尼日利亚伊莫州奥韦里游乐场儿童血液和尿液中多环芳烃浓度的生物监测。

Environmental analysis, health and toxicology Pub Date : 2019-12-01 Epub Date: 2019-12-09 DOI:10.5620/eaht.e2019011
Verla Andrew Wirnkor, Verla Evelyn Ngozi, Chigbo Medo Ajero, Lele Kelechi Charity, Okechukwu StellaMaris Ngozi, Enyoh Christian Ebere, Amaobi Collins Emeka
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引用次数: 0

摘要

多环芳烃(PAHs)具有持久性、生物累积性和毒性等特点,因此是与各种不良健康影响相关的主要空气污染物之一。儿童受这些污染物的影响最大,但在尼日利亚,与儿童直接相关的研究却很少。在这项研究中,36 名 4-14 岁儿童的血液和尿液由一名持证抽血医师按照无菌程序从他们的眶前窝采集到 BD vacutainer tubes® 中,而中段尿液样本则采集到酸洗过的 120 毫升 BD vacutainer 尿杯中,并在零下 4 摄氏度的冰箱中保存 6 小时,然后每 5 毫升用 10 毫升戊烷提取,并使用气相色谱-质谱仪分析 15 种多环芳烃。结果显示,血液中的多环芳烃浓度(53.48 至 70.8 微克/分升)低于尿液中的多环芳烃浓度(94.98 至 115.04 微克/分升)。学校之间的平均值没有明显差异(p>0.5),这可能是由于所有学校都受到了类似的人为干扰。在 5%的显著性水平下,血液样本中的芴-荧蒽(FLa)和苯并(a)蒽-荧蒽(FLa)分别呈正相关和强相关(r=0.83,r=0.73)。二环和三环多环芳烃在血液和尿液中的浓度普遍较低。尽管二苯并 (a,h) 蒽是分布最广的化合物,但其在尿液中的浓度却高于血液。尿液中致癌多环芳烃的浓度高于血液。苊(0.06)和蒽(Ant; 0.11)的消除比值(ER)被认为较低,而 FLa(1.36)和茚并[1, 2, 3-cd]芘(1.55)的消除比值被认为较高。消除比的变化趋势非常相似。总之,儿童血液和尿液中的多环芳烃含量较高,因此具有较高的致癌和非致癌风险。这项研究意义重大,它为更详细的工作奠定了基础,同时提醒决策者需要采取紧急缓解措施,减少儿童接触这类危险污染物的机会。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Biomonitoring of concentrations of polycyclic aromatic hydrocarbons in blood and urine of children at playgrounds within Owerri, Imo State, Nigeria.

Biomonitoring of concentrations of polycyclic aromatic hydrocarbons in blood and urine of children at playgrounds within Owerri, Imo State, Nigeria.

Biomonitoring of concentrations of polycyclic aromatic hydrocarbons in blood and urine of children at playgrounds within Owerri, Imo State, Nigeria.

Polycyclic aromatic hydrocarbons (PAHs) exposure is among the leading air pollutants associated with diverse adverse health effects due to their persistent, bio-accumulative and toxic characteristics. Children are most affected by these pollutants, yet studies directly related children to these pollutants are scarce in Nigeria. In this study, blood and urine from 36 children between the ages 4-14 years were collected as per sterile procedures by a licensed phlebotomist from the antecubital fossa into BD vacutainer tubes® while a mid-stream urine sample into acid-washed 120 mL BD vacutainer urine cups and stored in refrigerator at -4˚C for 6 hours, then each 5 mL was extracted with 10 mL of pentane and analyzed for 15 PAHs using GC-MS. Results revealed that PAHs concentrations (53.48 to 70.8 μg/dL) in blood was lower than in urine (94.98 to 115.04 μg/dL). Mean values had no significant (p>0.5) differences between schools, possibly due to the fact that all schools were experiencing similar anthropogenic disturbances. At 5% level of significance, positive and strong correlationships (r=0.83, r=0.73) were observed for fluorene-fluoranthene (FLa) and benzo (a) anthracene-FLa respectively in blood samples. Two and three rings PAHs had generally low concentrations in both blood and urine. Despite being the most distributed compound, the concentration of dibenzo (a,h) anthracene was highest for urine than in blood. Urine PAHs showed higher concentration of carcinogenic PAHs than blood. Elimination ratios (ER) such as for acenaphthene (0.06) and anthracene (Ant; 0.11) were considered low while values such as for FLa (1.36) and indeno [1, 2, 3-cd] pyrene (1.55) were considered high ER. Trends in elimination ratios showed close similarity. In conclusion there was elevated PAHs in blood and urine of children with consequent high carcinogenic and then non-carcinogenic risks. This research is significant in setting the stage for more detailed work at same time alerting policy makers on the need for urgent mitigation steps that will reduce children exposure to this class of dangerous pollutants.

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