A 13.3 MGD seawater RO desalination plant for Yanbu Industrial City

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A 13.3 MGD seawater RO desalination plant for Yanbu Industrial City

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  • Research Article
  • Cite Count Icon 4
  • 10.1016/0011-9164(87)90216-5
Seawater pretreatment by continuous sand filter for seawater RO (reverse osmosis) desalination plant
  • Dec 1, 1987
  • Desalination
  • S Kawana + 3 more

Seawater pretreatment by continuous sand filter for seawater RO (reverse osmosis) desalination plant

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  • 10.1016/j.rser.2012.09.022
Waste energy recovery in seawater reverse osmosis desalination plants. Part 1: Review
  • Nov 1, 2012
  • Renewable and Sustainable Energy Reviews
  • A.M.K El-Ghonemy

Waste energy recovery in seawater reverse osmosis desalination plants. Part 1: Review

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  • 10.1080/19443994.2014.940653
Influence of site-specific parameters on environmental impacts of desalination
  • Jul 18, 2014
  • Desalination and Water Treatment
  • Maedeh P Shahabi + 2 more

Influence of site-specific parameters on environmental impacts of desalination

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  • 10.1016/j.desal.2023.116827
A theoretical analysis on upgrading desalination plants with low-salt-rejection reverse osmosis
  • Jul 13, 2023
  • Desalination
  • Haoqi Zhao + 2 more

A theoretical analysis on upgrading desalination plants with low-salt-rejection reverse osmosis

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  • Cite Count Icon 120
  • 10.1016/s0376-7388(03)00217-5
Ion-exchange membrane electrodialytic salt production using brine discharged from a reverse osmosis seawater desalination plant
  • Aug 5, 2003
  • Journal of Membrane Science
  • Yoshinobu Tanaka + 3 more

Ion-exchange membrane electrodialytic salt production using brine discharged from a reverse osmosis seawater desalination plant

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  • Cite Count Icon 4
  • 10.4491/ksee.2019.41.7.389
Economic Assessment Based on Energy Consumption on the Capacities in Seawater Reverse Osmosis (SWRO) Plant in Korea
  • Jul 31, 2019
  • Journal of Korean Society of Environmental Engineers
  • Changkyoo Choi + 4 more

Objectives The production cost of reverse osmosis (RO) seawater desalination plant is determined by the CAPEX (Capital expenditure) and OPEX (Operating expenditure). In detail, CAPEX and OPEX are composed of direct cost, overhead cost, electricity cost, and other O&M costs. However, CAPEX and OPEX may vary by country and region. Therefore, this study tries to estimate the production cost by calculating the construction and maintenance costs depending on production capacities based on the operation results such as TDS concentration and the energy consumption from a seawater desalination plant in Korea. Methods A two-stage RO based seawater desalination plant with a capacity of 10 MIGD (45,000 m3/d) was used in this study. The plant consists of a 2 MIGD (9,000 m3/d) unit having DABF (Dissolved air bio-ball filter) and UF (Ultrafiltration) as pretreatment processes, and another 8 MIGD (36,000 m3/d) unit having DABF and DMF (Dual media filtration) as pretreatment processes. To estimate the production cost, construction and maintenance costs were calculated by using GWI's Desaldata cost estimator. CAPEX (Capital expenditure) was calculated based on production capacity, recovery rate, TDS concentration and temperature of seawater, while OPEX (Operating expenditure) was calculated based on production capacity, country, energy consumption, and electricity unit price. Results and Discussion The energy consumptions from EMS (Energy Management System) were 5.48 kWh/m3 at SLC (9,000 m3/d) and 3.4 kWh/m3 at MLC (45,000 m3/d), respectively. In the CAPEX, MLC was reduced by 395,954 ₩/m3 compared to SLC, and the LLC was lower by 192,019 ₩/m3 than MLC. Overall, CAPEX decreased as the production capacity increased. The CAPEX of small plants with production capacity between 10,000 and 50,000 m3/d was significantly different; however, there was no significant difference in larger plants having a capacity above 100,000 m3/d. The OPEX for the annual production capacity showed a sizable difference with 742.3 ₩/m3, 636.5 ₩/m3 and 580.3 ₩/m3 for SLC, MLC, and LLC, respectively. The electricity cost was a substantial portion of OPEX. Also, the production costs based on the interest rates (3% and 5%) were 1,326-1,384 ₩/m3, 1,163-1,209 ₩/m3, and 1,023-1,070 ₩/m3 for SLC, MLC, and LLC, respectively. The results were consistent with 1.0 US$/m3, which is the average production costs presented from other references. Conclusions The production cost estimated using the Desaldata cost estimator based on the CAPEX and OPEX tends to decrease as the capacity increases. However, when the capacity increased over 50,000 m3/d, the production cost decreased by an average of 40 ₩/m3. Thus the decrement of production cost reduced. From these results, the production cost of tap water through seawater desalination was estimated between 1,023 ₩/m3 and 1,070 ₩/m3 above 100,000 m3/d. Therefore, it is difficult to introduce a large-scale desalination plant in Korea, because the average tap water price was 834.6 ₩ in Korea in 2017. However, It is expected that the seawater desalination will be introduced as an alternative water source whenever drinking water price rises, or when the quantity of available drinking water sources reduce due to climate change and water pollution, or whenever energy consumption is reduced as a result of the steady development of the component technologies such as the reverse osmosis membrane, high-pressure pump, and energy recovery device. Key words: Reverse osmosis seawater desalination plant, Water price, Capital expenditure, Operating expenditure, Energy consumption

  • Research Article
  • Cite Count Icon 9
  • 10.1007/s11814-014-0356-0
Evaluation of multivariate statistical analyses for monitoring and prediction of processes in an seawater reverse osmosis desalination plant
  • Mar 17, 2015
  • Korean Journal of Chemical Engineering
  • Srinivas Sahan Kolluri + 3 more

Our aim was to analyze, monitor, and predict the outcomes of processes in a full-scale seawater reverse osmosis (SWRO) desalination plant using multivariate statistical techniques. Multivariate analysis of variance (MANOVA) was used to investigate the performance and efficiencies of two SWRO processes, namely, pore controllable fiber filter-reverse osmosis (PCF-SWRO) and sand filtration-ultra filtration-reverse osmosis (SF-UF-SWRO). Principal component analysis (PCA) was applied to monitor the two SWRO processes. PCA monitoring revealed that the SF-UF-SWRO process could be analyzed reliably with a low number of outliers and disturbances. Partial least squares (PLS) analysis was then conducted to predict which of the seven input parameters of feed flow rate, PCF/SF-UF filtrate flow rate, temperature of feed water, turbidity feed, pH, reverse osmosis (RO)flow rate, and pressure had a significant effect on the outcome variables of permeate flow rate and concentration. Root mean squared errors (RMSEs) of the PLS models for permeate flow rates were 31.5 and 28.6 for the PCF-SWRO process and SF-UF-SWRO process, respectively, while RMSEs of permeate concentrations were 350.44 and 289.4, respectively. These results indicate that the SF-UF-SWRO process can be modeled more accurately than the PCF-SWRO process, because the RMSE values of permeate flowrate and concentration obtained using a PLS regression model of the SF-UF-SWRO process were lower than those obtained for the PCF-SWRO process.

  • Research Article
  • Cite Count Icon 88
  • 10.1016/j.renene.2013.11.050
Environmental life cycle assessment of seawater reverse osmosis desalination plant powered by renewable energy
  • Dec 8, 2013
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  • Maedeh P Shahabi + 3 more

Environmental life cycle assessment of seawater reverse osmosis desalination plant powered by renewable energy

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Artificial neural network model for optimizing operation of a seawater reverse osmosis desalination plant
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Artificial neural network model for optimizing operation of a seawater reverse osmosis desalination plant

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  • 10.1016/j.desal.2007.02.049
SWRO process simulator
  • Jan 19, 2008
  • Desalination
  • Richard L Stover

SWRO process simulator

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