continuous production of amine-derivative silica for carbon capture

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    The place of useful learning

    The University of Strathclyde is a charitable body, registered in Scotland, number SC015263

    ContinuousProduction of

    Amine

    Derivatives ofGreen Silica forCarbon Capture

    Abdul Wadood Sharif

    Supervisors:Dr. Ashleigh FletcherDr. Siddharth Patwardhan

    Sponsored by:The Carnegie Trust

    Interns@Strathclyde

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    Table of Contents

    Acknowledgments 2Abstract 31 Background on Carbon Dioxide 42 Current Technologies 43 Aims and Objectives 54 Theory 55 Analytical Methods for Characterisation 66 Experimental 67 Results & Discussion 88 Conclusion & Recommendations 119 References 1210 Reflective Report 13

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    Acknowledgments

    I would like to thank my supervisors, Dr. Ashleigh Fletcher and Dr. Siddharth Patwardhan for their help,

    advice and encouragement for the duration of the placement.

    I would also like to personally thank Dr. Thomas Yip for his assistance, input and demonstrations in the

    laboratory.

    I would like to express thanks to the University of Strathclyde and the members of chemical and

    process engineering department for this invaluable opportunity.

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    Abstract

    With carbon dioxide emissions and mitigation becoming a pressing legal issue for industry, new

    solutions to the otherwise costly, established method currently used must be investigated.

    Alternative solutions include zeolites, activated carbons and amine grafted silica. Although promising

    these suffer from distinct disadvantages: loss of CO2capacity with presence of moisture, low CO2/N2selectivity and long, toxic, costly production respectively.

    A new method for production of amine-functionalised silica has been investigated by the Patwardhan

    group at Strathclyde University. This technique is inspired by biological processes and is a green

    method: quick reaction completion employs ambient conditions (both temperature and pH) and uses

    environmentally-friendly reagents.

    The aims of this report were to optimise the batch process of production and then investigate different

    methods of continuous production of the amine-silica sorbent using a plug flow reactor with

    poly(allylamine hydrochloride) as the amine adsorbent. Following reaction, the products were

    centrifuged and washed with deionised water three times and then allowed to dry in an oven overnight.

    From the results the yields for both the batch and semi-batch process were found to be the highest.

    This was due to the accuracy of the pH achieved (7 0.05) and the extended reaction time during the

    first centrifuge. The yield was a little lower for the batch run with excess acid at the end as the excess

    acid prevents further aggregation and this indicated that longer times should be given for full

    aggregation. The lowest yield was found with flow runs mostly due to the lack of pH measurement due

    to the excess acid present.

    Intelligent gravimetric analysis results indicated that the presence of amine in the samples were crucial

    for CO2uptake.

    All samples exhibited peaks at 1055 1035 cm-1and 1545 1520 cm-1from FTIR analysis. The former

    represents the presence of Si-O-Si bonds while the latter indicates NH bonds. This implies that there is

    both silica and amine present in samples.

    Further work includes CHN analysis for nitrogen loading, BET for porosity and surface area analysis

    and further IGA for CO2uptake of flow samples.

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    1 Background on Carbon Dioxide

    Global climate change due to greenhouse gas emissions is one of the key issues faced by industry

    today. Although many greenhouse gases exist, such as methane, the most significant is carbon

    dioxide, due to its abundance. The most recent estimate for carbon dioxide emission is approximately

    530 million metric tons (2010) for the United Kingdom. [1]With the introduction of legislation (Climate

    Change Act 2008), the United Kingdoms target for 2050 is to reduce carbon emissions by 80% fromthe 1990 baseline (approximately 600 million metric tons). [2]

    2 Current Technologies

    2.1 Amine scrubbing

    Currently the most established and widely-used method of carbon capture is the process of amine

    scrubbing. During this process flue gas, which is generated from combustion of fossil fuels and

    contains mainly carbon dioxide, nitrogen and water, is passed up through an absorption column whilst

    a liquid amine is pumped to the top of the column and passed down. The amine absorbs the carbondioxide and must then be regenerated for further use.

    Figure 1Amine Scrubbing Diagram

    Although widely implemented, the process suffers from one main disadvantage. This process is

    expensive, costing approximately $50 per ton CO 2 removed or 30% of the power generated by a

    power plant.[3]This cost is associated with high energy required for regeneration of the amine at the

    reboiler stage and the power for pumping.

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    2.2 Emerging Solutions

    Table 1 Comparison of possible solutions for carbon capture

    Solution Advantages Disadvantages

    Zeolites[4] High Capacity (3-4 mmol/g) Performance suffers with moisture.

    Activated

    Carbons[5] High Capacity (8.59 mmol/g) Low CO2/N2 Selectivity (bad for flue

    gas)

    Amine

    Grafted

    Silica[6][7]

    High Capacity (Up to 7.9 mmol/g)

    Favourable repeatability cyclic

    tests.

    Low Regeneration temperatures.

    Quick uptake (~10 mins)

    Unfavourable reaction conditions:oHarsh pH

    oHigh temperatures

    oToxic materials

    oLong reaction times

    oMulti-step Process

    Above lists some emerging solutions to the issue of carbon capture, although more exist such as

    membranes[REF: Pennline] and metal organic frameworks [REF: mason].

    Highlighted is amine-grafted silica, which shows promising capabilities but suffers from complicated,

    toxic

    3 Aims and Objectives

    The main aims of this study were:

    1) Study of batch manufacture of bio-inspired silica materials (See section4.1)

    2) Optimisation of batch processes for process scale-up

    3) Study of flowing manufacture with different arrangements

    These objectives were met by a combination of synthetic processes and characterisation of products to

    ensure the composition and properties were unaltered by the processing conditions. Characterisation

    methods included product yield, FTIR analysis and IGA analysis (See Analytical Methods for

    Characterisation).

    4 Theory

    4.1 Bio-inspired Green Silica

    To combat the problems faced by amine-silica production the Patwardhan group have utilised a

    biologically inspired procedure.

    Using a biologically inspired component (amine), it is possible to imitate nature. Furthermore the

    method of production is green: it employs ambient conditions, non-toxic materials and relatively quick

    reaction time (5 minutes).

    The procedure involves reacting an amine and silica precursor together at neutral pH (pH=7) which can

    be achieved via a titration with 1M HCl acid. Aggregation is best promoted at this pH. Further additionof acid to a obtain pH 2 results in a situation akin to freezing of aggregation. This is due to the

    interactions between the amine and precursor being less favourable in extreme pH.

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    For a material to be a viable candidate for carbon capture, it must be readily scaled up with as few

    complications as possible. Production of amine-grafted silica is difficult to scale up due to extreme

    conditions, toxic materials, long reaction times and multi-step process. The advantages of the green

    process should allow for promising scalability for large production.

    4.2 PAH - Poly(allylamine hydrochloride)

    The amine used for investigation was poly(allylamine hydrochloride) or PAH with average molecular

    weight of 15000 g/mol.

    Figure 2 Molecular Structure of PAH

    PAH was used as the amine component since previous investigation performed by the group

    highlighted PAH as one of the most promising for carbon capture. [8]Additionally, further research into

    PAH indicated this amine gave the highest yield in solid produced via batch synthesis. [9]

    5 Analytical Methods for Characterisation

    5.1 Intelligent Gravimetric Analysis (IGA)

    By employing IGA it is possible to investigate the CO2adsorbed on to the material surface in mmol/g.

    The intelligent gravimetric analyser is capable of measuring uptake by exposing a known quantity of

    sample with CO2and then precisely measuring the weight difference. For the purposes of this study,

    the CO2was exposed at 100 mbar, the industrially relevant pressure.

    5.2 Fourier Transform Infrared Spectroscopy (FTIR) analysis

    FTIR analysis was used to determine whether Silica and Poly (allylamine Hydrochloride) was present

    in the samples generated. By obtaining an infrared spectrum of absorbance, peaks can be assigned toa fingerprint region from literature, this in turn indicates which bonds and hence molecules are present.

    6 Experimental

    6.1 Reagents used

    Sodium metasilicate (Na2SiO3.5H2O) and Sodium Hydroxide (NaOH) pellets (99% purity) were

    purchased from Fisher Scientific. The amine polymer poly (allylamine hydrochloride) with average

    molecular weight 15,000 g/mol and 1M hydrochloric acid were purchased from Sigma Aldrich.

    Deionised water was readily available.

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    6.2 Experimental procedure

    6.2.1 Batch Synthesis

    Sodium metasilicate and PAH was weighed out to obtain a 30 mM solution on a 50 ml (0.3182 g) basis

    and 1mg/ml (0.05 g) solution respectively. 25ml deionised water was added to the sodium metasilicate

    and 22.5 ml deionised water was added to the PAH.

    The solutions were mixed separately then added together and after 1 minute the pH was recorded

    every 30 seconds until 5 minutes had elapsed. As this time elapsed the remaining 2.5ml was added in

    the form of 1M HCl acid in aliquots, this volume was determined previously to ensure an end pH of 7

    was achieved (See section7.1). The solution was transferred to a vial for centrifugation at 8000rpm for

    15 minutes followed by washing with deionised water. This was repeated twice more and finally the

    remaining solid was oven dried at 85C overnight.

    6.2.2 Semi-Batch Synthesis (FL)

    Figure 3 System Diagram with flows of amine (blue), silica (yellow) and product (green)

    All masses weighed and volumetric additions for the batch synthesis were multiplied by four so as to

    obtain a total output of 200 ml. Sodium Hydroxide pellets were weighed out to obtain a 2M solution on

    a 50ml basis (4g).

    The vessels were connected to two peristaltic pumps running at 2ml/min each to emulate a plug flowreactor (PFR). The solutions were mixed together in 3mm i.d. silicone tubing which ensured a 5 minute

    residence time was maintained. The solution was collected in a vessel until 50ml was collected. The

    output from reactor was immediately transferred to another vessel and the same time was allowed to

    pass. This process was repeated twice more.

    After each 50ml solution had been collected the process of centrifugation as done in the batch process

    was immediately initiated followed by drying in oven at 85C overnight.

    Following the complete run (after 4x50ml volume collected), 50ml deionised water was added to the

    NaOH pellets and allowed to dissolve. The tubing was then purged with this NaOH solution, followed

    by 1 litre of deionised water for cleansing purposes.

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    6.2.3 Flow Synthesis (FLA)

    Similar to the fed batch synthesis however 1.3ml HCl acid was added to each collection vessel prior to

    solution collection.

    7 Results & Discussion

    7.1 Evaluation of Volumetric HCl Requirement

    Table 2 HCl added and pH for batch runs (50ml basis)

    Sample Reference HCl Acid Added (ml) pH

    PAH-7 2.49 6.99

    PAH-10 2.50 6.96

    PAH-14 2.50 7.02

    PAH-15 2.50 7.05PAH-17 2.50 6.97

    Average: 2.50

    Note: The PAH-7 run was considered an outlier once flow synthesis was attempted.

    From the above table it can be observed that the HCl added showed excellent repeatability. Although

    the pH varied slightly, the range was considered acceptable (pH 7 0.05). The small variation resulted

    in errors associated with initial weighing.

    7.2 Yields

    Table 3 Number of samples, average mass and yi eld for PAH-Silica

    Synthesis Method No. of Samples

    Generated

    Average Mass

    (mg)

    Yield (%)

    Batch 4 76 6 63 5

    Batch w/ Excess Acid 4 56 3 46 1Semi-batch 16 69 2 57 2

    Flow 16 21 1 17 1

    Considering the higher yields, the highest on average was observed for batch runs, this is expected as

    these runs had greatest adaptability of acid added and assurance that a pH as close to 7 as possible

    was realised. Furthermore the aggregation of solid occurred continued during the first centrifugation.

    The semi-batch process also resulted in a high yield due to the monitoring of pH during reaction and

    repeated runs allowed for pH near 7 to be attained. Furthermore the extended run time resulted ingreater residence time.

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    The batch excess acid resulted in a lower average yield than that of both methods that did not involve

    excess acid additions described above. This was most likely due to incomplete aggregation of solid.

    The flow run resulted in a considerably low yield. Similar to the batch excess acid run, aggregation was

    most likely incomplete at the time the solution came in contact with the excess acid. There was also no

    assurance of good mixing in the plug flow reactor at such low speeds.

    7.3 IGA Results

    Figure 4 CO2 Capacity for batch, semi-batch, calcined batch and bare silica

    Both batch and semi-batch samples resulted in a considerably high uptake.

    A calcined batch sample (had amine was removed via heating in the presence of air) and MCM-41, or

    bare silica, were both run with IGA. From the results it can be observed that the amine has a very

    crucial role to play in the adsorption of CO2.

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    7.4 Results: FT-IR analysis

    Figure 5 FTIR Spectrum for (a) PAH-Silica, (b) PAH and (c) Sodium metasilicate precursor

    FromFigure 3a) peaks at 1055-1035 indicate Si-O-Si bonds and hence silica. The peak between 1545

    1520 represents N-H bonds and this indicates that amine is present in generated samples.Figure 3b&Figure 3cthe aligned peaks are further proof of silica and amine presence.

    1055-1035

    1545-1520

    a)

    b)

    c)

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    8 Conclusion & Recommendations

    The batch system required a consistent volume of acid for titration (2.5ml) with slight variations in end

    pH, most likely due to errors in initial weighing.

    High average yields were observed for semi-batch (57%) and low average yield were obtained with the

    flow system (17%). The former was possible because of pH monitoring and extended residence timesand the latter suffered without these advantages.

    IGA results indicated that the amine played a crucial role in adsorption of CO 2.

    FTIR confirmed the presence of silica and amines in all samples generated.

    Improvements to be made are higher flow rates and inclusion of a static mixer to ensure good mixing

    within PFR for flow system.

    Further work that can be carried out is CHN-analysis for amine loading, BET for porosity and surface

    area and further IGA studies.

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    9 References

    [1] S. Choudrie, N. Passant, J. MacCarthy, UK Greenhouse Gas Inventory: National Statistics UserGuide (Ed.: D. O. E. a. C. Change), Oxfordshire, 2012.[2] Climate Change Act (2008), (Ed.: U. Government), The Stationary Office Limited, 2008.[3] M. Ramezan, Carbon Dioxide Capture from Existing Coal-fired Power Plants, NETL, 2006.

    [4] L. Wang, Z. Liu, P. Li, J. G. Yu, A. E. Rodrigues, Chemical Engineering Journal 2012, 197, 151-161.[5] M. Radosz, X. D. Hu, K. Krutkramelis, Y. Q. Shen, Industrial & Engineering ChemistryResearch 2008, 47(10), 3783-3794.[6] G. G. Qi, Y. B. Wang, L. Estevez, X. N. Duan, N. Anako, A. H. A. Park, W. Li, C. W. Jones, E.P. Giannelis, Energy & Environmental Science 2011, 4(2), 444-452.[7] W. J. Choi, J. B. Seo, S. Y. Jang, J. H. Jung, K. J. Oh, Journal of Environmental Sciences-China 2009, 21(7), 907-913.[8] D. Prentice, A study of amine activated silica adsorption capabilities & the parameters ofevaporation, University of Strathclyde, Glasgow, 2011.[9] C. Scott, Developing Novel Adsorbents for Carbon Capture Technologies, University ofStrathclyde, Glasgow, 2012.

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    10 Reflective Report

    10.1 PresentationsEvery fortnight the group was required to present at progress meeting to their supervisor (since I had

    two supervisors this resulted in a progress meeting each week). During these meetings we were

    required not only present our progress but also critically analyse others work and our own. It was alsoan opportunity to raise questions to others and offer help in some areas. This was particularly useful for

    my project as there were several people working on similar projects and others findings were often

    useful for my own work and vice-versa. During my placement I was able to improve on presentation

    skills and also ask relevant questions pertaining to the subject matter.

    10.2 ConferencesThroughout my placement, my supervisors would invite myself and others from their group to

    conferences. Through these conferences we were able to observe current research developments and

    efforts by companies in particular fields. By attending these conferences, the group was given the

    chance to see others work and showcase our own. Furthermore these conferences gave theopportunity for myself to network and discuss my project to others. This improved communication skills

    as when an individual was unfamiliar with the background and area of my research I had to show

    versatility in my explanation for them to understand what I was doing.

    10.3 Self-teachingInitially, I was very unfamiliar with many aspects of my project: alternative solutions, theory behind

    analytical methods, previous work etc. Although some guidance was given with regards to these, often

    I had to find published papers for myself via Web of Knowledge for educating myself with regards to

    these topics. For previous work done by the group I was given these papers to read through and learn

    what were the limitations and techniques often used to characterise the samples. This method oflearning was very satisfying and having relevant papers I was able to prepare for the technical report at

    an early stage.

    10.4 Innovative thinkingMany problems were faced for the duration of my placement, some of which have still not been

    overcome at the time of writing. One particular example is of the systematic failure of an expensive

    piece of equipment, known as FlowSyn. This was the continuous flow reactor which was anticipated to

    be used for all flow synthesis of material. By meeting with my supervisor and discussing the issue we

    came to the conclusion that we could use a set of pumps and tubing to obtain a make-shift reactor

    that could be used instead. These situations I consider one of the most crucial invaluable practicalexperiences I obtained. It allowed me to develop my problem solving skills unlike any coursework had

    done thus far.

    10.5 Overall ExperienceI found the placement to be highly enjoyable both from an educational and practical experience. My

    assumptions on what research life would pertain to were quickly proven wrong. I found the social

    aspect to be pleasant and helpful with group lunches and departmental barbeques organised. Although

    I hope to experience an industrial placement first, I would be interested in continuing research by

    pursuing a PhD.