[Effect of toluene diisocyanate on lung function of workers].

OBJECTIVE: To investigate the effect of long-term exposure to toluene diisocyanate (TDI) on the lung function of TDI-exposed workers. METHODS: A factory was selected for this occupational epidemiological investigation. The workers who were exposed to TDI and had complete physical examination records in recent 3 years were the exposed group (n = 45), while the company's administrative staff, logistics staff, and other non-TDI-exposed workers who had complete physical examination records in recent 3 years were the control group (n = 47). The two groups were compared in terms of lung function indices. RESULTS: Compared with the control group, the 2009 exposure group had significantly lower forced expiratory volume in one second (FEV1.0), FEV1.0/forced vital capacity (FVC), and maximal expiratory flow at 25% of FVC (MEF25) (P < 0.05), the 2010 exposure group had significantly lower FEV1.0, FEV1.0/FVC,maximum voluntary ventilation (MVV), and maximal expiratory flow at 50% of FVC (MEF50) (P < 0.05), and the 2011 exposure group had significantly lower FEV1.0, FEV1.0/FVC, peak expiratory flow (PEF), MEF25, and MEF50 (P < 0.05). CONCLUSION: Long-term exposure to TDI can lead to certain impairment of lung function in workers, which may be reflected by decreased lung function indices such as vital capacity, FVC, FEV1.0, FEV1.0/FVC, PEF, and MVV.

[The inhibitory effect of latent transforming growth factor ß1 activation and silicosis by CD36 targeted RNA interference in silicosis model of rat].

OBJECTIVE: To investigate the inhibitory effects of CD36-targeting RNA interference on the latent transforming growth factor ß1 (L-TGF-ß1) activation and silicotic fibrosis in rat silicosis model. METHODS: Wistar rats were divided into four groups: saline control group (n=24), SiO2 model group (10 mg SiO2 per rat) (n=24), SiO2+Lv-shCD36 group (lentiviral vector expressing specific shRNA against CD36) (n=24), and SiO2+Lv-shCD36-NC group (non-silence control lentivirus) (n=24). At 7, 21, and 28 d after instillation, the rats were sacrificed. The activity of TGF-ß1 in bronchoalveolar lavage fluid (BALF) was measured by evaluating its inhibitory effect on the proliferation of mink lung epithelial cells. The pathological changes of lung tissue were observed by HE staining and van Gieson staining. The hydroxyproline content in the lungs was determined by alkaline lysis method. RESULTS: At 7 d after instillation, the expression of CD36 mRNA in alveolar macrophages was significantly lower in the SiO2+Lv-shCD36 group than in the saline control group, SiO2 model group, and SiO2+Lv-shCD36-NC group (P < 0.05); the quantity and percentage of active TGF-ß1 in BALF were significantly lower in the SiO2+Lv-shCD36 group than in the SiO2 model group and SiO2+Lv-shCD36-NC group (P < 0.05). At 28 d after instillation, there were cellular silicotic nodules in the lungs of rats in SiO2+Lv-shCD36 group and fibrotic cellular silicotic nodules in the lungs of rats in SiO2 model group and SiO2+Lv-shCD36-NC group. At 21 and 28 d after instillation, the hydroxyproline content was significantly lower in the SiO2+Lv-shCD36 group than in the SiO2 model group and SiO2+Lv-sh CD36-NC group (P < 0.05). CONCLUSION: CD36-targeting RNA interference has inhibitory effects on the L-TGF-ß1 activation and silicotic fibrosis in rat silicosis model.

[Pathological changes of major organs after rats inhaled methyl ethyl ketone peroxide aerosol].

OBJECTIVE: To investigate the pathological changes of major organs in rats that have inhaled methyl ethyl ketone peroxide (MEKP) aerosol and to provide clues to the oxidative damage mechanism of MEKP. METHODS: A total of 100 Sprague-Dawley rats (male-to-female ratio = 1:1) were randomly and equally divided into blank control group, solvent control group, and 50, 500, and 1000 mg/m(3) MEKP exposure groups to inhale clean air, solvent aerosol, or MEKP for 6 h per day, 5 d per week, for 13 weeks. A rat model of subchronic MEKP exposure was established. The clinical manifestations during exposure were recorded. The organ coefficients of the kidney, thymus, and testis were calculated. The histopathological changes of the lung, liver, and testis were observed by HE staining. RESULTS: The male rats in 1000 mg/m(3) MEKP exposure group had significantly lower organ coefficients of the kidney and testis than those in blank control group, solvent control group, and 50 and 500 mg/m(3) MEKP exposure groups (P < 0.05). The rats in 1000 mg/m(3) MEKP exposure group had a significantly lower organ coefficient of the thymus than those in blank control group and solvent control group (P < 0.05). Some rats in 500 and 1000 mg/m3 MEKP exposure groups had significant damage to the lung, liver, and testis, which demonstrated a worsening trend as the dose increased. Pulmonary hyperinflation, hyperemia, bleeding, interstitial pneumonia, and even lung abscess were seen in the damaged lung. Nuclear enrichment, hepatocyte steatosis, and mild cellular edema in the portal area were seen in the damaged liver. Variable degeneration, necrosis, and dysplasia of spermatogenic cells and significant decrease in sperms in spermatogenic cells were seen in the damaged testis. The female rats in blank control group, solvent control group, and 50, 500, and 1000 mg/m(3) MEKP exposure groups showed no pathological changes in the ovary. CONCLUSION: Inhalation of MEKP aerosol can cause oxidative damage to the liver, lung, kidney, thymus, and testis in rats, particularly to the testis in male rats.

[Effect of subchronic inhalation of ethylbenzene on expression of heme oxygenase-1 in rat renal tissues].

OBJECTIVE: To investigate the effect of ethylbenzene on the expression of heme oxygenase-1 (HO-1) intrarenal tissues. METHODS: Forty male Sprague-Dawley rats were randomly and equally allocated to control group, low-dose exposure group, moderate-dose exposure group, and high-dose exposure group to inhale different doses of ethylbenzene (0, 433.5 mg/m(3) (100 ppm), 4335.0 mg/m(3) (1000 ppm), and 6500.0 mg/m(3) (1500 ppm)) for 6 h per day, 5 days per week, for 13 weeks. After the rat model of subchronic ethylbenzene exposure was established, the activities of glutathione peroxidase (GSH-Px), superoxide dismutase (SOD), and catalase (CAT) in renal tissues were measured, and the mRNA and protein expression levels of HO-1 in renal tissues were measured by real-time PCR and Western blot. RESULTS: Compared with the control group, all exposure groups showed significantly decreased activities of GSH-Px and CAT in renal tissues and the moderate- and high-dose exposure groups showed significantly decreased activity of SOD in renal tissues (P < 0.05). All exposure groups showed significantly higher expression of HO-1 than the control group (P < 0.05). The high-dose exposure group showed significantly higher expression of HO-1 than the low- and moderate-dose exposure group (P < 0.05), and the moderate- and high-dose exposure group had significantly higher expression of HO-1 than the control group and low-dose exposure group (P < 0.05). CONCLUSION: A certain dose of ethylbenzene can induce elevated expression of HO-1 and decreased antioxidant levels in rat renal tissues, thus leading to oxidative stress damage.

[Influence of ethylbenzene on oxidative damage and apoptosis in rat renal epithelial cells NRK-52e].

OBJECTIVE: To study the oxidative damage and apoptosis of renal tubular epithelial cells (NRK-52e cell line) induced by ethylbenzene. METHODS: NRK-52e cells were exposed to 30, 60, 90, 120 µmol/L ethylbenzene for 24 hours. Cell viability were measured using MTT, the activities of superoxide dismutase (SOD), glutathione peroxidase (GSH-Px) and catalase (CAT), the contents of malondialdehyde (MDA) and glutathione (GSH) were detected respectively. PI fluorescent staining assay was applied to detect percentage of apoptosis in ethylbenzene-treated groups. RESULTS: Compared with control group, cell outline became clear, cell diopter increased, cell became smaller and shrinkage, some cells broke in 60 µmol/L ethylbenzene-treated group. Plenty of cells died, suspension cells increased significantly in 90 µmol/L ethylbenzene-treated group. Compared with control group, cell viability the activities of SOD and CAT and the content of GSH were significantly decreased in 60 and 90 µmol/L ethylbenzene-treated groups (P<0.05). The MDA content were remarkably elevated in 90 µmol/L ethylbenzene-treated groups (P<0.05). CONCLUSION: Ethylbenzene can induce oxidative stress and apoptosis in NRK-52e cells (P<0.05).

[The changes of blood neurotransmitter levels in workers occupationally exposed to ethylbenzene].

OBJECTIVE: To explore the effects of occupational ethylbenzene exposure on blood neurotransmitter levels in population. METHODS: The exposure group consisted of 246 workers occupationally exposed to ethylbenzene and the control group was composed of 122 staffs from the offices. The basic information on ethylbenzene exposure was collected by the questionnaire. The mandelic acid (MA) and phenylglyoxylic acid (PGA) in the post-working urine were measured using the high performance liquid chromatography. The levels of gamma-aminobutyric acid (GABA), dopamine (DA) and acetylcholinesterase (AchE) activity were detected by reversed phase high performance liquid chromatography, spectrofluorometry and DTNB method, respectively. The blood biochemical indexes: alanine transaminase (ALT), aspartate aminotransferase (AST), total protein (TP), albumin (ALB), alkaline phosphatase (ALP), total bilirubin (TBIL) were examined. Also the hematologic indexes: red blood cell (RBC), white blood cell (WBC), hemoglobin (HGB) and platelet (PLT) were determined. RESULTS: The levels of MA, PGA and MA+PGA of urine in the exposed group were significantly higher than those in the control group (P < 0.05). There were no significant differences of the biochemical indexes (AST, ALT, TP, ALB, BUN, Cr, ALP and TBIL), hematologic indexes (WBC, RBC, Hb and PLT) and serum GABA between the exposure group and the control group (P > 0.05). But the serum DA [(0.21 ± 0.011) mg/L] and AChE levels [(0.321 ± 0.066) U/L] in the exposure group were significantly lower than those in the control group [(0.25 ± 0.015) mg/L, (0.583 ± 0.125) U/L], respectively (P < 0.05). CONCLUSION: MA and PGA in urine can serve as the biomarkers of internal exposure dose. Before the obvious changes of biochemical indexes and hematologic indexes appear, the exposure to ethylbenzene can influence the blood neurotransmitter levels in workers exposed to ethylbenzene.

[The neurobehavioral effects of population occupationally exposed to ethylbenzene].

OBJECTIVE: To evaluate the influence of ethylbenzene on the neurobehavior of occupationally exposed workers. METHODS: The exposure group consisted of 246 workers occupationally exposed to ethylbenzene and 172 staffs from the offices served as controls. The basic information on ethylbenzene exposure was collected by the questionnaire. The nervous behavior and function of workers were evaluated by Neurobehavioral Core Test Battery (NCTB). RESULTS: There were no differences of the scores for four emotional states (tension, depression, angry and bewilderment) between exposure group and control group (P > 0.05). The score of emotion (vigor) in exposure group was significantly lower than that in control group (P < 0.05), but the fatigue score in exposure group was significantly higher than that in control group (P < 0.05). The score of mean reaction time in exposure group was significantly higher than that in control group (P < 0.05), the scores of digital span, manual dexterity, visual retention and target tracking in exposure group were significantly lower than those in control group (P < 0.05). The exposure group was divided into 5 sub-groups, according to working duration. There were no differences for the scores of visual retention and target tracking among 5 sub-groups (P > 0.05). The scores of five emotional states (tension, depression, angry, fatigue and bewilderment) in 3 sub-groups exposed to ethylbenzene for 3 ∼, 4 ∼ and 5 ∼ years were significantly higher than those in 2 sub-groups exposed to ethylbenzene for 0 ∼ and 2 ∼ years (P < 0.05). The scores of digital span in 2 sub-groups exposed to ethylbenzene for 3 ∼ or 4 ∼ years and the scores of manual dexterity and digital symbol in 3 sub-groups exposed to ethylbenzene for 3 ∼, 4 ∼ and 5 ∼ years were significantly lower than those in 2 sub-groups exposed to ethylbenzene for 0 ∼ and 2 ∼ years (P < 0.05). CONCLUSION: Ethylbenzene can depress the neurobehavioral functions of exposed workers. The neurobehavioral functions of workers exposed to ethylbenzene for 3 years changed significantly. The workers exposed to ethylbenzene for 3 years may be the susceptible population of neurobehavioral function impairment.

[Effects of ethylbenzene on oxidative damage, ultrastructure and expressions of apoptosis-related genes in rat brain tissues].

OBJECTIVE: To investigate the influence of ethylbenzene on oxidative damage, ultrastructure and the expressions of apoptosis-related genes in the rat brain tissues. METHODS: Four groups of 10 males of Sprague-Dawley rats were allocated randomly, and inhaled daily with different doses of ethylbenzene: 0, 433.5 mg/m³, 4335.0 mg/m³, and 6500.0 mg/m³ 6 h daily, 5 days per week for 13 weeks. The contents of glutathione (GSH) and malondialdehyde (MDA) and activity of acetylcholinesterase (AChE) were assayed, respectively. The ultrastructure of brain tissues was observed via electron microscope. The gene expression levels of Bax, Bcl-2, cytochrome C, caspase-9 and caspase-3 in brain tissues were measured by real-time polymerase chain reaction (PCR), respectively. RESULTS: The contents of MDA [(2.03 ± 0.56), (4.17 ± 1.31) nmol/mg pro] in the brain tissues of 4335.0 mg/m³ and 6500.0 mg/m³ ethylbenzene-treated groups were significantly higher than that [(1.08 ± 0.26) nmol/mg pro] in the control group (P < 0.05), while AChE activities [(0.321 ± 0.066), (0.276 ± 0.031), (0.202 ± 0.041) U/mg] and GSH contents [(35.19 ± 15.08), (33.42 ± 15.32), (27.99 ± 7.53) mg/g pro] in all ethylbenzene-treated groups were remarkably depressed (P < 0.05, P < 0.05, respectively). After 6500.0 mg/m³ ethylbenzene inhalation, the nucleolus exhibit demilune with decreased mitochondria. Electrondense of myelin occurred in the injured nerve, ascribing to lipid peroxidationed membrane. The gene expression level of Bax in brain tissue of 4335.0 mg/m³ and 6500.0 mg/m³ ethylbenzene-treated group was significantly higher than that in the control group (P < 0.05). Compared with the control group, the gene expression levels of cytochrome C, caspase-9 and caspase-3 in all ethylbenzene-treated groups were enhanced (P < 0.05, P < 0.05, respectively), while bcl-2 gene expression levels in all ethylbenzene-treated groups were decreased (P < 0.05). CONCLUSION: Ethylbenzene can induce oxidative damage and apoptosis in brain tissues. The apoptotic mechanism might be involved with up-regulation of Bax, cytochrome C, caspase-9 and caspase-3, as well as restraint of Bcl-2.

[Influence of ethylbenzene on the levels of mandelic acid and phenylglyoxylic acid in urine, ultrastructure and the expressions of Mitochondrial apoptotic-related proteins in the rat nephridial tissues].

OBJECTIVE: To investigate the influence of ethylbenzene on the levels of mandelic acid (MA) and phenylglyoxylic acid (PGA) in urine, the ultrastructure and the expressions of mitochondrial apoptotic-related genes in the rat nephridial tissues. METHODS: Four groups of 10 males of Sprague-Dawley rats were allocated randomly into four groups: control (C) group, low (L) group, moderate (M) group and high (H) group, and inhaled daily with different doses of ethylbenzene: 0, 433.5 mg/m(3), 4335 mg/m(3), and 6500 mg/m(3) 6 h per day, 5 days per week for 13 weeks. The mandelic acid and phenylglyoxylic acid in the urine was assayed by high performance liquid chromatography. The ultrastructure of nephridial tissue was observed via electron microscope. The protein expression levels of Bax, Bcl-2, cytochrome C, Caspase-9 and Caspase-3 in nephridial tissues were measured by Western blot, respectively. RESULTS: The levels of MA [(0.303 +/- 0.148) mg/L, (0.404 +/- 0.154) mg/L] and PGA [(0.168 +/- 0.104) mg/L, (0.174 +/- 0.092) mg/L] in the urine of M and H groups were significantly higher than that in the control and L group [(0.084 +/- 0.070) mg/L, (0.041 +/- 0.029) mg/L] (P < 0.05, respectively). It has been shown a dose-effect relationship between the contents of MA, PGA and MA + PGA and inhaled ethylbenzene, respectively. The mitochondria of rat nephridial tissue of H group became a compact and vacuolar structure with disorder and loss of cristae. The expression levels of Bax in mitochondria of nephridial tissues of M and H groups were significantly lower than that in the control group (P < 0.05). Caspase-3 expression level in H group was remarkably higher than that in the control group (P < 0.05). Compared with the control group, the expression levels of cytochrome C and Caspase-9 were enhanced, while the expression levels of Bcl-2 were restrained in all ethylbenzene-treated groups (P < 0.05, P < 0.05, respectively). The expression levels of Caspase-3 in M and H groups were significantly higher than that in the control group and L group (P < 0.05). CONCLUSION: Ethylbenzene can induce apoptosis in the cells of nephridial tissues. The apoptotic mechanism might be involved with up-regulation of Bax, cytochrome C, Caspase-9 and Caspase-3, as well as restraint of Bcl-2. The level of MA and PGA in the rat urine could be a parameter of biological dose in vivo after ethylbenzene inhalation.

Exposure of mother-child and postpartum woman-infant pairs to DDT and its metabolites in Tianjin, China.

1,1,1-trichloro-2,2'-bis(4-chlorophenyl)ethane (DDT) exhibits its long persistence in the environment, unusual bioaccumulation, effects on wildlife, and the possibility of long-term adverse effects on human health, especially reproductive toxicity. Despite the prohibition of most persistent organochlorine pesticides in China, the presence of organochlorine residue, including DDT, has been widely indicated in environmental substance. However, scarce information is available about accumulative levels of DDT in human tissues in China. To evaluate levels of DDT and its potential effects on women and children's health in a Chinese pesticide-exposed area, we recruited 50 pairs of mother-child and 50 postpartum women, and determined the levels of total DDT and its four main metabolites (p,p'-DDE, p,p'-DDT, p,p'-DDD, o,p'-DDT) in venous blood, breast milk and umbilical blood cord by gas chromatography. Accordingly, data on reproductive outcomes of mothers and postpartum women and healthy status of children and infants were gathered through a questionnaire and medical examinations. Furthermore, we also assayed the DDT levels of some environmental samples (soil, food, milk, et al.). The levels of DDT in children's blood were higher than that in the women's. As compared to breast milk, the umbilical blood cord and the ventral fat individually demonstrated a significantly lower and higher level of DDT in the postpartum women. DDT was lower in milk and crucian carp than in the soil near the chemical plant. p,p'-DDT and p,p'-DDE were the main metabolites of DDT. Our findings suggested the cumulative effect of DDT in human body in Tianjin, China.