Agriculture and Agri-Food Canada, Ottawa, ON, Canada K1A 0C6.
Chemosphere. 2012 Apr;87(2):194-203. doi: 10.1016/j.chemosphere.2011.12.018. Epub 2012 Jan 31.
Dewatered municipal biosolids (DMBs) were applied to a field at a rate of 22 Mg dw ha(-1) in October 2008. Pharmaceuticals and personal care products (PPCPs) were monitored in groundwater, tile drainage, soil, DMB aggregates incorporated into the soil post-land application, and in the grain of wheat grown on the field for a period of ~1 year following application. Over 80 PPCPs were analyzed in the source DMB. PPCPs selected for in-depth monitoring included: antibiotics (tetracyclines, fluoroquinolones), bacteriocides (triclosan, triclocarban), beta-blockers (atenolol, propranolol, metaprolol), antidepressants (fluoxetine, citalopram, venlafaxine, sertraline), antifungals (miconazole), analgesics (acetaminophen, ibuprofen) and anticonvulsants (carbamazepine). PPCPs in tile were observed twice, ~3 weeks and 2 months post-application. Of all PPCPs measured in tile drainage, only carbamazepine, ibuprofen, acetaminophen, triclosan, triclocarban, venlafaxine, and citalopram were detected (5-74 ng L(-1)). PPCPs were not detected in groundwater >2 m depth below the soil surface, and concentrations above detection limits at 2 m depth were only observed once just after the first rain event post-application. In groundwater, all compounds found in tile, except carbamazepine, acetaminophen and citalopram, were detected (10-19 ng L(-1)). PPCPs were detected in DMB aggregates incorporated in soil up to 1 year post-application, with miconazole and fluoxetine having the lowest percent reductions over 1 year (50%). For several compounds in these aggregates, concentration declines were of exponential decay form. No PPCPs were detected in the grain of wheat planted post-application on the field. No PPCPs were ever detected in water, soil or grain samples from the reference plot, where no DMB was applied.
2008 年 10 月,脱水市政生物固体(DMB)以22 Mg dw ha(-1)的速率施用于农田。在施药后约 1 年的时间里,监测了地下水、排水渠、土壤、施药后混入土壤中的 DMB 团聚体以及在该田地上种植的小麦中的药物和个人护理产品(PPCP)。在源 DMB 中分析了 80 多种 PPCP。选择用于深入监测的 PPCP 包括:抗生素(四环素类、氟喹诺酮类)、杀菌剂(三氯生、三氯卡班)、β-受体阻滞剂(阿替洛尔、普萘洛尔、美托洛尔)、抗抑郁药(氟西汀、西酞普兰、文拉法辛、舍曲林)、抗真菌药(咪康唑)、镇痛药(对乙酰氨基酚、布洛芬)和抗惊厥药(卡马西平)。排水渠中的 PPCP 被观察了两次,施药后约 3 周和 2 个月。在排水渠中测量的所有 PPCP 中,只有卡马西平、布洛芬、对乙酰氨基酚、三氯生、三氯卡班、文拉法辛和西酞普兰被检测到(5-74ng L(-1))。在距土壤表面 2 米以下的地下水深处未检测到 PPCP,仅在施药后第一次降雨事件后不久,在 2 米深度处的检测限以上观察到一次。在地下水中,除卡马西平、对乙酰氨基酚和西酞普兰外,在排水渠中发现的所有化合物均被检测到(10-19ng L(-1))。施药后 1 年内,在混入土壤中的 DMB 团聚体中检测到 PPCP,其中咪康唑和氟西汀在 1 年内的去除率最低(50%)。对于这些团聚体中的几种化合物,浓度下降呈指数衰减形式。施药后种植的小麦籽粒中未检测到 PPCP。在未施 DMB 的对照地块的水样、土壤或谷物样本中,从未检测到 PPCP。