Microwave-assisted and conventional hydrothermal carbonization of lignocellulosic waste material: Comparison of the chemical and structural properties of the hydrochars

Microwave-assisted and conventional hydrothermal carbonization of lignocellulosic waste material: Comparison of the chemical and structural properties of the hydrochars

Accepted Manuscript Title: Microwave-assisted and conventional hydrothermal carbonization of lignocellulosic waste material: Comparison of the chemica...

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Accepted Manuscript Title: Microwave-assisted and conventional hydrothermal carbonization of lignocellulosic waste material: Comparison of the chemical and structural properties of the hydrochars Author: Sunday E. Elaigwu Gillian M. Greenway PII: DOI: Reference:

S0165-2370(15)30098-X http://dx.doi.org/doi:10.1016/j.jaap.2015.12.013 JAAP 3630

To appear in:

J. Anal. Appl. Pyrolysis

Received date: Accepted date:

30-7-2015 5-12-2015

Please cite this article as: Sunday E.Elaigwu, Gillian M.Greenway, Microwaveassisted and conventional hydrothermal carbonization of lignocellulosic waste material: Comparison of the chemical and structural properties of the hydrochars, Journal of Analytical and Applied Pyrolysis http://dx.doi.org/10.1016/j.jaap.2015.12.013 This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.

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Microwave-assisted and conventional hydrothermal carbonization of lignocellulosic

2

waste material: Comparison of the chemical and structural properties of the

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hydrochars

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Sunday E. Elaigwua,b*, Gillian M. Greenway a

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a

6

b

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Corresponding author. Tel. +44 7733680543; fax: +44 1482466410

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Email addresses: [email protected], [email protected]

Department of Chemistry, University of Hull, Cottingham Road, Hull, HU6 7RX, UK Department of Chemistry, University of Ilorin, PMB 1515, Ilorin, Kwara State, Nigeria

9 10

Abstract

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This study compares the chemical and structural properties of the hydrochars prepared

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from microwave-assisted and conventional hydrothermal carbonizations of Prosopis

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africana shell, a waste plant material. The preparation involved heating the raw material

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in de-ionized water at 200 °C for 5-20 min, and 120-240 min in the microwave and

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conventional oven respectively. The prepared hydrochars were characterized using the

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scanning electron microscope, nitrogen sorption measurement, Fourier transform infrared

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spectroscopy, CHN analyzer, thermogravimetric analysis, and nuclear magnetic

18

resonance. The results showed that the microwave-assisted hydrothermal carbonization

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process is fast in the carbonization of the Prosopis africana shell as shown by the level of

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conversion attained within the short time. This study presents new data on the

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comparison of the hydrochars from microwave-assisted and conventional hydrothermal

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carbonization processes of the same lignocellulosic material in terms of their properties.

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Keywords: Microwave, hydrothermal carbonization, carbonized material, Prosopis africana shell

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1. Introduction

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Various methods exist for the preparation of carbonaceous materials from waste

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biomasses, with the aim of managing, sequestering carbon, and converting the waste

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materials into useful products that can find application in the environment, separation

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science, catalysis, and as electrode material [1]. One of such methods is the

1

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environmentally friendly hydrothermal carbonization process, which involves the heating

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of biomass under pressure in water at about 180-200 °C to form char called hydrochar,

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and water-soluble organic substances [2,3]. Thus, in the hydrothermal carbonization

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process the stored energy in the biomass is used more efficiently. It is an important

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process because water acts as both the reagent and reactive environment, and it has been

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applied in the synthesis of different types of carbonaceous materials [4].

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Microwave technology has been shown to be more energy efficient than

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conventional methods of heating in many applications, because it provides selective, fast

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and homogenous heating, which reduces processing time and costs significantly [5,6]. As

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such it can be an attractive alternative to the conventional method of hydrothermal

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carbonization of waste materials. Hydrothermal carbonization process was first reported

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in 1913 by Bergius and Specht [7], and has been proven to be a promising and a

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sustainable waste management method. The ultimate goal of the process is to convert

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waste materials into value-added products, while promoting the integration of the carbon

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formed in the solid-phase. Several other researches have been carried out over the years

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using conventional and microwave heating to produce valuable products, from different

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kinds of materials, for various applications [8-17]. Despite all these studies, a direct

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comparison of the solid product (hydrochar) obtained from the microwave-assisted and

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conventional hydrothermal carbonization methods of the same lignocellulosic material

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has not been reported to the best of our knowledge. Therefore, in this study we made

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comparisons between the hydrochars prepared from a waste plant material (Prosopis

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africana shell) using these methods, with focus on the similarities between the structural

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and chemical properties of the hydrochars, in order to provide useful information about

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the microwave-assisted and conventional oven hydrothermal carbonization processes.

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The Prosopis africana (Mimosaceae) used in this study is a multi-purpose tree of

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great economic value among the rural communities in Nigeria. The shell is one of the

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widely available waste products obtained from it numerous uses. Detailed information on

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the Prosopis africana can be found elsewhere [18].

2

58 59 60

2. Materials and Methods The Prosopis africana shell was collected in Benue State, Nigeria. It was crushed and sieved to 2 mm size and stored for use in the preparation of the hydrochars.

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It is important to state that this study was restricted to 200 °C for safety reason

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based on previous report by Titirici et al., [1] that temperatures below 180 °C produces

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only weak or no conversions for cellulose containing materials; while temperatures

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exceeding 220 °C could cause a runaway of the reaction, and hydrothermal reactions at

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250 °C tend to generate too much heat and pressure, which could burst the safety plate of

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the autoclave.

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2.1 Preparation of the hydrochars

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2.1.1 Microwave-assisted hydrothermal carbonization

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This experiment was conducted in a 2.45 GHz, and 1600 W microwave oven

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(MARS, CEM, Milton Keynes, UK equipped with XP1500 digestion vessels). The

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reaction temperature was monitored with an infrared fibre optic sensor fitted into the

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ceramic sleeve of the reference vessel, while the reaction pressure was monitored with a

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pressure sensor fitted to the same reference vessel.

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The procedure has been described in our previous study [18]. Briefly, 2 g of the

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ground Prosopis africana shell was weighed into a reaction vessel made of Teflon and 30

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ml of de-ionized water was added to cover the solid. The reaction vessel was sealed and

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placed in the microwave oven. The sample was then heated at 200 °C in the microwave

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oven which was set to ramp to the temperature in 5 min and was held at the temperature

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for 5-20 min (pressure at 200 °C was about 1.80 MPa). The reaction system was allowed

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to cool to room temperature, and the carbonized material was filtered off using filter

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paper (Whatman filter paper number 3, ashless 11 cm). The hydrochar obtained was

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washed several times with de-ionized water until a neutral pH was reached. It was then

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dried in a conventional oven at 80 °C for 16 h, and stored in the desiccator for further

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analysis. The hydrochars were denoted as M-PASx-y, where x and y represent temperature

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(°C) and time (min) for the carbonization respectively.

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2.1.2 Conventional hydrothermal carbonization

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This experiment was conducted in a Teflon-lined autoclave (Parr Instruments,

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Illinois, USA) placed in a preheated conventional oven. Experiments conducted using the

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same set-up to investigate the time the autoclave will take to reach the set temperature

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showed an average time of about 20 min.

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The preparation was carried based on previous report [19]. 2 g of Prosopis

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africana shell was weighed into a Teflon-lined autoclave and 30 ml of deionized water

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was added. The autoclave was placed in a preheated conventional oven at 200 °C and

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was held for 120–240 min. The oven was allowed to cool down to room temperature and

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the autoclave was removed. The prepared hydrochar was filtered off with filter paper

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(Whatman filter paper number 3, ashless 11 cm), washed several times with deionized

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water until a neutral pH was obtained. It was then dried at 80 °C for 16 h, and stored in

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the desiccator for further analysis. The hydrochars were denoted as C-PASx-y, where x

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and y represent temperature (°C) and time (min) for the carbonization respectively.

100 101 102

2.2 Product yield (%) In each case, the dry mass of the carbonized material was measured and the product yield (dry mass percentage of the raw material) was calculated as follows:

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(Equation 1) 2.3 Ash Content Determination

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2 g of the carbonized material was placed into weighed ceramic crucible. The

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carbonized material and crucible were dried for 16 h at 80 °C and reweighed to obtain the

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dry carbon weight. The sample and the crucibles were then heated in a furnace at 760 °C

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for 6 hrs. The crucible was removed from the furnace, cooled in a desiccator and the

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remaining solid (ash) was weighed. Percentage ash content was calculated as follows:

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(Equation 2)

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2.4 pH Measurement

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1 % (wt/wt) suspension of carbon material in deionized water was prepared. The

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pH of the suspension was measured with a pH meter (FisherBrand Hydrus 500, Fisher

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Scientific, Loughborough, UK), which has been calibrated with pH 4 and pH 7 buffer

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solutions. The calibration was confirmed by analysis of a pH 7 buffer after every five

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analyses and a recalibration done if the value varied by more than ± 0.1 pH units.

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2.5 Energy properties of the hydrochars

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The higher heating value (HHV) was calculated using Equation 3 as reported by Gao et al. [20]

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(Equation 3)

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The energy densification ratios of the hydrochars were calculated using the

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equation below

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(Equation 4)

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All experiments were carried out in triplicate, and the results are presented in

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Table 1.

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2.5 Characterization Methods

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The characterizations of the materials were carried out using the following

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instruments. The elemental analysis was carried out using Fisons instruments EA 1108

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CHN analyzer. The surface areas were measured on a Micromeritics Tristar BET-N2

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surface area analyzer, before the analysis the samples were degassed at 120 °C for 3 h.

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FT-IR spectra were recorded using Thermoscientific Nicolet 380 FT-IR (Themo

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Scientific, Hemel Hempstead, UK), equipped with attenuated total reflectance (ATR).

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The morphology and particle size were visualized using a ZEISS EVO 60 SEM (Carl

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Zeiss, Cambridge, UK); the samples were coated with gold and platinum alloy and

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impregnated on a sticky disc before analysis. Thermogravimetic analysis (TGA) were

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carried out under N2 atmosphere at a heating rate of 30 °C min−1 using a Mettler Toledo-

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TGA/DSC 1 instrument.

C solid-state magic angle spinning NMR experiments were

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carried out using a Bruker Avance II 500 MHz (11.74T) spectrometer (Bruker, Coventry,

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UK); the samples were packed without further treatment into a 4 mm zirconia rotor

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sample holder spinning at MAS rate νMAS = 8 KHz. Carbon sensitivity was enhanced

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using Proton-to-carbon CP MAS: recycle delay for all CP experiments was 3 s and TPPM

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decoupling was applied during signal acquisition. Cross polarization transfer was carried

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out under adiabatic tangential ramps to enhance the signal with respect to other known

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methods. CP time tCP = 500 ms. The number of transients was 200 for all the carbon

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samples.

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3. Results and Discussion

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3.1 Product yields, CHN analysis, ash, and pH content

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The main objective of this work was to compare the similarity between the

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hydrochars (solid products) from the microwave-assisted and conventional hydrothermal

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carbonization of a lignocellulosic waste biomass (Prosopis africana shell) in terms of

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their product yields and properties. The results of the product yield are shown in Table 1.

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Despite having a longer processing time, the conventional hydrothermal process

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generated more or almost the same amount of product as the microwave-assisted process,

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which could be attributed to the amorphous cellulose activation under the irradiation with

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microwaves [21,22]. The product yields for the hydrochars decreased, while the carbon

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contents increased with increase in the processing time, due to the loss of oxygen during

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the increasing liquefaction and gasification reactions, which are parallel reactions to the

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hydrothermal process of the biomass [13,23,24].

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In contrast to the carbon content, the hydrogen and oxygen contents of the

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hydrochars decreased with increase in the processing time. This observed trend in the

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hydrothermal carbonization process of biomasses has been attributed to the loss of

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hydrogen and oxygen due to deoxygenating, dehydration and decarboxylation reactions

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that occur during the hydrothermal carbonization process [25-28]. The ash content was

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low for the M-PAS and C-PAS because most of the inorganic compounds contained in

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the Prosopis africana shell dissolved in water during the hydrothermal carbonization

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processes, while their low pH values is as a result of the high content of oxygen

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containing functional groups [18,29].

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Table 1

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The van Krevelen diagram (Figure 1) was also used to provide information about

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the transformation in the chemical structure of the raw material after carbonization, and

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also to qualitatively assess the carbonization process by plotting atomic ratios of H/C

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against O/C for the raw material and the hydrochars from both processes. The ratios of

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the H/C and O/C of the hydrochars decreased as the carbonization time was increased,

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and were lower than that of the raw material. This suggests that there was transformation

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during the hydrothermal carbonization processes resulting from dehydrogenation,

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decarboxylation, deoxygenation and dehydration reactions [8,30]. The raw Prosopis

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africana shell fell into a region that is typical for biomasses, while the hydrochars have

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O/C and H/C ratios akin to that of peat [31]. The graph of H/C versus O/C atomic ratios

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follows at diagonal line from the raw material to the hydrochars, which implies that the

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reaction that predominates during the hydrothermal process is dehydration reactions [30].

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Figure 1

186 187

3.2 Energy properties of the hydrochars

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A vital characteristic of biomass and hydrochars is their higher heating values

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(HHVs). It shows the total amount of energy that is present in a sample. In both

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processes, the HHVs calculated for the M-PAS and C-PAS increased with increase in

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residence time (Table 1), which is an indication of the level of carbonization attained.

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The HHVs of the hydrochar were similar to that of wood and paper due to lignocellulosic

7

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nature of the raw material [19]. Hydrothermal carbonization process is associated with

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dehydration, decarboxylation, and condensation reactions leading to the carbonization of

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the raw biomass and thus resulting in energy densification, which is used to assess the

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effectiveness of the hydrothermal carbonization processes [19,32]. In this study, the

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energy densification ratios of the hydrochars are in the range of 1.24 – 1.27 and 1.12 –

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1.28 for the M-PAS and C-PAS respectively, which is within the range previously

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reported (19,32,33].

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The closeness in the properties of the M-PAS200-20 and C-PAS200-240 could mean

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that other characteristics of these hydrochars may also be comparable. Hence, further

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characterization will be limited to these hydrochars.

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3.3 Chemical Characteristics

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ATR-FTIR Analysis

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ATR-FTIR spectroscopy was used to assess the changes in the Prosopis africana

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shell during the hydrothermal carbonization process. The FTIR spectra of the hydrochars

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(M-PAS200-20 and C-PAS200-240) shown in Figure 2a differ in intensity from that of the raw

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material in Figure 2b, indicating the chemical transformations that occurred when the raw

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material was hydrothermally carbonized. The strong presence of single bond components,

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such as, C-O, C-H and O-H is expected since the hydrochars were obtained from

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lignocellulosic biomass that contains cellulose, hemicelluloses and lignin [34]. The broad

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peak between 3700-3000 cm-1 (Section 1) comes from the stretching vibration of

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aliphatic O-H (hydroxyl and carboxyl), while the peaks between 1200-1000 cm-1 (Section

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6) correspond to C-O stretching vibration from esters, phenols and aliphatic alcohols. The

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weak intensity of these peaks (Sections 1 and 6) in the hydrochars shows that dehydration

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and decarboxylation reactions occurred during the hydrothermal carbonization process

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[32]. The peak between 1800-1650 cm-1 (Section 3) corresponds to the C=O stretching

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vibration of esters, carboxylic acids or aldehydes from cellulose or lignin. This peak was

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almost absent in the hydrochars due to the breakdown of cellulose during the

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hydrothermal carbonization process, while the peak between 1650-1500 cm-1 (Section 4)

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represents the C=C vibrations of the aromatic rings in lignin. This peak was still present

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after the carbonization process; although with reduced intensity indicating the presence of

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lignin fragments and intermediate structures in the hydrochars, which implies that under

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the conditions studied lignin did not totally breakdown [35]. The peaks between 3000-

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2800 cm-1 (Section 2) are due to the stretching vibration of aliphatic C-H bonds, while the

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peaks between 1450-1200 cm-1 (Section 5) are due to the bending vibration of C-H bond

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of the aliphatic carbons, methylene, and methyl groups indicating the presence of

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aliphatic structures [23]. The notable absence in the hydrochars of peaks below 1000 cm-1

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(Section 7) due to the deformation of the C-H out of plane bending vibrations is

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consistent with previous report [25]

232 233

Figure 2

234 235

NMR Analysis

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The 13C solid state NMR analysis of the M-PAS200-20 and C-PAS200-240 shown in

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Figure 3 provided further information on their chemical composition, and also used to

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confirm the functional groups present. It is usually a valuable complementary method to

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the FT-IR analysis in describing biomass conversion during hydrothermal carbonization

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process. A close comparison between the NMR spectra of the hydrochars shows very

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similar features. The peaks between 14–60 ppm shows the presence of aliphatic carbons,

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while those in the region between 100–160 ppm usually referred to as the aromatic region

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are all due to C=C double bond from lignin, but between 140–160 ppm are specifically

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due to the oxygen bound O-C=C (O-aryl) [36,37]. Due to the residual lignin, and the

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cellulose and hemicellulose content of the raw material, the spectra show carbohydrate

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resonances (CH2OH groups around 62 ppm, CHOH groups around 72 ppm, and anomeric

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O-C-O carbons around 90 ppm) in the O-alkyl region between 60 and 100 ppm [14,38].

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The ATR-FTIR analysis has already indicated the presence of these functional groups.

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Therefore, the 13C NMR and ATR-FTIR results are in good agreement with each other.

250 9

251

Figure 3

252 253

Thermo-gravimetric analysis (TGA)

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In order to further assess the extent of conversion of the raw material under the

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microwave-assisted and conventional hydrothermal carbonization conditions, TGA

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analysis was carried out on M-PAS200-20 and C-PAS200-240. The TGA curve in Figure 4

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showed obvious similarities in the behaviour of the hydrochars. The TGA curves can be

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grouped into three weight loss stages. The first stage below 200 °C where there was no

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significant weight loss was because the hydrothermal processes have already decomposed

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the components of the raw materials that would have decomposed at these temperatures.

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The slight loss in weight at the first stage corresponds to moisture loss and release of

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volatile compounds [32,39]. The second stage which occurred at about 220–410 °C,

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represents the temperature range at which chemical bonds begin to break and the lightest

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volatile compounds are released and it corresponds to the decomposition of cellulose and

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hemicellulose [32,40]. The third combustion stage from 410–650 °C is usually assigned

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to thermal degradation of lignin. Among the three components (cellulose, hemicellulose

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and lignin) of the raw material, lignin is the most difficult to decompose. Its

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decomposition usually occurs slowly under the whole temperature range used [41]. The

269

TGA result is in agreement with that of ATR-FTIR and NMR.

270 271

Figure 4

272 273

3.4 Structural Characteristics

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SEM Analysis

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A close inspection of the raw material and hydrochars by means of scanning

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electron microscopy technique shown in Figure 5 revealed interesting transformations in

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the morphologies of the hydrochars vis-a-vis the raw material. The SEM images of the

10

278

M-PAS200-20 and C-PAS200-240 shown in Figures 5 b and c respectively are alike, and are

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different from that of the raw material (Figure 5 a). The raw material showed a cellular

280

structure that is characteristic of lignocellulosic materials, while the hydrochars have

281

aggregates of spherical microparticles of about 1–10 μm in diameter. These

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microparticles originate from the decomposition of cellulose, and the subsequent

283

precipitation and growth into spheres [25]. The lignin component of the raw material on

284

the other hand, probably underwent only partial degradation due to its high thermal

285

stability, producing the rough texture observed in the SEM images of hydrochars [32].

286

This result implies that the lignocellulosic structure of the raw material was broken

287

during the hydrothermal carbonization process.

288 289

Figure 5

290 291

Nitrogen Sorption Measurement

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The nitrogen sorption isotherms for the M-PAS200-20 and C-PAS200-240 are shown

293

in Figure 6. Both hydrochars showed characteristics that are representative of Type II

294

isotherms based on the IUPAC system of classification, which is a typical type of

295

isotherm obtained with non-porous materials [42]. It is therefore not surprising that the

296

hydrochars have relatively small BET surface areas (6.1±2.2 m2/g for M-PAS200-20, and

297

5.9±1.8 m2/g for C-PAS200-240) due to the absence of porosity. In such situation the values

298

of the specific surface area calculated only correspond to the external surface [43]. The

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hydrothermal carbonization process involves carbonization as well as solubilization of

300

the organics, and the formation of tarry substances. The hydrochar produced becomes

301

contaminated with these substances, which block their pores, and make the apparent BET

302

surface area of the hydrochar to be very small [44]. Therefore, improvements of the

303

porosity and the surface area of hydrochars are usually necessary to enable them fit into

304

specific applications, such as, hydrogen storage or electrical energy storage

305

(supercapacitors) [32].

11

306

Figure 6

307 308

4. Conclusion

309

This article provided some new insights into the similarities between hydrochars

310

prepared from microwave-assisted and conventional hydrothermal carbonization

311

processes of Prosopis africana shell, a waste plant material at a low temperature. It is

312

clear from the study that similar transformation can be achieved at 200 °C. The

313

microwave-assisted process proved to be faster in decomposing the waste material as

314

evidenced by the degree of transformation achieved within a short time when compared

315

to the conventional approach. It can therefore be seen, that hydrochar produced for 20

316

min in the microwave oven exhibited a comparable decomposition pattern to that

317

produced for 240 min in the conventional oven and thus it can be concluded that the

318

materials achieved similar levels of conversion. This work therefore suggests that the

319

microwave-assisted process could have the potential for use in the large-scale production

320

of hydrochars.

321 322

Acknowledgement

323

We wish to thank the Petroleum Technology Development Fund (PTDF), Nigeria

324

for providing the funding for the PhD studentship of Dr. Sunday E. Elaigwu. We also

325

acknowledge Dr. Mark Lorch and Bob Knight of the Department of Chemistry,

326

University of Hull for providing assistance with the NMR, and CEM microwave oven

327

respectively.

328 329

References

330

[1] M.M. Titirici, A. Thomas, S.H. Yu, J.O. Muller, M. Antonietti, A direct synthesis of

331

mesoporous carbons with bicontinuous pore morphology from crude plant material by

332

hydrothermal carbonization, Chem. Mater. 19 (2007) 4205-4212.

12

333

[2] S.M. Heilmann, H.T. Davis, L.R. Jader, P.A. Lefebvre, M.J. Sadowsky, F.J. Schendel,

334

et al., Hydrothermal carbonization of microalgae, Biomass Bioenerg. 34 (2010) 875-882.

335

[3] M. Sevilla, A.B. Fuertes, The production of carbon materials by hydrothermal

336

carbonization of cellulose. Carbon 47 (2009) 2281-2289.

337

[4] I. Pavlovič, Ž. Knez, M. Škerget, Hydrothermal reactions of agricultural and food

338

processing wastes in sub- and supercritical water: A review of fundamentals,

339

mechanisms, and state of research, J. Agric. Food Chem. 61 (2013) 8003–8025.

340

[5] S.E. Elaigwu, G. Kyriakou, T.J. Prior, G.M. Greenway, Microwave-assisted

341

hydrothermal synthesis of carbon monolith via a soft-template method using resorcinol

342

and formaldehyde as carbon precursor and pluronic F127 as template, Mater. Lett. 123

343

(2014) 198-201.

344

[6] M. Nuchter, B. Ondruschka, W. Bonrath, A. Gum, Microwave assisted synthesis - a

345

critical technology overview, Green Chem. 6 (2004) 128-141.

346

[7] F. Bergius, H. Specht, Die Anwendung hoher Drucke bei chemischen Vorgangen und

347

eine Nachbildung des Entstehungsprozesses der Steinkohle. Wilhelm Knapp Halle ad

348

Saale (1913) 41-58.

349

[8] M. Guiotoku, C.R. Rambo, F.A. Hansel, W.L.E. Magalhaes, D. Hotza, Microwave-

350

assisted hydrothermal carbonization of lignocellulosic materials, Mater. Lett. 63 (2009)

351

2707-2709.

352

[9] M.M. Titirici, M. Antonietti, N. Baccile, Hydrothermal carbon from biomass: a

353

comparison of the local structure from poly- to monosaccharides and pentoses/hexoses,

354

Green Chem. 10 (2008) 1204-1212.

355

[10] M. Antonietti, M.M. Titirici, Coal from carbohydrates: The "chimie douce" of

356

carbon, Cr Chim. 13 (2010) 167-173.

357

[11] S.H. Yu, B. Hu, K. Wang, L.H. Wu, M. Antonietti, M.M. Titirici, Engineering

358

carbon materials from the hydrothermal carbonization process of biomass, Adv. Mater.

359

22 (2010) 813-828.

360

[12] S.K. Hoekman, A. Broch, C. Robbins, Hydrothermal carbonization (HTC) of

13

361

lignocellulosic biomass, Energ. Fuel 25 (2011) 1802-1810.

362

[13] N. Baccile, G. Laurent, C. Coelho, F. Babonneau, L. Zhao, M.M. Titirici, Structural

363

insights on nitrogen-containing hydrothermal carbon using solid-state magic angle

364

spinning

365

8982.

366

[14] J.D. Mao, X.Y. Cao, K.S. Ro, M. Chappell, Y.A. Li, Chemical structures of swine-

367

manure chars produced under different carbonization conditions investigated by

368

advanced solid-state

369

25 (2011) 388-397.

370

[15] E. Sabio, A. Álvarez-Murillo, S. Román, B. Ledesma, Conversion of tomato-peel

371

waste into solid fuel by hydrothermal carbonization: Influence of the processing

372

variables, Waste Manage (2015) http://dx.doi.org/10.1016/j.wasman.2015.04.016

373

[16] O.O.D. Afolabi, M. Sohail, C.P.L. Thomas, Microwave hydrothermal carbonization

374

of human biowastes, Waste Biomass Valor 6 (2015) 147-157.

375

[17] J.F.R. Flora, X. Lu, L. Li, J.R.V. Flora, N.D. Berge, The effects of alkalinity and

376

acidity of process water and hydrochar washing on the adsorption of atrazine on

377

hydrothermally produced hydrochar, Chemosphere 93 (2013) 1989–1996.

378

[18] S.E. Elaigwu, V. Rocher, G. Kyriakou, G.M. Greenway, Removal of Pb2+ and Cd2+

379

from aqueous solution using chars from pyrolysis and microwave-assisted hydrothermal

380

carbonization of Prosopis africana shell, J. Ind. Eng. Chem. 20 (2014) 3467-3473.

381

[19] Q. Xu, Q. Qian, A. Quek, N. Ai, G. Zeng, J. Wang, Hydrothermal carbonization of

382

macroalgae and the effects of experimental parameters on the properties of hydrochars,

383

ACS Sustainable Chem. Eng. 1 (2013) 1092–1101.

384

[20] Y. Gao, X. Wang, J. Wang, X. Li, J. Cheng, H. Yang, et al., Effect of residence time

385

on chemical and structural properties of hydrochar obtained by hydrothermal

386

carbonization of water hyacinth, Energy 58 (2013) 376-383.

13

C and

15

N nuclear magnetic resonance, J. Phys Chem. C 115 (2011) 8976-

13

C nuclear magnetic resonance (NMR) spectroscopy, Energ. Fuel

14

387

[21] O. Mašek, V. Budarin, M. Gronnow, K. Crombie, P. Brownsort, E. Fitzpatrick, P.

388

Hurst, Microwave and slow pyrolysis biochar-Comparison of physical and functional

389

properties, J. Anal. Appl. Pyrol. 100 (2013) 41-48.

390

[22] V.L. Budarin, J.H. Clark, B.a. Lanigan, P. Shuttleworth, D.J. Macquarrie,

391

Microwave assisted decomposition of cellulose: a new thermochemical route for biomass

392

exploitation, Bioresource Technol. 101 (2010) 3776-3779.

393

[23] A. Kruse, A. Gawlik, Biomass Conversion in Water at 330-410 °C and 30-50 MPa.

394

Identification of key compounds for indicating different chemical reaction pathways, Ind.

395

Eng. Chem. Res. 42 (2003) 267-279.

396

[24] M. Möller, P. Nilges, F. Harnisch, U. Schröder, Subcritical water as reaction

397

environment: Fundamentals of hydrothermal biomass transformation, ChemSusChem 4

398

(2011) 566-579.

399

[25] M. Sevilla, J.A. Macia-Agullo, A.B. Fuertes, Hydrothermal carbonization of

400

biomass as a route for the sequestration of CO2: chemical and structural properties of the

401

carbonized products, Biomass Bioenerg. 35 (2011) 3152-3159.

402

[26] C. Falco, N. Baccile, M.M. Titirici, Morphological and structural differences

403

between glucose, cellulose and lignocellulosic biomass derived hydrothermal carbons,

404

Green Chem. 13 (2011) 3273-3281.

405

[27] S. Kang, X. Li, J. Fan, J. Chang, Characterization of hydrochars produced by

406

hydrothermal carbonization of lignin, cellulose, d-xylose, and wood meal, Ind. Eng.

407

Chem. Res. 51 (2012) 9023-9031.

408

[28] N.D. Berge, K.S. Ro, J. Mao, J.R.V. Flora, M.A. Chappell, S. Bae, Hydrothermal

409

carbonization of municipal waste streams, Environ. Sci. Technol. 45 (2011) 5696-5703.

410

[29] Z. Liu, F.S. Zhang, J. Wu, Characterization and application of chars produced from

411

pinewood pyrolysis and hydrothermal treatment, Fuel 89 (2010) 510-514.

412

[30] E. Erdogan, B. Atila, J. Mumme, M.T. Reza, A. Toptas, M. Elibol, J. Yanik,

413

Characterization of products from hydrothermal carbonization of orange pomace

15

414

including anaerobic digestibility of process liquor, Bioresource Technol. 196 (2015) 35-

415

42.

416

[31] M.T. Reza, M.H. Uddin, J.G. Lynam, S.K. Hoekman, C.J. Coronella, Hydrothermal

417

carbonization of loblolly pine: reaction chemistry and water balance, Biomass Conv.

418

Bioref. 4 (2014) 311-321.

419

[32] G.K. Parshetti, S.K. Hoekman, R. Balasubramanian, Chemical, structural and

420

combustion characteristics of carbonaceous products obtained by hydrothermal

421

carbonization of palm empty fruit bunches, Bioresource Technol. 135 (2013) 683-689.

422

[33] M.H. Thomsen, A. Thygesen, A.B. Thomsen, Hydrothermal treatment of wheat

423

straw at pilot plant scale using a three-step reactor system aiming at high hemicellulose

424

recovery, high cellulose digestibility and low lignin hydrolysis, Bioresource Technol. 99

425

(2008) 4221-4228.

426

[34] S.V. Vassilev, D. Baxter, L.K. Andersen, C.G. Vassileva, T.J. Morgan, An overview

427

of the organic and inorganic phase composition of biomass, Fuel 94 (2012) 1-33.

428

[35] Z. Liu, A. Quek, S.K. Hoekman, R. Balasubramania, Production of solid biochar

429

fuel from waste biomass by hydrothermal carbonization, Fuel 103 (2013) 943-949.

430

[36] M.M. Titirici, R. Demir-Cakan, N. Baccile, M. Antonietti, Carboxylate-rich

431

carbonaceous materials via one-step hydrothermal carbonization of glucose in the

432

presence of acrylic acid, Chem. Mater. 21 (2009) 484-490.

433

[37] N. Baccile, G. Laurent, F. Babonneau, F. Fayon, M.M. Titirici, M. Antonietti,

434

Structural characterization of hydrothermal carbon spheres by advanced solid-state MAS

435

13

436

[38] J. Mao, K.M. Holtman, J.T. Scott, J.F. Kadla, K. Schmidt-Rohr, Differences

437

between lignin in unprocessed wood, milled wood, mutant wood, and extracted lignin

438

detected by 13C solid-state NMR, J. Agric. Food Chem. 54 (2006) 9677-9686.

C NMR investigations, J. Phys. Chem. C 113 (2009) 9644-9654.

16

439

[39] M.A. Islam, G. Kabir, M. Asif, B.H. Hameed, Combustion kinetics of hydrochar

440

produced from hydrothermal carbonisation of Karanj (Pongamia pinnata) fruit hulls via

441

thermogravimetric analysis, Bioresource Technol. 194 (2015) 14–20.

442

[40] M. Lapuerta, J.J. Hernandez, J. Rodriguez, Kinetics of devolatilisation of forestry

443

wastes from thermogravimetric analysis, Biomass Bioenerg. 27 (2004) 385-391.

444

[41] H. Yang, R. Yan, H. Chen, D. Lee, C. Zheng, Characteristics of hemicellulose,

445

cellulose and lignin pyrolysis, Fuel 86 (2007) 1781-1788.

446

[42] K.S.W. Sing, D.H. Everett, R.A.W. Haul, L. Moscou, R.A. Pierotti, J. Rouquerol, et

447

al., Reporting physisorption data for gas/solid systems, Pure Appl. Chem. 57 (1985) 603-

448

619.

449

[43] A.B. Fuertes, M.C. Arbestain, M. Sevilla, J.A. Maciá-Agulló, S. Fiol, R. López, et

450

al., Chemical and structural properties of carbonaceous products obtained by pyrolysis

451

and hydrothermal carbonisation of corn stover, Aust. J. Soil Res. 48 (2010) 618-626.

452

[44] K. Mochidzuki, N. Sato, A. Sakoda, Production and characterization of

453

carbonaceous adsorbents from biomass wastes by aqueous phase carbonization,

454

Adsorption 11 (2005) 669-673.

455 456 457 458 459 460 461 462

17

463

Figure 1: van Krevelen diagram of raw Prosopis africana shell and hydrochars

464

obtained at 200 °C and different residence time for the microwave-assisted (M-PAS)

465

and conventional (C-PAS) hydrothermal carbonization

466 467 468 469

Figure 1

470 471 472 473 474 475 476 477 478 479

Figure 2: ATR-FTIR spectra showing the different sections of the wavelength for

480

the functional groups present (a) ATR-FTIR spectra of M-PAS200-20 (blue) and C-

481

PAS200-240 (red); (b) ATR-FT-IR spectrum of raw Prosopis africana shell

18

482 483 484

Figure 2

a

M-PAS 200-20 (Blue) C-PAS 200-240 (Red) 6 1

2

3 4 7 5

100

b

PASR 95

90

85

2

80

%T

1

6

3

Raw Prosopis africana shell

75

4 7

70

5 65

60

55 350 0

485 486

300 0

2500

2000

Wav enumber s (c m-1)

487

19

1500

1000

488 489 490 491 492 493 494

Figure 3: 13C solid state cross-polarization magic-angle spinning NMR spectra of MPAS200-20 (red) and C-PAS200-240 (black) Figure 3

M-PAS200-20

C-PAS200-240

495 496 497 498 499 500 501 502 503 504 505 506 507 508 509 20

510 511 512 513

Figure 4: TGA curves for of M-PAS200-20, and C-PAS200-240 Figure 4

514 515 516 517 518 519 520 521 522 523 524 525 526 527 528 529 530 531 532 533 534 21

535 536 537 538 539

Figure 5: SEM images of (a) raw Prosopis africana shell; (b) M-PAS200-20, and (c) CPAS200-240 Figure 5

540 541 542 543 544 545 546 547 548 549 550 551 552 553 554 555 556 557 558 559 560 22

561 562 563

Figure 6: N2 sorption isotherms of (a) M-PAS200-20; (b) C-PAS200-240

564 565 566

Figure 6

a

b

567 568

23

Materials

Yields (%)

C (%)

H (%)

N (%)

Oa (%)

O/C*

H/C *

pH

Ash (%)

HHV

Energy

(MJ

densific

−1

kg )

ation ratio

P. africana

46.58±0.01

6.94±0.04

1.57±0.09

44.91±0.10

0.73

1.77

5.34±0.02

3.77±1.13

17.64

shell M-PAS M-PAS200-20

30.60±2.13

58.08±1.12

6.18±0.80

1.61±0.01

34.13±0.31

0.44

1.27

4.05±0.03

9.32±0.50

22.37

1.27

M-PAS200-15

32.21±1.55

55.81±0.06

6.61±0.09

1.60±0.01

35.98±0.14

0.48

1.41

4.21±0.01

9.05±0.45

21.88

1.24

M-PAS200-10

33.01±0.98

55.69±0.00

6.67±0.03

1.57±0.02

36.07±0.05

0.49

1.43

4.37±0.01

9.10±0.10

21.91

1.24

M-PAS200-5

36.37±2.01

55.46±0.08

6.71±0.05

1.48±0.00

36.35±0.06

0.49

1.44

4.51±0.00

8.72±0.85

21.84

1.24

C-PAS200-240

30.85±0.53

57.86±1.10

6.37±0.06

1.46±0.05

34.31±1.21

0.44

1.31

4.34±0.01

9.25±0.45

22.53

1.28

C-PAS200-180

34.78±0.04

53.85±1.02

6.53±0.01

1.47±0.05

38.15±0.96

0.53

1.44

4.41±0.02

9.01±0.32

20.72

1.18

C-PAS200-120

37.87±0.20

51.25±0.90

6.72±0.02

1.65±0.03

40.38±0.95

0.59

1.56

4.57±0.01

8.87±0.75

19.72

1.12

C-PAS

569

a

570

* Atomic ratios

571

Table 1: Product yields, CHN analysis, pH, ash contents and energy properties of

572

the raw Prosopis africana shell and hydrochars from microwave-assisted and

573

conventional hydrothermal carbonization processes

The oxygen content was determined by difference [100% - (C%+H%+N%)] [8]

574 575 576

24

577 578 579 580 581

25