Environmental Monitoring ; Humans ; Occupational Exposure ; Toluene ; analysis

Environmental Monitoring ; methods ; Inhalation Exposure ; Occupational Exposure ; analysis ; Workplace

China ; Dust ; analysis ; Environmental Exposure ; Environmental Pollutants ; chemistry ; Environmental Pollution ; analysis ; Humans ; Metals ; chemistry

Environmental Exposure ; analysis ; Environmental Monitoring ; instrumentation ; Environmental Pollutants ; analysis ; metabolism ; Humans ; Risk Assessment

Air Pollution/analysis* ; Environmental Exposure/analysis* ; China/epidemiology* ; Air Pollutants/analysis* ; Particulate Matter/analysis* ; Environmental Monitoring

Triclosan, a broad-spectrum antimicrobial agent, was reported to have been widely detected in various human biological samples such as urine, blood and human milk among foreign populations. In China, limited reports have been found on human exposure to triclosan, and the reported urinary triclosan concentrations were significantly lower than that of American populations. Besides, the potential influencing factors still remain unclear regarding human exposure to triclosan, but evidences suggest that those in middle age and with higher household income and higher social class tend to have higher urinary triclosan concentrations. Furthermore, triclosan exposure tend to differ by sex, geography, heredity, metabolism and life style.
China ; Environmental Exposure ; analysis ; Humans ; Middle Aged ; Triclosan ; analysis

OBJECTIVETo assess the current status of the acrylamide in the Chinese food supply, the dietary acrylamide exposure in the Chinese population and to estimate the public health risks of the current consumption.

METHODSThe acrylamide content in the total diet study (TDS) food samples was analyzed using an LC-MS/MS method. Based on the analytical results, the dietary exposure calculations were performed using a deterministic method, combining mean acrylamide concentrations from the food group composite with their associated food consumptions.

RESULTSAcrylamide was detected in 43.7% of all samples collected and acrylamide concentration varied from ND to 526.6 µg/kg. The estimated dietary intakes of acrylamide among Chinese general population given as the mean and the 95th percentile (P95) were 0.286 and 0.490 µg•kg(-1) bw•day(-1), respectively. The margins of exposure (MOEs) for the population calculated using both benchmark dose lower confidence limit for a 10% extra risk of tumors in animals (BMDL10) 0.31 and 0.18 µg•kg(-1) bw•day(-1), were 1069 and 621 for the mean dietary exposure, and 633 and 367 for the high dietary exposure respectively.

CONCLUSIONThese MOE values might indicate a human health concern on acrylamide for Chinese population. Efforts should continue to reduce acrylamide levels in food in order to reduce the dietary risks to the human health.

Acrylamide ; chemistry ; China ; Diet ; Environmental Exposure ; analysis ; Environmental Pollutants ; chemistry ; Food Analysis ; Food Contamination ; Humans

Plastics are extensively used in our daily life. However, a significant amount of plastic waste is discharged to the environment directly or via improper reuse or recycling. Degradation of plastic waste generates micro- or nano-sized plastic particles that are defined as micro- or nanoplastics (MNPs). Microplastics (MPs) are plastic particles with a diameter less than 5 mm, while nanoplastics (NPs) range in diameter from 1 to 100 or 1000 nm. In the current review, we first briefly summarized the environmental contamination of MNPs and then discussed their health impacts based on existing MNP research. Our review indicates that MNPs can be detected in both marine and terrestrial ecosystems worldwide and be ingested and accumulated by animals along the food chain. Evidence has suggested the harmful health impacts of MNPs on marine and freshwater animals. Recent studies found MPs in human stool samples, suggesting that humans are exposed to MPs through food and/or drinking water. However, the effect of MNPs on human health is scarcely researched. In addition to the MNPs themselves, these tiny plastic particles can release plastic additives and/or adsorb other environmental chemicals, many of which have been shown to exhibit endocrine disrupting and other toxic effects. In summary, we conclude that more studies are necessary to provide a comprehensive understanding of MNP pollution hazards and also provide a basis for the subsequent pollution management and control.
Environmental Exposure ; Environmental Monitoring ; Microplastics ; adverse effects ; analysis ; Water Pollutants ; adverse effects ; analysis

OBJECTIVETo investigate the feasibility of using the concentration of 1,2-DCE in blood as a biological monitoring indicators and build the determination method of 1,2-DCE in blood.

METHODSDose-response relationship of the exposure of 1,2-DCE and the level of 1,2-DCE in rat blood were investigated using the Pearson's correlation analysis. The concentration of 1,2-DCE in blood was determined using Headspace Sampler-Gas Chromatography-Mass Spectrometer (HS-GC-MS). 3.0 ml blood sample diluting with 2.0 ml 1,2-DCE standard serial solution was placed in 15 headspace bottles respectively and heated at 80 ℃ for 20 min.The vapor upon the headspace bottle was separated by capillary column and the concentration of 1,2-DCE was determined by massspectrum in SIM mode to draw a standard work curve. The within-run precision and the between-run precision were calculated by the relative standard deviation (RSD) of the concentration of 1,2-DCE in blood which was determined 6 times in a day and 6 times within 3 days respectively. The recovery rate was calculated by P=(C2 -C0)/C1 × 100%.

RESULTSWhen the treatment groups were exposed at dosage of 1,472, 2,550, 3,093, 3,976, and 4 418 mg/m(3), the average concentration of 1,2-DCE in rat blood was 24.1,231.6,344.3,395.1,538.5 μg/L. There was a positive correlation between the concentration of 1,2-DCE in rat blood and the exposed level of 1,2-DCE.The equation of dose-response relationship was y=0.162x -195.8,r=0.982 2,P=0.003 and the precision of exposure experiments was 7.04% -13.15%. 1,2-DCE contents within 0.259 -2 587 μg/L showed a good linear relationship and the regression equation was y=47 901x -357 446, r= 0.999 8. When the blood containing 0.259 μg/L 1,2-DCE was determined for six times, the average peak/peak signal-to-noise ratio was 56.55. The limit of detection (LOD) was 0.014 μg/L and the limit of quantification (LOQ) was 0.046 μg/L. The within-run precision was 1.23% -2.76% and the between-run precision was 2.21% -4.64%. The average recovery rate was 93.3% - 98.6%.

CONCLUSIONThe concentration of 1,2-DCE in blood could be used as a biological monitoring indicator. The method of the concentration of 1,2-DCE in blood determining by HS-GC-MS was characterized by high sensitivity, wide linear range, small interference, high precision and easy operation.

Animals ; Environmental Exposure ; analysis ; Environmental Monitoring ; Ethylene Dichlorides ; blood ; Gas Chromatography-Mass Spectrometry ; Limit of Detection ; Rats

OBJECTIVEThe main purpose of this work was to give the evidence of reasonable and feasible dust control measures which will be taken in the future by analyzing the trend of dust concentration from 1991 to 2010 and identifying working faces with the severe dust contamination in one underground iron mine.

METHODSThe data was from routine monitoring between the years 1991 and 2010, which enclosed the total dust concentrations and silica contents. China National Standard of Occupational exposure limits for hazardous agents in the workplace used to judge whether the dust concentration exceeded the National Standard.

RESULTSThe general trend of total dust concentration from 1991 to 2010 was decreased, especially maximum and average levels. The highest exceeding rate was 43.16% in 1993 and the best years were 2009 and 2010, but the exceeding rates were still over 30%. The dust exposure levels varied with different work faces. The mining and supporting were the most severe dust pollution faces which the highest ultra exceeding rates were 51.61% and 51.48% and the maximum exceeding times were 64.6 and 16.4 respectively. The next was constructing face with 40.23% exceeding rate and 24.6 times more than standard.

CONCLUSIONThe trend of total dust concentration from 1991 to 2010 was decreased, but the dust exceeding rate was still high. The strong measures should be taken to control the dust pollution in this iron mine, especially mining and supporting faces.

Air Pollutants, Occupational ; analysis ; Dust ; analysis ; Environmental Monitoring ; Iron ; analysis ; Mining ; Occupational Exposure ; analysis