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Combining environmental isotopes with Contaminants of Emerging Concern (CECs) to characterise wastewater derived impacts on groundwater quality
被引:25
|作者:
McCance, W.
[1
,5
]
Jones, O. A. H.
[2
,3
]
Cendon, D. I.
[4
]
Edwards, M.
[5
]
Surapaneni, A.
[6
]
Chadalavada, S.
[7
]
Wang, S.
[8
]
Currell, M.
[1
,3
]
机构:
[1] RMIT Univ, Sch Engn, GPO Box 2476, Melbourne, Vic 3001, Australia
[2] RMIT Univ, Sch Sci, Australian Ctr Res Separat Sci, Bundoora West Campus,POB 71, Bundoora, Vic 3083, Australia
[3] RMIT Univ, Water Effect Technol & Tools Res Ctr, GPO Box 2476, Melbourne, Vic 3001, Australia
[4] Australian Nucl Sci & Technol Org, Inst Environm Res, Kirrawee Dc, NSW 2232, Australia
[5] BlueSphere Environm, 113 Ferrars St, Southbank, Vic 3006, Australia
[6] South East Water, 101 Wells St, Frankston, Vic 3199, Australia
[7] Univ Newcastle, Cooperat Res Ctr Contaminat Assessment & Remediat, ATC Bldg, Callaghan, NSW 2308, Australia
[8] Chinese Acad Sci, Inst Genet & Dev Biol, Key Lab Agr Water Resources, Shijiazhuang 050021, Hebei, Peoples R China
来源:
关键词:
Environmental tracers;
Wastewater treatment plants;
Contaminants of emerging concern (CECs);
Contaminant delineation;
Environmental isotopes;
ARTIFICIAL SWEETENER;
TREATMENT PLANTS;
BORON ISOTOPES;
TRACERS;
AQUIFER;
NITRATE;
PHARMACEUTICALS;
RECHARGE;
URBAN;
FATE;
D O I:
10.1016/j.watres.2020.116036
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
The potential for Wastewater Treatment Plants (WWTPs) to cause adverse impacts to groundwater quality is a major global environmental challenge. Robust and sensitive techniques are required to characterise these impacts, particularly in settings with multiple potential contaminant sources (e.g. agricultural vs. site-derived). Stable (delta H-2(H2O), delta O-18(H2O), delta N-15(NO3), delta O-18(NO3) and delta C-13(DIC)) and radioactive (H-3 and C-14) isotopes were used in conjunction with three Contaminants of Emerging Concern (CECs) - carbamazepine, simazine and sulfamethoxazole - to discriminate between multiple potential contamination sources at an Australian WWTP. The radioactive isotope tritium provided a sensitive indicator of recent (post-1990s) leakage, with groundwater activities between 0.68 and 1.83 TU, suggesting WWTP infrastructure (activities between 1.65 and 2.41) acted as a recharge 'window', inputting treated or partially treated effluent to the underlying groundwater system. This was corroborated by water stable isotopes, which showed clear demarcation between delta O-18(H2O) and delta H-2(H2O) in background groundwater (delta O-18(H2O) and delta H-2(H2O) values of approximately -5 and -28 parts per thousand, respectively) and those associated with on-site wastewater (median delta O-18(H2O) and delta H-2(H2O) values of -1.2 and -7.6 parts per thousand, respectively), with groundwater down-gradient of the plant plotting on a mixing line between these values. The CECs, particularly the carbamazepine:simazine ratio, provided a means to further distinguish wastewater impacts from other sources, with groundwater down-gradient of the plant reporting elevated ratios (median of 0.98) compared to those up-gradient (median of 0.11). Distinctive CEC ratios in impacted groundwater close to the WWTP (similar to 3.0) and further down-gradient (2.7-9.3) are interpreted to represent a change in composition over time (i.e., recent vs. legacy contamination), consistent with the site development timeline and possible changes in effluent composition resulting from infrastructure upgrades over time. The data indicate a complex set of co-mingled plumes, reflecting different inputs (in terms of both quantity and concentration) over time. Our approach provides a means to better characterise the nature and timing of wastewater derived impacts on groundwater systems, with significant global implications for site management, potentially allowing more targeted monitoring, management and remedial actions to be undertaken. (C) 2020 Elsevier Ltd. All rights reserved.
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