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Finished Water sentence examples within drinking water treatment

drinking water treatment

AOM affects the drinking water treatment processes and finished water quality.

Adsorption isotherms and kinetics for the removal of algal organic matter by granular activated carbon.

drinking water treatment

Amino acids are ubiquitous as dissolved nitrogenous organic matter in source water and can pass through drinking water treatment processes to react with disinfectants in finished water and in the distribution system.

Derivates variation of phenylalanine as a model disinfection by-product precursor during long term chlorination and chloramination.

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Finished Water sentence examples within finished water sample

finished water sample

The occurrence of the most common NSAIDs (diclofenac, ibuprofen, naproxen, and ketoprofen) in river water, groundwater, finished water samples, WWTPs, and hospital wastewater effluents along with their toxicity effects were reviewed.

A review on environmental occurrence, toxicity and microbial degradation of Non-Steroidal Anti-Inflammatory Drugs (NSAIDs).

finished water sample

5% of decanter biofilm, and 32% of finished water samples.

Legionella feeleii: Ubiquitous Pathogen in the Environment and Causative Agent of Pneumonia

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Finished Water sentence examples within finished water quality

finished water quality

AOM affects the drinking water treatment processes and finished water quality.

Adsorption isotherms and kinetics for the removal of algal organic matter by granular activated carbon.

finished water quality

Furthermore, the finished water quality indices of the Mopanshan Reservoir all could meet the “Standards for drinking water quality” (GB57492006), except for the chloral exceeding 20% of the limit after the conventional treatment.

Diversity comparison of water quality between the Mopanshan Reservoir and Songhuajiang Reservoir - northeast China

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10.1016/J.CEJ.2021.128519

Efforts were made to determine the association between different fluorescence moieties in DOM of finished water and chlorine consumption through excitation-emission matrix coupled with parallel factor analysis (EEM-PARAFAC).

Fluorescence moieties as a surrogate for residual chlorine in three drinking water networks

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10.1088/1755-1315/643/1/012116

In order to know the water quality of rural water supply projects, the water samples are collected from finished water and tap water of administrative villages in some counties and districts of the Pearl River Basin for sampling inspection in 2019.

A Study of Water Quality Safety of Rural Water Supply Projects in the Pearl River Basin

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10.1016/j.scitotenv.2021.145277

Two HBQs, 2,6-dichloro-1,4-benzoquinone (2,6-DCBQ) and 2,6-dibromo-1,4-benzoquinone (2,6-DBBQ), were detected in finished water and tap water in China.

Occurrence and toxicity of halobenzoquinones as drinking water disinfection byproducts.

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10.2166/ws.2021.284

After the treatments, there were still considerable QNs in the finished water (total amounts of 74.

Investigation on the fate of quinolone antibiotics in three drinking water treatment plants of China

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10.1016/j.watres.2021.117162

In loop-structured DWDSs, finished water with different PFAS characteristics could mix along the pipeline, with the corresponding DWTP as the center, ultimately forming a relatively uniform distribution in the entire DWDS.

Field study on the transportation characteristics of PFASs from water source to tap water.

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10.1016/j.chemosphere.2021.129894

The turbidity removal by all AMCs obeyed with World Health Organization (WHO) acceptable limit of finished water, where HCl treated AMC clarified 15.

Kinetic modelling of high turbid water flocculation using native and surface functionalized coagulants prepared from shed-leaves of Avicennia marina plants.

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10.3724/SP.J.1123.2020.08026

Haloacetonitriles (HANs) are widely used in finished water as unregulated disinfection by-products.

[Simultaneous determination of six haloacetonitriles in finished water for drinking by purge and trap-gas chromatography-triple quadrupole mass spectrometry].

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10.1016/j.ecoenv.2021.112421

Meanwhile, health risk of exposure to organic micropollutants in finished water through three exposure routes (ingestion, dermal absorption and inhalation) was assessed with the method proposed by U.

Mutagenicity, health risk, and disease burden of exposure to organic micropollutants in water from a drinking water treatment plant in the Yangtze River Delta, China.

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10.1016/j.chemosphere.2021.132587

Full-scale conventional treatment removed 52 % of anthropogenic particles when comparing raw (42 ± 18 particles/L) and finished water (20 ± 8 particles/L).

Conventional and biological treatment for the removal of microplastics from drinking water.

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10.1007/s13762-020-03039-7

The concentration of TOC in finished water was 0.

Advanced removal of water NOM by Pre-ozonation, Enhanced coagulation and Bio-augmented Granular Activated Carbon

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10.2166/h2oj.2021.103

Regrowth potential evaluated by indigenous microbial community in finished water was reduced to 22% of that in raw water, while 75% of assimilable organic carbon in raw water remained in finished water.

Characterization of microbial regrowth potential shaped by advanced drinking water treatment

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10.1016/J.JHAZMAT.2020.123986

3 ng L-1, whereas in finished waters significantly decreased to a range of <LOQ to 269 ng L-1.

Effective abatement of 29 pesticides in full-scale advanced treatment processes of drinking water: From concentration to human exposure risk.

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10.1016/j.chroma.2019.05.048

This proposed method was successfully applied to surface water, ground water, raw water, finished water, tap water, and bottled water samples.

Solid-phase extraction of seventeen alternative flame retardants in water as determined by ultra-high-performance liquid chromatography-tandem mass spectrometry.

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10.1039/C9EW00291J

The changes in eight metals (Al, Fe, Mn, Zn, Cu, Ba, Cr, and As) were investigated from the finished water (water treated by a drinking water treatment process before entering the distribution process) to the tap water of 10 water treatment plants in 5 cities of eastern China.

Accumulation and re-release of metallic pollutants during drinking water distribution and health risk assessment

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10.1155/2019/7851354

The results confirmed that different antibiotics including fluoroquinolones and B-lactams were detected in the raw and finished water.

Detection of Antibiotics in Drinking Water Treatment Plants in Baghdad City, Iraq

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10.1007/s11783-019-1109-4

Totally 24 of the 39 targeted PPCPs were detected in raw water, and 12 PPCPs were detected in the finished water.

PPCPs in a drinking water treatment plant in the Yangtze River Delta of China: Occurrence, removal and risk assessment

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10.1016/j.envres.2019.108553

Outcomes were linked with county-specific monthly estimates of the nitrate concentration in finished water, based on data collected for compliance with the Safe Drinking Water Standard.

Prenatal exposure to nitrate in drinking water and the risk of congenital anomalies.

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10.1186/s12302-019-0229-6

ResultsThe O3–BAC–sand yielded lower turbidity but higher CODMn (by approximately 7%) in the finished water than regular O3–BAC (sand–O3–BAC).

Treatment performance comparison between regular O3–BAC and O3–BAC with rear sand filtration: verification in a full-scale study

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10.1007/s12517-019-4875-1

The study aims to ensure that the finished water is safe to drink and meet the international drinking water regulations.

Assessment of drinking water quality along Port Said Canal treatment plants, Suez Canal corridor, Egypt

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10.1016/j.chroma.2019.07.004

The performance of the method was checked along different strategic sampling points of three potabilization plants serving the city of Turin (Italy), including intermediate treatments and finished waters.

Towards the revision of the drinking water directive 98/83/EC. Development of a direct injection ion chromatographic-tandem mass spectrometric method for the monitoring of fifteen common and emerging disinfection by-products along the drinking water supply chain.

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10.1002/smll.201804436

Drinking water treatment processes (DWTPs) impact pathogen colonization and microbial communities in finished water; however, their efficacies against opportunistic pathogens are not fully understood.

Removal Efficacy of Opportunistic Pathogens and Bacterial Community Dynamics in Two Drinking Water Treatment Trains.

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10.3390/membranes9070090

Therefore, it is of prime importance to design a simple and compact, yet robust, system for Mn and Fe control of the domestic GW sources, which can reliably guarantee the desired Mn limit in the finished water (20μg/L).

Hybrid Hollow Fiber Nanofiltration–Calcite Contactor: A Novel Point-of-Entry Treatment for Removal of Dissolved Mn, Fe, NOM and Hardness from Domestic Groundwater Supplies

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10.1016/j.watres.2019.115283

In addition, the occurrence of the aromatic DBPs in tap water and finished water was studied in a mega city Shenzhen located in South China.

Comparative cytotoxicity of halogenated aromatic DBPs and implications of the corresponding developed QSAR model to toxicity mechanisms of those DBPs: Binding interactions between aromatic DBPs and catalase play an important role.

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10.3133/sir20185130

By 2040, the public supply of raw and (or) finished water to meet demand for the 10 RCAs is projected to increase 48 percent to 532.

Estimated use of water in the Cumberland River watershed in 2010 and projections of public-supply water use to 2040

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10.1016/j.envpol.2019.03.041

In this study, an investigation covering the odor characteristics, algal distribution and possible odorants contributing to swampy/septic odor, including dimethyl disulfide (DMDS), dimethyl trisulfide (DMTS), diisopropyl sulfide (DIPS), dipropyl sulfide (DPS), dibutyl sulfide (DBS), 2-methylisoborneol (2-MIB) and geosmin (GSM), was performed in source and finished water of 56 drinking water treatment plants (DWTPs) in 31 cities across China.

Occurrence of swampy/septic odor and possible odorants in source and finished drinking water of major cities across China.

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10.1016/j.ijheh.2019.07.008

In this study we propose a procedure to evaluate the health risk related to turbidity in finished water by determining the cases of drinking water-related gastrointestinal diseases.

Water safety plans and risk assessment: A novel procedure applied to treated water turbidity and gastrointestinal diseases.

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10.1016/j.chemosphere.2019.05.259

Incomplete removal of NDMA precursors by RO and the UV/advanced oxidation process (UV/AOP) led to NDMA formation in the finished water and miles downstream in the transmission pipelines.

Influence of reverse osmosis membrane age on rejection of NDMA precursors and formation of NDMA in finished water after full advanced treatment for potable reuse.

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10.1080/15569543.2018.1431676

6) µg/L) were found in finished water of WTP1 and WTP2, respectively.

Removal of heavy metals by conventional water treatment plants using poly aluminum chloride

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10.2166/WS.2019.026

The results suggested that DBP concentrations of the finished water were higher in spring (82.

Speciation and seasonal variation of various disinfection by-products in a full-scale drinking water treatment plant in East China

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10.1016/j.watres.2019.03.026

Additionally, a weekly sampling monitoring of 1,4-dioxane and alkyl-1,3-dioxanes and dioxolanes in raw water, groundwater and finished water was performed at a DWTP over more than two years.

Dioxanes and dioxolanes in source waters: Occurrence, odor thresholds and behavior through upgraded conventional and advanced processes in a drinking water treatment plant.

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10.1016/J.PSEP.2019.07.014

Finally, we applied the WHO guideline and an empirical quantitative microbial risk assessment (QMRA) model to estimate probable health risk based on a residual number of rotavirus in finished water.

Evaluation of the physical and chemical characteristics of water on the removal efficiency of rotavirus in drinking water treatment plants and change in induced health risk

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10.1016/j.mimet.2018.11.022

parvum oocysts were spiked into 10 l of source or finished water in triplicate followed by recovery using Envirochek HV sampling capsules.

A highly sensitive method for detecting Cryptosporidium parvum oocysts recovered from source and finished water using RT-PCR directed to Cryspovirus RNA.

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10.13227/j.hjkx.201907083

The THMs in finished water and tap water of TH Waterworks were in the range 8.

[Disinfection By-products and the Relevant Health Risk in the Water Supply System in H City of Zhejiang Province].

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10.1021/acs.est.8b07363

We compared the finished water of two water treatment plants (WTP-A, WTP-B) serving Shanghai, China.

Carcinogenic risk of N-Nitrosamines in Shanghai Drinking Water: Indications for the Use of Ozone Pretreatment.

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10.1016/j.watres.2019.06.076

The infection risk and the burden of disease attributed to the parasite presence in finished water were estimated incorporating physical and chemical log reduction values (LRVs), using stochastic modeling and disinfection profiling.

Optimizing the performance of conventional water treatment system using quantitative microbial risk assessment, Tehran, Iran.

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10.1039/C9EW00286C

Accepted concentrations for per- and polyfluoroalkyl substances (PFASs) in finished water are lower than ever before with new regulations often enacted based on findings made possible by improved analytical techniques and correspondingly justified health concerns.

Efficient removal of per- and polyfluoroalkyl substances (PFASs) in drinking water treatment: nanofiltration combined with active carbon or anion exchange

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10.1016/j.scitotenv.2019.03.143

9 × 104 genes/mL) in finished water.

Occurrence and reduction of antibiotic resistance genes in conventional and advanced drinking water treatment processes.

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10.1016/j.chemosphere.2019.04.095

The occurrence and transformation behaviors of disinfection byproducts (DBPs) were investigated in the finished water and tap water of 14 water treatment plants in rural areas of eastern China.

The occurrence and transformation behaviors of disinfection byproducts in drinking water distribution systems in rural areas of eastern China.

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10.1016/j.ecoenv.2018.12.004

Concentrations of THMs in finished water of study WTPs varied, ranging from 18.

Health risk assessment of trihalomethanes in water treatment plants in Jiangsu Province, China.

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10.1007/s10661-019-7997-8

The bromide concentration in water source (WS) of Yancheng City in China increased unexpectedly due to industrial discharge and saltwater intrusion, which leads to the formation of trihalomethane (THMs) in finished water of water treatment plants (WTP), especially brominated THMs.

Risk associated with increasing bromide in drinking water sources in Yancheng City, China

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10.1016/j.watres.2019.114897

Field studies were conducted at seven full-scale DWDS to investigate the deposition and release behaviors of Mn in different forms and at different concentrations in finished water.

Field studies of manganese deposition and release in drinking water distribution systems: Insight into deposit control.

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What is/are Finished Water?

Finished Water - Efforts were made to determine the association between different fluorescence moieties in DOM of finished water and chlorine consumption through excitation-emission matrix coupled with parallel factor analysis (EEM-PARAFAC). [1] In order to know the water quality of rural water supply projects, the water samples are collected from finished water and tap water of administrative villages in some counties and districts of the Pearl River Basin for sampling inspection in 2019. [2] Two HBQs, 2,6-dichloro-1,4-benzoquinone (2,6-DCBQ) and 2,6-dibromo-1,4-benzoquinone (2,6-DBBQ), were detected in finished water and tap water in China. [3] After the treatments, there were still considerable QNs in the finished water (total amounts of 74. [4] In loop-structured DWDSs, finished water with different PFAS characteristics could mix along the pipeline, with the corresponding DWTP as the center, ultimately forming a relatively uniform distribution in the entire DWDS. [5] The turbidity removal by all AMCs obeyed with World Health Organization (WHO) acceptable limit of finished water, where HCl treated AMC clarified 15. [6] Haloacetonitriles (HANs) are widely used in finished water as unregulated disinfection by-products. [7] Meanwhile, health risk of exposure to organic micropollutants in finished water through three exposure routes (ingestion, dermal absorption and inhalation) was assessed with the method proposed by U. [8] Full-scale conventional treatment removed 52 % of anthropogenic particles when comparing raw (42 ± 18 particles/L) and finished water (20 ± 8 particles/L). [9] The concentration of TOC in finished water was 0. [10] Regrowth potential evaluated by indigenous microbial community in finished water was reduced to 22% of that in raw water, while 75% of assimilable organic carbon in raw water remained in finished water. [11] 3 ng L-1, whereas in finished waters significantly decreased to a range of [12] This proposed method was successfully applied to surface water, ground water, raw water, finished water, tap water, and bottled water samples. [13] The changes in eight metals (Al, Fe, Mn, Zn, Cu, Ba, Cr, and As) were investigated from the finished water (water treated by a drinking water treatment process before entering the distribution process) to the tap water of 10 water treatment plants in 5 cities of eastern China. [14] The results confirmed that different antibiotics including fluoroquinolones and B-lactams were detected in the raw and finished water. [15] Totally 24 of the 39 targeted PPCPs were detected in raw water, and 12 PPCPs were detected in the finished water. [16] Outcomes were linked with county-specific monthly estimates of the nitrate concentration in finished water, based on data collected for compliance with the Safe Drinking Water Standard. [17] ResultsThe O3–BAC–sand yielded lower turbidity but higher CODMn (by approximately 7%) in the finished water than regular O3–BAC (sand–O3–BAC). [18] The study aims to ensure that the finished water is safe to drink and meet the international drinking water regulations. [19] The performance of the method was checked along different strategic sampling points of three potabilization plants serving the city of Turin (Italy), including intermediate treatments and finished waters. [20] Drinking water treatment processes (DWTPs) impact pathogen colonization and microbial communities in finished water; however, their efficacies against opportunistic pathogens are not fully understood. [21] Therefore, it is of prime importance to design a simple and compact, yet robust, system for Mn and Fe control of the domestic GW sources, which can reliably guarantee the desired Mn limit in the finished water (20μg/L). [22] In addition, the occurrence of the aromatic DBPs in tap water and finished water was studied in a mega city Shenzhen located in South China. [23] By 2040, the public supply of raw and (or) finished water to meet demand for the 10 RCAs is projected to increase 48 percent to 532. [24] In this study, an investigation covering the odor characteristics, algal distribution and possible odorants contributing to swampy/septic odor, including dimethyl disulfide (DMDS), dimethyl trisulfide (DMTS), diisopropyl sulfide (DIPS), dipropyl sulfide (DPS), dibutyl sulfide (DBS), 2-methylisoborneol (2-MIB) and geosmin (GSM), was performed in source and finished water of 56 drinking water treatment plants (DWTPs) in 31 cities across China. [25] In this study we propose a procedure to evaluate the health risk related to turbidity in finished water by determining the cases of drinking water-related gastrointestinal diseases. [26] Incomplete removal of NDMA precursors by RO and the UV/advanced oxidation process (UV/AOP) led to NDMA formation in the finished water and miles downstream in the transmission pipelines. [27] 6) µg/L) were found in finished water of WTP1 and WTP2, respectively. [28] The results suggested that DBP concentrations of the finished water were higher in spring (82. [29] Additionally, a weekly sampling monitoring of 1,4-dioxane and alkyl-1,3-dioxanes and dioxolanes in raw water, groundwater and finished water was performed at a DWTP over more than two years. [30] Finally, we applied the WHO guideline and an empirical quantitative microbial risk assessment (QMRA) model to estimate probable health risk based on a residual number of rotavirus in finished water. [31] parvum oocysts were spiked into 10 l of source or finished water in triplicate followed by recovery using Envirochek HV sampling capsules. [32] The THMs in finished water and tap water of TH Waterworks were in the range 8. [33] We compared the finished water of two water treatment plants (WTP-A, WTP-B) serving Shanghai, China. [34] The infection risk and the burden of disease attributed to the parasite presence in finished water were estimated incorporating physical and chemical log reduction values (LRVs), using stochastic modeling and disinfection profiling. [35] Accepted concentrations for per- and polyfluoroalkyl substances (PFASs) in finished water are lower than ever before with new regulations often enacted based on findings made possible by improved analytical techniques and correspondingly justified health concerns. [36] 9 × 104 genes/mL) in finished water. [37] The occurrence and transformation behaviors of disinfection byproducts (DBPs) were investigated in the finished water and tap water of 14 water treatment plants in rural areas of eastern China. [38] Concentrations of THMs in finished water of study WTPs varied, ranging from 18. [39] The bromide concentration in water source (WS) of Yancheng City in China increased unexpectedly due to industrial discharge and saltwater intrusion, which leads to the formation of trihalomethane (THMs) in finished water of water treatment plants (WTP), especially brominated THMs. [40] Field studies were conducted at seven full-scale DWDS to investigate the deposition and release behaviors of Mn in different forms and at different concentrations in finished water. [41]

drinking water treatment

AOM affects the drinking water treatment processes and finished water quality. [1] Amino acids are ubiquitous as dissolved nitrogenous organic matter in source water and can pass through drinking water treatment processes to react with disinfectants in finished water and in the distribution system. [2] In this study, the data from this monitoring program were used to investigate the changes in six N-nitrosamine substances in the finished water of 33 drinking water treatment plants (DWTPs) in South Korea from 2013 to 2020, based on time and location. [3]

finished water sample

The occurrence of the most common NSAIDs (diclofenac, ibuprofen, naproxen, and ketoprofen) in river water, groundwater, finished water samples, WWTPs, and hospital wastewater effluents along with their toxicity effects were reviewed. [1] 5% of decanter biofilm, and 32% of finished water samples. [2] In this study, raw water samples (n=20), finished water samples (n=20), and tap water samples (n=165) originating from the Han River and the Yangtze River in Wuhan, Central China, were collected during 2018 for the determination of the NNI residues. [3] Forty-three pharmaceuticals were detected in finished water samples, with detection rates of 1. [4]

finished water quality

AOM affects the drinking water treatment processes and finished water quality. [1] Furthermore, the finished water quality indices of the Mopanshan Reservoir all could meet the “Standards for drinking water quality” (GB57492006), except for the chloral exceeding 20% of the limit after the conventional treatment. [2] Finished water quality from the DPR pilot was compared to drinking water standards, and emerging microbial and chemical contaminants were also evaluated. [3]