracellular-regulated kinase (ERK), p38 mitogen-activated protein kinase (p38MAPK), and protein kinase B (AKT) proteins was evaluated by western blotting as well as apoptosis in GC1-spg cells measured using flow cytometry. Treatment with BMSC-exos enhanced cell proliferation and reduced apoptosis of CP-injured GCI-spg cells. Phosphorylated levels of ERK, AKT, and p38MAPK proteins were reduced in CP-injured spermatogonia when co-treated with BMSC-exos, indicating that BMSC-exos acted against the reproductive toxicity of CP via the p38MAPK/ERK and AKT signaling pathways. In experiments in vivo, CP-treated rats received BMSC-exos by injection into the tail vein, and testis morphology was compared between treated and control groups. Histology showed that transfusion of BMSC-exos inhibited the pathological changes in CP-injured testes. Thus, BMSC-exos could counteract the reproductive toxicity of CP via the p38MAPK/ERK and AKT signaling pathways. The findings provide a potential treatment for CP-induced male spermatogenic dysfunction using BMSC-exos.
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Acrylamide is a potential carcinogen, with proven neurotoxicity and genotoxicity. In the current scenario, neurotoxicity and reproductive toxicity of acrylamide have not been conclusively established for humans; however, the same has been established in laboratory animal species. In this review, we summarize the factors dictating the exposure of acrylamide to humans and subsequently caused toxicity to humans. Further, we review the neurotoxic and genotoxic effects of acrylamide on animal models, with a particular emphasis on reproductive toxicity. We also talk about various strategies such as physical, chemical, and biological approaches, employed for acrylamide. Overall, we discuss that consumption of acrylamide through food products has toxic effects on the endocrine system, and it is deleterious for human health. A novel aspect of this review is that we provide a molecular mechanism of action in conjunction with clinical data on acrylamide toxicity along with relevant examples. This review also highlights the requirement of further research on the consequences of acrylamide toxicity, molecular modes of action, and the overall impact on the human body
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OBJECTIVE: To obtain information on the toxicity of lufenuron on the reproduction ability and the growth and development of offspring in female and male rats through two-generation reproduction toxicity study. METHODS: The specific pathogen free healthy SD rats were randomly divided into control group and low-, medium-and high-dose lufenuron groups, with 60 rats in each group, half females and half males. Rats in the low-, medium-and high-dose lufenuron groups were respectively fed with lufenuron at the dose of 5.0, 20.0 and 80.0 mg/(kg body weight·day) for 8 weeks before mating. The control group was fed with standard foot. The reproductive index, brain and reproductive organ coefficients and pathological changes were observed in P and F1 parents. The birth and growth indexes of the offspring were measured. RESULTS: i) P generation: from the 14 th day, the female rats in the medium-dose group had lower body weight than that of the female control group(P<0.05); from the 35 th day, the body weight was lower than that of the female low-dose group(P<0.05). From the 14 th day, the female rats in the high-dose group had lower body weight than that of the other three female groups(P<0.05). From the 14 th day, the male rats in the medium-and high-dose groups had lower body weight than that of the male control group and low-dose group(P<0.05). The body weight of pregnant rats in the parental high-dose group was lower than that of the control group, low-dose group, and medium-dose group at day 0, 7, 14, 19 of the pregnancy duration(P<0.05). The body weight of pregnant rats in the parental medium-dose group was lower than that of the low-dose group on day 0 of the pregnancy duration, and lower than that of the control and low-dose groups on day 7 and 14(P<0.05). The conception rate, the new-borne survival rates and the feeding survival rate of female rats in the high-dose group was lower than that of the other three female groups(P<0.008). The new-borne feeding survival rate of female rats in the medium-dose group was lower than that of the control group and low-dose group(P<0.008). The organ coefficients of brain in female rats in the medium-and high-dose groups were higher than that of the female control group and low-dose group(P<0.05). The organ coefficients of brain and testis in male rats in the medium-and high-dose groups were higher than that of the control group and low-dose group(P<0.05). The organ coefficient of epididymis in male rats in the high dose group was lower than that of the other three male groups(P<0.05). ii) F1 generation: the body weight of female rats in the low-and medium-dose group was higher than that of the female control group on the 42 th day(P<0.05). The body weight of male rats in the low-dose group was higher than that of the male control group on the 42 th, 49 th, and 56 th days(P<0.05). The body weight of male rats in the medium-dose group was higher than that of the male control group on the 14 th, 21 th, 42 th, 49 th, and 56 th days(P<0.05). The new-borne survival rate in the low-dose group was lower than that of the control group(P<0.017). The body weight of new-borne rats in the high-dose group on day 4 of birth was lower than that in the other three female groups(P<0.05). iii) F2 generation: the body weight of male rats in the male medium-dose group was lower than that in the control group on day 21 of birth(P<0.05). CONCLUSION: The reproductive and developmental toxicity of lufenuron is found in rats in the medium-and high-dose groups. Toxicities including low body weight, conception rate, new-borne survival rate and feeding survival rate are found in P generation; low body weight and feeding survival rate are found in F1 generation; low body weight is found in male F2 generation. The no-observed-adverse-effects levels of lufenuron in two-generation reproductive study are 5.87 mg/(kg·d) for females and 5.09 mg/(kg·d) for males in SD rats.
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OBJECTIVE：To study the toxic effect of the extract from Tripterygium hypoglaucum on pregnant animal and embryo-fetal development . METHODS ：Successfully mated New Zealand female rabbits were randomly divided into solvent control group，positive control group （cyclophosphamide，20 mg/kg）and T. hypoglaucum extract high-dose ，medium-dose and low- dose groups（15.0，7.50，3.75 g/kg，by the amount of crude drug ）according to their body weight ，with 18 rabbits in each group at least. The female rabbits in solvent control group and T. hypoglaucum extract groups were given water or the corresponding T. hypoglaucum extract solution from 6th to 18th day of pregnancy ，5 mL/kg，once a day. Positive control group was given cyclophosphamide subcutaneously into the neck from 10th to 13th day of pregnancy ，1 mL/kg，once a day. According to the related requirements of Technical Guidelines for the Study of Drug Reproductive Toxicity ，the general situation ，body weight ，body weight increase and food intake of female rabbits were observed and recorded during the experiment ，and euthanasia was carried out on 28th day of pregnancy ；the relative indexes of main organs ，fetal uterus ，placenta uterus ，placenta，ovary，implantation gland ， absorption fetus ，stillbirth，live fetus and corpus luteum were observed and recorded after anatomy ；the relative indexes of body weight，appearance，visceral and skeletal alterations of the fetus were detected . RESULTS ：Compared with solvent control group ， the body weight ，body weight increase ，food intake ，main organs ，pregnancy of pregnant rabbits ，as well as reproductive function，embryo formation ，fetal growth and development ，appearance，visceral and skeletal development indexes in T. hypoglaucum extract groups had no significant abnormal changes （P＞0.05）；above indexes in the positive control group had significant changes （P＜0.05），and significant maternal toxicity and embryotoxicity were found. CONCLUSIONS ：T. hypoglaucum extract 15.00-3.75 g/kg（by the amount of crude drug ）have no significant maternal toxicity ，embryotoxicity or fetal development toxicity to New Zealand rabbits.
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Reproductive toxicity is the toxicity of reproductive system caused due to environmental factors such as chemicals, heavy metals etc. They interfere in some way with normal reproduction, such substances are called reprotoxic. It includes hazardous effects on fertility and sexual function in adult males and females as well as developmental toxicity in the offspring. Developmental toxicity is abnormal structure or functional development following exposure of pregnant or lactating females. In environment there are various factors which are responsible for causing adverse effect on reproductive system. Heavy metals like cadmium, lead, mercury, Industrial chemicals like phthalates, BPA, Agricultural chemicals, radiations, some of the narcotics drugs like morphine, ethanol, psychotropic drugs like diazepam, chlorpromazine, hypotensives like methyldopa, reserpine. All these factors acts as reproductive toxicants and affects male and female reproductive system causing spontaneous abortion, miscarriage, reduced fertility, preterm delivery, LBW, affect sertoli cells in the testis, affect leydig cell function etc. In ancient Ayurvedic texts also it is described that the heavy metal such as mercury, copper affects the reproductive system. Metals and metallic compounds, pesticides, some food additives have a nature of accumulations within the living body when it exposed since prolonged period. These factors accumulate in the body day by day. This is nothing but Dushivisha (cumulative toxins). Dushivishas vitiates the Dhatus after the laps of a long time on obtaining a favorable condition. It also affects the Shukradhatu causing Shukrashaya (diminish semen). People should be aware of all these factors to take adequate precaution.
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OBJECTIVE@#Bisphenol A (BPA) is a monomer primarily used in the production of polycarbonate plastic and epoxy resins. Bisphenol F (BPF) is apparently the main BPA replacement that is used increasingly. BPF has been detected in canned food, thermal paper receipts, and soft drinks. In the present experiment, we did both in vitro and in vivo studies to evaluate the effect of low and high-dose BPF exposures on testosterone concentration, oxidative stress, and antioxidants activity in reproductive tissues of male rats.@*METHODS@#Adult (80-90 days old) male Sprague Dawley rats (n = 36) obtained from the rodent colony of Animal Sciences Department of Quaid-i-Azam University. The direct effects of BPF on the antioxidant enzymes and testosterone secretion were measured in vitro and in vivo studies. In an in vivo experiment, adult male Sprague Dawley rats (n = 42) were exposed to different concentrations of bisphenol F (1, 5, 25, and 50 mg/kg/d) for 28 days. Various biochemical parameters were analyzed including the level of catalase (CAT), superoxide dismutase (SOD), peroxidase (POD), reactive oxygen species (ROS), and lipid peroxidation (LPO). Moreover, sperm motility, daily sperm production (DSP), comet assay, and histological analysis were performed.@*RESULTS@#In vitro study showed that BPF exposure significantly (p < 0.05) induced oxidative stress biomarkers, i.e., ROS and LPO, while it did not change antioxidant enzyme and testicular testosterone concentration. Whereas, an in vivo study revealed that BPF induced dose-dependent effect and high-dose (100 mg/kg) exposure of BPF significantly reduced tissue protein (p < 0.05) content, CAT (p < 0.001), SOD (p < 0.05), and POD (p < 0.05) levels while significantly (p < 0.05) augmented ROS and lipid peroxidation. Furthermore, BPF reduces testosterone, LH, and FSH secretion in a dose-dependent manner. Significant (p < 0.001) reduction in plasma and intra-testicular testosterone, LH, and FSH was noticed at 100 mg/kg BFP dose. High-dose exposure reduces spermatogenesis.@*CONCLUSION@#BPF showed an antagonistic effect on male reproductive hormones and induce alterations in testicular morphology. Increased oxidative stress and decreased testicular antioxidant status might be the underlying mechanism of BFP-induced testicular toxicity.
Subject(s)
Animals , Male , Rats , Antioxidants , Metabolism , Benzhydryl Compounds , Toxicity , Dose-Response Relationship, Drug , Environmental Pollutants , Toxicity , Oxidative Stress , Phenols , Toxicity , Rats, Sprague-Dawley , Testosterone , MetabolismABSTRACT
The plasticizer di(2-ethylhexyl) phthalate (DEHP) has been widely used in the manufacture of polyvinyl chloride-containing products such as medical and consumer goods. Humans can easily be exposed to it because DEHP is ubiquitous in the environment. Recent research on the adverse effects of DEHP has focused on reproductive and developmental toxicity in rodents and/or humans. DEHP is a representative of the peroxisome proliferators. Therefore, peroxisome proliferator-activated receptor alpha (PPARα)-dependent pathways are the expected mode of action of several kinds of DEHP-induced toxicities. In this review, we summarize DEHP kinetics and its mechanisms of carcinogenicity and reproductive and developmental toxicity in relation to PPARα. Additionally, we give an overview of the impacts of science policy on exposure sources.
Subject(s)
Animals , Humans , Mice , Rats , Diethylhexyl Phthalate , Toxicity , Environmental Pollutants , Toxicity , Haplorhini , PPAR alpha , Genetics , Metabolism , Plasticizers , ToxicityABSTRACT
This paper summarizes the research progress of reproductive toxicity of Tripterygium wilfordii from 1979,and the toxicity characterization,damage mechanism,and attenuated measures are summarized. It was found that,the reproductive toxicity caused by T. wilfordii is mainly distributed on components of Tripterygium glycosides,triptolide,tripchlorolide,and clinically preparations,such as Leigongteng Tablets and Tripterygium Glycosides Tablets. Adverse reactions to male reproductive system caused by Tripterygium preparations mainly include decreased sperm motility,oligospermia or spermatozoa,decreased fertility or infertility,etc. Long-term drug use may also lead to testicular atrophy and decreased sexual desire. Adverse reactions to women are mainly manifested as menstrual disorders,decreased menstrual volume or even amenorrhea,decreased sexual desire,infertility,etc. The reproductive toxicity of T. wilfordii is related to apoptosis of reproductive cells,disturbance of spermatogenesis or oogenesis,damage of testis and ovary in reproductive target tissues,and changes of internal environment in gonad tissues( hormones,hormone synthesis rate-limiting enzymes and energy metabolism). Drug compatibility,hormone replacement,medication duration and dosage form changes can help reduce the damage of T. wilfordii to the reproductive system. In addition,in view of the existing problems in the current study,the author proposes new directions in clinical studies,pharmacological metabolism mechanism,preparation quality standards and new therapeutic effects,etc.,to provide a basis for the safe and reasonable clinical application of T. wilfordii.