EVALUATION OF MAGNETIC NANO- ADSORBENTS FOR SELECTIVELY REMOVING METALS OF VALUE FROM REVERSE OSMOSIS REJECT STREAMS Leah V. Birgen and Dr. Jonathan Brant.

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Presentation transcript:

EVALUATION OF MAGNETIC NANO- ADSORBENTS FOR SELECTIVELY REMOVING METALS OF VALUE FROM REVERSE OSMOSIS REJECT STREAMS Leah V. Birgen and Dr. Jonathan Brant Department of Civil & Architectural Engineering

Overview  Introduction and background information  Coalbed Methane (CBM) produced water  Desalination Using Reverse Osmosis (RO)  Magnetic nanoparticles having tailored surface chemistries  Experimental Approach  Synthesis and modification of magnetic nano-adsorbents  Applications  Cost Benefit Analysis  Preliminary Conclusions  Future research directions

Introduction and Background

Coalbed Methane Produced Water Production: Produced during extraction of Coalbed Methane (CBM) Volumes: U.S. CBM production can generate between bgd A single CBM well can produce as much 3,500 gpd Powder River Basin produces as much as 100 mgd

Inorganic Constituents: Minerals Salts High TDS Organic Constituents: Oil and grease BTEX compounds phenols Produced Water, USSeawater Constituent Low, mg/L High, mg/L Low, mg/L High, mg/L Calcium (Ca 2+ )ND74, Magnesium (Mg 2+ )601301,4001,550 Sodium (Na + )ND150,00012,000 Sulfate (SO 4 2- )ND15,0002,4002,670 Bicarbonate (HCO 3 - ) ND15, ChlorideND250,00021,00023,000 TDS1,000400,00018,00048,000 (ND) Not Detected, (TDS) Total Dissolved Solids Coalbed Methane Produced Water

Composition: Potential constituents of value SourceLi μ g/L Mo μ g/L Sn μ g/L Ni μ g/L Cu μ g/L Constituent Average Market Value (February 2011) US$/gUS$/lb Li Mo Sn Ni Cu Possible Element Recovery?

Coalbed Methane Produced Water Disposal Options: Evaporation Ponds Deep well injection Land application Constructed wetlands Surface water discharge Treatment / Desalination Reverse Osmosis Mechanical evaporation Ion exchange

Reverse Osmosis (RO) Operation: High Pressure Membrane Process Removal by Differences in Diffusion Multi-Stage System Typically 2-3 stages (RO train)

Reverse Osmosis (RO) Challenges: Membrane Fouling (Ca 2+, Mg 2+, SO 4 2- ) Generation of Concentrated Waste Stream Where: C f = Concentration factor R f =Recovery factor

Useful Characteristics: nm particle diameter High surface area to volume ratio (specific surface area) Ability to tailor surface chemistry to selectively remove contaminants Can be removed with a magnet Magnetic Nanoparticles Particle Size, nm Specific Surface Area, m 2 /g Adsorption Capacity, mg As(III)/g Fe 3 O ,

Surface Coatings Desired Characteristics: Hydrophilic High Charge Density Selectivity for certain ions: Ca 2+, Mg 2+,SO 4 2-, Li + Nanoparticle usedCoating Constituent Removed/RecoveredReference Fe 3 O 4 (Magnetite) Humic Acid Mercury, Lead, Copper, Cadmium Liu et al Fe 3 O 4 (Magnetite) DMSAMercury Yantasee et al, 2007 Fe 3 O 4 (Magnetite) Chitosan Gold, Cobalt, Copper, Nickel, Lead Chang and Chen, 2005, Chang et al., 2006, Tran et al., 2010 Fe 3 O 4 (Magnetite) NTHPlatinum, Palladium Uheida et al., 2006 γ -Fe 2 O 3 (Maghemite) δ -FeOOH Chromium Hu et al., 2007 dimercaptosuccinic acid (DMSA), nonylthiourea (NTH), Feroxyhyte ( δ -FeOOH)

Research Objectives  Research potential magnetic nano-adsorbents:  Magnetite, Maghemite  Research potential surface coatings  Potentially removes desired dissolved ions from CBM produced water  Cost/Benefit Analysis  Potential value in recovering constituents from CBM produced water

Experimental Approach

Synthesis  Options:  Many options  Coprecipitation chosen Most common and least complicated Most economic and energy efficient  Procedure:  Coprecipitation of Fe 3+ and Fe 2+ ions to form magnetite  Oxidation to produce maghemite

Surface Coatings Potential Coatings: DMSA- dimercaptosuccinic acid EDTA- ethylenediaminetetraacetic acid Chitosan Based on selectivity of certain ions: Ca 2+, Mg 2+,SO 4 2-, Li + Magnetic Adsorbent: Magnetite, Maghemite Surface Coating: DMSA, EDTA, Chitosan

Applications Current Applications: Removal of toxins: Arsenic Chromium Mercury Lead Recovery of constituents of value: Gold Platinum Molybdenum Copper Nickel Nanoparticle used Constituent Removed (toxin) Constituent Recovered (value) Fe 3 O 4 (Magnetite) Arsenic, Chromium, Mercury, Lead Gold, Platinum, Copper, Nickel, γ -Fe 2 O 3 (Maghemite) Arsenic, Chromium Molybdenum

Applications Potential Applications:  Decrease surface fouling (due to scaling) of RO membranes Remove: Ca 2+, Mg 2+, SO 4 2-  Recover constituents of potential value from CBM produced water Recover: Lithium, Molybdenum, Tin, Nickel, Copper

Preliminary Conclusions

Results Original size: 106 nm Original composition: magnetite Measured size: 33 (peak 1) 156 (peak 2) 1521 (peak 3) Possible oxidation to maghemite

Results Constituent Average Concentration, WY ( μ g/L) Lithium (Li)2,220 Molybdenum (Mo)3 Tin (Sn)6 Nickel (Ni)66 Average CBM produced water generated in WY million gallons per day billion gallons per year

Results Assumptions: 100% recovery of constituent Conclusion: Potential value in recovering constituents from CBM produced water

Conclusions  Maghemite chosen over Magnetite  Further oxidation not a concern  Surface Coating  DMSA, EDTA, chitosan  Potential value in recovering constituents from CBM produced water  Lithium

Future Research  Synthesis and surface modification of Maghemite (magnetic nano-adsorbents)  Optimize size and stability of nanoparticles  Maximize theoretical adsorption capacity  Adsorption Tests  Measure adsorption capacity in fluidized reactor configuration  Evaluate regeneration of nano-adsorbents  Quantify recovery of dissolved metals as a function of RO recovery and solution chemistry

Leah V. Birgen Department of Civil & Architectural Engineering Questions?