Fertilizer drawn forward osmosis as an alternative to 2nd pass seawater reverse osmosis: Estimation of boron removal and energy consumption

Hailan Wang , Baoyu Gao , Li’an Hou , Ho Kyong Shon , Qinyan Yue , Zhining Wang

Front. Environ. Sci. Eng. ›› 2021, Vol. 15 ›› Issue (6) : 135

PDF (2120KB)
Front. Environ. Sci. Eng. ›› 2021, Vol. 15 ›› Issue (6) : 135 DOI: 10.1007/s11783-021-1428-0
RESEARCH ARTICLE
RESEARCH ARTICLE

Fertilizer drawn forward osmosis as an alternative to 2nd pass seawater reverse osmosis: Estimation of boron removal and energy consumption

Author information +
History +
PDF (2120KB)

Abstract

• The boron concentration in diluted DS can satisfy the irrigation water standard.

• The boron concentration in diluted DS equaled that in two-pass RO permeate.

• FDFO process SEC was slightly lower than the 2nd pass RO SEC.

• FDFO has potential as an alternative to 2nd pass RO for irrigation water production.

Agriculture is the largest consumer of freshwater. Desalinated seawater is an important alternative water source for sustainable irrigation. However, some issues of the current desalination technology hinder its use for agriculture irrigation, including low boron removal and high energy consumption. This study systematically explored the feasibility of employing fertilizer drawn forward osmosis (FDFO) as an alternative to 2nd pass reverse osmosis (RO) by considering the boron removal performance and specific energy consumption (SEC). Different operating conditions were investigated, such as the boron and NaCl concentrations in feed solution (FS), draw solution (DS) concentration, pH, the volume ratio of FS to DS, membrane orientation, flow rate, and operating temperature. The results indicated that a low boron concentration in FS and high pH DS (pH= 11.0) decreased the boron solute flux, and led to low final boron concentration in the DS. The other operating conditions had negligible influence on the final DS boron concentration. Also, a lower flow rate and higher specific water flux with certain permeate water volumes were conducive to reducing the SEC of the FDFO process. Overall, our study paves a new way of using FDFO in irrigation, which avoids the phytotoxicity and human health risk of boron. The results show the potential of FDFO as an alternative to 2nd pass RO for irrigation water production.

Graphical abstract

Keywords

Fertilizer drawn forward osmosis (FDFO) / Boron removal / Specific energy consumption (SEC) / Seawater reverse osmosis (SWRO) / Irrigation water production

Cite this article

Download citation ▾
Hailan Wang, Baoyu Gao, Li’an Hou, Ho Kyong Shon, Qinyan Yue, Zhining Wang. Fertilizer drawn forward osmosis as an alternative to 2nd pass seawater reverse osmosis: Estimation of boron removal and energy consumption. Front. Environ. Sci. Eng., 2021, 15(6): 135 DOI:10.1007/s11783-021-1428-0

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Ban S, Im S, Cho J, Jang A (2019). Comparative performance of FO-RO hybrid and two-pass SWRO desalination processes: Boron removal. Desalination, 471: 114114

[2]

Bhojwani S, Topolski K, Mukherjee R, Sengupta D, El-Halwagi M M (2019). Technology review and data analysis for cost assessment of water treatment systems. Science of the Total Environment, 651(2): 2749–2761

[3]

Chekli L, Kim Y, Phuntsho S, Li S, Ghaffour N, Leiknes T, Shon H K (2017). Evaluation of fertilizer-drawn forward osmosis for sustainable agriculture and water reuse in arid regions. Journal of Environmental Management, 187: 137–145

[4]

Chung H J, Kim J, Kim D I, Gwak G, Hong S (2020). Feasibility study of reverse osmosis-flow capacitive deionization (RO-FCDI) for energy-efficient desalination using seawater as the flow-electrode aqueous electrolyte. Desalination, 479: 114326

[5]

Du Y, Liu Y, Zhang S, Xu Y (2016). Optimization of seawater reverse osmosis desalination networks with permeate split design considering boron removal. Industrial & Engineering Chemistry Research, 55(50): 12860–12879

[6]

Fam W, Phuntsho S, Lee J H, Cho J, Shon H K (2014). Boron transport through polyamide-based thin film composite forward osmosis membranes. Desalination, 340: 11–17

[7]

Farhat A, Ahmad F, Hilal N, Arafat H A (2013). Boron removal in new generation reverse osmosis (RO) membranes using two-pass RO without pH adjustment. Desalination, 310(SI): 50–59

[8]

Gulied M, Al Nouss A, Khraisheh M, AlMomani F (2020). Modeling and simulation of fertilizer drawn forward osmosis process using Aspen Plus-MATLAB model. Science of the Total Environment, 700: UNSP 134461

[9]

Hawari A H, Kamal N, Altaee A (2016). Combined influence of temperature and flow rate of feeds on the performance of forward osmosis. Desalination, 398: 98–105

[10]

Jones E, Qadir M, van Vliet M T H, Smakhtin V, Kang S (2019). The state of desalination and brine production: A global outlook. Science of the Total Environment, 657: 1343–1356

[11]

Kayaci S, Tantekin-Ersolmaz S B, Ahunbay M G, Krantz W B (2020). Technical and economic feasibility of the concurrent desalination and boron removal (CDBR) process. Desalination, 486: 114474

[12]

Kim C, Lee S, Shon H K, Elimelech M, Hong S (2012). Boron transport in forward osmosis: Measurements, mechanisms, and comparison with reverse osmosis. Journal of Membrane Science, 419: 42–48

[13]

Kim Y, Woo Y C, Phuntsho S, Nghiem L D, Shon H K, Hong S (2017). Evaluation of fertilizer-drawn forward osmosis for coal seam gas reverse osmosis brine treatment and sustainable agricultural reuse. Journal of Membrane Science, 537: 22–31

[14]

Lambrechts R, Sheldon M S (2019). Performance and energy consumption evaluation of a fertiliser drawn forward osmosis (FDFO) system for water recovery from brackish water. Desalination, 456: 64–73

[15]

Li M, Li K, Wang L, Zhang X (2020). Feasibility of concentrating textile wastewater using a hybrid forward osmosis-membrane distillation (FO-MD) process: Performance and economic evaluation. Water Research, 172: 115488

[16]

MWRC (Ministry of Water Resources China) (2018). China National Water Bulletin. Beijing: Ministry of Water Resources China (in Chinese)

[17]

Park K, Kim J, Yang D R, Hong S (2020). Towards a low-energy seawater reverse osmosis desalination plant: A review and theoretical analysis for future directions. Journal of Membrane Science, 595:

[18]

Patel S K, Ritt C L, Deshmukh A, Wang Z, Qin M, Epsztein R, Elimelech M (2020). The relative insignificance of advanced materials in enhancing the energy efficiency of desalination technologies. Energy & Environmental Science, 13:

[19]

Phuntsho S, Hong S, Elimelech M, Shon H K (2013). Forward osmosis desalination of brackish groundwater: Meeting water quality requirements for fertigation by integrating nanofiltration. Journal of Membrane Science, 436: 1–15

[20]

Phuntsho S, Kim J E, Johir M A H, Hong S, Li Z, Ghaffour N, Leiknes T, Shon H K (2016). Fertiliser drawn forward osmosis process: Pilot-scale desalination of mine impaired water for fertigation. Journal of Membrane Science, 508: 22–31

[21]

Phuntsho S, Lotfi F, Hong S, Shaffer D L, Elimelech M, Shon H K (2014). Membrane scaling and flux decline during fertiliser-drawn forward osmosis desalination of brackish groundwater. Water Research, 57: 172–182

[22]

Phuntsho S, Shon H K, Hong S, Lee S, Vigneswaran S (2011). A novel low energy fertilizer driven forward osmosis desalination for direct fertigation: Evaluating the performance of fertilizer draw solutions. Journal of Membrane Science, 375(1–2): 172–181

[23]

Phuntsho S, Shon H K, Hong S, Lee S, Vigneswaran S, Kandasamy J (2012). Fertiliser drawn forward osmosis desalination: the concept, performance and limitations for fertigation. Reviews in Environmental Science and Biotechnology, 11(2SI): 147–168

[24]

Qiu G, Wong G K W, Ting Y (2020). Electrostatic interaction governed solute transport in forward osmosis. Water Research, 173: 115590

[25]

Suwaileh W, Johnson D, Hilal N (2020). Membrane desalination and water re-use for agriculture: State of the art and future outlook. Desalination, 491: 114559

[26]

Tang C Y, She Q, Lay W C L, Wang R, Fane A G (2010). Coupled effects of internal concentration polarization and fouling on flux behavior of forward osmosis membranes during humic acid filtration. Journal of Membrane Science, 354(1–2): 123–133

[27]

Tang Y P, Luo L, Thong Z, Chung T S (2017). Recent advances in membrane materials and technologies for boron removal. Journal of Membrane Science, 541: 434–446

[28]

Thi P N N, Jun B, Park H G, Han S, Kim Y, Lee H K, Kwon Y (2016). Concentration polarization effect and preferable membrane configuration at pressure-retarded osmosis operation. Desalination, 389: 58–67

[29]

UNESCO (United Nations Educational, Scientific and Cultural Organization) (2019). The United Nations World Water Development Report 2019. Paris: United Nations Educational, Scientific and Cultural Organization World Water Assessment Programme (WWAP)

[30]

Voutchkov N (2018). Energy use for membrane seawater desalination: Current status and trends. Desalination, 431(SI): 2–14

[31]

Wang C, Gao B, Zhao P, Li R, Yue Q, Shon H K (2017a). Exploration of polyepoxysuccinic acid as a novel draw solution in the forward osmosis process. RSC Advances, 7(49): 30687–30698

[32]

Wang Y, Li W, Wang R, Tang C Y (2017b). Enhancing boron rejection in FO using alkaline draw solutions. Water Research, 118: 20–25

[33]

Yang S, Gao B, Jang A, Shon H K, Yue Q (2019). Municipal wastewater treatment by forward osmosis using seawater concentrate as draw solution. Chemosphere, 237: 124485

[34]

Zheng L, Price W E, McDonald J, Khan S J, Fujioka T, Nghiem L D (2019). New insights into the relationship between draw solution chemistry and trace organic rejection by forward osmosis. Journal of Membrane Science, 587: UNSP 117184

RIGHTS & PERMISSIONS

Higher Education Press

AI Summary AI Mindmap
PDF (2120KB)

Supplementary files

FSE-21022-OF-WHL_suppl_1

3044

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/