Elsevier

Journal of Membrane Science

Volume 501, 1 March 2016, Pages 199-208
Journal of Membrane Science

Mass balance for a novel RO/FO hybrid system in seawater desalination

https://doi.org/10.1016/j.memsci.2015.11.047Get rights and content

Highlights

  • A novel hybrid reverse osmosis – forward osmosis (RO/FO) system was proposed.

  • Large and small scale seawater reverse osmosis plants have been considered.

  • Increased water recovery and reduced backwash sludge volume were calculated.

  • FO membrane area required and dilution in RO reject was estimated.

  • Small scale plants tend to show better performance with the hybrid system.

Abstract

Seawater Reverse Osmosis (SWRO) desalination is being used by several countries to aid the current demand for fresh water, hence numerous large scale and small scale desalination plants have been built during last decade. Despite major advancements in SWRO technology, the desalination industry is still facing significant practical issues. Two of the major issues are (1) generation of higher volumes of pre-treatment sludge, and (2) overall water recovery. This paper proposes a novel hybrid reverse osmosis (RO) – forward osmosis (FO) system to overcome the above two drawbacks. Mass balance calculations based on laboratory experiments have been used to predict increased water recovery and reduced pre-treatment sludge volume arising from large scale (340,000 m3/day of intake) and small scale (15,000 m3/day of intake) hybrid SWRO desalination plants. The percentage reduction of pre-treatment sludge volume, increase in overall RO water recovery, FO membrane area required and dilution in RO reject have been estimated.

Introduction

It is well-known that the demand for fresh water is increasing and its reserves are depleting. Desalination of seawater has come to aid the demand for fresh water. Desalination processes have evolved from multi-stage flash (MSF) and multi-effect distillation (MED) to reverse osmosis (RO). Approximately 40–50% of the seawater treated by reverse osmosis (SWRO) is converted in to fresh water [1], [2]. SWRO has three major draw backs: (i) high volumes of concentrate due to low water recovery, (ii) significant amounts of pre-treatment sludge that needs treatment and disposal and (iii) high energy consumption due to the use of high pressures to overcome the osmotic pressure of concentrated seawater [3], [4], [5], [6], [7]. Although the last draw back has been addressed well by the introduction of energy recovery devices [8], [9], the first two draw backs still need solutions. Application of forward osmosis (FO) may be able to provide a solution to those two draw backs.

A novel hybrid RO/FO system is proposed that will improve both water recovery and reduce the volume of pre-treatment sludge. In a typical pre-treatment sludge treatment process, clarified backwash sludge gets mechanically treated until the solids content meets the required landfill conditions. However, this process yields high operations and maintenance (O&M) costs [3]. Table 1 shows the O&M cost for a sludge treatment process where daily sludge generation is 275 m3/day. Transportation and disposal of sludge cost AUD 465 and AUD 1978/day, respectively, which is significantly high cost. Fig. 1 shows an existing treatment process (see System E in the Figure) for pre-treatment of sludge in a seawater desalination plant where a centrifuge increases the sludge solids content from 2–4% to 25% [3]). The final sludge solids content is an important factor to be considered when proposing a FO system for sludge dewatering, as solids contents similar to those currently achieved or higher are required. However, existing FO membranes are incapable of producing solids contents of up to 25%, so the FO system considered was to be installed between the clarifier and the centrifuge. The FO system increases the solids content to a designated extent following which the sludge is centrifuged until solids content reaches 25%. This solids content increment may reduce the power requirement [10], as the FO system uses comparatively less energy to function and maintain than a centrifuge. FO system consumes merely 17.3 kW h/day of power to increase sludge content from 3% to 10% (see supplementary material). Further, the volume of filtrate from the centrifuge that is known as centrate will be reduced, which generally needs treatment before discharge.

Three options of RO/FO hybrid system, detailed in Section 2, are considered and mass balance calculations are applied in order to evaluate the feasibility of those systems.

Section snippets

Option 1

In addition to an existing 2 stage RO desalination process, a FO system is proposed to reduce the volume of pre-treatment sludge. This Option is suggested for the RO processes, where 2nd pass RO concentrate (significantly low in salt concentration since 2nd pass RO treats the permeate from the 1st pass) is used to backwash media filter. Fig. 2a shows the process flow diagram. An optimised proportion of 1st pass RO concentrate is used to draw water through FO as it has high concentration (hence

Mass balance

Several factors need to be considered while conducting the mass balance for a hybrid RO/FO system. It is essential to establish the water recovery of RO at various osmotic pressures of the feed, as the feed will be a mixture of pre-treated sea water and the diluted draw solution from the FO. Information on the amount of back wash water required for the pre-treatment process (generally sand filters) will help to decide how much of this volume could be reduced through the FO process. The above

Materials and method for FO experiments

Flat sheet CTA membranes were purchased from HTI, USA and Fe(OH)3 sludge (feed solution) was received from the Perth Seawater Desalination Plant (PSDP), Australia. Draw solution (RO reject) was prepared at laboratory scale following the SWRO process in Fig. 1. Spiral wound RO membranes with effective area of 0.32 m2 were used. Operating pressure and the frequency of the RO unit were 30 bar and 20 Hz, respectively. The concentrate was recirculated back to the feed until the electrical conductivity

FO experiments

Pre-treatment sludge solids content was 3.4% total solids (TS), as received. When diluted by 1:4, the solids content reduced to 0.6% TS. Fig. 3 shows the effect of solids content on the water flux, along with the solids content values. Significantly higher water flux was observed when EC of the feed solution was unadjusted, compared to constant EC feeds. Water flux of EC adjusted and constant EC samples were 6.1 and 8.0 LMH, respectively (at 1:4 dilution). Added EC controller increases the salt

Conclusions

Experiments and mathematical modelling suggest that proposed FO/RO hybrid systems are capable of reducing the volume of pre-treatment sludge. A draw to feed flow ratio of less than 4 for both scales would be the optimum ratio, with a membrane area of 900 m2 and 500 m2 for large and small scale plants, respectively. Table 4 shows the final volume reduction, increase in water recovery and final solids content of both large and small desalination plants considered. By increasing FO membrane area up

References (17)

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