Journal Pre-proof Highly efficient renewable heterogeneous base catalyst derived from waste Sesamum indicum plant for synthesis of biodiesel Biswajit Nath, Pranjal Kalita, Bipul Das, Sanjay Basumatary PII:
S0960-1481(19)31710-0
DOI:
https://doi.org/10.1016/j.renene.2019.11.029
Reference:
RENE 12576
To appear in:
Renewable Energy
Received Date: 24 November 2018 Revised Date:
23 August 2019
Accepted Date: 8 November 2019
Please cite this article as: Biswajit Nath, Pranjal Kalita, Bipul Das, Sanjay Basumatary, Highly efficient renewable heterogeneous base catalyst derived from waste Sesamum indicum plant for synthesis of biodiesel, Renewable Energy (2019), doi: 10.1016/j.renene.2019.11.029 This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. 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. © 2019 Elsevier Ltd. All rights reserved.
Graphical abstract:
Highlights:
•
Renewable heterogeneous catalyst derived from waste Sesamum indicum plant was employed in biodiesel synthesis.
•
High amounts of K and Ca in the catalyst were confirmed by AAS, EDX and XPS techniques.
•
Yield of 98.9% biodiesel was achieved at optimum conditions in a short reaction time of 40 min.
•
The catalyst showed promising catalytic activity up to 3rd cycle of reaction without any significant loss of activity.
•
Properties of produced biodiesel are compatible with international standard.
1
Highly efficient renewable heterogeneous base catalyst derived from waste
2
Sesamum indicum plant for synthesis of biodiesel
3
Biswajit Natha, Pranjal Kalitab,*, Bipul Dasc, Sanjay Basumatarya,*
4 5
a
6
b
7
c
8
Jorhat-785006, Assam, India
Department of Chemistry, Bodoland University, Kokrajhar-783370, Assam, India Department of Chemistry, Central Institute of Technology, Kokrajhar-783370, Assam, India
Chemical Engineering Division, CSIR-North East Institute of Science and Technology,
9 10
*
11
*
12
E-mail addresses:
[email protected] (S. Basumatary),
[email protected] (P. Kalita).
These authors contributed equally to this work. Corresponding authors.
13 14
Abstract
15
Waste Sesamum indicum plant derived heterogeneous catalyst was utilized for the first time
16
for biodiesel synthesis from sunflower oil. The derived catalyst was characterized by using
17
Powder XRD, FT-IR, BET, TGA, XRF, AAS, XPS, SEM-EDX and TEM, and the
18
characterization revealed the presence of Na, K, Ca, Mg, Fe, Mn, Zn, Si, Sr and Cl with high
19
percentage of K (29.64 wt. %) and Ca (33.80 wt. %) as oxides and carbonates. The catalyst
20
with a moderate surface area of 3.66 m2 g-1 exhibited excellent catalytic activity producing a
21
yield of 98.9 % biodiesel under the optimized conditions of 12:1 methanol to oil molar ratio
22
and catalyst loading of 7 wt. % at the reaction temperature of 65 oC in a short reaction time of
23
only 40 min. The catalyst could be reused up to the 3rd cycle of reaction with the yield of 94.2
24
% biodiesel. The characterization of biodiesel composition was done by using FT-IR, NMR,
25
and GC-MS techniques. The fuel property of produced biodiesel meets the prescribed limits
26
of international standard. The prepared catalyst is easy to handle, reusable, and found to be
27
highly efficient green catalyst that could help in reduction of biodiesel cost. Thus, the catalyst
28
can be recommended as a potential candidate for cost-effective biodiesel production at a large
29
scale.
30 31
Keywords: Biodiesel; heterogeneous catalyst; sunflower oil; transesterification; waste
32
Sesamum indicum.
33 1
34
1. Introduction
35
Fossil fuels are the major sources to meet the present requirement of energies worldwide
36
for transport and other allied industries [1]. Fossil fuels are obtained from non-renewable
37
sources and these fuels may be exhausted by 2050 due to limited resources and current
38
depletion of their reserves at a high rate [2]. Currently, increasing usage of fossil fuels in
39
vehicles leads to more environmental pollutions due to the emission of greenhouse gases [3].
40
Hence, researchers are searching for viable alternate sources of energy to cope with the
41
present dwindling situation. In this context, biodiesel obtained from various oil resources is
42
gaining worldwide attention as an alternate source of energy as biodiesel is beneficial over
43
conventional fossil fuels due to less emission of greenhouse gases, low viscosity, high cetane
44
number, high flash point, non-toxic, biodegradability and lubricity [4, 5]. The properties of
45
biodiesel are comparable with conventional diesel fuels and its blend with diesel fuel up to 40
46
% can be used in any diesel-engine [6]. Moreover, the usage of biodiesel as the alternative
47
fuel reduces the effects on the environment [1]. In search of biodiesel feedstocks, researchers
48
reported various edible and non-edible oil sources for biodiesel synthesis such as soybean oil
49
[4], palm oil [7, 8], Jatropha curcas oil [9, 10], Mesua ferrea oil [11], Thevetia peruviana oil
50
[5, 12], Bauhinia monandra oil [13], Azadirachta indica oil [14, 15], waste cooking oil [16],
51
animal fats [17], and many others.
52
Biodiesel is the mixture of fatty acid methyl esters (FAME) obtained by catalytic
53
transesterification of triglycerides (oils or fats) with alcohol preferably methanol.
54
Homogeneous, heterogeneous and enzyme catalysts are utilized in biodiesel synthesis.
55
Homogeneous catalyzed transesterification uses acids or bases as the catalyst. Acid catalyzed
56
transesterification reaction requires high molar ratio of alcohol to oil, high pressure and
57
temperature with longer reaction times as well as the catalysts are corrosive and not
58
recyclable [18]. Homogeneous base catalyzed transesterification takes shorter reaction times
59
for conversion of oil to FAME with a high yield but possesses the difficulty of soap
60
formation during conversion and the catalyst cannot be separated easily [1, 4]. Enzyme
61
catalysts are not feasible for wider application in biodiesel production because of higher cost
62
and very slow reaction rate [4, 19]. In search of other convenient methods for
63
transesterification, heterogeneous catalysts are reported with promising results in conversion
64
of oil to biodiesel which is gaining much more attention worldwide. Heterogeneous base
65
catalysts are more advantageous and have more potential over heterogeneous acid and
66
enzyme catalysts as they can achieve complete conversion in shorter reaction times at
67
ambient conditions, catalysts can be separated easily by filtration and can be reused for 2
68
several cycles of reaction [20]. Moreover, heterogeneous catalysts do not form soaps during
69
the reaction which can enhance the yield of biodiesel. Both chemical and natural resources
70
for the generation of heterogeneous catalysts are reported by the researchers. Heterogeneous
71
catalysts derived from chemical sources showed good catalytic activity with 100 %
72
conversion of oil to biodiesel but these catalysts are quite expensive as the preparation steps
73
are longer and more complex which utilized intensive energy [1]. Moreover, these catalysts
74
are generated from non-renewable resources and they are not biodegradable, not environment
75
friendly and they are not cost-effective for the production of biodiesel [1]. Hence, prime
76
importance should be given to obtain the ideal heterogeneous catalyst that is eco-friendly,
77
low-cost and recyclable apart from demonstrating the high catalytic activity in biodiesel
78
production.
79
Considering the various facts of homogeneous, enzyme and heterogeneous catalyst from
80
chemical sources, nowadays the researchers are attracted more towards the heterogeneous
81
catalysts derived from renewable natural resources for biodiesel synthesis. The solid catalysts
82
obtained from natural resources exhibit excellent catalytic activity and after use, these can be
83
thrown out to the environment without any potential harm as they are biodegradable. In
84
recent years, heterogeneous base catalysts derived from agricultural wastes are being used as
85
the efficient green heterogeneous catalysts for biodiesel synthesis without any further
86
chemical modification [1]. Lemna perpusilla ash [21], Musa balbisiana peel ash [16], Musa
87
balbisiana underground stem ash [9, 11], coconut husk ash [22], banana peel (Musa Gross
88
Michel) ash [13], Musa paradisiacal peel ash [12], Musa acuminata peel ash [23], plantain
89
fruit peel ash [14], cocoa pod husk ash [7, 15], Astrocaryum aculeatum ash [4], Birch bark
90
ash [8], Acacia nilotica wood ash [24] etc. are some of the agricultural wastes derived
91
heterogeneous catalysts reported with remarkable catalytic activities for synthesis of
92
biodiesel. These catalysts are highly basic in nature which can be utilized for several cycles
93
of reaction with a high yield of biodiesel [1] and further such catalysts could reduce the
94
overall biodiesel production cost.
95
In the present study, an efficient heterogeneous catalyst is introduced from the waste
96
Sesamum indicum (sesame) plant for biodiesel synthesis. Sesamum indicum plant belonging
97
to the family Pedaliaceae is cultivated in the tropical region of the world for the nutritional
98
values of the edible seed as well as for its high quality oil. Sesame is used as a medicinal and
99
religious crop in Iran and India [25, 26]. Gouveia et al. [27] and Prasad et al. [28] studied the
100
medicinal properties of sesame and reported anti-oxidative, anti-hypersensitive, anticancer,
101
and anti-diabetic properties. In the state of Assam of Northeast (NE) India, the Bodo people 3
102
and other tribal communities widely cultivate Sesamum indicum plant for its seed and
103
traditionally use the grinded seeds in making of the rice cake. The plant materials after
104
untying seeds are usually thrown out as wastes which have no economic value. These dry
105
post-harvest plants are ignited thoroughly in the open air and the ashes obtained are used as
106
an insect repellent in cultivating crops by the rural people of NE India. It is noteworthy to
107
mention that the water extract of ash obtained from Sesamum indicum plant being highly
108
basic (alkaline) in nature is traditionally used by the people of this region as a food-additive
109
to make several traditional dishes which replaces the commercially available “SODA” whose
110
chemical composition is K2CO3. This water extract is locally known as Khar or Khardwi and
111
the people also use it as a medicine for recovery from gas related problems in the stomach.
112
Hence, we are motivated to utilize highly basic Sesamum indicum ash as an efficient
113
heterogeneous catalyst for production of biodiesel through transesterification reaction. The
114
literature study also showed that this waste plant ash has yet not been reported as a catalyst
115
for the production of biodiesel as well as in the area of organic chemistry. Moreover, the raw
116
materials could be obtained from easily available renewable sources and will provide an easy
117
process for the preparation of catalyst at minimum cost. As a result, it will significantly
118
reduce the cost of biodiesel. Since the agro-waste being renewable is taken as raw materials
119
for preparation of catalyst, the derived heterogeneous catalyst is considered as non-corrosive,
120
green and environmental friendly. In this study, for the first time, we are reporting the
121
catalytic activity of calcined Sesamum indicum ash as a green heterogeneous base catalyst for
122
biodiesel synthesis which is found to be highly efficient, reusable and has a very strong
123
potential as a candidate for reducing the cost for biodiesel production. The prepared catalyst
124
was characterized by various sophisticated analytical techniques and chemical composition
125
reported.
126 127
2. Materials and methods
128
2.1. Materials
129
In this study, the waste Sesamum indicum plant was collected after harvesting the seeds
130
from Dotma village of Kokrajhar, Assam, India for the preparation of the catalyst. Sunflower
131
oil was purchased from the Kokrajhar market, Assam, India to investigate the catalytic
132
activity in the synthesis of biodiesel. Methanol (≥ 99.0 %), ethyl acetate (≥ 99.5 %), silica gel
133
G (particle size through BSS 350 ≥ 95 %), and anhydrous sodium sulphate (≥ 99.0 %) were
134
obtained from Merck, Mumbai, India. Petroleum ether (40–60 oC) of analytical reagent grade
4
135
and acetone (99 %) were purchased from Rankem, Maharashtra, India. All the chemicals
136
were used as received.
137 138
2.2. Catalyst preparation
139
The waste Sesamum indicum plants obtained after untying seeds from the plant were dried
140
under the sun for 15 days. The dry materials were completely burnt into ash in the open air
141
and the ash obtained was further calcined at 550 oC for 2 h in a programmable muffle furnace
142
(Havells, B 25, DHMCBSPF025). The calcined Sesamum indicum ash was milled to obtain
143
the powder with the help of pestle and mortar, and stored in sealed plastic container for
144
further analysis and use.
145 146
2.3. Catalyst characterization
147
The Powder X-ray diffraction (XRD) technique was applied to characterize the calcined
148
Sesamum indicum catalyst using the X-ray diffractometer (Bruker AXS, D8 FOUS,
149
Germany). The credible chemical components present in the catalyst were identified
150
comparing the peaks of XRD spectrum located at different angles (2θ) against the Joint
151
Committee on Powder Diffraction Standards (JCPDS). Fourier transform infrared (FT-IR)
152
spectrophotometer (Perkin Elmer, C-107727, USA) was used for recording the FT-IR spectra
153
in the range of 4000–400 cm-1. The surface area of the catalyst was examined by Brunauer–
154
Emmett–Teller (BET) method using Quantachrome ASiQwin™ version 3.0 instrument. The
155
analysis was performed using N2 gas at a bath temperature of 77.4 K and an outgas
156
temperature of 373 K for 1 h. Thermogravimetric analysis (TGA) of the catalyst was
157
performed using a thermogravimetric analyzer (Make: TA, Model: SDTQ600, USA) at the
158
heating rate of 10 oC/min up to 800 oC at the constant flow of N2 gas. The surface
159
morphology was investigated using scanning electron microscopy (SEM) instrument (JEOL,
160
JSM 6390LV, Japan). The elements present in the catalyst were investigated by using X-ray
161
fluorescence (XRF) spectrometer (PANalytical, AXIOS DY824, Netherland). Quantitative
162
analysis of the elements present in the catalyst was done using the atomic absorption
163
spectrophotometer (AAS) (AAS-ICE 3500, Thermo Scientific, UK). The surface chemical
164
composition of the catalyst was determined employing X-ray photoelectron spectrometer
165
(XPS) (Make: Thermo Fischer Scientific, Model: ESCALAB Xi+, USA). Energy dispersive
166
X-ray (EDX) spectroscopic technique was used for analysis of the elemental composition of
167
the catalyst by using SEM (JEOL, JSM 6390LV, Japan). The structural information of the
168
catalyst was studied from transmission electron microscopy (TEM) image and selected area 5
169
electron diffraction (SAED) pattern recorded from JEM-2100, 200 kV, JEOL instrument. The
170
pH value of the catalyst was determined by using a digital pH meter (Labtronics Auto deluxe
171
pH meter, LT10). Separately, 1 g of calcined catalyst was dissolved in the volume of 10, 20,
172
30, 40 and 60 mL of distilled water. Each solution was well-stirred for few min and filtered
173
through Whatman no. 1 filter paper and the pH value of the filtrate was measured.
174 175
2.4. Biodiesel synthesis and characterization
176
The biodiesel synthesis was carried out by reacting sunflower oil with methanol using the
177
prepared catalyst in a round bottomed flask fitted with a magnetic stirrer (650 rpm) at a
178
temperature of 65 oC. The desired amount of oil was taken in a 100 mL round bottomed flask
179
and required methanol was added in a particular molar ratio to oil followed by the addition of
180
the catalyst for transesterification reaction. The optimum reaction conditions were
181
investigated and the reactions were performed by varying the methanol to oil ratio such as
182
3:1, 6:1, 9:1, 12:1, 15:1, and 18:1 with different catalyst load of 3 wt. %, 5 wt. %, 7 wt. %
183
and 9 wt. % of oil. Under the above optimized conditions, the reaction was also investigated
184
at different temperatures of 32, 45, and 55 oC. The conversion of oil to biodiesel was
185
monitored by using thin layer chromatography. The biodiesel synthesized was extracted with
186
petroleum ether (40–60 oC) using a separating funnel, dried over anhydrous sodium sulphate
187
followed by removal of the solvent in a rotary vacuum evaporator (Almicro, QuickVap) at 45
188
o
189
C. 1
H NMR and
13
C NMR spectra of oil and biodiesel were recorded in CDCl3 at 400 MHz
190
and 100 MHz, respectively using FT-NMR Spectrometer (Bruker Avance II, 400 MHz) for
191
comparison of structural changes in the conversion of oil to biodiesel. Biodiesel composition
192
was determined by gas chromatography-mass spectrometer (GC-MS) using Perkin Elmer,
193
Claurus 680 Gas Chromatograph/Claurus 600C Mass spectrometer. During analysis, initially
194
the oven temperature was held at 60 oC for 6 min, increased at the rate 5 oC/min to 180 oC
195
followed by 10 oC/min to 280 oC. After 20 min when the temperature dropped to 250 oC, the
196
sample was injected and analysed with Turbomass Ver5.4.2 software. The source and transfer
197
temperatures were 160 and 180 °C. The carrier gas used is helium at a flow rate of 1 mL/min,
198
split ratio is 20:1, GC column used is Elite 35 MS with the dimension of 60.0 m × 250 µm,
199
and mass scan is from 50 to 500 Da.
200 201 202 6
203
2.5. Determination of biodiesel fuel properties
204
The fuel properties of the produced biodiesel such as density, kinematic viscosity, pour point,
205
cold filter plugging point were tested following IS 1448 method, and cetane number (ASTM
206
D4737 method) and total sulphur (ASTM D2622 method) were also determined at the quality
207
control laboratory of Indian Oil Corporation, Bongaigaon Refinery, Assam, India. Other
208
parameters such as higher heating value (HHV), American petroleum index (API), aniline
209
point, and diesel index were determined following ASTM D2015 standard equations [29],
210
and the saponification number was also determined following standard equation [30].
211 212
3. Results and discussion
213
3.1. Characterization of catalyst derived from waste plant
214
3.1.1. Powder XRD analysis
215
The crystalline components of metals present in calcined Sesamum indicum catalyst were
216
identified from the XRD pattern shown in Fig. 1 by comparing with JCPDS data and reported
217
literatures. This analysis of the catalyst indicated the complex mixture of oxides of metals
218
such Na, K, Ca, Mg, Sr, Si and Fe, carbonates of metals like Na, K and Ca, and hydroxide of
219
Ca. The XRD analysis also revealed that the various components of potassium are present in
220
the form of KCl, K2CO3 and K2O. The JCPDS study shows that the peaks at 2θ values of
221
28.27, 40.47, 49.53, 58.74 and 73.74 are due to KCl and the presence of K2CO3 is represented
222
by the peaks at 2θ values of 26.71, 29.67, 30.93, 31.72, 34.06 and 41.87. The peaks at 2θ
223
values of 27.64, 39.84, 46.70, 48.12, 52.18, 56.71, 63.27 and 65.16 are due to the presence of
224
K2O in the catalyst. The presence of KCl in the calcined Sesamum indicum catalyst is
225
supported with the results of calcined coconut husk catalyst reported by Vadery et al. [22]
226
and calcined banana peel catalyst reported by Betiku et al. [13]. Gohain et al. [16] also
227
characterized the catalyst derived from Musa balbisiana peel and reported that 2θ values at
228
26, 31 and 41 are due to the presence of K2CO3 and the 2θ value at 46 is due to K2O which
229
are supporting the results of current study. The existence of CaO in the catalyst is revealed by
230
the 2θ values of 32.33, 37.18, 43.00, 54.21, 64.22, 66.55 and 69.39 which are also
231
comparable with the recently reported 2θ values of CaO in the works of Uprety et al. [8],
232
Gohain et al. [16], Kumar et al. [31] and Jin et al. [32]. The peak at 2θ value of 48.70 is due
233
to CaCO3 present in the current catalyst which is in accordance with the result reported by Ho
234
et al. [33]. A minor peak of Ca(OH)2 is also observed in the XRD pattern of the catalyst at 2θ
235
value of 51.55 which conforms the results reported by Kumar et al. [31, 34]. The JCPDS data
236
predicted the existence of SiO2 in the catalyst at 2θ values of 21.39, 25.78 and 72.78 (Fig. 1). 7
237
The presence of SiO2 was also found in the calcined wood ash catalyst [24] and M. balbisiana
238
underground stem catalyst [9] reported for biodiesel synthesis. According to JCPDS data, the
239
presence of SrO in the catalyst is represented by the peaks at 2θ values of 30.46, 50.62 and
240
62.33 and the Fe2O3 is indicated by the peaks at 2θ values of 23.74 and 32.96. The presence
241
of Na in the form of Na2O is identified from the peaks at 2θ values of 32.19 and 54.98 and
242
Na2CO3 is indicated by the peak at 37.95. The peak at 2θ value of 43.50 showed the presence
243
of MgO. The study of XRD pattern reveals that the catalyst is a mixture mainly composed of
244
oxides and carbonates of metals and also predicts that K and Ca are the dominant elements
245
which are responsible for their catalytic activity.
246
247 248
Fig. 1. Powder XRD pattern of calcined Sesamum indicum catalyst.
249 250
3.1.2. FT-IR analysis
251
The FT-IR spectrum of calcined Sesamum indicum catalyst is shown in Fig. 2. In the
252
spectrum, the broad peak at 3442 cm-1 indicates the -OH group which is due to the water
253
molecules adsorbed on the surface of the catalyst. The peak at 2143 cm-1 is attributed to M-O-
254
K stretching vibration which shows the presence of potassium in the catalyst and this is in
255
accordance with the IR peak (2178 cm-1) of Musa acuminata peel catalyst reported by Pathak
256
et al. [23]. The existence of peaks at 1645 cm -1, 1445 cm -1 and 1404 cm-1 are indicative of C8
257
O stretching vibrations due to the presence of metal carbonates in the catalyst which is in
258
compliance with the FT-IR study results of catalysts reported by Betiku et al. [15], Gohain et
259
al. [16] and Pathak et al. [23]. The peaks at 1106 cm-1, 1030 cm-1 and 957 cm-1 may be due to
260
Si-O-Si bond vibration which is supporting the SiO2 component in the XRD pattern (Fig. 1).
261
The peak at 622 cm-1 corresponds to the K-O and Ca-O stretching vibrations which may be
262
due to the presence of K2O and CaO in the catalyst which was also predicted in the XRD
263
analysis (Fig. 1). Similarly, Pathak et al. [23] also reported FT-IR peak at 687 cm-1 for K-O
264
and Ca-O stretching vibrations in the catalyst derived from Musa acuminata peel. In this
265
study, the FT-IR analysis is in well agreement with the XRD pattern which confirmed the
266
presence of oxides and carbonates of metals in the calcined Sesamum indicum catalyst.
267 60 3 41 2
Transmittance (%)
55 50
3 29 2
5 4 6 1
45 40
2 44 3
35
3 78
4 04 1
54 4 1
7 5 9
30 6 0 11
25 4000
3500
3000
2500
2000
1500
0 74 0 3 0 1
1000
2 2 6
500
0
-1
268 269
Wavenumber (cm ) Fig. 2. FT-IR spectrum of calcined Sesamum indicum catalyst.
270 271
3.1.3. Surface area, pore size and pore volume determination
272
The BET surface area analysis of the calcined catalyst resulted in a surface area of 3.66 m²
273
g-1. The BJH (Barrett-Joyner-Halenda) average pore volume of the catalyst is found to be
274
0.012 cm3 g-1. The pore diameter of the catalyst is 1.677 nm and its adsorption pore size
275
distribution (1.47–2.25 nm) is clearly shown in Fig. 3a. In a study reported by Pathak et al.
276
[23], the surface area of Musa acuminata peel ash catalyst is lower (1.45 m² g-1) compared to
277
the current study. Sharma et al. [24] also prepared a solid heterogeneous catalyst from Acacia
9
278
nilotica wood by calcining at different temperatures for 3 h and they reported their surface
279
areas in the range of 1.33–3.72 m² g-1. It is reported that calcination temperature and time are
280
the main factors that affect the surface area of the heterogeneous catalyst that is directly
281
linked to the catalytic activity providing superior results of oil transesterification reaction
282
with higher surface area [4, 24]. The N2 adsorption‐desorption isotherm shown in Fig. 3b is
283
the characteristic of a type‐IV isotherm which indicated that the calcined Sesamum indicum
284
catalyst is mesoporous materials. Similarly, other waste biomass derived catalysts with type-
285
IV isotherm showing mesoporous materials were also reported in the works of Pathak et al.
286
[23] and Laskar et al. [35] for biodiesel synthesis.
287 288
0.0040 1.67 0.0035
0.0025 0.0020
3
-1 -1
dV(d) (cm nm g )
0.0030
0.0015 0.0010 0.0005 0.0000 -0.0005 -2
0
2
4
6
8
10
12
14
16
18
20
Pore diameter (nm)
289 290
Fig. 3a. Adsorption pore size distribution of calcined Sesamum indicum catalyst.
291 292
10
12
Desorption Adsorption
3 -1
Volume (cm g )
10
8
6
4
2
0 0.0
0.2
0.4
0.6
0.8
1.0
Relative pressure, P/Po 293 294
Fig. 3b. N2 adsorption‐desorption isotherm of calcined Sesamum indicum catalyst.
295 296 297
3.1.4. Thermogravimetric analysis
298
The thermal stability of the uncalcined catalyst was checked by TGA and the thermogram
299
is shown in Fig. 4. It is observed that on heating the catalyst till about 150 °C the weight loss
300
takes place which is due to the loss of water molecules adsorbed on the surface of the
301
catalyst. The catalyst was found to be stable from about 150 °C to about 350 °C as indicated
302
by the almost constant weight at this range. The weight loss at a slow rate from about 150 to
303
500 oC was observed and this might be due to the slow loss of water of crystallization as no
304
decomposition of chemicals is expected in this range. However, the carbonaceous materials
305
present in the catalyst are expected to decompose in between 500 and 800 °C, and the loss of
306
weight at this range may be linked to the release of CO and CO2 [4, 23].
307
11
102 100
Weight loss (%)
98 96 94 92 90 88 86 84 0
100
200
300
400
500
600
700
800
o
Temperature ( C)
308
Fig. 4. TGA thermogram of uncalcined catalyst.
309 310 311 312
3.1.5. SEM analysis
313
The morphological characteristic of the surface of the catalyst was studied from the SEM
314
image of calcined Sesamum indicum catalyst. The SEM images (Fig. 5A–C) showed the
315
formation of agglomeration of particles and layers like sheets of different sizes. The SEM
316
image also reveals that the catalyst contains oxygenated matters represented by the bright
317
particles which may be the oxides of metals [36].
318 319 320
12
321 322
Fig. 5. SEM (A–C) and EDX (D) images of calcined Sesamum indicum catalyst.
323 324 325
3.1.6. Elemental analysis
326
The XRF study for the elemental composition of the catalyst was performed and the
327
spectra are shown in Fig. 6. The various peaks in XRF spectra reveal the presence of Na, K,
328
Ca, Mg, Si, Mn, Fe, Zn and Sr as the metallic constituents, and the oxides and carbonates of
329
these are confirmed from the XRD pattern (Fig. 1). The XRF spectra showed a high intense
330
peak for K and Ca and nearly equal intense peak for Si and Mg. From the peak area and
331
intensity of XRF spectra, the higher percentage of K and Ca in the calcined catalyst can be
332
predicted. The SEM-EDX (Fig. 5D) study provides the quantitative composition of the
333
elements and the elemental composition is depicted in Table 1. As that of XRF spectra, the
334
EDX analysis shows that K (29.64 wt. %) and Ca (33.80 wt. %) are the dominant metals
335
followed by Si, Sr and Mg in comparison to other elements present in the catalyst. The AAS
336
analysis (Table 1) of the catalyst also indicated the existence of K (289.26 ppm) at the highest
337
concentration in the calcined Sesamum indicum catalyst followed by Ca (265.32 ppm) and
338
Mg (231.08 ppm). Low levels of Na, Mn, Fe and Zn were observed in the AAS study which 13
339
is in agreement with EDX report. However, some values of concentration of the elements as
340
determined by SEM-EDX and AAS techniques are quite different and not in the similar
341
trend. These differences may be because of employing different analytical tools and
342
procedures. EDX is a qualitative and semi-quantitative technique for detection of elemental
343
distributions. However, AAS is a quantitative tool. It is to be noted that EDX analysis is
344
usually done at different areas or locations of the sample where the elements may not be
345
distributed uniformly for which the concentration of elements detected at a particular area
346
may not be same at different areas of the sample, and this might be the reason for not being in
347
the line with AAS results. Although, the concentrations of K and Ca are not so significantly
348
different in both EDX and AAS analyses, it is not disturbing in obtaining the satisfactory
349
yields of biodiesel. However, the concentrations of some elements determined by the AAS
350
and XPS techniques are almost in the similar trend in the order of K > Ca > Mg > Mn > Fe >
351
Na > Zn (AAS, Table 1) and K > Ca > Mg > Na > Mn > Fe > Zn (XPS, Table 2). The main
352
aim of using these analytical techniques is to determine the alkali elements from the agro-
353
waste ash as expected. Thus, the characterization confirmed the presence of high
354
concentration of K and Ca for which we could successfully utilized the agro-waste ash as a
355
base catalyst in biodiesel synthesis. The higher concentration of K and Ca depicted by XRF,
356
EDX and AAS analyses is accrediting the high basicity of the calcined catalyst which in turn
357
showed higher catalytic activity in biodiesel synthesis. Mendonça et al. [4] reported that
358
higher percentage of alkaline elements in the heterogeneous catalyst derived from waste
359
biomass contribute better catalytic activity in the transesterification reaction of oil to
360
biodiesel. Gohain et al. [16] studied EDX for determination of elemental composition in their
361
catalyst prepared from Musa balbisiana peel and reported higher levels of K (41.37 %)
362
followed by Ca (36.08 %) and Mg (12.02 %) compared to other elements. Chouhan et al. [21]
363
studied a heterogeneous catalyst derived from Lemna perpusilla for biodiesel production and
364
reported higher amount of silica (82.51 %) followed by K (11.32 %) compared to other
365
elements. In most of the heterogeneous catalysts derived from waste biomasses which are
366
reported for biodiesel synthesis, higher concentration of K and Ca in the form of oxides and
367
carbonates are reported resulting in good catalytic activity [1, 5, 12, 23].
14
368 369
Fig. 6. XRF spectra of calcined Sesamum indicum catalyst.
370 371 372 373 374 375 376 15
377
Table 1
378
Elemental composition of calcined Sesamum indicum catalyst. Element
SEM-EDX Analysis
AAS Analysis
Weight (%)
Atomic (%)
Na
1.42
2.33
Concentration (ppm) 6.51
Mg
9.68
15.06
231.08
Si
11.32
15.25
–
K
29.64
28.66
289.26
Ca
33.80
31.89
265.32
Mn
0.80
0.55
21.27
Fe
1.70
1.15
19.74
Zn
0.54
0.31
5.84
Sr
11.09
4.79
–
379 380 381
The surface property of Sesamum indicum catalyst and the 3rd recycled catalyst was
382
determined using XPS study and their full scan and the high-resolution spectra are depicted in
383
Fig. 7. The elemental compositions are presented in Table 2. The XPS analysis confirmed the
384
presence of C, O, Na, K, Ca, Mg, Mn, Zn, Fe, Si, Sr and Cl which agrees with the results of
385
XRD, XRF and EDX studies. The high resolution spectrum of O 1s (Fig. 7B) shows a peak at
386
531.11 eV representing the binding energy of elemental oxygen of oxides present in the
387
catalyst. The spectrum of C 1s (Fig. 7C) shows two peaks at 284.01 eV and 288.05 eV
388
showing the binding energies of sp2 hybridized carbon (C=O) of carbonates [23]. The two
389
peaks in the spectrum of K 2p (Fig. 7D) at the binding energies of 292.22 eV and 294.96 eV
390
may be due to potassium in the form of oxide or carbonate [23]. Two peaks are observed in
391
the spectrum of Ca 2p (Fig. 7E) with binding energies 346.05 eV and 349.52 eV representing
392
the calcium oxide or carbonate present in the catalyst [37]. Furthermore, the Si 2p spectrum
393
(Fig. 7F) with a single peak at the binding energy of 101.6 eV may be due to the oxide of
394
silicone. Comparison of the elemental composition of the ash catalyst reported from various
395
agro-wastes for biodiesel synthesis is summarized in Table 3. In the present work, it is
396
observed that a high amount of K (29.64 %) and Ca (33.8 %) are found in Sesamum indicum
397
ash catalyst followed by Si (11.32 %), Sr (11.09 %) and Mg (9.68 %) along with other
398
elements as minor components. However, it is observed from Table 3 that different ashes
399
obtained from different agro-wastes have different chemical compositions as the quality and 16
400
composition of plant derived ash is mainly dependent on the soil, climatic condition,
401
geographical locations and age of the plants. Further, Table 3 indicates that Sesamum indicum
402
ash catalyst contained higher amounts of K and Ca compared to the ash catalysts of Musa
403
balbisiana underground stem [9], Lemna perpusilla Torrey [21], Acacia nilotica tree stem
404
[24], Camphor tree leaf [38], and uncalcined red banana peduncle [39], and as a result, the
405
present ash catalyst is showing superior catalytic activity for the synthesis of biodiesel.
406 407 408 409 410
17
411 412
Fig. 7. (A) XPS survey spectra of calcined Sesamum indicum catalyst and 3rd recycled
413
catalyst; XPS spectra of (B) O 1s, (C) C 1s, (D) K 2p, (E) Ca 2p and (F) Si 2p.
414 415 416 417 418 18
419
Table 2
420
XPS analysis of surface composition of the catalyst. Elements
Calcined catalyst
O1s K2p Na1s Si2p C1s Ca2p Mg1s Mn2p1 Mn2p3 Fe2p1 Fe2p3 Zn2p1 Zn2p3 Sr3d Cl2p
Atomic (%) 52.53 6.13 0.48 8.33 22.78 5.27 3.08 0.25 – 0.15 0.11 0.1 0.1 0.27 0.43
Recycled catalyst (3rd) Atomic (%) 47.46 1.14 0.14 5.29 33.97 6.21 4.9 0.11 0.04 0.13 0.04 0.06 0.1 0.4 0.01
421 422
19
423
Table 3
424
Comparison of elemental composition of the ash catalyst derived from various agro-wastes. Ash catalyst Present study (EDX) Lemna perpusilla Torrey [21] Acacia nilotica tree stem [24] Acacia nilotica tree stem [24] Musa balbisiana underground stem [9] Musa balbisiana peels [16] Musa paradisiacal peels [14] Camphor tree leaf [38] Red banana peduncle [39] Red banana peduncle [39]
Calcination conditions
Composition (%)
o
550 C, 2 h
Na 1.42
K 29.64
Ca 33.80
Mg 9.68
Al –
Si 11.32
P –
Cl –
Fe 1.70
Mn 0.80
Zn 0.54
Sr 11.09
550 oC, 2 h
0.53
11.32
–
–
–
82.51
–
–
–
–
–
–
500 oC
0.6
6.7
13.3
2.7
8.3
15.7
0.80
–
–
–
–
–
800 oC
5.7
5.7
17.8
4.5
1.2
21.5
0.5
–
–
–
–
–
550 oC, 2 h
0.61 (Na2O)
25.09 (K2O)
10.44 (CaO)
10.04 (MgO)
4.07 (Al2O3)
35.92 (SiO2)
4.47 (P2O5)
–
1.88 (Fe2O3)
–
–
1.89 (SrO)
700 oC, 4 h
10.41
41.37
36.08
12.02
–
–
–
–
–
–
–
–
700 oC, 4 h
–
51.02
–
1.15
0.29
2.51
1.84
6.27
–
–
–
–
800 oC, 2 h
0.23
1.22
12.05
1.82
2.70
–
–
–
–
–
–
–
Uncalcined
–
25.63
–
0.97
–
0.56
0.78
–
–
–
–
–
700 oC, 4 h
–
42.23
1.70
1.39
–
1.54
1.91
–
–
–
–
–
20
425
3.1.7. TEM analysis
426
The structural information of the catalyst was studied by TEM. From the TEM images,
427
various informations about the structure of the catalyst are obtained. The low resolution (100
428
nm) TEM image (Fig. 8A) shows that the particles are in irregular shapes with cylindrical and
429
hexagonal of which the large particles may be the crystallites and smaller particles are metal
430
oxides [40]. The smaller clusters of particles give effective surface area for the catalytic
431
activity of the catalyst. The high resolution TEM images of the catalyst showed the well-
432
ordered porous materials which are shown in Fig. 8B–E. The SAED (Fig. 8F) pattern shows
433
the presence of mixed polycrystalline components in the catalyst. Similarly, a heterogeneous
434
catalyst with polycrystalline nature which is prepared from Eichhornia crassipes plant was
435
also reported in the works of Talukdar et al. [41].
436 437
438 439
Fig. 8. TEM images (A–E) and SAED pattern (F) of calcined Sesamum indicum catalyst.
440 441 442 21
443
3.1.8. Measurement of pH value of the catalyst
444
The variation of pH value with the volume of water dissolving 1 g of calcined Sesamum
445
indicum catalyst is shown in Fig. 9. The pH value was found to be 11.4 when 1 g catalyst is
446
dissolved in 10 mL of distilled water indicating the highly basic nature of the catalyst. With
447
dilution, the pH value of the catalyst changes (Fig. 9) and it is observed that the pH value
448
slightly decreases with dilution up to 60 mL (pH = 10.9). Higher amounts of metals like K
449
and Ca detected through AAS, EDX and XPS analyses are the major factors for the high
450
basic nature of the catalyst that could be potentially utilized for base catalytic
451
transesterification in biodiesel synthesis. Talukdar and Deka [41] successfully utilized a
452
heterogeneous catalyst derived from Eichhornia crassipes in organic transformation reaction
453
and reported the pH value of the catalyst to be 9.6 (1 g in 20 mL water) which is relatively
454
lower compared to the catalyst of this study (pH = 11.3; 1 g in 20 mL).
455 11.4
11.4
11.3
pH value
11.3
11.2
11.2
11.1
11.1
11.0
10.9
10.9 10
456 457 458
20
30
40
50
60
Volume of water (mL) Fig. 9. Variation of pH value with volume of water dissolving 1 g of calcined catalyst.
459 460
3.2. Catalytic activity for transesterification of sunflower oil
461
3.2.1. Effect of catalyst loading
462
The rate of transesterification reaction of triglyceride to biodiesel is greatly influenced by
463
the load of catalyst applied. For the investigation of the effect of catalyst loading on the yield
464
of biodiesel and reaction time, four different catalyst concentrations such as 3, 5, 7 and 9 wt.
465
% of the oil were tested in transesterification of sunflower oil using 12:1 methanol to oil ratio 22
466
at 65 oC and the results are depicted in Fig. 10. It was observed that 7 wt. % of catalyst
467
loading showed considerably better results giving 98.9 % of biodiesel yield in a minimum
468
time period of 40 min which is reasonably shorter reaction time compared to other
469
concentration (loading) of catalyst. On increasing the catalyst concentration from 3 wt. % to 7
470
wt. %, the reaction time decreases from 80 min to 40 min, and the yield of reaction slightly
471
increases. Further, if catalyst loading is increased to 9 wt. %, the time taken for reaction
472
completion is 40 min and no significant increase in biodiesel yield was noticed. Therefore,
473
the catalyst loading of 7 wt. % of the oil was considered as the optimum catalyst
474
concentration for this transesterification reaction. Gohain et al. [16] also reported that an
475
increase of catalyst concentration increases the biodiesel yield to a certain level; however,
476
catalyst loading beyond the optimum level does not increase the biodiesel yield which almost
477
remains unchanged.
478 479 480 Reaction time (min) Yield (%) 98.2
Reaction time (min) and yield (%)
100
98.9
98.6
98.9
90 80
80 70
70 60 50
40
40
40
30 20 10 0 3
481
5
7
9
Catalyst load (wt.%)
482
Fig. 10. Effect of catalyst loading on reaction time and yield of biodiesel. Reaction
483
conditions: reaction temperature = 65 oC and methanol to oil molar ratio = 12:1.
484 485 486 23
487
3.2.2. Effect of methanol to oil molar ratio
488
Like catalyst concentration, the molar ratio of methanol to oil also plays an important role
489
in the rate of transesterification reaction. By varying the methanol to oil ratio such as 3:1, 6:1,
490
9:1, 12:1, 15:1 and 18:1, the reaction time and yield of biodiesel were investigated using
491
optimum catalyst concentration (7 wt. %) at 65 oC and the results are depicted in Fig. 11. It
492
was noticed that the reaction time decreases from 70 min (3:1 molar ratio) to 40 min (12:1
493
molar ratio) and then it remains constant when the methanol ratio is increased beyond 12:1.
494
Similarly, the biodiesel yield increases to a maximum level of 98.9 % in 12:1 molar ratio and
495
no significant increase in yield of biodiesel could be achieved beyond 12:1 molar ratio. It was
496
reported that the rate of reaction decreases at higher methanol concentration due to dilution of
497
oil and flooding of active sites of catalyst leading to reduced interaction in the reaction
498
mixture which leads to a decrease in rate and biodiesel yield [40, 42]. Hence, 12:1 molar ratio
499
of methanol to oil was taken as the optimum condition for the transesterification of sunflower
500
oil to biodiesel in the present study. The biodiesel synthesis using the heterogeneous catalysts
501
investigated by Uprety et al. [8], Vadery et al. [22], Sharma et al. [24] and Wang et al. [40]
502
also reported 12:1 as the optimum molar ratio of methanol to oil.
503 Reaction time (min) Yield (%)
Reaction time (min) and yield (%)
100
97.9
97.2
98.9
98.9
98.2
98.8
90 80 70
70
70
60
55
50 40
40
40
40
30 20 10 0 3:1
504
6:1
9:1
12:1
15:1
18:1
Molar ratio of methanol to oil
505
Fig. 11. Effect of methanol to oil molar ratio on reaction time and yield of biodiesel. Reaction
506
conditions: reaction temperature = 65 oC and catalyst loading = 7 wt. %.
507 24
508
3.2.3. Effect of reaction temperature on biodiesel synthesis
509
To know the effect of temperature, we have also investigated the reaction at different
510
temperatures of 32, 45, 55, 75 and 85 oC using the identical reaction conditions of 12:1
511
methanol to oil ratio and 7 wt. % of catalyst loading, and the results are depicted in Fig. 12. It
512
is observed that there is a significant decrease in the reaction time for completion of the
513
reaction from 140 to 40 min while the temperature is increased from room temperature (32
514
o
515
mention that there is no significant decrease in reaction time while increasing the temperature
516
from 65 to 75 oC and then to 85 oC. Moreover, it is noticed that there is no further increase in
517
biodiesel yield beyond 65 oC. Hence, among the investigated temperatures, better result was
518
found to be at 65 oC with promising catalytic activity and satisfactory yield of biodiesel.
519
Thus, 65 °C is chosen as the optimum reaction temperature for our study.
C) to 65 oC with the biodiesel yields of 97.2 and 98.9 %, respectively. It is noteworthy to
520
Reaction time (min) and yield (%)
150
Reaction time (min)
140
105 100
97.2
98.2
Yield (%)
98.9
98.0
98.8
98.7
75
50
40
35
35
0 32
45
55
65
75
85
o
Temperature ( C)
521 522
Fig. 12. Effect of temperature on the reaction of biodiesel synthesis. Reaction conditions:
523
catalyst loading = 7 wt. % and methanol to oil ratio = 12:1.
524 525
3.3. Comparative study of the catalyst with other reported heterogeneous catalysts in
526
biodiesel synthesis
527
In current study, investigation on the effects of catalyst loading, molar ratio of methanol to
528
oil, and reaction temperature on biodiesel synthesis showed that the optimum reaction
25
529
conditions were 12:1 methanol to oil ratio and 7 wt. % of catalyst load which significantly
530
produced good biodiesel yield (98.9 %) at 65 oC in a reaction time of 40 min only. A
531
comparison of the present catalyst with previously reported heterogeneous base catalysts for
532
the synthesis of biodiesel is briefly summarized in Table 4. It is observed that in the works of
533
Sarma et al. [9], Kumar et al. [10], Aslam et al. [11] and Wang et al. [40], heterogeneous
534
catalysts derived from agricultural wastes were tested for biodiesel synthesis and
535
transesterification reactions were performed at higher temperatures and longer reaction times
536
were reported, but the product yields are comparable to that of the calcined Sesamum indicum
537
catalyst reported in this study (Table 4). On the contrary, Mendonça et al. [4], Deka et al. [5],
538
Uprety et al. [8], Chouhan et al. [21], Gohain et al. [16] and Laskar et al. [35] reported longer
539
reaction times in biodiesel synthesis employing heterogeneous base catalysts derived from
540
waste biomasses, however the product yields are comparable to that of the present catalyst
541
reported herein. It is also noticed that the surface areas reported by Mendonça et al. [4], Deka
542
et al. [5], Kumar et al. [10] and Wang et al. [40] are comparatively smaller to that of
543
Sesamum indicum catalyst which showed a surface area of 3.66 m2 g-1 and this might be the
544
reason for the higher catalytic activity of the present catalyst. In addition to this, the better
545
performance of Sesamum indicum catalyst may be due to its high basic nature (Fig. 7),
546
presence of alkali and alkaline earth metal oxides and carbonates depicted by XRD (Fig. 1)
547
and FT-IR (Fig. 2) spectra and due to higher levels of K and Ca as revealed from XRF, AAS,
548
EDX and XPS analyses which facilitate the active species formation. However, it is observed
549
from Table 3 that the ash catalysts derived from Musa balbisiana underground stem [9],
550
Lemna perpusilla Torrey [21], Acacia nilotica tree stem [24], Camphor tree leaf [38], and
551
uncalcined red banana peduncle ash [39] are exhibiting lower amounts of K and Ca compared
552
to the Sesamum indicum catalyst, and this is the reason for lower catalytic activities in the
553
biodiesel synthesis reported using these catalysts (Table 4). In summary, it is noticeable that
554
under the optimized reaction conditions, the calcined Sesamum indicum catalyst is excellent
555
and superior in terms of reaction time, temperature and biodiesel yield amongst the other
556
catalysts listed in Table 4. The post-harvest Sesamum indicum plants which are normally
557
thrown out as wastes have no economic value. The raw materials for the preparation of
558
catalyst are readily available and these can be obtained with nominal cost. The process for
559
preparation of catalyst from waste material is found to be easy with minimum cost which is
560
carrying the major advantage for reducing the cost of biodiesel production. It is noteworthy to
561
mention that the prepared catalyst is easy to handle, non-corrosive, renewable, green and
562
environmental friendly. 26
563 564
Table 4
565
Comparison of activity of catalyst derived from waste Sesamum indicum plant with other
566
reported heterogeneous catalyst in biodiesel synthesis.
Biodiesel feed stock
Catalyst source
Surface area
Met/Oil ratio
(m2 g-1)
Parameter Catalyst (wt. %)
Temp (oC)
Time (min)
References Y or C (%)
Sunflower oil
Sesamum indicum
3.66
12:1
7
65
40
98.9 (Y)
This work
Soybean oil
Astrocaryum aculeatum
1.0
15:1
1
80
240
97.3 (C)
[4]
Thevetia peruviana oil
Musa balbisiana
1.487
10:1
20
32
180
96 (Y)
[5]
Palm oil
Birch bark
–
12:1
3
60
180
69.7 (C)
[8]
Jatropha curcas oil
Musa balbisiana underground stem
39
9:1
5
275
60
98 (Y)
[9]
Jatropha curcas oil
SrO-Musa Balbisiana underground stem
0.043
9:1
5
200
60
96 (Y)
[10]
Mesua ferrea oil
Musa balbisiana underground stem
38.71
9:1
5
275
60
95 (C)
[11]
Waste cooking oil
Musa balbisiana peel
10.176
6:1
2
60
180
100 (C)
[16]
Jatropha curcas oil
Lemna perpusilla
9.622
9:1
5
65
300
89.43 (Y)
[21]
Jatropha curcas oil
Acacia nilotica tree
3.72
12:1
5
65
180
98 (C)
[24]
27
stem Soybean oil
Snail shell
7
6:1
3
28
420
98 (Y)
[35]
Soybean oil
K2CO3Camphor tree ash
–
14:1
5
65
210
92 (Y)
[38]
Jatropha curcas oil
K2CO3Wood ash
12
12:1
5
65
180
99 (C)
[24]
Jatropha curcas oil
CaCO3Wood ash
14
12:1
5
65
180
91.7 (C)
[24]
Rapeseed oil
Gasified straw slag
1.266
12:1
20
200
480
95 (C)
[40]
Met–Methanol; Temp–Temperature; min–minute; Y–Yield; C–Conversion. 567 568 569
3.4. Study of the catalyst reusability
570
The heterogeneous catalysts have the major advantages and important property that they
571
can be reused for the subsequent cycle of reactions [3, 4]. Accordingly, in this study, the
572
reusability test was investigated under the optimum reaction conditions. The reaction mixture
573
after completion of the first transesterification reaction was filtered using vacuum pump to
574
separate the catalyst. The filtered catalyst was washed several times with petroleum ether
575
followed by acetone for residual removal of the product and glycerol. The washed catalyst
576
taken in a silica crucible was kept in a hot air oven at 110 oC for 4 h. The dried catalyst was
577
cooled in a desiccator, and in the subsequent reaction, the reactants are taken with respect to
578
the catalyst obtained after each reaction cycle. From the study, it was found that the catalyst
579
could be reusable up to the 3rd cycle of reaction with a good catalytic activity and the yields
580
of biodiesel achieved with the fresh catalyst, 1st, 2nd, and 3rd recycled catalysts were 98.9,
581
97.1, 96.1, and 94.2 % in the reaction times of 40, 85, 125, and 165 min, respectively. These
582
results specify that the catalytic activity of the Sesamum indicum catalyst is decreased
583
gradually after every subsequent reaction cycle and this is due to loss of catalyst during its
584
recovery process. This is in line with the results reported by Deka et al. [5], Sarma et al. [9]
585
and Gohain et al. [16]. Further, XPS analysis of the calcined catalyst and 3rd recycled catalyst
586
showed the substantial leaching of K and oxygen concentration from 6.13 % to 1.14 %, and
587
52.53 % to 47.46 %, respectively and also confirmed the little loss of Na and Si in the 28
588
recycled catalyst (Fig. 7, Table 2). The XPS study clearly indicated that potassium oxide due
589
to its high basicity played the main role in the transesterification of sunflower oil to biodiesel.
590
Other metal oxides and carbonates, to some extent, are also contributing to the catalytic
591
activity which is confirmed with the leaching of metals (K, Na and Si). The loss and leaching
592
of these components in the recycled catalyst results in reduced active sites of the catalyst
593
which in turn decreases the catalytic activity [16]. Further, during repeated use of the catalyst
594
in the reaction, there is a potential chance of agglomeration of ester and glycerol molecules
595
over the surface of catalyst in which the active sites of catalyst would be blocked resulting to
596
a reduced conversion of biodiesel [23].
597 598
3.5. FT-IR and NMR analyses of biodiesel
599
The C=O stretching vibration at 1745 cm-1 of sunflower oil (Fig. 13) changes to 1741 cm-1
600
in biodiesel (Fig. 14) and this predicts the conversion of oil to biodiesel due to change from
601
glyceride linkage in triglyceride to methyl esters. The peaks at 3006 cm-1 (Fig. 13) and 3007
602
cm-1 (Fig. 14) are due to =C-H (–CH=CH–) stretching frequencies present in triglyceride and
603
methyl ester molecules. The weak peak at 1657 cm-1 in both the IR spectra indicates the
604
stretching frequency of C=C present in both the molecules. The signals at 2855 cm-1 and 2927
605
cm-1 (Fig. 13), and signals at 2850 cm-1 and 2923 cm-1 (Fig. 14) are because of C-H stretching
606
vibrations. The IR peaks at 1463 and 1370 cm-1 (Fig. 13) and peaks at 1462, 1435 and 1361
607
cm-1 (Fig. 14) are due to CH3 bending vibrations. The C-O stretching bands of triglycerides
608
are observed at 1242, 1167, and 1106 cm-1 and that of methyl esters are seen at 1167 and
609
1013 cm-1. The IR band at 725 cm-1 in both the spectra is due to –CH2– rocking of the long
610
fatty acid chain.
611 612
29
80
Transmittance (%)
75 70 65
7 56 1
87 43
36 4 1 2 4 7 21 61 1
60 60 0 3
55
52 7
0 73 1 6 01 1
50 45 40 4000
72 9 2
3500
3000
54 71
5 58 2
2500
2000
1500
1000
500
0
500
0
-1
Wavenumber (cm )
613
Fig. 13. FT-IR spectrum of sunflower oil.
614 615 616
Transmittance (%)
80
60
7 5 61
6 4 43
0 78
40
1 63 1
20 70 0 3 32 92
0
4000
3 10 1
3500
3000
05 82
14 7 1
2500
2000
26 4 1
1500
52 7
5 3 7 41 6 11
1000
-1
617 618
Wavenumber (cm ) Fig. 14. FT-IR spectrum of biodiesel obtained from sunflower oil.
619 620
30
621
The 1H NMR (Fig. 15 and Fig. 16) and 13C NMR (Fig. 17 and Fig. 18) spectral analyses of
622
the sunflower oil and biodiesel clearly showed the major differences in the signals which
623
indicated the conversion of oil to its biodiesel. It is observed that the signals at δ 4.11–4.15
624
(dd, 3J = 6, 12 Hz) ppm and δ 4.28–4.32 (dd, 3J = 4, 12 Hz) ppm in the 1H NMR spectrum of
625
oil (Fig. 15) representing the protons of the glycerol moiety of the glyceride is disappearing
626
in the 1H NMR spectrum of biodiesel (Fig. 16) and new a singlet signal at δ 3.65 ppm is seen
627
due to methoxy protons (-CO-OCH3) which indicated the formation of methyl esters
628
(biodiesel). Similarly, the signals at δ 61.96 ppm and δ 68.83 ppm in the 13C NMR spectrum
629
of oil (Fig. 17) due to the methylene and methine carbons of the glycerine moiety are not
630
observed in the
631
signal at δ 51.28 ppm due to methoxy carbon (OCH3) of the methyl esters which confirmed
632
the conversion of oil to biodiesel. The signals at δ 5.25–5.38 ppm in 1H NMR spectrum of oil
633
and the signals at δ 5.31–5.38 ppm in the 1H NMR spectrum of biodiesel showed the olefinic
634
protons (-CH=CH-). On the other hand, the signals at δ 127.81–129.97 ppm in
635
spectrum of oil and signals at δ 127.80–129.99 ppm in the
636
indicated the olefinic carbons present in the oil and biodiesel. The signals at δ 2.74–2.77 ppm
637
(t, 3J=6.2) in 1H NMR spectrum of oil and at δ 2.75–2.78 ppm (t, 3J= 6.2) in 1H NMR
638
spectrum of biodiesel are due to bis-allylic protons (-C=C-CH2-C=C-) of the unsaturated
639
fatty acid chains present in oil and biodiesel. The α-methylene protons to ester (-CH2-CO2R)
640
of the oil and biodiesel are represented by the signals at δ 2.28–2.31 ppm (t, 3J = 7.4) and
641
signals at δ 2.27–2.31 ppm (t, 3J = 7.6), respectively. The α-methylene protons to double
642
bond (-CH2-C=C-) is seen at signals δ 2.001–2.07 ppm (Fig. 15) and at signals δ 1.985–2.071
643
ppm (Fig. 16). The signals at δ 1.608 ppm (Fig. 15) and δ 1.59–1.63 ppm (Fig. 16) represent
644
the β-methylene protons to ester (-CH2-C-CO2R) of oil and biodiesel, respectively. The
645
protons of backbone methylenes of the long fatty acid chain of oil and biodiesel are seen at
646
signals δ 1.25–1.38 ppm (Fig. 15) and at δ 1.26–1.39 ppm (Fig. 16), respectively. The signals
647
at δ 0.861–0.905 ppm (Fig. 15) and δ 0.862–0.905 ppm (Fig. 16) are due to the terminal
648
methyl protons. In 13C NMR study, the signals at δ 172.51, 172.89 and 172.92 ppm (Fig. 17),
649
and δ 174.19 ppm (Fig. 18) represent the carbonyl carbon of the triglyceride and biodiesel,
650
respectively. The signals at δ 14.003–34.05 ppm and δ 13.911–33.94 ppm are indicating the
651
methylene and methyl carbons of fatty acid moiety of the oil and biodiesel, respectively.
13
C NMR spectrum of biodiesel (Fig. 18) and there is appearance of a new
652
31
13
13
C NMR
C NMR spectrum of biodiesel
5.379 5.370 5.355 5.352 5.343 5.338 5.328 5.313 5.301 5.297 5.285 5.279 5.264 5.253 5.250 4.323 4.313 4.293 4.283 4.157 4.142 4.127 4.112 2.778 2.762 2.747 2.318 2.300 2.281 2.070 2.054 2.037 2.019 2.001 1.608 1.389 1.369 1.305 1.303 1.283 1.268 1.259 0.905 0.888 0.879 0.871 0.861 NAME EXPNO PROCNO Date_ Time INSTRUM PROBHD PULPROG TD SOLVENT NS DS SWH FIDRES AQ RG DW DE TE D1 TD0
1H FO-1 1 1 20180508 14.39 spect 5 mm BBO BB-1H zg 131072 CDCl3 8 0 20000.000 0.152588 3.2768500 4.5 25.000 6.00 300.0 1.00000000 1
Hz Hz sec usec usec K sec
653 654
12
11
10
9
8
7
6
5
4
1
3
2
1.39
1.01 8.22
1.00 1.73
0.59
0.66
1.53
======== CHANNEL f1 ======== NUC1 1H P1 11.50 usec PL1 -1.00 dB SFO1 400.1310305 MHz SI 65536 SF 400.1299795 MHz WDW EM SSB 0 LB 0.50 Hz GB 0 PC 1.00
1
Fig. 15. H NMR spectrum of sunflower oil.
32
0 ppm
5.376 5.361 5.359 5.349 5.343 5.333 5.318 3.653 2.782 2.766 2.751 2.316 2.297 2.278 2.071 2.056 2.039 2.018 2.002 1.985 1.632 1.616 1.599 1.390 1.371 1.304 1.269 NAME EXPNO PROCNO Date_ Time INSTRUM PROBHD PULPROG TD SOLVENT NS DS SWH FIDRES AQ RG DW DE TE D1 TD0
1H FP-1 1 1 20180508 14.36 spect 5 mm BBO BB-1H zg 131072 CDCl3 8 0 20000.000 0.152588 3.2768500 4.5 25.000 6.00 300.0 1.00000000 1
Hz Hz sec usec usec K sec
655 656
12
11
10
9
8
7
6
5
4
1
3
2
1.07
6.59
1.01
0.99
0.87
0.28
1.00
0.68
======== CHANNEL f1 ======== NUC1 1H P1 11.50 usec PL1 -1.00 dB SFO1 400.1310305 MHz SI 65536 SF 400.1299712 MHz WDW EM SSB 0 LB 0.50 Hz GB 0 PC 1.00
1
0 ppm
Fig. 16. H NMR spectrum of biodiesel obtained from sunflower oil.
657 658
33
172.928 172.895 172.513 129.976 129.833 129.782 129.759 129.559 129.536 127.986 127.970 127.813 77.472 77.151 76.832 68.831 61.964 34.050 33.882 31.898 31.876 31.479 30.374 29.723 29.684 29.651 29.600 29.554 29.502 29.453 29.352 29.305 29.280 29.134 29.059 29.022 28.983 27.150 27.123 27.004 25.556 24.792 24.767 22.650 22.540 14.046 14.003 NAME EXPNO PROCNO Date_ Time INSTRUM PROBHD PULPROG TD SOLVENT NS DS SWH FIDRES AQ RG DW DE TE D1 D11 TD0
13C FO-1 1 1 20180508 15.04 spect 5 mm BBO BB-1H zgpg 66560 CDCl3 252 0 40760.871 0.612393 0.8165193 362 12.267 6.00 300.0 5.00000000 0.03000000 1
Hz Hz sec usec usec K sec sec
======== CHANNEL f1 ======== NUC1 13C P1 7.00 usec PL1 0.00 dB SFO1 100.6208180 MHz ======== CHANNEL f2 ======== CPDPRG2 waltz16 NUC2 1H PCPD2 80.00 usec PL2 -1.00 dB PL12 16.00 dB PL13 20.00 dB SFO2 400.1320007 MHz SI 32768 SF 100.6127690 MHz WDW EM SSB 0 LB 0.50 Hz GB 0 PC 1.40
659 660
200
180
160
140
120
100
80
60
13
40
20
Fig. 17. C NMR spectrum of sunflower oil.
661 662 663
34
0
ppm
174.196 129.991 129.830 129.584 127.927 127.802 86.299 77.442 77.124 76.804 51.286 33.940 33.906 32.544 31.839 31.714 31.442 31.364 29.684 29.632 29.590 29.528 29.501 29.456 29.391 29.303 29.265 29.245 29.195 29.081 29.034 29.005 28.920 28.859 28.837 27.103 27.079 27.054 25.519 24.831 24.770 22.605 22.491 22.452 13.997 13.949 13.911 NAME EXPNO PROCNO Date_ Time INSTRUM PROBHD PULPROG TD SOLVENT NS DS SWH FIDRES AQ RG DW DE TE D1 D11 TD0
13C FP-1 1 1 20180508 14.35 spect 5 mm BBO BB-1H zgpg 66560 CDCl3 310 0 40760.871 0.612393 0.8165193 362 12.267 6.00 300.0 5.00000000 0.03000000 1
Hz Hz sec usec usec K sec sec
======== CHANNEL f1 ======== NUC1 13C P1 7.00 usec PL1 0.00 dB SFO1 100.6208180 MHz ======== CHANNEL f2 ======== CPDPRG2 waltz16 NUC2 1H PCPD2 80.00 usec PL2 -1.00 dB PL12 16.00 dB PL13 20.00 dB SFO2 400.1320007 MHz SI 32768 SF 100.6127690 MHz WDW EM SSB 0 LB 0.50 Hz GB 0 PC 1.40
664 665
200
180
160
140
120
100
80
60
40
20
0
ppm
Fig. 18. 13C NMR spectrum of biodiesel obtained from sunflower oil.
666 667 668
3.6. GC-MS analysis of biodiesel
669
The chemical composition of biodiesel was analyzed by GC-MS study. The library search
670
with S/W Turbomass NIST 2008 software revealed the presence of ten different fatty acid
671
methyl esters (FAMEs) in the sunflower biodiesel (Table 5). The mixture is composed of
672
both saturated and unsaturated FAME. The predominant methyl ester present is found to be
673
methyl linoleate (68.72 %), an unsaturated fatty acid ester followed by methyl palmitate
674
(11.25 %) which is a saturated fatty acid ester. The other saturated FAMEs are methyl
675
myristate, methyl stearate, methyl arachidate, methyl behenate, and methyl lignocerate. Other
676
unsaturated fatty acid esters such as methyl oleate, methyl gondoate and methyl erucate were
677
also detected in the study.
678 679 680 681 35
682
Table 5
683
GC-MS analysis of chemical composition of biodiesel. FAME
Composition (%)
Methyl myristate (C14:0)
0.29
Methyl palmitate (C16:0)
11.25
Methyl linoleate (C18:2)
68.72
Methyl oleate (C18:1)
4.40
Methyl stearate (C18:0)
1.59
Methyl gondoate (C20:1)
3.24
Methyl arachidate (C20:0)
1.47
Methyl erucate (C22:1)
3.08
Methyl behenate (C22:0)
4.93
Methyl lignocerate (C24:0)
0.95
684 685 686
3.7. Study of properties of produced biodiesel
687
The fuel properties of sunflower biodiesel and standard values for biodiesel prescribed by
688
ASTM D6751 along with fuel properties of other reported biodiesel prepared from agro-
689
waste base catalysts are listed in Table 6 for comparison. The density at 15 oC of sunflower
690
biodiesel is found to be 0.859 g cm-3 which is comparable to the values of other reported
691
biodiesel properties (Table 6), and the specific gravity of biodiesel is 0.854. The viscosity of
692
the biodiesel must be low for good combustibility and non-deposition in the engine [5].
693
Accordingly, the kinematic viscosity of biodiesel was found to be 3.11, which is well within
694
the standard limit as prescribed by ASTM D6751, and is lower compared to the values 4.3,
695
4.33 and 4.75 reported by Odude et al. [7], Deka et al. [5] and Kumar et al. [10], respectively.
696
The cetane number of the biodiesel is found to be 53.95, which is higher than the minimum
697
value prescribed in ASTM D6751, and also higher than the reported biodiesel results of
698
Jatropha oil [9], and soybean oil [43] indicating the good ignition and combustion quality of
699
the biodiesel. There is no specification found about the saponification number in the ASTM
700
D6751 standard. The saponification number (SN) indicates the number of saponifiable unit
701
present per unit weight of the biodiesel [44], and the SN (mg KOH/g) found in this study is
702
188.57. The pour point and cold filter plugging point were found to be -6 oC and -3 oC,
703
respectively. The API, diesel index and aniline point of the biodiesel are 34.277, 50.82, and
36
704
148.27, respectively. The total sulphur detected was 3 ppm which is well below the
705
maximum limits given in the international standards. The higher heating value (HHV) of the
706
biodiesel was found to be 39.79 MJ/kg which is comparable with 39.25, 40.20, 44.986, 43.19,
707
and 40.37 MJ/kg as reported by Sarma et al. [9], Gohain et al. [16], Deka et al. [5], Betiku et
708
al. [13], and Nath et al. [45].
709 710 711
Table 6
712
Comparison of properties of produced biodiesel with ASTM D6751 and reported biodiesel
713
properties.
Properties
0.875
Waste cooking oil [16] 0.89
Reported biodiesel Thevetia Palm oil peruviana [7] oil [5] 0.875 0.86
Bauhinia monandra oil [13] 0.876
0.885
0.86–0.90 1.9–6.0
0.875 5.7
– 3.12
– 4.33
0.86 4.3
0.876 4.90
0.885 4.9
53.95 188.57
47 (min) NS
48.6 –
55 –
61.5 –
76.93 –
59.83 –
50 –
-6
NS
3
-9
+3
-6
0
0
CFPP ( C)
-3
NS
–
–
+6
–
–
–
API
34.277
36.95
0.875
–
–
32.42
30.03
–
Diesel index
50.82
50.4
–
–
–
92.95
69.21
–
Aniline point
148.27
331
–
–
–
–
–
–
Total sulphur (ppm) HHV (MJ/kg)
3
15 (max)
9
–
–
–
–
–
39.79
NS
39.25
40.20
44.986
–
43.19
–
Density (15 oC, g/cm3) Specific gravity Kinematic viscosity (40 oC, mm2/s) Cetane number Saponification number (mg KOH/g) Pour point (oC) o
Biodiesel (This work)
ASTM D6751
0.859
NS
0.854 3.11
Jatropha oil [9]
Soybean oil [43]
NS–Not specified; min– minimum; max– maximum; CFPP–Cold filter plugging point; API–American petroleum index; HHV–Higher heating value.
714 715 716
4. Conclusions
717
In this study, we have reported a renewable heterogeneous base catalyst derived from
718
waste Sesamum indicum plant for efficient biodiesel synthesis. Characterization of catalyst
719
confirms the well-ordered porous materials polycrystalline in nature. Moreover, the presence
720
of high amounts of K and Ca in the form of oxides and carbonates in the catalyst are 37
721
confirmed that plays a key role in the high catalytic activity for transesterification of
722
sunflower oil into biodiesel. The catalyst yielded 98.9 % of biodiesel under the optimized
723
conditions of 12:1 methanol to oil ratio and 7 wt. % of catalyst loading at 65 oC in a reaction
724
time of 40 min, and was found to be reusable with good catalytic activity. The raw materials
725
for the preparation of this catalyst are readily available, and the cost of catalyst depends
726
mainly on the energy spent for its production which may be considered very nominal. Thus,
727
this catalyst has the advantage for reducing the cost of biodiesel production. Since the
728
catalyst is derived from biodegradable raw materials, it is non-corrosive, easy to handle, and
729
green catalyst. In addition, large scale disposal of this catalyst after use would not produce
730
any potential harm to the environment and society as well. Moreover, utilization of the wastes
731
in a convenient way to the benefit of mankind as a part of waste management is highly
732
encouraged and thus the present catalyst which is a highly efficient green catalyst can be
733
recommended as a potential candidate for biodiesel production at industrial scale in a cost-
734
effective manner.
735 736
Acknowledgments
737
The authors are thankful to SAIF, Gauhati University, India for XRF analysis, SAIC, Tezpur
738
University, India for XRD, SEM, and AAS analyses, CSIR-NEIST, Jorhat, India for TGA
739
and XPS analyses, SAIF, NEHU, India for NMR and TEM analyses, Bholanath College,
740
Dhubri, India for FT-IR analysis, Biotech Park, Guwahati, India for GC-MS analysis and
741
IOCL, Bongaigaon refinery, India for testing fuel properties of biodiesel.
742 743
References
744
[1]
Basumatary S, Nath B, Kalita P. Application of agro-waste derived materials as
745
heterogeneous base catalysts for biodiesel synthesis. J Renew Sustain Energy
746
2018;10(4):043105.
747
[2]
Banković–Ilić IB, Miladinović MR, Stamenković OS, Veljković VB. Application of
748
nano CaO–based catalysts in biodiesel synthesis. Renew Sustain Energy Rev
749
2017;72:746–60.
750
[3]
rice husk ash-based catalysts. Fuel Process Technol 2015;133:8–13.
751 752 753
Chen GY, Shan R, Shi JF, Yan BB. Transesterification of palm oil to biodiesel using
[4]
Mendonça IM, Paes OA, Maia PJ, Souza MP, Almeida RA, Silva CC, Duvoisin S, Freitas FA. New heterogeneous catalyst for biodiesel production from waste tucumã
38
754
peels (Astrocaryum aculeatum Meyer): Parameters optimization study. Renew Energy
755
2019;130:103–10.
756
[5]
peruviana) seed oil. Biomass Bioenergy 2011;35:1797–803.
757 758
Deka DC, Basumatary S. High quality biodiesel from yellow oleander (Thevetia
[6]
Subramaniam D, Murugesan A, Avinash A. Performance and emission evaluation of
759
biodiesel fuelled diesel engine abetted with exhaust gas recirculation and Ni-coated
760
catalytic converter. J Renew Sustain Energy 2013;5(2):023138.
761
[7]
Odude VO, Adesina AJ, Oyetunde OO, Adeyemi OO, Ishola NB, Etim AO, Betiku E.
762
Application of agricultural waste-based catalysts to transesterification of esterified palm
763
kernel oil into biodiesel: A case of banana fruit peel versus cocoa pod husk. Waste
764
Biomass Valor 2019;10:877–88.
765
[8]
Uprety BK, Chaiwong W, Ewelike C, Rakshit SK. Biodiesel production using
766
heterogeneous catalysts including wood ash and the importance of enhancing by
767
product glycerol purity. Energy Convers Manage 2016;115:191–9.
768
[9]
Sarma AK, Kumar P, Aslam M, Chouhan AP. Preparation and characterization of Musa
769
balbisiana Colla underground stem nano-material for biodiesel production under
770
elevated conditions. Catal Lett 2014;144:1344–53.
771
[10] Kumar P, Sarma AK, Bansal A, Jha MK. Formulation of SrO-MBCUS agglomerates
772
for esterification and transesterification of high FFA vegetable oil. Bull Chem React
773
Eng Catal 2016;11(2):140–50.
774 775
[11] Aslam M, Saxena P, Sarma AK. Green technology for biodiesel production from Mesua ferrea L. seed oil. Energy Environ Res 2014;4(2):11.
776
[12] Betiku E, Ajala SO. Modelling and optimization of Thevetia peruviana (yellow
777
oleander) oil biodiesel synthesis via Musa paradisiacal (plantain) peels as
778
heterogeneous base catalyst: A case of artificial neural network vs. response surface
779
methodology. Ind Crops Prod 2014;53:314–22.
780
[13] Betiku E, Akintunde AM, Ojumu TV. Banana peels as a biobase catalyst for fatty acid
781
methyl esters production using Napoleon's plume (Bauhinia monandra) seed oil: A
782
process parameters optimization study. Energy 2016;103:797–806.
783
[14] Etim AO, Betiku E, Ajala SO, Olaniyi PJ, Ojumu TV. Potential of ripe plantain fruit
784
peels as an ecofriendly catalyst for biodiesel synthesis: Optimization by artificial neural
785
network integrated with genetic algorithm. Sustainability 2018;10(3):707.
39
786
[15] Betiku E, Etim AO, Pereao O, Ojumu TV. Two-step conversion of neem (Azadirachta
787
indica) seed oil into fatty methyl esters using a heterogeneous biomass-based catalyst:
788
An example of cocoa pod husk. Energy Fuels 2017;31(6):6182–93.
789 790 791 792 793 794
[16] Gohain M, Devi A, Deka D. Musa balbisiana Colla peel as highly effective renewable heterogeneous base catalyst for biodiesel production. Ind Crops Prod 2017;109:8–18. [17] Muniyappa PR, Brammer SC, Noureddini H. Improved conversion of plant oils and animal fats into biodiesel and co-product. Bioresour Technol 1996;56:19–24. [18] Canacki M, Gerpen JV. Biodiesel production via acid catalysis. Trans ASAE. 1999;42(5):1203–10.
795
[19] Sandoval G, Casas-Godoy L, Bonet-Ragel K, Rodrigues J, Ferreira-Dias S, Valero F.
796
Enzyme-catalyzed production of biodiesel as alternative to chemical-catalyzed
797
processes: Advantages and constraints. Current Biochem Eng 2017;4(2):109–41.
798 799
[20] Chen X, Qian WW, Lu XP, Han PF. Preparation of biodiesel catalysed by KF/CaO with ultrasound. Nat Prod Res 2012;26(13):1249–56.
800
[21] Chouhan AP, Sarma AK. Biodiesel production from Jatropha curcas L. oil using
801
Lemna perpusilla Torrey ash as heterogeneous catalyst. Biomass Bioenergy
802
2013;55:386–9.
803
[22] Vadery V, Narayanan BN, Ramakrishnan RM, Cherikkallinmel SK, Sugunan S,
804
Narayanan DP, Sasidharan S. Room temperature production of jatropha biodiesel over
805
coconut husk ash. Energy 2014;70:588–94.
806
[23] Pathak G, Das D, Rajkumari K, Rokhum L. Exploiting waste: Towards a sustainable
807
production of biodiesel using Musa acuminata peel ash as a heterogeneous catalyst.
808
Green Chem 2018;20(10):2365–73.
809 810 811 812 813 814
[24] Sharma M, Khan AA, Puri SK, Tuli DK. Wood ash as a potential heterogeneous catalyst for biodiesel synthesis. Biomass Bioenergy 2012;41:94–106. [25] Miraj S, Kiani S. Bioactivity of Sesamum indicum: A review study. Der Pharmacia Lett 2016;8(6):328-34. [26] Shah NC. Sesamum indicum (sesame or til): Seeds and oil – An historical and scientific evaluation from Indian perspective. Indian J Hist Sci 2013;48(2);151–174.
815
[27] Gouveia LAV, Cardoso CA, Oliveira JMF, Rosa G, Moreira ASB. Effects of the intake
816
of sesame seeds (Sesamum indicum L.) and derivatives on oxidative stress: A
817
systematic review. J Med Food 2016;19(4):337–45.
818 819
[28] Prasad MNN, Sanjay KR, Prasad DS, Vijay N, Kothari R, Swamy SN. A review on nutritional and nutraceutical properties of sesame. J Nutr Food Sci 2012;2:127. 40
820
[29] Adepoju TF, Olatunbosun BE, Olatunji OM, Ibeh MA. Brette pearl spar mable
821
(BPSM): A potential recoverable catalyst as a renewable source of biodiesel from
822
Thevetia peruviana seed oil for the benefit of sustainable development in West Africa.
823
Energy Sustain Soc 2018;8(1):23.
824 825
[30] Kalayasiri P, Narumon J, Krisnangkura K. Survey of seed oils for use as diesel fuels. J Am Oil Chem Soc 1996;73:471–4.
826
[31] Kumar D, Kim SM, Ali A. Solvent-free one step aminolysis and alcoholysis of low-
827
quality triglycerides using sodium modified CaO nanoparticles as a solid catalyst. RSC
828
Adv 2016;6(61):55800–8.
829
[32] Jin H, Kolar P, Peretti SW, Osborne JA, Cheng JJ. Kinetics and mechanism of NaOH-
830
impregnated calcined oyster shell-catalyzed transesterification of soybean oil. Energies
831
2017;10(11):1920.
832
[33] Ho WW, Ng HK, Gan S. Development and characterisation of novel heterogeneous
833
palm oil mill boiler ash-based catalysts for biodiesel production. Bioresour Technol
834
2012;125:158–64.
835
[34] Kumar D, Kuk H, Ali A. One-pot solvent-free synthesis of fatty acid alkanoamides
836
from natural oil triglycerides using alkali metal doped CaO nanoparticles as
837
heterogeneous catalyst. J Ind Eng Chem 2016;38:43–9.
838
[35] Laskar IB, Rajkumari K, Gupta R, Chatterjee S, Paul B, Rokhum L. Waste snail shell
839
derived heterogeneous catalyst for biodiesel production by the transesterification of
840
soybean oil. RSC Adv 2018;8:20131–42.
841 842 843 844
[36] Kumar KV, Azhagurajan A, Stephen VK. Synthesis of rice husk nano-particles for biodiesel production. J Chem Pharm Sci 2016;9(4):2671–73. [37] Zhao C, Yang L, Xing S, Luo W, Wang Z, Lv P. Biodiesel production by a highly effective renewable catalyst from pyrolytic rice husk. J Clean Prod 2018;199:772–80.
845
[38] Li C, Hu X, Feng W, Wu B, and Wu K. A supported solid base catalyst synthesized
846
from green biomass ash for biodiesel production. Energy Sources, Part A
847
2018;40(2):142–7.
848
[39] Balajii M, Niju S. A novel biobased heterogeneous catalyst derived from Musa
849
acuminata peduncle for biodiesel production–Process optimization using central
850
composite design. Energy Convers Manage 2019;189:118–31.
851
[40] Wang J, Xing S, Huang Y, Fan P, Fu J, Yang G, Yang L, Lv P. Highly stable gasified
852
straw slag as a novel solid base catalyst for the effective synthesis of biodiesel:
853
Characteristics and performance. Appl Energy 2017;190:703–12. 41
854
[41] Talukdar A, Deka DC. Preparation and characterization of a heterogeneous catalyst
855
from water hyacinth (Eichhornia crassipes): Catalytic application in the synthesis of bis
856
(indolyl) methanes and bis (pyrrolyl) methanes under solvent free condition. Current
857
Catal 2016;5(1):51–65.
858
[42] Syazwani ON, Rashid U, Yap YH. Low-cost solid catalyst derived from waste
859
Cyrtopleura costata (angel wing shell) for biodiesel production using microalgae oil.
860
Energy Convers Manage 2015;101:749–56.
861
[43] Ofori-Boateng C, Lee KT. The potential of using cocoa pod husks as green solid base
862
catalysts for the transesterification of soybean oil into biodiesel: Effects of biodiesel on
863
engine performance. Chem Eng J 2013;220:395–401.
864
[44] Ismail SA, Ali RF. Physico-chemical properties of biodiesel manufactured from waste
865
frying oil using domestic adsorbents. Sci Technol Adv Mater 2015;16(3):034602.
866
[45] Nath B, Das B, Kalita P, Basumatary S. Waste to value addition: Utilization of waste
867
Brassica nigra plant derived novel green heterogeneous base catalyst for effective
868
synthesis of biodiesel. J Clean Prod 2019.
869
Doi: https://doi.org/10.1016/j.jclepro.2019.118112.
870 871 872
42