2014
DOI: 10.1021/es5048057
|View full text |Cite
|
Sign up to set email alerts
|

Spatial and Temporal Variation in De Facto Wastewater Reuse in Drinking Water Systems across the U.S.A.

Abstract: De facto potable reuse occurs when treated wastewater is discharged into surface waters upstream of potable drinking water treatment plant (DWTP) intakes. Wastewater treatment plant (WWTP) discharges may pose water quality risks at the downstream DWTP, but additional flow aids in providing a reliable water supply source. In this work de facto reuse is analyzed for 2056 surface water intakes serving 1210 DWTPs across the U.S.A. that serve greater than 10,000 people, covering approximately 82% of the nation’s po… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
4
1

Citation Types

4
124
0

Year Published

2016
2016
2022
2022

Publication Types

Select...
6
2

Relationship

2
6

Authors

Journals

citations
Cited by 134 publications
(128 citation statements)
references
References 24 publications
4
124
0
Order By: Relevance
“…Regional‐scale multimedia models provide uniform exposure estimates for the surface‐water compartment based on regional or default general environmental fate properties rather than accounting for spatial variability (e.g., ChemCAN; Mackay et al ). More sophisticated screening‐level exposure models have been developed to better incorporate a spatial context to in‐stream exposure estimation, such as the following examples: GREAT‐ER model: Feijtel et al ; Koormann et al P h ATE model: Anderson et al ; Cunningham et al HydroROUT model: Lehner and Grill ScenAT model: Early approach detailed in Hodges et al ; CM Holmes, Waterborne Environmental, Leesburg, Virginia, USA, personal communication De facto wastewater reuse estimation: Rice et al …”
Section: Introductionmentioning
confidence: 99%
“…Regional‐scale multimedia models provide uniform exposure estimates for the surface‐water compartment based on regional or default general environmental fate properties rather than accounting for spatial variability (e.g., ChemCAN; Mackay et al ). More sophisticated screening‐level exposure models have been developed to better incorporate a spatial context to in‐stream exposure estimation, such as the following examples: GREAT‐ER model: Feijtel et al ; Koormann et al P h ATE model: Anderson et al ; Cunningham et al HydroROUT model: Lehner and Grill ScenAT model: Early approach detailed in Hodges et al ; CM Holmes, Waterborne Environmental, Leesburg, Virginia, USA, personal communication De facto wastewater reuse estimation: Rice et al …”
Section: Introductionmentioning
confidence: 99%
“…The study also provides a first step towards linking WWTP emissions to de facto reuse within the Netherlands. Indeed, this is one of very few studies to explore this problem [1,3,31], and to date, the only one that follows initial TWW emissions to the planar surface of agricultural fields. This is an important step in that it outlines a pathway by which TWW associated contaminants may spread through the surface water network and even to the subsurface.…”
Section: Model Successes Limitations Uncertaintiesmentioning
confidence: 99%
“…However, the majority of agricultural water reuse globally is the indirect or de facto reuse that occurs when wastewater is a dominant component of available surface water flows. Effluent from wastewater treatment plants can constitute a major portion of available surface water downstream of urban areas [13]. Consequently, alternate water reuse strategies such as industrial or domestic reuse or spatial redistribution of wastewater return flows, can have significant impacts on downstream farmers reliant on these urban wastewater return flows [14].…”
Section: Introductionmentioning
confidence: 99%