Mineralization of Steroidal Hormones by Biosolids in Wastewater Treatment Systems in Tennessee U.S.A.

Citations Over TimeTop 10% of 2000 papers

Abstract

During the past several years, concern has risen over potential pollution of waterways with estrogenic compounds, including steroidal hormones from human and animal sources. One potential source of steroid hormone contamination is through the incomplete removal of these compounds in wastewater treatment systems (WTS). To address this issue, laboratory mineralization assays using 14C-labeled estrogens and testosterone were performed with biosolids from four municipal treatment plants and one industrial system. The importance of adapted microbial populations in the removal of estrogen was shown by the dramatic differences in mineralization of 14C-17β-estradiol by biosolids from a municipal plant compared to that from the industrial plant, 84% versus 4%, respectively. Indeed, biosolids from all of the municipal plants mineralized 70−80% of added 14C-17β-estradiol to 14CO2 in 24 h. Removal of 14C-17β-estradiol from the aqueous phase by biodegradation and/or biosorption to cell matter was greater than 90%. A recombinant yeast estrogen assay (YES assay) also confirmed that biological estrogenic activity was removed from the biosolid samples to below the detection limit (1.56 nM). 14C-Testosterone was mineralized to 14CO2 in all four municipal biosolids in amounts ranging from 55% to 65%; moreover, total removal of 14C-testosterone from the aqueous phase was 95%. First-order rate constants k were obtained for the mineralization and removal from the aqueous phase of natural and a synthetic steroid hormone in biosolids from one WTP. In these biosolids, 14C-17β-estradiol and 14C-testosterone were rapidly mineralized to 14C-CO2 (k = 0.0042 ±0.0002 min-1 and 0.0152 ± 0.0021 min-1, respectively), whereas the mineralization of the synthetic estrogen 14C-17α-ethinylestradiol was 25−75-fold less (k = 0.0002 ± 0.0000 min-1). In addition, mineralization of 14C-ethinylestradiol did not reach completion in 24 h with only 40% mineralized to 14C-CO2. Approximately 20% of the 14C-ethinylestradiol remained in the aqueous phase and was biologically active as determined by the YES assay. Changes in temperature of approximately 15 °C had a statistically significant effect on the rate of mineralization and removal of 14C-17β-estradiol from the aqueous phase but not for 14C-testosterone or 14C-17α-ethinylestradiol. These results suggest that biosolids in municipal plants in this region have the capability to remove natural steroid hormones in their influents over a range of temperatures but may be less effective at removing the synthetic estrogen 17α-ethinylestradiol.

Related Papers

• → Triclosan adsorption using wastewater biosolids-derived biochar(2016)98 cited
• → Integrated photocatalytic-biological reactor for accelerated phenol mineralization(2010)54 cited
• → Occurrence and removal of triclosan in Canadian wastewater systems(2019)44 cited
• Rening av mikrobryggeriers avloppsvatten(2017)
• → Structural Analysis and Characterization of Biosolids. A Case Study of Biosolids from Wastewater Treatment Plants in Western Greece(2023)