Research Center for Environmental Quality Management, Graduate School of Engineering, Shiga, Japan.
Environment Preservation Center, Kanazawa University, Kanazawa, Ishikawa, Japan.
J Appl Toxicol. 2020 Jul;40(7):908-917. doi: 10.1002/jat.3952. Epub 2020 Feb 20.
Pharmaceuticals are widely detected in aquatic environments, and their potential risks to aquatic species are of concern because they are designed to be biologically active. Here, we used an in vitro assay, called the transforming growth factor α shedding assay, to measure the biological activities of G protein-coupled receptor (GPCR)-acting pharmaceuticals present in river water and effluents from municipal wastewater treatment plants (WWTPs) in Japan from 2014 to 2016. Antagonistic activities against angiotensin (AT1), dopamine (D2), adrenergic (β1), acetylcholine (M1) and histamine (H1) receptors were detected in river water, and were stronger downstream than upstream owing to effluent from WWTPs along the river. Ozonation at one WWTP reduced these activities. Concentrations of sulpiride (D2 antagonist) could explain 73% of antagonistic activities against the D2 receptor; those of metoprolol, atenolol and propranolol (β1 antagonists) could explain 16% of activities against the β1 receptor; and those of pirenzepine (M1 antagonist) could explain 15% of activities against the M1 receptor. Therefore, other receptor antagonists also occur. GPCR-acting pharmaceuticals should be given more attention in environmental monitoring and toxicity testing.
药品广泛存在于水生环境中,由于其被设计成具有生物活性,因此对水生生物的潜在风险引起了关注。在这里,我们使用了一种称为转化生长因子 α 脱落测定法的体外测定法,来测量 2014 年至 2016 年期间日本河流和城市污水处理厂(WWTP)废水中存在的作用于 G 蛋白偶联受体(GPCR)的药物的生物活性。在河水中检测到了对血管紧张素(AT1)、多巴胺(D2)、肾上腺素能(β1)、乙酰胆碱(M1)和组胺(H1)受体的拮抗活性,由于河流沿线 WWTP 的废水,下游的活性比上游更强。一个 WWTP 的臭氧化作用降低了这些活性。舒必利(D2 拮抗剂)的浓度可以解释 73%的 D2 受体拮抗活性;美托洛尔、阿替洛尔和普萘洛尔(β1 拮抗剂)的浓度可以解释 16%的β1 受体活性;而哌仑西平(M1 拮抗剂)的浓度可以解释 15%的 M1 受体活性。因此,还存在其他受体拮抗剂。在环境监测和毒性测试中,应更加关注作用于 GPCR 的药物。