Subscriber access provided by READING UNIV
Article
Correlating the Cloud Point of Biodiesel to the Concentration and Melting Properties of the Component Fatty Acid Methyl Esters (FAME) Robert O. Dunn Energy Fuels, Just Accepted Manuscript • DOI: 10.1021/acs.energyfuels.7b02935 • Publication Date (Web): 11 Dec 2017 Downloaded from http://pubs.acs.org on December 30, 2017
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Energy & Fuels is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28
Energy & Fuels
Correlating the Cloud Point of Biodiesel to the Concentration and Melting Properties of the Component Fatty Acid Methyl Esters (FAME) Robert O. Dunn* Bio-Oils Research, United States Department of Agriculture, Agricultural Research Service, National Center for Agricultural Utilization Research, 1815 N. University St., Peoria, Illinois 61604, United States *Chemical Engineer; Voice: 309-681-6101; Fax: 309-681-6524; E-mail:
[email protected]. Mention of trade names or commercial products in this publication is solely for the purpose of providing specific information and does not imply recommendation or endorsement by the U.S. Department of Agriculture. USDA is an equal opportunity provider and employer. The author declares no competing financial interest.
KEYWORDS: Cold Flow Properties, Enthalpy of Fusion, Melting Point, Solid-Liquid Equilibrium Properties of neat biodiesel fuels, six empirical cloud point correlation models from the literature, validation tests for Dunn (1997) and Davis models, melting properties of fatty acid methyl esters, example calculation of solid-liquid equilibrium transition temperature of palm oilfatty acid methyl ester biodiesel and melting properties of free fatty acids in canola oil- and palm oil-fatty acid methyl esters supplied as Supplemental Information.
ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
29
ABSTRACT: Biodiesel is a renewable alternative diesel fuel made from plant oils and animal
30
fats. In the form of fatty acid methyl esters (FAME), it is usually obtained by transesterification
31
of plant oil or animal fat with methanol in the presence of catalyst. Most of the fuel properties of
32
biodiesel compare well with conventional diesel fuel (petrodiesel). One major disadvantage of
33
biodiesel is its relatively poor cold flow properties which must be monitored during cold weather
34
in moderate temperature climates. Two correlation models were developed to accurately
35
calculate the cloud point (CP) of biodiesel. Both models were developed using measured CP
36
data from binary admixtures of biodiesel fuels made from canola, palm and soybean oils and
37
yellow grease (CaME, PME, SME and YGME). One model was based on solid-liquid
38
equilibrium (SLE) thermodynamics in organic mixtures. This model required fatty acid
39
concentrations (FA Profile) and melting point (MP) and enthalpy of fusion (∆Hfus) data for each
40
FAME species in the mixture. A high degree of correlation (R² = 0.949) was found between CP
41
and the calculated mixture SLE transition temperature (TSLE). Regression analysis yielded an
42
equation for calculating the CP of FAME mixtures. The MODified Empirical Correlation
43
(MODEC) model (R² = 0.893) was derived from (1/CP) versus ln(yC16) data where yC16 was the
44
mass fraction of methyl palmitate (MeC16) in the mixture. The performances of both models in
45
predicting the CP of multicomponent FAME mixtures (biodiesel) were compared against results
46
from six empirical correlation models from the literature. The SLE model performed best by
47
having close to a 1:1 correlation between calculated (CP-calc) and measured CP data and the
48
highest accuracy with respect to average deviations. Although the MODEC model did not
49
exhibit a 1:1 correlation, it performed nearly as well as the SLE model in accurately calculating
50
the CP of biodiesel. The main benefit of the MODEC model is that it requires only a measured
51
yC16 value vis-à-vis complete analysis of the FA Profile in order to apply the SLE model.
2 ACS Paragon Plus Environment
Page 2 of 37
Page 3 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
52 53
1. INTRODUCTION
54
Biodiesel is an alternative diesel fuel made from renewable plant oils and animal fats. Biodiesel
55
in the form of fatty acid methyl esters (FAME) is obtained by transesterification of the feedstock
56
lipid with methanol in the presence of catalyst.1 It has properties that compare well with
57
conventional diesel fuel (petrodiesel) and may be used in blends, or as a neat (100 %; ‘B100’)
58
fuel, to power compression-ignition engines. In the US, 10.6 billion L (2.8 billion gal) of
59
biodiesel and renewable diesel fuels was produced in 2016.2
60
Biodiesel has many advantages that make it attractive for use as an alternative fuel in
61
modern compression-ignition (diesel) engines. It is safe to store and handle because it is
62
environmentally innocuous and has a high flash point, low toxicity and a rapid biodegradation
63
rate.3-5 Blending with biodiesel enhances the ignition quality, lubricity and anti-wear properties
64
of petrodiesel.6 Combustion of fuels containing biodiesel reduces hydrocarbons, carbon
65
monoxide, sulfur dioxide, polyaromatic hydrocarbons and particulate matter in exhaust
66
emissions.3-5,7 Soybean oil-FAME (SME) biodiesel has an energy output/fossil fuel input ratio
67
of 4.568 and reduces net greenhouse gas emissions by 66 %.9
68
Among the disadvantages of biodiesel are its poor cold flow properties. Biodiesel has a
69
high cloud point (CP; defined as the temperature where a haziness is detected in a cooled
70
sample10) that may compromise its deployment and performance in cold weather. Throughout
71
much of the world, biodiesel must conform to fuel property specifications such as the ASTM D
72
6751 or CEN EN 14214 standards. Both of these standards have guidelines and/or requirements
73
for cold flow properties of biodiesel.
3 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
74
Soybean oil biodiesel (SME) develops operability issues when ambient overnight
75
temperatures approach 0 to 2 °C.10 These temperatures are generally within the range of CP data
76
for SME (−2 to 3 °C). Similarly, palm oil-FAME (PME) has CP in the range 10 to 18 °C and
77
may become problematic when ambient temperatures are slightly below room temperature.
78
Long-chain saturated-FAME (SFAME) have higher melting points (MP) than unsaturated-
79
FAME (UFAME) with the same chain length. Since PME typically has four times the
80
concentration of methyl palmitate (MeC16) than SME, it has a higher CP.
81
The objective of the present study is to develop an accurate correlation for calculating the
82
CP of biodiesel based on two factors: 1) its fatty acid concentration profile, referred to as the ‘FA
83
Profile’ and defined as the identity and concentration of each FAME species present; and 2) the
84
MP and enthalpy of fusion (∆Hfus) of each FAME species. Several studies11-20 examined
85
biodiesel admixtures (blends of two or more biodiesel fuels derived from different feedstocks)
86
with the goal of mitigating deficiencies associated with poor cold flow properties or oxidative
87
stability, or high kinematic viscosity (ν) in unblended biodiesel fuels. Some of these studies
88
reported correlations for estimating CP (or cold filter plugging point) only as functions of FA
89
Profile concentrations with little or no attention paid to the melting properties of FAME species.
90
This work investigates FAME made from four feedstocks: canola (CaME), palm (PME)
91
and soybean (SME) oils and yellow grease (YGME). Four binary admixtures were prepared for
92
each of the six admixture systems in varying mass fractions (y1). The preparation of admixtures
93
was intended primarily to diversify the number of FAME mixtures (28) from a starting point of
94
four neat biodiesel fuels. The FA Profiles of the admixtures were calculated from analyses
95
performed on the component biodiesel fuels. The CP of each mixture was measured directly in
96
the course of the present work.
4 ACS Paragon Plus Environment
Page 4 of 37
Page 5 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
97
Energy & Fuels
Six mathematical models from the scientific literature17,21-24 were tested for validation by
98
applying them to FA Profile data obtained for the mixtures and comparing results for calculated
99
and measured CP data. Two new correlations for calculating the CP of biodiesel were also
100
developed. First, the solid-liquid equilibrium (SLE) transition temperature (TSLE) of the mixtures
101
were calculated from melting properties of the pure FAME species and correlated with
102
corresponding measured CP data. The second correlation, termed the MODified Empirical
103
Correlation (MODEC) model, was based on thermodynamic theory for the SLE in mixtures of
104
compounds. This model correlated CP as a function of the mass fraction of MeC16 (yC16) in the
105
mixtures.
106 107 108
2. EXPERIMENTAL SECTION 2.1. Materials. The biodiesel (FAME) samples were acquired as finished products:
109
CaME was from Archer-Daniels-Midland (Decatur, IL); PME produced by Sime Darby
110
Biodiesel Sdn. Bhd. (Selangor, Malaysia) was obtained courtesy of the Malaysian Palm Oil
111
Board (Washington, DC); SME was an experimental sample obtained via the National Biodiesel
112
Board (NBB; Jefferson City, MO); and YGME was from Superior Process Technologies
113
(Minneapolis, MN). Biodiesel samples were tested for fuel quality by analysis of acid value
114
(AV), oxidation induction period (IP) at 110 °C, ν at 40 °C, water content, free and total
115
glycerides and total monoacylglycerols (MAG) using standard test methods. Experimental
116
methods, instruments and a summary of the data are presented in the supplemental information.
117
2.2. Methods. Fatty acid concentration profiles (FA Profiles) were determined for the
118
four neat biodiesel fuels. Concentration (mass fraction) data were from analyses performed on a
119
Varian (Walnut Creek, CA) model 8400 gas chromatograph (GC) with a flame-ionization
5 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
120
detector (FID) and a Supelco (Bellefonte, PA) SP2380 GC column. The carrier gas was helium
121
and FAME species were identified by retention times and quantified by peak areas.
122
Concentration data for the admixtures were calculated by applying mass balances to each FAME
123
species based on GC-analysis of the FA Profiles of the two component biodiesel fuels.
124
In the present work, the term ‘admixture’ refers to binary mixtures of two component
125
biodiesel fuels (24 mixtures); ‘neat biodiesel’ refers to the biodiesel fuel components (4
126
mixtures); and ‘mixture’ refers collectively to all admixtures and neat biodiesel fuels (28
127
mixtures). Each admixture was prepared by weighing the appropriate masses of the neat
128
biodiesel components and mixing in a laboratory flask. Admixtures with mass fractions (y1) =
129
0.2, 0.4, 0.6 and 0.8 were prepared for each system (the subscript ‘1’ refers to the biodiesel fuel
130
designated with the heading ‘Biodiesel 1’). Admixture samples were sealed in vials and stored
131
in a dark refrigerator when not in use. None of the comparison models were developed
132
considering the melting properties (MP and ∆Hfus) of the individual FAME components.
133
Cloud point (CP) data of the biodiesel and biodiesel admixtures were measured with a
134
model PSA-70S automatic analyzer from Phase Technology (Richmond, BC, Canada). Data
135
were measured according to ASTM test method D 5773.25
136
2.3. Correlations. Six empirical correlation models from the literature were found for
137
calculating the CP of biodiesel based on FA Profile concentration factors. These correlations are
138
outlined in eqs S1-S6 in the supplemental information. Three correlations were linear functions
139
based on the mass concentration of total-SFAME (ΣSFAME), total-UFAME (ΣUFAME) or
140
MeC16.17,23 One correlation was a non-linear function of ΣUFAME mass concentration.24 The
141
remaining two are multivariate expressions based on 1) weighted average number of C-atoms in
142
the fatty acid chain (NC) plus the ΣUFAME molar concentration21; and 2) the mass fractions (yi)
6 ACS Paragon Plus Environment
Page 6 of 37
Page 7 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
143
of five FAME, MeC16, methyl stearate (MeC18), methyl oleate (MeC18:1), methyl linoleate
144
(MeC18:2) and methyl linolenate (MeC18:3).22
145
Solid-liquid equilibrium transition temperatures (TSLE) were used to develop a correlation
146
for calculating the CP of biodiesel fuels based on thermodynamic theory. The TSLE data were
147
calculated using the equation reported in Imahara et al.26:
148 149
=
−
∆
(1)
150 151
where MP (K) and ∆Hfus (J/mol) are melting properties of the pure FAME species, xi is the mole
152
fraction of the FAME and Rg is the gas constant. The transition temperature of FAME species ‘i’
153
in the admixture is Tf. This equation assumes an ideal solution in the liquid phase and
154
independent crystallization of FAME species into the solid phase (that is, no solid solutions).
155
Equation 1 was used to calculate Tf values for each FAME species present and the mixture TSLE
156
value was taken as the maximum Tf value. The mixture TSLE was determined from the maximum
157
of the calculated Tf values and its associated FAME defined as the “controlling” species in the
158
mixture. In the present work, MP and ∆Hfus data were acquired from the scientific literature for
159
use in eq 1. Measured CP data were then matched in data pairs with the corresponding mixture
160
TSLE data for all admixtures, including the four neat biodiesels, and subjected to linear regression
161
analysis to establish the SLE correlation.
162
The MODEC equation was developed by rearranging and modifying eq 1 as follows:
163 164
= + !
(2)
165 7 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 37
166
where CP (K) is the measured CP of the mixture, yC16 is the mass fraction of MeC16 and A and B
167
are constants determined from linear regression of (1/CP) versus ln(yC16) data. Once constants A
168
and B were inferred, the correlation for calculating CP (°C) was obtained by rearranging eq 2:
169 170
"# = $1(&
+ !') − 273.15
(3)
171 172 173
Note this model assumes MeC16 is the SLE controlling FAME in the mixtures. All mathematical operations used to calculate mean values, perform regression and
174
statistical analysis of experimental results, and validation testing of calculated CP data (CP-calc)
175
against measured CP data were conducted using Microsoft (Redmond, WA) Excel® 2013
176
spreadsheets.
177 178 179
3. RESULTS AND DISCUSSION 3.1. Neat Biodiesel Fuel Properties. Results from analysis of AV, IP, ν, water content,
180
free and total glycerols and total MAG content are summarized in Table S1 in the supplemental
181
information. Based on these properties, the overall quality of the neat biodiesel samples used in
182
the study was very good. Free and total glycerols and total MAG concentrations were very low
183
indicating the fuels were well refined. Viscosities (ν) were in a narrow range, 4.09-4.622 mm²/s,
184
and water contents were within maximum limits in ASTM standard D 6751.27
185
Three of the property data points were outside the specified limits. The AV of both
186
CaME and PME exceeded the maximum limit (0.50 mg KOH/g).27 These results indicated
187
relatively low free fatty acid (FFA) concentrations (0.27 and 0.44 mass%) and were not expected
188
to influence the outcome of the present study. The IP of SME was very low as a result of this 8 ACS Paragon Plus Environment
Page 9 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
189
biodiesel having the highest polyunsaturated-FAME concentration among the four neat
190
biodiesels and no added oxidation inhibitors.
191
3.2. FA Profiles of Admixtures. Results from GC/FID analysis of the four neat biodiesel
192
fuels are summarized in Table 1. The most abundant species present in the neat biodiesel fuels
193
were MeC16, MeC18, MeC18:1, MeC18:2 and MeC18:3. The neat fuels had diverse ranges in
194
FA Profile with respect to yC16 = 0.0413-0.448, yC18:1 = 0.1970-0.6490 and ΣSFAME = 0.0688-
195
0.504 (or ΣUFAME = 0.496-0.9312). PME had the highest ΣSFAME content mainly due to its
196
yC16 = 0.448. Although CaME had the highest ΣUFAME content (0.9312), SME had the highest
197
concentration in total polyunsaturated-FAME (ΣPUFAME = 0.6634). The high ΣPUFAME
198
content of SME likely caused it to fail the IP specification in ASTM standard D 6751 as
199
discussed earlier. YGME had the highest yC18 (0.0655), possibly the result of partial
200
hydrogenation of oleic acid moieties in the parent oil during its use as a cooking oil.
201 202 203 204
205 206 207 208 209 210 211 212
Table 1. Fatty Acid Concentration Profiles (FA Profile) of Biodiesel Derived from Canola, Palm and Soybean Oils and Yellow Grease (CaME, PME, SME and YGME).a Mass fractions (yi) are mean values from n = 3 analyses. FAME CaME PME SME YGME yi SD yi SD yi SD yi SD MeC14 0.000515 8×10−6 0.0099 1×10−4 ND Traceb MeC16 0.0413 2×10−4 0.448 2×10−3 0.1101 6×10−4 0.1375 7×10−4 −6 b MeC16:1 0.000242 8×10 Trace ND 0.0088 2×10−4 −5 −4 −4 MeC18 0.02038 2×10 0.0418 2×10 0.0395 2×10 0.0655 4×10−4 −4 −3 −4 MeC18:1 0.6490 3×10 0.407 1×10 0.1970 4×10 0.406 3×10−3 −5 −4 −4 MeC18:2 0.18709 5×10 0.0887 6×10 0.5746 5×10 0.340 1×10−3 −5 b −4 MeC18:3 0.08199 7×10 Trace 0.0788 4×10 0.0349 3×10−4 −5 −5 b MeC20 0.00659 7×10 0.00374 3×10 Trace 0.00765 8×10−5 −5 b b MeC20:1 0.01286 9×10 Trace ND Trace Total 1.0000 1.000 1.0000 1.000 CaME contained traceb of methyl erucate (MeC22:1). PME contained tracesb of methyl laurate (MeC12); YGME contained traces of methyl docosanoate (MeC22) and MeC22:1. a FAME = Fatty acid methyl esters; SD = standard deviation; MeC14 = methyl myristate; MeC16 = methyl palmitate; MeC16:1 = methyl palmitoleate; MeC18 = methyl stearate; MeC18:1 = methyl oleate; MeC18:2 = methyl linoleate; MeC18:3 = methyl linolenate; MeC20 = methyl arachidate; MeC20:1 = methyl eicosenoate; ND = not detected. b yi < 0.0001 (ignored).
9 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
213
Many empirical models developed to estimate the cold flow properties of biodiesel were
214
based on FAME compositional factors. This is common despite the more fundamental approach
215
of using molar concentrations to directly correlate with the molecular structures of the
216
components. Shown in Figure 1 is a plot of concentration data from FA Profiles of the
217
admixtures prepared for study. These profiles were calculated from the concentration data in
218
Table 1. The graph shows the mole fraction (xi) plotted against mass fraction (yi) corresponding
219
to 196 FAME concentrations in the admixtures. Regression analysis yielded a straight line with
220
slope = 1.006 (standard error [SE] = 0.0026), intercept = −7×10−4 (5.3×10−4), adjusted
221
correlation coefficient (R²) = 0.9987 and standard error of the y-estimate (σy) = 0.0059. This line
222
matched the 1:1 correlation xi = yi for yi = 0.0-0.6. The likely explanation for the high degree of
223
correlation resides in the studied biodiesel fuels being composed of 98+ mass% FAME species
224
with C16 or C18 tailgroup chain lengths. The data in Figure 1 suggest that using mass
225
concentrations instead of molar concentrations to derive composition-based correlations for
226
predicting the properties of biodiesel introduces little error in the results.
227
Another common feature of empirical correlations is the use of the MeC16 concentration
228
as a surrogate for ΣSFAME concentration in the biodiesel fuel. This assumption may be
229
intuitively based on the relative abundance of palmitic acid in many feedstock oils and fats
230
including camelina, canola, corn, cottonseed, jatropha, linseed, low-erucic acid rapeseed
231
(LEAR), olive, palm, peanut, sesame, soybean and sunflowerseed oils plus lard and tallow.28,29
232
The results in Figure 2 show that ΣSFAME increases linearly as yC16 increases for the 28 FAME
233
mixtures. Regression analysis yielded slope = 1.04 (SE = 0.020), intercept = 0.041 (0.0042), R²
234
= 0.991 and σy = 0.012. Nearly identical results were obtained from analysis of mole fraction
235
data (slope = 1.04 [0.018], intercept = 0.039 [0.0041], R² = 0.992 and σy = 0.011). These results
10 ACS Paragon Plus Environment
Page 10 of 37
Page 11 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
236
showed that for the correlations tested in the present study, variations in the ΣSFAME
237
concentration were highly correlated to variations in the MeC16 concentration in FAME
238
mixtures.
239
240 241 242 243 244
Figure 1. Comparison of mass and mole fractions (yi and xi) of fatty acid methyl ester (FAME) species present in binary biodiesel admixtures.
245 246 247 248 249
Figure 2. Comparison of total saturated-FAME (ΣSFAME) and methyl palmitate (yC16) mass fractions in multicomponent FAME mixtures. See Figure 1 for abbreviations.
11 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
250
3.3. CP of Neat Biodiesel Fuels. Data from CP measurements conducted on the four neat
251
biodiesel fuels are presented in Table 2. In general, the results compared well with results in the
252
literature for CaME, PME, SME and YGME. CaME had CP = −2.3 °C which agreed with
253
results in four studies.30-33 Canola oil is similar in FA Profile to LEAR oil29 and results for
254
CaME in the present work compared well with data reported for LEAR-FAME.30,34 Data in
255
Table 2 agreed with results in three studies30,35,36 on PME and compared well with data in two
256
studies37,38 on SME. The CP values for CaME, PME and SME were within temperature ranges
257
reported in a recent review article.10
258 259 260
261 262
Table 2. Measured Cloud Point (CP) Data and Calculated Mixture Solid-Liquid Equilibrium (SLE) Temperatures.a CP data are mean values from n = 3 measurements. Biodiesel 1 Biodiesel 2 y1 CP TSLE FAME xi °C SD °C CaME None 1.000000 −2.3 0.1 −0.73 MeC20 0.00595 PME None 1.000000 13.1 0.7 20.28 MeC16 0.470 SME None 1.000000 −2.8 0.4 4.75 MeC16 0.1188 YGME None 1.000000 2.8 0.2 8.44 MeC18 0.0640 SME PME 0.200171 11.1 0.5 18.41 MeC16 0.402 0.399814 8.0 0.4 16.19 MeC16 0.332 0.599748 5.5 0.5 13.47 MeC16 0.262 0.798622 2.57 0.06 9.93 MeC16 0.191 SME YGME 0.200661 1.8 0.2 7.62 MeC18 0.0589 0.399936 0.5 0.1 6.74 MeC18 0.0539 0.599850 −0.5 0.3 5.77 MeC18 0.0488 0.797861 −2.0 0.2 5.27 MeC16 0.1248 CaME PME 0.200004 10.7 0.3 18.00 MeC16 0.388 0.400049 5.7 0.6 15.18 MeC16 0.304 0.599914 2.8 0.1 11.46 MeC16 0.219 0.799717 −2.0 0.1 5.95 MeC16 0.133 CaME YGME 0.200463 0.5 0.1 7.00 MeC18 0.0553 0.400044 −1.07 0.06 5.32 MeC18 0.0465 0.600012 −2.07 0.06 3.31 MeC18 0.0378 0.799926 −2.6 0.1 0.79 MeC18 0.0290 CaME SME 0.200043 −3.1 0.2 3.35 MeC16 0.1042 0.400280 −4.8 0.0b 1.75 MeC16 0.0895 0.596710 −4.8 0.0b 0.34 MeC18 0.0277 0.799914 −4.1 0.0b −1.03 MeC18 0.0239 PME YGME 0.200191 4.2 0.3 11.20 MeC16 0.214 0.399940 6.8 0.4 14.20 MeC16 0.279 0.599861 9.23 0.06 16.59 MeC16 0.344 0.800095 11.3 0.3 18.58 MeC16 0.407 a y1 = Mass fraction of Biodiesel 1 in admixture; TSLE = SLE transition temperature; xi = mole fraction of controlling FAME species. See Table 1 for abbreviations.
12 ACS Paragon Plus Environment
Page 12 of 37
Page 13 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
263 264 265
Energy & Fuels
b
Same result after three replicate measurements (SD = 0).
Comparison of the CP value for YGME with values reported in the literature was
266
performed keeping in mind there is a large variety in yellow greases characterized by industry.
267
Yellow grease is obtained as a waste material from food processing and interchangeably referred
268
to as used cooking or used frying oil (note: brown grease, another waste oil from food
269
processing, is generally lower in quality). Nevertheless, the measured CP value for YGME in
270
Table 2 agreed well with data reported for used cooking/frying oil-FAME12,39 and other
271
YGME.40,41 Based on the fuel properties (including CP) and FA Profile data, the YGME used in
272
the present study appears to have been well processed with no measurable “trans” type UFAME
273
content.
274
3.4. CP of Admixtures. Measured CP data for the 24 admixtures are summarized in
275
Table 2. Each data point is matched with y1 = mass fraction of ‘Biodiesel 1’ in the
276
corresponding binary admixture. CP data for the SME/PME, CaME/PME and CaME/SME
277
systems were compared with data for these admixtures reported in another study.18 Similarly,
278
CP data from the CaME/YGME admixture system were compared with results reported in a
279
study on LEAR-FAME/used cooking oil-FAME due to the similarities in the respective FA
280
Profiles of the component biodiesel fuels.12
281
Comparison of the measured CP data for these four admixture systems is made in the
282
four graphs shown in Figure 3 where the data are plotted as a function of y1. All four admixture
283
systems exhibit consistent trends in the data-curves for the present study and comparison data.
284
The results exhibit some separation between CP data in the present study and data from the
285
literature. The separations were most likely caused by small deviations in the CP of the
286
component biodiesel fuels. Nevertheless, deviations between curves were generally small, 2.513 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
287
3.8 °C for SME/PME, 2-3.9 °C for CaME/PME, 2.5-4.8 °C for CaME/SME and 0.2-0.5 °C for
288
CaME/YGME.
289 290 291 292 293 294 295 296 297 298 299 300 301 302 303 304 305 306
Figure 3. Cloud point (CP)-composition charts of admixture systems: (a) soybean oil-FAME (SME)/palm oilFAME (PME; (b) canola oil-FAME (CaME)/PME; (c) CaME/SME; and (d) CaME/yellow grease-FAME (YGME). Results from ‘This study’ are compared with superimposed data from references.12,18 Measured CP data are average values from three replicates (standard deviations ≤ 0.66). See Figure 1 for abbreviations.
307
The SME/PME, CaME/PME and CaME/YGME admixture systems showed steady
308
decreases in CP as y1 increases. The CaME/PME curve [Figure 3(b)] exhibited concave upward
309
behavior where CP decreased steadily at y1 = 0-0.8 before nearly leveling off at y1 > 0.8. This
310
trend is repeated in the data from the comparison study.18 Similar behavior was observed for the
311
CaME/YGME system [Figure 3(d)] where CP leveled off at y1 ~ 0.7-0.8.
14 ACS Paragon Plus Environment
Page 14 of 37
Page 15 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
312
The phase behavior observed in Figure 3(c) for the CaME/SME system was the result of
313
narrow deviations in measured CP data for the component biodiesel fuels (0.5 °C for the present
314
study; 1 °C for the comparison study18). In the comparison study, CP decreased from 1 °C at y1
315
= 0.0 to 0 °C at all other mass fractions. In contrast, the results for the present work show a
316
slight decrease from −2.8 to −3.1 °C at y1 = 0.0-0.2, a sharp decrease from −3.2 to −4.8 °C at y1
317
= 0.2-0.4 and a steady increase back to −2.5 °C at y1 = 0.4-1.0.
318
3.5. Testing the Six Literature Correlations. Six correlation models taken from the
319
literature were tested for validation against measured CP data for the 28 FAME mixtures studied
320
herein. Presented in Table 3 is a summary of the model names (Dunn, Davis, Sarin #1, Sarin #2,
321
Su and Clements) and compositional and structural factors inferred from FA Profile data in Table
322
1. These factors were used in the associated models to calculate CP data (CP-calc) for
323
comparison with measured CP data in Table 2. Measured CP and CP-calc data for the 28
324
mixtures were organized into data pairs, one set for each model, and tested for validation by
325
regression analysis. Results are summarized in Table 4.
326 327
328 329 330 331
Table 3. Correlation Factors of Neat Biodiesel Fuels Calculated from FA Profile Data in Table 1.a Correlation Factor CaME PME SME YGME Dunn (1997) ΣSFAME, mass% 6.8788 50.4 14.96 21.06 Sarin #2; Clements ΣUFAME, mass% 93.12 49.6 85.04 78.9 Sarin #1 YC16, mass% 4.13 44.8 11.01 13.75 Davis yC16 0.0413 0.448 0.1101 0.1375 Davis yC18 0.02038 0.04183 0.0395 0.0655 Davis yC18:1 0.6490 0.407 0.1970 0.406 Davis yC18:2 0.18709 0.0887 0.5746 0.340 Davis yC18:3 0.08199 N/A 0.0788 0.0349 Su NC 18.94 18.0 18.76 18.7 Su ΣUFAME, mol% 92.82 47.5 84.25 78.1 a ΣSFAME = Total saturated-fatty acid methyl ester (FAME) concentration; ΣUFAME = total unsaturated-FAME concentration; YC16 = mass fraction of MeC16; yCm:n = mass fraction of FAME ‘MeCm:n’; N/A = not applicable; NC = weighted-average number of C-atoms in ester chain. See Table 1 for abbreviations.
332 15 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
333 334
335 336 337 338 339 340 341 342 343 344 345
Table 4. Results from Regression Analysis of Calculated CP (CP-calc) versus Measured CP Data for the Six Literature Empirical Correlations and the SLE and MODEC Models.a Model Slope SE Intercept SE σy F R² Dunn (1997)b 3.2 0.11 1.4 0.65 0.968 3.2 816 Davisc 3.9 0.36 13 2.1 0.810 10 116 Sarin #1d 1.10 0.050 2.2 0.29 0.947 1.4 486 Sarin #2d 1.28 0.045 1.1 0.26 0.968 1.3 816 Sue 0.98 0.031 2.3 0.18 0.974 0.9 995 Clementsf 0.86 0.053 3.0 0.31 0.907 1.5 266 SLE (eq 4) 0.95 0.042 0.1 0.25 0.949 1.2 507 MODEC (eq 6) 0.89 0.059 0.3 0.34 0.893 1.7 227 MODEC (modified eq 6)g 0.93 0.049 0.2 0.29 0.932 1.4 357 a MODEC = MODified Empirical correlation; SE = Standard error of slope or intercept; R² = adjusted correlation coefficient; σy = standard error of the y-estimate; F = variance ratio (model/residuals). See Table 2 for abbreviations. b Ref. 23. c Ref. 22. d Ref. 17. e Ref. 21. f Ref. 24. g Omitting data for neat CaME.
Shown in Figure 4 are CP-calc results for four correlation models versus measured CP
346
data in the present work. Two models were omitted because they deviated significantly from the
347
desired 1:1 correlation between CP-calc and measured CP data (results are presented in the
348
supplemental information). For the Dunn (1997) model, correlation between CP-calc and
349
measured data was second highest for the six correlations tested, based on R² = 0.968 and σy =
350
3.2. The performance of this model was likely affected by 11 admixtures plus neat PME and
351
YGME having ΣSFAME concentrations outside the range (0.06-0.20) of correlation.23 The
352
Davis model yielded the highest slope, intercept and σy values and the lowest R² from the
353
validation tests. This model probably failed because it accounted only for five FAME species
354
present in the admixtures and ignored the remaining FAME species.22
355
The Su model demonstrated the best validation results among the six literature models
356
with slope = 0.98, intercept = 2.3 and the lowest σy = 0.9. The second-best model was Sarin #1
357
with slope = 1.10, intercept = 2.2 and σy = 1.4. Although it had a lower intercept and σy than
358
Sarin #1, the slope (1.28) of the Sarin #2 model caused it to fail validation. These three models 16 ACS Paragon Plus Environment
Page 16 of 37
Page 17 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
359
demonstrated a nearly linear correlation (R² = 0.947-0.974) between CP-calc and measured CP
360
data. The Clements model yielded a low slope = 0.86, a high intercept = 3.0 and σy = 1.2.
361
Results for this correlation were clearly non-linear (R² = 0.91) showing a concave upward pattern
362
in Figure 4(d).
363 364 365 366 367 368 369 370 371 372 373 374 375 376 377 378 379 380
Figure 4. Validation graphs showing calculated CP (CP-calc) versus measured CP results for literature correlations: (a) Sarin #1; (b) Sarin #2; (c) Su; and (d) Clements. Dashed lines = 1:1 correlation between calculated and measured data. See Figure 3 for abbreviations.
Summarized in Table 5 are results from direct comparison of CP-calc and measured CP
381
data for the six literature correlation models. The Dunn (1997) and Davis models had very high
382
maximum absolute deviations (ADmax) of 34.66 and 48.57. The remaining four models had
383
lower ranges in absolute deviation (AD) = 0.02-6.56; however, each of these models yielded
17 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
384
positive deviations (CP-calc > CP) for 24+ of the mixtures tested. The lowest average absolute
385
deviation (AAD) = 2.1 was observed for the Sarin #2 model which correlated the CP of biodiesel
386
with MeC16 mass% (YC16).17 The Su model yielded the lowest root-mean-squared deviation
387
(RMSD) = 2.4 and had the lowest range in AD = 0.45-3.93.
388 389 390
391 392 393 394 395 396 397 398 399
Table 5. Deviations between Measured CP and CP-Calc from the Six Literature Empirical Correlations and the SLE and MODEC Models.a Model Deviations ADmin ADmax AAD RMSD Dunn (1997)b 0.34 34.66 9.9 14 Davisc 1.05 49.31 21 27 Sarin #1d 0.18 5.47 2.5 2.8 Sarin #2d 0.02 6.56 2.1 2.6 Sue 0.45 3.93 2.2 2.4 Clementsf 0.52 5.91 2.7 3.2 SLE (eq 4) 0.05 3.06 0.94 1.2 MODEC (eq 6) 0.03 4.96 1.4 1.7 MODEC (modified eq 6)g 0.01 2.93 1.2 1.4 a ADmin = Minimum absolute deviation; ADmax = minimum absolute deviation; AAD = average absolute deviation; RMSD = root-mean-squared deviation. See Tables 1, 2 and 4 for abbreviations. b Ref. 23. c Ref. 22. d Ref. 17. e Ref. 21. f Ref. 24. g Omitting CP data for neat CaME.
400
3.6. Mixture TSLE Data. Equation 1 was applied to determine the Tf of each FAME
401
species present in the 28 FAME mixtures. FA Profile data were from Table 1 and MP and ∆Hfus
402
data were from the literature (Table S2 in the supplemental information). An example showing
403
how TSLE = 20.28 °C was inferred from Tf data for neat PME is given in Table S3 in the
404
supplemental information. The data in the last three columns of Table 2 are a summary of the
405
mixture TSLE values, identity and mole fraction (xi) of the controlling FAME species in the 28
406
mixtures. These results were determined in accordance with SLE thermodynamic theory for
407
ideal solutions in the liquid phase and independent crystallization of FAME species.
18 ACS Paragon Plus Environment
Page 18 of 37
Page 19 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
408
Fifteen admixtures and two neat biodiesel fuels had MeC16 identified as the TSLE-
409
controlling FAME. YGME had MeC18 as the controlling FAME leading to three SME/YGME
410
and four CaME/YGME admixtures having the same controlling FAME. The same was true for
411
two CaME/SME admixtures despite neither component biodiesel having MeC18 as the
412
controlling FAME. Although neat CaME had a small concentration of MeC20 (yC20 = 0.00659
413
[xC20 = 0.00595]), this species was the controlling FAME according to SLE theory. Thus, small
414
concentrations of higher-MP species can have a disproportionate effect on the TSLE of FAME
415
mixtures. These results also showed that neither MeC14 nor any of the UFAME species present
416
in the FAME mixtures had an impact on the SLE phase transitions.
417
Two admixture systems had two different controlling FAME species depending on the
418
composition (y1). The SME/YGME system had MeC18 at y1 ≤ 0.600 and MeC16 at y1 > 0.600.
419
At y1 = 0.600, calculated Tf values were nearly identical (5.77 and 5.76 °C) for MeC18 and
420
MeC16 indicating that the SLE curves for these two FAME intersect near this composition.
421
Increasing SME content decreased xC16 and xC18 in the admixtures causing the Tf values for both
422
FAME to decrease. The intersection of the SLE curves was due to the Tf of MeC18 decreasing
423
in larger increments than MeC16.
424
The second admixture system demonstrating an intersection in SLE curves was
425
CaME/SME where the controlling FAME changed from MeC16 to MeC18 at 0.400 < y1 < 0.598.
426
Increasing the CaME content decreased both xC16 and xC18 causing Tf for both FAME to decrease
427
in a fashion similar to the SME/YGME admixture data. The calculated point of intersection
428
between the SLE curves for MeC16 and MeC18 was at y1 = 0.475 and Tf = 2.81 °C for
429
CaME/SME.
19 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
430
At 0.800 < y1 < 1.000, the CaME/SME system exhibited a second intersection between
431
SLE curves for MeC18 and MeC20. This occurs because MeC20 was identified as the
432
controlling FAME in neat CaME. This admixture system appears to undergo a eutectic-like
433
phase transition because Tf values for MeC20 trended upward with increasing CaME content
434
(that is, xC20) in the admixtures. The calculated intersection of SLE curves for MeC18 and
435
MeC20 occurred at y1 = 0.8865 and Tf = ‒1.67 °C, corresponding to a mole ratio (xC18/xC20) =
436
4.22. Such transitions have been observed for binary mixtures of pure MeC16/MeC1826,42,43 and
437
MeC16/MeC20.43,44 The behavior discussed earlier for experimental data in Figure 3(c) may
438
have been affected by intersecting SLE curves for controlling FAME in this admixture system.
439
When calculating the TSLE data (Table 2), it was observed that for the nine admixtures
440
with MeC18 as the controlling FAME, Tf values calculated for MeC16 were within −1.9 °C of
441
TSLE of those mixtures. Neat YGME also had MeC18 as the controlling FAME and the Tf value
442
for MeC16 in this biodiesel fuel deviated by −1.3 °C from the mixture TSLE. These narrow
443
deviations, combined with MeC16 being identified as the controlling FAME for 15 admixtures
444
plus neat PME and SME, may explain the high correlation observed earlier between ΣSFAME
445
and yC16 (Figure 2). Apparently, MeC16 has a Tf value that allows the assumption that it is the
446
SLE-determining FAME species in the FAME mixtures being studied. The lone exception was
447
neat CaME where MeC20 was identified as the controlling FAME with the corresponding
448
mixture TSLE = −0.79 °C, compared to Tf = −5.25 °C for MeC16 in the mixture.
449
Equation 1 was used to check the assumption made earlier that elevated AV (FFA) of
450
CaME and PME did not affect the SLE in mixtures composed of these two biodiesels. Melting
451
properties (MP and ∆Hfus data) were used in the equation to calculate Tf values of fatty acids that
452
may have been present in these biodiesel fuels. Mole fractions of fatty acids were assumed to be
20 ACS Paragon Plus Environment
Page 20 of 37
Page 21 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
453
equal in proportion to the corresponding FAME concentrations. Results presented in Table S4 in
454
the supplemental information demonstrated that all fatty acids had calculated Tf values below the
455
mixture TSLE values of the neat biodiesel fuels (Table 2). These results appear to confirm that the
456
elevated AV did not impact the SLE phase transition results in the present study.
457
3.7. SLE Model for CP. Comparing the data in Table 2 shows that TSLE > CP for each
458
FAME mixture studied. Deviations (CP − TSLE) ranged from −1.8 to −9.4 °C. The TSLE is
459
defined as the SLE transition temperature of a mixture at equilibrium. Since the CP of biodiesel
460
is measured under non-equilibrium conditions (rapid cooling, no agitation), it does not represent
461
an equilibrium transition temperature.45,46 Instead, it is likely that the effects of supercooling
462
caused CP < TSLE in the multicomponent FAME mixtures. Supercooling is the phenomenon
463
where substances remain in a liquid phase at temperatures below the normal freezing point
464
unless a seed crystal or nucleus is present.47,48 Such effects have been observed when comparing
465
cooling and heating differential scanning calorimetry (DSC) analyses performed on FAME
466
mixtures38,47,49-51 and petrodiesel and jet fuels.52,53
467
The development of the SLE model began with statistical analysis and linear regression
468
of 28 (CP, TSLE) data pairs for corresponding FAME mixtures. A paired two sample t-test of the
469
mean values yielded a Pearson coefficient (PC) = 0.975 favoring correlation between CP and
470
TSLE data. Linear regression analysis resulted in the following equation:
471 472
"# = 0.82 123 − 5.0
(4)
473 474
where CP and TSLE are in °C, R² = 0.949, σy = 1.2 and variance ratio (F = model/residuals) = 507.
21 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
475
These regression results supported two main conclusions from the present study. First,
476
eq 4 has a high probability of predicting CP within 1.2 °C. Second, although CP itself is not an
477
equilibrium transition temperature, it demonstrates a nearly linear correlation with the TSLE of
478
multicomponent FAME mixtures (biodiesel) determined from SLE thermodynamic theory.
479
Given these considerations, eq 4 was applied to calculate a separate set of CP-calc data from TSLE
480
data in Table 2 and the results tested against the measured CP data.
481
Figure 5 is a graph showing CP-calc versus measured CP for the SLE model. Regression
482
analysis (results summarized in Table 4) yielded close to a 1:1 correlation with the slope (0.95)
483
being closer to unity than all literature models except Su. The SLE model also had a smaller
484
intercept coefficient (0.1) than any of the literature models tested. Deviations between CP and
485
CP-calc from the SLE model (Table 5) were in the range AD = 0.05-3.06. Lastly, results from
486
the SLE model had the lowest AAD (0.94) and RMSD (1.2) among the correlations compared.
487
Overall, these results suggested that the SLE model was the most accurate model for calculating
488
the CP of the multicomponent FAME mixtures studied in this work.
489
490 491 492
Figure 5. Comparison of CP-calc versus measured CP data for the solid-liquid equilibrium (SLE) model for FAME mixtures (eq 4).
22 ACS Paragon Plus Environment
Page 22 of 37
Page 23 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
493 494 495
Dashed line = 1:1 correlation. See Figures 1, 3 and 4 for abbreviations.
496
3.8. MODEC Model for CP. Performing a paired two sample t-test on 28 (CP, yC16) data
497
pairs for corresponding FAME mixtures yielded PC = 0.974. The data plotted as (1/CP) versus
498
ln(yC16) [eq 2] are shown in Figure 6(a). Linear regression analysis of the data yielded the
499
equation:
500 501
= −1.02 × 105 ln − 3.44 × 10:
(5)
502 503
where CP is in K, R² = 0.887, σy = 2.4×10‒5 and F = 212. The low R² for this equation was
504
mainly the result of scatter.
505
It was observed earlier that neat CaME was the only mixture where the SLE controlling
506
FAME was MeC20 instead of MeC16 or MeC18. This data point, labeled “C” in Figure 6(a),
507
clearly demonstrates the largest deviation from the regression line drawn through the data.
508
Omitting point “C” from the regression analysis increased the relative correlation to nearly linear
509
(R² = 0.929) while only slightly affecting the slope (1.12×10−4) and intercept (3.42×10−5)
510
coefficients.
511
Results from the regression analysis yielded the following MODEC model equation:
512 513
CP = ;1(& −1.02 × 105 ln
− 3.44 × 10: '< − 273.15
(6)
514 515
where CP is in °C. Equation 6 was subsequently used to calculate a separate set of CP-calc
516
values to be tested against corresponding measured CP data. Results are shown graphically in 23 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
517
Figure 6(b) and summarized in Table 4. Two sets of data were obtained, one for CP-calc data
518
from eq 6 and the other for data generated from the analysis omitting the neat CaME data.
519 520 521 522 523 524 525 526 527 528 529
Figure 6. Development of the MODified Empirical Correlation (MODEC) model for the CP of FAME mixtures (eq 6): (a) (1/CP) versus ln(yC16), linear trend line (R² = 0.887); (b) comparison of CP-calc versus measured CP data, dashed line = 1:1 correlation. See Figures 1-3 and 4 for abbreviations.
The results in Table 4 for the MODEC model in eq 6 did not indicate a 1:1 correlation
530
with respect to the slope (0.89) of the regression line. The R² = 0.893 indicated non-linear
531
behavior due in part to deviation at point “C” (neat CaME) in Figure 6(b). The results from the
532
analysis omitting neat CaME yielded a nearly linear (R² = 0.932) correlation that was close to a
533
1:1 relationship with respect to slope (0.93) and intercept (0.2) coefficients. Both eq 6 and the
534
modified correlation had σy < 2. Deviation results (Table 5) show that both MODEC equations
535
had AAD and RMSD < 2, values that were lower than all models tested except the SLE model.
536
The MODEC model modified by omitting the CaME data had the lowest ADmax (2.93) among
537
the models tested in this work.
538
This preliminary validation test showed that the MODEC model worked well when
539
multicomponent FAME mixtures (biodiesel) have MeC16 or MeC18 as the SLE controlling
540
FAME species. As observed earlier, neat CaME had MeC20 as the controlling FAME species
541
and did not fit the correlation as well as the other 27 mixtures. Noting that 12 admixtures had
24 ACS Paragon Plus Environment
Page 24 of 37
Page 25 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
542
CaME as a component, it was concluded that only the admixtures with higher concentrations (y1
543
> 0.800) of CaME were likely to demonstrate deviations from the pattern. This is remarkable
544
considering that the MODEC model was based on the hypothesis that (1/CP) was correlated to
545
ln(yC16). The results in the present study indicated that despite not yielding a good preliminary
546
validation results for calculating the CP of biodiesel, the MODEC model performed nearly as
547
well as the more theoretically-based SLE model.
548 549
4. CONCLUSIONS
550
This work evaluated six empirical correlations from the literature for accuracy in calculating the
551
cloud point (CP) of biodiesel fuels. Validation tests against measured CP data were conducted
552
for fatty acid methyl esters (FAME) from canola, palm and soybean oil and yellow grease
553
(CaME, PME, SME and YGME) plus 24 binary biodiesel admixtures. Two models, Su and
554
Sarin #1, demonstrated close to a 1:1 correlation.
555
Two new correlation models were developed that out-performed the literature models.
556
The solid-liquid equilibrium (SLE) model yielded a nearly linear correlation (R² = 0.949)
557
between temperatures calculated from thermodynamic theory (TSLE) and CP of the mixtures.
558
Results helped explain why methyl palmitate (MeC16) is often successfully used as a surrogate
559
for total saturated-FAME (ΣSFAME) concentration in physical property correlations for FAME
560
mixtures when concentrations of longer-chain FAME were very low. This model had the lowest
561
absolute average deviation (AAD) and root-mean-squared deviation (RMSD) values among the
562
correlations tested in the present study.
563 564
This work showed that 99.1 % of variations in the ΣSFAME concentration were driven by variations in the MeC16 concentration of the mixtures studied. The MODified Empirical
25 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
565
Correlation (MODEC) model was a direct relationship between 1/CP and ln(yC16[mass fraction
566
of MeC16]). This model yielded a good correlation (R² = 0.893) between calculated and
567
predicted CP values. Neat CaME contained a small concentration of methyl arachidate (MeC20)
568
and omitting this mixture increased R² to 0.932. The MODEC model had the second lowest
569
AAD and RMSD values.
570
Comparing these two models, the benefit of the MODEC model is that it required only
571
yC16 to calculate the CP of most FAME mixtures. This model becomes less accurate when
572
FAME with alkyl chains of C20+ were able to affect the SLE of the mixtures. The benefit of the
573
more accurate SLE model is that it can predict the CP of all FAME mixtures. For this model to
574
be applied, it is important that the fatty acid concentration profile be known to approximately
575
100 %.
576 577
ACKNOWLEDGEMENTS
578
Kimberly L. Ascherl and Kevin Steidley provided technical assistance for experiments and
579
measurement of fuel properties.
580 581
This work was funded as part of the in-house research of the Agricultural Research Service of
582
the United States Department of Agriculture.
583 584 585 586
REFERENCES (1) Knothe, G. The Biodiesel Handbook 2nd Edition; Knothe, G.; Krahl, J.; Van Gerpen, J., Eds.; AOCS Press: Urbana, IL, 2010; pp 1–3.
26 ACS Paragon Plus Environment
Page 26 of 37
Page 27 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
587
Energy & Fuels
(2) National Biodiesel Board. Biodiesel Production Statistics; National Biodiesel Board:
588
Jefferson City, MO, 2016; http://www.biodiesel.org/production/production-statistics (accessed
589
August 28, 2017).
590 591 592 593
(3) Knothe, G.; Dunn, R. O. Industrial Uses of Vegetable Oils; Erhan, S. Z., Ed.; AOCS Press: Champaign, IL, 2005; pp 42–89. (4) Knothe, G.; Dunn, R. O. Oleochemical Manufacture and Applications; Gunstone, F. D.; Hamilton, R. J., Eds.; Sheffield Academic: Sheffield, UK, 2001; pp 106–163.
594
(5) Graboski, M. S.; McCormick, R. L. Prog. Energy Combust. Sci. 1998, 24, 125–164.
595
(6) Knothe, G. The Biodiesel Handbook 2nd Edition; Knothe, G.; Krahl, J.; Van Gerpen, J.,
596
Eds.; AOCS Press: Urbana, IL, 2010; pp 219–229
597
(7) U.S. EPA. Technical Report No. EPA420-P-02-001: A Comprehensive Analysis of
598
Biodiesel Impacts on Exhaust Emissions. United States Environmental Protection Agency:
599
Washington, DC, 2002.
600
(8) Pradhan, A.; Shrestha, D. S.; McAloon, A.; Yee, W.; Haas, M.; Duffield, J. A.; Shapouri,
601
H. Agricultural Economic Report No. 845: Energy Life-cycle Assessment of Soybean Biodiesel.
602
United States Department of Agriculture, Office of Energy Policy and New Uses, Washington,
603
DC, 2009.
604
(9) Huo, H.; Wang, M.; Putsche, V. Report No. ANL/ESD/08-2: Life-cycle Assessment of
605
Energy and Green House Gas Effects of Soybean-derived Biodiesel and Renewable Fuels.
606
Argonne National Laboratory, Energy Systems Division: Argonne, IL.
607 608
(10) Dunn, R. O.; Moser, B. The Biodiesel Handbook 2nd Edition; Knothe, G.; Krahl, J.; Van Gerpen, J., Eds.; AOCS Press: Urbana, IL, 2010; pp 147–203.
27 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
609 610
(11) Serrano, M.; Oliveros R.; Sánchez, M.; Moraschini, A.; Martínez, M.; Aracil, J. Energy 2014, 65, 109-115.
611
(12) Jurac, Z.; Zlatar, V. Fuel Process Technol. 2013, 106, 108-113.
612
(13) Chen, Y.-H.; Chiang, T.-H.; Chen, J.-H. Fuel 2012, 92, 377-380.
613
(14) Echim, C.; Maes, J.; De Greyt, W. Fuel 2012, 93, 642-648.
614
(15) Zuleta, E. C.; Rios, L. A.; Benjumea, P. N. Fuel Process Technol. 2012, 102, 96-101.
615
(16) Sarin, A.; Arora, R.; Singh, N. P.; Sarin, R.; Malhotra, R. K.; Sarin, S. Energy Fuels
616 617 618
2010, 24, 1996-2001. (17) Sarin, A.; Arora, R.; Singh, N. P.; Sarin, R.; Malhotra, R. K.; Kundu, K. Energy 2009, 34, 2016-2021.
619
(18) Moser, B. R. Energy Fuels 2008, 22, 4301-4306.
620
(19) Park, J.-Y.; Kim, D.-K.; Lee, J.-P.; Park, S.-C.; Kim, Y.-J.; Lee, J.-S. Bioresour.
621
Technol. 2008, 99, 1196-1203.
622
(20) Sarin, R.; Sharma, M.; Sinharay, S.; Malhotra, R. K. Fuel 2007, 86, 1365-1371.
623
(21) Su., Y.-C.; Liu, Y. A.; Tovar, C. A. D.; Gani, R. Ind. Eng. Chem. Res. 2011, 50, 6809-
624 625
6836. (22) Davis, R.; Mohtar, S.; Tao, B. Production of low-tem biodiesel through urea
626
clathration. In Proceedings of the 2007 ASABE Annual International Meeting; American Society
627
of Agricultural and Biological Engineers: St. Joseph, MI, USA, 2007; Paper No. 076235.
628 629 630 631
(23) Dunn, R. O.; Shockley, M. W.; Bagby, M. O. SAE Trans., Sec. 4: J. Fuels Lubr. 1997, 106, 640–649. (24) Clements, L. D. Blending rules for formulating biodiesel fluid. In Liquid Fuel and Industrial Products from Renewable Resources: Proceedings of the Third Liquid Fuel
28 ACS Paragon Plus Environment
Page 28 of 37
Page 29 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
632
Conference; Cundiff, J. S.; Gavett, E. E.; Hansen, C.; Peterson, C.; Sanderson, M. A.; Shapouri,
633
H.; VanDyke, D. L. Eds. American Society of Agricultural Engineers: St. Joseph, MI, USA,
634
1996; pp 44-53.
635
(25) Standard Test Method for Cloud Point of Petroleum Products (Constant Cooling Rate
636
Method). In Annual Book of ASTM Standards; ASTM International: West Conshohocken, PA.,
637
USA, 2003; Vol. 05.01; method D 5773.
638
(26) Imahara, H.; Minami, E.; Saka, S. Fuel 2006, 85, 1666-1670.
639
(27) Standard Specification for Biodiesel Fuel Blend Stock (B100). ASTM D 6751-15a. U.
640
S. Department of Energy, Office of Energy Efficiency and Renewable Energy, Alternative Fuels
641
Data Center: Washington, DC 2016; http://www.afdc.energy.gov/fuels/biodiesel_
642
specifications.html (accessed August 3, 2016).
643 644 645 646
(28) Cermak, S. C.; Evangelista, R. L.; Kenar, J. A. Distillation – Advances from Modeling to Applications; Zereshki, S., ed.; InTech: Rijeka, Croatia, 2012; pp 109-140. (29) Knothe, G.; Krahl, J.; Van Gerpen, J., eds. The Biodiesel Handbook, 2nd Edition; AOCS Press: Urbana, IL, USA, 2010; p 462.
647
(30) Giakoumis, E. G. Renew. Energy 2013, 50, 858-878.
648
(31) Giraldo, S.Y.; Rios, L. A.; Suárez, N. Fuel 2013, 108, 709-714.
649
(32) Joshi, H.; Toler, J.; Moser, B. R.; Walker, T. Eur. J. Lipid Sci. Technol. 2009, 111,
650 651
464-473. (33) Tyson, K. S.; McCormick, R. L. Technical Report No. NREL/TP-540-40555: Biodiesel
652
Handling and Use Guidelines. National Renewable Energy Laboratory: Golden, CO, 2006; pp
653
17-38.
29 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
654 655 656 657
(34) Pérez, A.; Casas, A.; Fernández, C. M.; Ramos, M. J.; Rodríguez, L. Bioresour. Technol. 2010, 101, 7375-7381. (35) Sern, C. H.; May, C. Y.; Zakaria, Z.; Daik, R.; Foon C. S. Eur. J. Lipid Sci. Technol. 2007, 109, 440-444.
658
(36) Fukuda, H.; Kondo, A.; Noda, H. J. Biosci. Bioeng. 2001, 92, 405-416.
659
(37) Wang, P. S.; Tat, M. E.; Van Gerpen, J. J. Am. Oil Chem. Soc. 2005, 82, 845-849.
660
(38) Lee, I.; Johnson, L. A.; Hammond, E. G. J. Am. Oil Chem. Soc. 1995, 72, 1155-1160.
661
(39) Warasanam, S.; Pengprecha, S. Synthesis of Pour Point Depressant from Dicarboxylic
662
Acid for Biodiesel. In Proceedings of the International Conference on Chemical Processes and
663
Environmental Issues (ICCEE’2010); Singapore, July 15-16, 2012; pp 183-186.
664
(40) Moser, B. R. Energy Fuels 2014, 28, 3262-3270.
665
(41) Dmytryshyn, S. L.; Dalai, A. K.; Chaudari, S. T.; Mishra, H. K.; Reaney, M. J.
666 667 668
Bioresour. Technol. 2004, 92, 55-64. (42) Costa, M. C.; Boros, L. A. D.; Coutinho, J. A. P.; Krähenbühl, M. A.; Meirelles, A. J. A. Energy Fuels 2011, 25, 3244-3250.
669
(43) Dörfler, H.-D.; Pietschmann, N. Colloid Polym. Sci. 1990, 268, 567-577.
670
(44) Lopes, J. C. A.; Boros, L.; Krahenbuhl, M. A.; Meirelles, A. J. A.; Daridon, J. L.;
671 672 673
Pauly, J.; Marrucho, I. M.; Coutinho, J. A. P. Energy Fuels 2008, 22, 747-752. (45) Yoshida, S.; Sugami, Y.; Minami, E.; Shisa, N.; Hayashi, H.; Saka, S. J. Am. Oil Chem. Soc. 2017, 94, 1087-1094.
674
(46) Coutinho, J. A. P.; Daridon, J.-L. Pet. Sci. Technol. 2005, 23, 1113-1158.
675
(47) Dunn, R. O. Trans. ASABE 2012, 55, 637-646.
676
(48) Sear, R. P. J. Phys. Cond. Matt. 2007, 19, paper no. 033101.
30 ACS Paragon Plus Environment
Page 30 of 37
Page 31 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
677 678
Energy & Fuels
(49) Teixeira, G. A. A.; Maia, A. S.; Santos, I. M. G.; Souza, A. L.; Souza, A. G.; Queiroz, N. J. Therm. Anal. Calorim. 2011, 106, 563-567.
679
(50) Dunn, R. O. J. Am. Oil Chem. Soc. 2008, 85, 961-972.
680
(51) Dunn, R. O. J. Am. Oil Chem. Soc. 1999, 76, 109-115.
681
(52) Zabarnick, S.; Widmor, N. Energy Fuels 2001, 15, 1447-1453.
682
(53) Moynihan, C. T.; Shahriari, M. R.; Bardakci, T. Thermochim. Acta 1982, 52, 131-141.
31 ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Figure 1 84x62mm (300 x 300 DPI)
ACS Paragon Plus Environment
Page 32 of 37
Page 33 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
Figure 2 84x60mm (300 x 300 DPI)
ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Figure 3 165x118mm (300 x 300 DPI)
ACS Paragon Plus Environment
Page 34 of 37
Page 35 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
Figure 4 165x115mm (300 x 300 DPI)
ACS Paragon Plus Environment
Energy & Fuels 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Figure 5 84x60mm (300 x 300 DPI)
ACS Paragon Plus Environment
Page 36 of 37
Page 37 of 37 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Energy & Fuels
Figure 6 167x59mm (300 x 300 DPI)
ACS Paragon Plus Environment