Pratik Desai AMIChemE AMInstP GradEI Professor William B S - - PowerPoint PPT Presentation

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Pratik Desai AMIChemE AMInstP GradEI Professor William B S - - PowerPoint PPT Presentation

Hot Microbubble Injection in Thin Liquid Layers for Ammonia Water Separations Pratik Desai AMIChemE AMInstP GradEI Professor William B S Zimmerman BSc PhD Problem Description S Ammonia in Leachate is an environmental hazard - Lowering


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S Hot Microbubble Injection in Thin Liquid Layers for Ammonia – Water Separations

Pratik Desai AMIChemE AMInstP GradEI Professor William B Zimmerman BSc PhD

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Problem Description

S Ammonia in Leachate is an environmental hazard - Lowering

Ecotoxicity - Requires High Cost for Ammonia Removal! EQS = 0.39 mg/l, landfill conc. = 50-3000 mg/l

S Ammonia Production (Haber-Bosch) is energy intensive -High

Pressure , Low Temperature

S 2 % of world’s energy used for ammonia production , 0.5% used for

remediation. Ammonia used for several products – fertilisers, adjuvants, fuels, explosives, high value chemicals

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Proposed Solution

Tackle problem in two steps Design new microbubble unit operation – Microbubble Stripping Lower leachate ecotoxicity by ammonia recovery & try to sell ammonia either as a pure product or upgrade it and sell it as a more valuable chemical via Desai-Zimmerman MMARP

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Research Interest - Publications

Increase in publication on ammonia removal from landfill leachate. Source: Scopus

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  • 1. Identification of key performance indicators

S Processing Time designated as Indicator (Efficiency as well) S Variables decided – Benchmarking to be performed once

results are obtained

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Microbubbles (Mb) > 1µm <1000 µm >HX & MX for smaller bubbles ( >> SA/V ratio) Microbubble Generation - requires surface energy

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Fluidic Oscillator

No-moving part bi-stable diverter valve – Several benefits

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Fluidic Oscillation Reduces Bubble Size

Steady Flow Bubble Formation Oscillatory Bubble Formation

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Block Diagram

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Hypothesis - Basis

Temperature gradient (Ethanol-Water) Concentration gradient (Ammonia-Water)

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identification of operational parameters

Ammonia -Water used for identifying operational parameters Selected as main performance together with efficiency – Shorter the processing time, greater is the throughput possibility!

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Experimental Design

S Factorial Design of Experiment

Runs determined by the interaction between the different effects and therefore lot more information obtained from the same set of data obtained differently!

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Set up Schematic

FC PC TI FI TI

AIR INLET FLUIDIC OSCILLATOR DIFFUSER BLEED VALVES ELECTRIC HEATER MICROBUBBLE GENERATION (HXRig)

TI TI TC TI

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S Sintered Steel Sparger –

S Inexpensive S Bespoke design based on calculations S Material Selection – Sintered SS – Durable , easy

to manufacture, possibility to make it really thin – 100 m μ

S Low pressure drop- 20 mbar – Calculations from

Holdich et al ,2006 – maintained by larger orifice – 100-150 m , greater porosity & thinner sparger μ

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Key Results - Ammonia - Water

S Very effective separation observed for Ammonia Water! S Operational conditions identified for leachate

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Possibly reduced need for Caustic!

Removal at pH < 9 still achieved. NH3 + H2O NH4+ + OH- ↔ Bubbles are vapourising water and driving equilibrium towards ammonia generation

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What happens to Mass Transfer Coefficients ?

S KD is on the 101 magnitude. S Srinath and Loehr (1974) report KD on the 10-3

magnitude; Smith and Arab (1988) between 10-3 and 10-2.

1000 times greater mass transfer!

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  • 2. Do Hot Microbubbles mediated by FO work for

Ammonia Removal in Leachate ?

YES!

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Three modes of operations

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Where we are compared to

  • thers?

Cheung et al. (1997) Cheung et al. (1997) Cheung et al. (1997) Kabdasli et al. (2000) Marttinen et al. (2002) Marttinen et al. (2002) Silva et al. (2004) Collivignarelli et al. (1998) 20 40 60 80 100 0.1 1 10 100 1000 Stripping efficiency (%) Processing time (h) Stripping Adsorption Chemical precipitation Oxidation

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Latest modifications

15,000 times for some ammonia rich liquors!

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MMARP – Waste Factory

Pratik D Desai Professor William B J Zimmerman

Microbubble Mediated Ammonia Recovery Processes

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Desai-Zimmerman MMARP

Leachate

Ammonia Removal, COD/BOD Reduction, Heavy Metal Ion Densi ication and Increase in Optical Transparency Removal of Heavy Metal Ions & Need for BOD/ COD, Lipid Production

Micro lotation

Separation of MAC & Recovery of Metals, Sewering the remnant off.

Flue Gas enriched using FO mineral carbonation/ Ammonia Mb Intervention 1 – Preprocessing Mb Intervention 2 – Increased Growth Rate Mb Intervention 4 – Algal flotation and separation Ammonia converted to other products –

  • 1. Pall Knorr Synthesis - Grantham Scholar co-supervised

by WBJZ and PD – High Value product

  • 2. Conversion to Tuneable salts- IIKE2 Scale up – Energy

Cat

  • 3. Used as fertilizer via microbubble condenser (Project

running)

  • 4. Upgraded via plasma microreactor(depends on today)
  • 5. Used as a source for MAC growth by in situ urea

conversion – Patent pending – work proceeding from IIKE 1 and IIKE 2 Mb Intervention 3 – Microbubble condenser Lipid rich MACs to be used for energy recovery Biomass used for AD – Energy plus CHP – Energy Catalyst

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What happens to the recovered Ammonia?

We can make Carbamate at RT and Atm P without catalyst. 50% Ratio but tuneable – Carbamate and Carbonate. 70% conversion per pass.

+ NH3 (aq) Optimise to select for mono- di- tri-ethanolamines Scheme 2 O H2N OH HN OH 2 N OH 3 O HO + NH3 (aq) HO NH2 OH High value chiral intermediates

R1 O R2 O + NH3 (aq) N H R2 R1 Stable aromatic products Relatively poor aqueous solubility Scheme 1

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Microbubble Anaerobic Digestion fit into MMARP

S CO2 injection can cause 110% (unoptimised) increase in

production rate for biogas ( untreated wet foodwaste)

S We can sustainably recover ammonia from ammonia rich

liquor.

S We can generate tuneable salts of carbamate and carbonate

at RT/AtmP and this is exothermic and this can sequester CO2

S Combining these concepts together, we have a sweetening

process and a reduced CAPEX ,increased payback AD with process integration

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Innovate UK Energy Catalyst Perlemax and University of Sheffield

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Recapitulation

S Hot microbubbles can achieve up to 97% efficiency in 30

minutes for a broad range of concentrations – up to 25% greater and in 98% less time than industry

S Cold microbubbles yield a MTC 1000 times greater than

conventional stripping. 3000 times for hot microbubbles and 15000 times for certain liquors

S Adding alkali increased efficiency by up to 105 % BUT…

Stripping at pH> 9.0 can be achieved with hot microbubbles

S Microbubbles can influence chemical equilibria to generate and

strip ammonia

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MMARP

S Hot microbubble mediated ammonia recovery – in talks

with large waste management company

S Microbial algal consortia – 1. IIKE award for PoC , NERC

award for pilot scale, 2.Grantham Scholar supervision

S Tunable salts of Ammonium Carbonate/Carbamate – 50%

generation of each salt , 70% conversion per pass for POC. Pilot scale- Energy Catalyst

S Working on larger scale implementation of MMARP-

‘Waste Factory’ led by me.

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Thanks

Any Questions ?