Friedrich-Alexander-Universität Erlangen-Nürnberg, Institute and Outpatient Clinic of Occupational, Social and Environmental Medicine, Henkestr. 9-11, 91054, Erlangen, Germany.
Institute for Prevention and Occupational Medicine of the German Social Accident Insurance, Institute of the Ruhr-Universität Bochum (IPA), Bürkle-de-la-Camp Platz 1, 44789, Bochum, Germany.
Arch Toxicol. 2019 Aug;93(8):2185-2195. doi: 10.1007/s00204-019-02468-9. Epub 2019 Jun 20.
Up to date, information on the validity of human biomonitoring (HBM) parameters of naphthalene exposure is poor. This study was performed to reveal the relation between occupational exposure to naphthalene and biological exposure markers. Therefore, ten lowly and highly exposed workers from the abrasives industry were selected to characterise a broad exposure range. Naphthalene in air was determined by personal air monitoring during one shift. For biological monitoring, pre- and post-shift urine samples collected on 2 days of a working week were analysed for 1,2-dihydroxynaphthalene (1,2-DHN), 1- and 2-naphthol, 1- and 2-naphthylmercapturic acid (NMA). The naphthalene concentration in air was in the range of 0.5 to 11.6 mg/m. The biomarkers in urine showed post-shift concentration in the range of 114-51,809 µg/L for 1,2-DHN, 0.8-666 µg/L for 1-NMA, 2-2698 µg/L for 1-naphthol and 4-1135 µg/L for 2-naphthol, respectively. 2-NMA was not detected. The urinary levels increased significantly from pre- to post-shift for all analysed parameters and an accumulation over the working week was observed. Significant positive correlations were observed between 1,2-DHN, 1-NMA, 1- and 2-naphthol in post-shift urine samples and personal exposure to naphthalene in the air. 1-NMA and 1,2-DHN, 1- and 2-naphthol have been demonstrated as suitable biomarkers for naphthalene exposure monitoring. Of the determined biomarkers, 1,2-DHN is by far the metabolite with the highest concentration in the urine samples.
目前,有关萘暴露的人体生物监测 (HBM) 参数有效性的信息还很有限。本研究旨在揭示职业性萘暴露与生物暴露标志物之间的关系。为此,选择了来自磨料行业的 10 名低暴露和高暴露工人,以描述广泛的暴露范围。在一个班次期间通过个人空气监测来测定空气中的萘含量。为了进行生物监测,在一个工作周的两天内采集班前和班后尿样,分析 1,2-二羟萘(1,2-DHN)、1-萘酚、2-萘酚、1-萘基硫代尿酸(NMA)。空气中的萘浓度在 0.5 至 11.6mg/m3 之间。尿样中的生物标志物显示,1,2-DHN 的班后浓度范围为 114-51,809μg/L,1-NMA 的浓度范围为 0.8-666μg/L,1-萘酚的浓度范围为 2-2698μg/L,2-萘酚的浓度范围为 4-1135μg/L。未检测到 2-NMA。所有分析参数的尿样中,班前到班后的浓度均显著增加,且在整个工作周内呈积累趋势。在班后尿样中,1,2-DHN、1-NMA、1-和 2-萘酚之间观察到显著的正相关,且与空气中的萘个人接触呈正相关。1-NMA 和 1,2-DHN、1-和 2-萘酚已被证明是监测萘暴露的合适生物标志物。在所测定的生物标志物中,1,2-DHN 是迄今为止尿液样本中浓度最高的代谢物。