Department of Civil Engineering, Indian Institute of Technology Delhi, New Delhi, 110016, India.
J Environ Manage. 2021 Feb 1;279:111626. doi: 10.1016/j.jenvman.2020.111626. Epub 2020 Nov 23.
This research provides a framework for the human health risk assessment due to exposure of AR (antibiotic resistance) E. coli from recreational water (swimming activity). Literature-based epidemiological studies were used for f-value formulation (i.e., AR E. coli/total number of E. coli isolates) and the theoretical calculation of AR and non-AR E. coli concentrations. Risk was estimated using calculated values by considering four different dose-response (D-R) scenarios with known characteristics due to current lack of availability of D-R for AR bacteria. f-values ranged between 0.14 and 0.59 and the order of calculated theoretical values of maximum AR E. coli are as follows: ampicillin or amoxicillin (38 CFU/dip) > co-trimoxazole (19 CFU/dip) ~ tetracycline (18 CFU/dip) > ceftriaxone or cefotaxime or ceftazidime (10 CFU/dip) ~ ciprofloxacin or ofloxacin (9 CFU/dip). The risk of infection was considerably high for theoretical calculated concentration values regardless of the chosen D-R model (annual risk of infection (95th percentile) = 1, Spearman's rank correlation coefficient = -0.06 to 0.94), under the conditions studied. Further, AR levels of human gastrointestinal-tract were determined using literature-reported data in stool samples and indicated that the resistance level was very high in healthy human (range: 3.7 × 10-8.4 × 10 CFU/g of wet lumen content). The maximum allowable concentration values for AR E. coli and non-ARB (0.0075 CFU/dip and 2.56 CFU/dip) were found to be smaller than the USEPA recreational water quality guidelines (≤126 CFU/100 mL), which can help the USEPA and other regulatory bodies in revisiting the current guidelines. So based on the noted results, we can conclude that the maintenance of inventory of actual measured concentration of ARB in the recreational water sites is needed to prevent unwanted complication related to the treatment of infectious sustained by resistant microbes.
本研究提供了一个框架,用于评估人类因接触休闲水中(游泳活动)的抗药性大肠杆菌(antibiotic resistance,AR)而产生的健康风险。采用基于文献的流行病学研究来制定 f 值(即 AR 大肠杆菌/大肠杆菌分离株总数)并对 AR 和非 AR 大肠杆菌浓度进行理论计算。由于目前缺乏针对 AR 细菌的剂量-反应(dose-response,D-R)关系,因此使用计算值来估计风险,同时考虑了四个不同的 D-R 场景,这些场景的特征是已知的。f 值范围在 0.14 到 0.59 之间,计算得到的最大 AR 大肠杆菌理论值的顺序如下:氨苄青霉素或阿莫西林(38 CFU/dip)>复方新诺明(19 CFU/dip)四环素(18 CFU/dip)>头孢曲松或头孢噻肟或头孢他啶(10 CFU/dip)环丙沙星或氧氟沙星(9 CFU/dip)。无论选择哪种 D-R 模型,理论计算浓度值的感染风险都相当高(95%百分位的年感染风险=1,Spearman 秩相关系数=-0.06 至 0.94),在所研究的条件下。此外,通过对粪便样本中文献报道的数据进行研究,确定了人类胃肠道中的 AR 水平,结果表明健康人群的耐药水平非常高(范围:3.7×10-8.4×10 CFU/g 湿腔内容物)。发现 AR 大肠杆菌和非 ARB(0.0075 CFU/dip 和 2.56 CFU/dip)的最大允许浓度值小于美国环保署休闲水质量指南(≤126 CFU/100 mL),这有助于美国环保署和其他监管机构重新审查当前的指南。因此,根据上述结果,我们可以得出结论,需要维护休闲水场所实际测量的 ARB 浓度的库存,以防止因耐药微生物引起的感染持续而导致不必要的并发症。