Skip to main content

A novel design for biodiesel production from methanol + mutton bone fat mixture

Abstract

Bioenergy plays a significant role in the green transition. In this work, the conversion of methanol and mutton bone fat oil (as a low-cost feedstock) for bioenergy production was studied. The five-level, three-factor response surface methodology (RSM) was used to optimize the transesterification reaction conditions for produced biodiesel. Twenty ultrasonic-assisted experiments at the frequency of 25 kHz were conducted to investigate the effects of methanol/oil molar ratio (M/O) and concentrations of KOH and NaOH as catalysts on biodiesel yield. A second-order polynomial equation was developed by fitting the RSM experimental data using Design-Expert software. Results showed that the optimum biodiesel yield of 90.087% could be achieved by the KOH catalyst with 2.5 wt% concentration and 15:1 M/O during 3 h of the reaction. Furthermore, the biofuel analyses showed that methanol and mutton bone fat oil can be used as a proper feedstock for biofuel production. In the following, a membrane filtration package system is proposed and modeled. The reaction kinetics was determined based on experimental data. The results of the mathematical modeling showed the reaction time appears to be 6 times shorter in a membrane setup (30 min). Consequently, membrane application is highly recommended for biodiesel production from mutton bone fat oil.

Introduction

The demand for new energy sources is rising fast, because of rapid population growth and transportation networks. Therefore, one of the main issues for humanity in the current century is providing energy and natural sources being depleted [1]. It is predicted that by 2030, 80% of energy sources will comprise fossil fuels [2], which can last only a few decades in the twenty-first century. For example, diesel is a fossil fuel that causes many environmental problems due to releasing toxic compounds such as carbon monoxide, sulfur dioxide and nitrogen dioxide [2].

Biodiesel (monoalkyl ester) is one of the diesel-alternatives with less contamination potential, which can be obtained from renewable or natural resources [3]. Compared to fossil fuels, biodiesel has similar chemical properties to petroleum–diesel and emits fewer greenhouse gases and air-pertinent pollutants [4]. However, biodiesel is denser and more viscous with a higher cetane number than fossil diesel [5]. Biodiesels have high flash points and therefore they are inflammable [6]. Mixing biodiesel with diesel fuel leads to a decrease in unburned and polycyclic aromatic hydrocarbons released from diesel engines [7].

Methanol is the most frequently applied alcohol to achieve transesterification of biofuel production due to its low cost, physical and chemical advantages. It is as a key component of biodiesel and makes up about 20% of the biodiesel weight. Methanol as a fuel additive also can be blended with biodiesel in a car engine. A variety of edible oils could be used as feedstocks for biodiesel production (for example, rapeseed, sunflower, soybean, and palm oil). Still, it is not economically feasible to use edible oils for fuel. Thus, recent research has focused on non-edible oils, wastes of cooking oils, and waste animal fats as new alternatives for biodiesel production [8,9,10,11]. The volume of oil-free fatty acid (FA) has a direct impact on the biodiesel production process. When FA concentration is higher than 3% by weight, soap is formed during the production process and the catalytic activity decreases, and therefore the biodiesel generation efficiency is reduced [12, 13]. For high free fatty acids feedstocks, a two-step esterification–transesterification mechanism is often employed to improve the quality of biodiesel [14].

Vicente et al. [15] produced biodiesel from sunflower oil by the transesterification method using various catalysts. Because of the low free-FA content of the sunflower oil, biodiesel is generated by using only a one-step in situ transesterification reaction. In their study, biodiesel synthesis was carried out at 65 °C, the methanol to sunflower oil molar ratio of 6:1 and the catalyst concentration 1 wt% by weight in 4 h.

Wyatt et al. [16] have reported biofuel production from beef fat, chicken fat, and pork fat. They showed that the animal fats were featured with higher lubrication and oxidation stability as well as lower NOx content compared to soybean oil. Besides, the production of biodiesel from waste animal fat in the presence of methanol was experimentally examined in a work prepared by Srinivasan et al. [17]: the maximum yield of 94% was reported at the optimal conditions (M/O of 6:1, 0.5wt% catalyst, 60 °C, and 2 h).

Sonochemistry or ultrasound has been proven as a proficient way to increase the rate of chemical synthesis [18,19,20,21,22,23]. As the findings have shown, ultrasonic mixing can yield smaller droplets compared to a conventional mixer and therefore generates a much larger surface area available for the reaction process [24]. Normal-chain alcohols have a faster reaction rate, compared to the secondary and tertiary alcohols with an alcohol-to-oil moral ratio of 6:1. The low-frequency ultrasonic (28–40 kHz) is an effective way to lower the reaction time (10–20 min). Higher efficiency, but longer reaction time was obtained from the 28-kHz frequency [25].

Various vegetable oils, such as palm, soybean and sunflower oils, were studied for biodiesel production by Stavarache et al. [23]. The transesterification reactions were conducted using conventional and 45 kHz frequency ultrasound-assisted methods at 38 °C to 40 °C, ultrasonic waves are found to increase reaction efficiency and lower the reaction temperature.

Kelkar et al. [26] examined the effects of ultrasonic cavitation on the esterification process. The reaction between fatty acid and methanol took place in an ultrasonic system by the H2SO4 catalyst. The authors argued that ultrasonic waves increased biodiesel yield in comparison to conventional methods and lowered the reaction time. At optimized conditions (alcohol-to-oil molar ratio of 10:1, H2SO4 catalyst concentration of 2 wt%, reaction temperature of 40 °C and reaction time of 90 min), a yield of over 95% was obtained.

The soybean oil biodiesel production by ultrasonic waves was conducted by Naresh et al. [27], who obtained a biodiesel yield of 90% by using 0.5 wt% KOH catalyst concentration, 6:1 methanol:oil molar ratio, 611 kHz ultrasonic frequency and 30 min reaction time. The results showed that by high-frequency ultrasound more than 90% reaction yield was obtained in 30 min.

Deng et al. [28] worked on the Jatropha oil biodiesel production. An appropriate physical property of the product was reported by applying a two-step process using mechanical stirring at 600 rpm and ultrasound-assisted methods via the H2SO4 catalyst and transesterification with the NaOH catalyst. The results of the two-stage reaction showed that during 1 h reaction time of the esterification process and 30 min of the transesterification stage, the yield of biodiesel reached 96.4%. In addition, this research indicates the two-step process using ultrasonic system is the most effective method to produce biodiesel from high free fatty acid oils.

Gole and Gogate [29] investigated the application of ultrasonic devices for biodiesel generation from non-edible oils. The reaction rate was examined in a temperature change from 30 °C to 50 °C and a frequency of 20 kHz. They optimized the process by changing parameters such as alcohol/oil ratio, catalyst concentration, reaction time, and temperature. The optimal conditions for biodiesel synthesis in their research are: alcohol-to-oil molar ratio of 6:1, KOH catalyst concentration of 1 wt%, transesterification reaction temperature and time of 40 °C and 40 min, respectively.

Choudhury et al. [30], studied the ultrasonic-assisted biodiesel manufacturing from Jatropha oil. The results showed the highest transesterification efficiency is obtained by the alcohol-to-oil molar ratio of 11:1, the catalyst concentration is 5.5 wt% and the reaction temperature of 64 °C. Furthermore, by applying the ultrasonic method, it is possible to reduce the required energy for biodiesel synthesis by 20% compared to the conventional method.

Khan et al. [31] examined the biodiesel synthesis from Eucalyptus oil by the sonication system at various frequencies, powers, and temperatures. The maximum efficiency of 96.73% was achieved by the ultrasonic power of 110.25 W, alcohol/oil molar ratio of 6.36:1, a frequency of 29.54 kHz and reaction temperature and time of 35 °C and 8 min, respectively.

The chicken fat oil is used as a feedstock for producing biodiesel in an ultrasound-assisted system prepared by Fayyazi et al. [32]. The results showed that the yield of biodiesel production from chicken fat is 94.8% by 24 kHz ultrasonic frequency, the catalyst concentration of 1 wt%, alcohol-to-oil molar ratio of 7:1: and the reaction time of 9 min. In their work, the reaction time was reduced by 87.5% in the ultrasonic method in comparison to the conventional method.

Mirab et al. [33] studied the effect of ultrasound on biodiesel production from chicken feet oil. The results showed that using the methanol to oil molar ratio of 12:1, the KOH catalyst concentration of 1 wt% and the 45-kHz ultrasound frequency, the highest efficiency of 89.74% can be achieved.

In other study, a two-step esterification and transesterification process of diseased swine fat based biodiesel production was tested by ultrasound method [34]. The results showed that the transesterification reaction optimal condition are catalyst concentration 1.11 wt%, reaction temperature 62.3 °C, methanol/oil molar ratio 7.42:1 and reaction time 116.14 min. In their study, the catalyst concentration consumption was reduced by 63.3% in comparison with the previous works.

Nevertheless, conventional methods for biodiesel production have some disadvantages, such as the high methanol consumption for reversible transesterification [35, 36]. This will lead to enhanced reaction time as well as biodiesel production cost. Other drawbacks include the significant loss of methanol and water unreacted during biodiesel purification [37]. To overcome these problems, the membrane technique is suggested as an appropriate modification method by researchers over the last decade [36].

Membranes are widely used to separate a desirable or undesirable substances from a mixture (e.g., hydrogen, CO2, CH4, H2S, etc.) from gas mixtures [38,39,40,41]. The membrane separation process can remove the biodiesel from products after reacting in the reactor. The residue could be recycled back to the reactor for further reactions. On the other hand, the membrane dry-washing procedure could reduce water consumption and offer high fuel quality [42,43,44].

Sokac et al. [37] worked on polymeric membranes for biodiesel purification. The membranes include polyethersulfone, polyacrylonitrile, polypropylene and regenerated cellulose. They showed that polyacrylonitrile membrane could have a good performance for separating biodiesel produced by lipase-catalyzed transesterification. Alves et al. [44] used a 30-kDa membrane for biodiesel purification and indicated that the membrane technology is a suitable alternative for biodiesel purification. They approved that membrane technology is a suitable alternative for biodiesel purification [45].

Poly (ether sulfone) hollow fiber membranes (PES-HFM) were selected as a membrane in a work prepared by Noriega [46, 47] and the process was experimentally tested and modeled. Results showed that high-quality biodiesel could be obtained in a membrane reactor, generating 10 times better purity than that of the conventional reactor [47].

Cao et al. [48, 49] used a Filtanium ceramic membrane for canola oil biodiesel purification. By recycling the retentate to the reactor, high purity biodiesel was produced in their work. They also modeled the process and evaluated the reaction rate constants [50], considering NaOH catalyst with different weight percent (0.05, 0.1, and 0.5 wt %) and a methanol/oil ratio of 24:1 was used in their work. They showed that membrane technology enhances the reaction rate.

Talaghat et al. [51] modeled a continuous membrane tubular reactor used for biodiesel generation in the presence of an alkaline catalyst, comparing membrane and conventional reactors. The highest conversion was achieved in a membrane reactor with a methanol/oil ratio of 24.

In this work, the mutton bone oil, for the first time, was used as a raw material for producing biodiesel. Attempts have been made to accelerate the reaction rate by simultaneous application of an ultrasonic bath and magnetic stirrer. An experimental setup is designed to evaluate the impact of the alkaline catalysts (NaOH and KOH) in the transesterification process. The various variables (alkali catalysts, catalyst concentration and M/O) were optimized by using a central composite design (CCD) approach-based response surface methodology (RSM) to maximize the biodiesel yield with the aid of Design-Expert software. Finally, a mathematical model of biodiesel production in a membrane system is developed, and the reaction constants are calculated.

Materials and methods

Raw materials

The mutton bones were heated in water (1:3) at 80 °C for 4 h. The melted bone fat was collected from the water surface and centrifuged for 20 min to accumulate the oil. The methanol (99.85%) catalysts (KOH and NaOH) were supplied by Merck Company. The other used chemicals were analytical grade and obtained from Merck, Samchun, Carlo Erba, Scharlau, Alfa Aesar and Sigma-Aldrich.

Experimental setup

The reaction was conducted in a 500-ml three-neck lab glass flask with a reflux condenser, a mechanical mixer (TAT, 1500 rpm), and a digital thermometer (TFA, 30.1048) submerged in an ultrasonic bath (Elma Ultrasonic TI-H-5 type, Germany, 3.5L, 25.45 kHz, and 100 W). The tests were conducted under atmospheric pressure.

Transesterification process

The three-neck glass flask was filled with methanol and an alkali catalyst (KOH or NaOH). The flask was fixed in the ultrasonic cleaning bath and the mutton oil was poured into the flask. The reaction continued for 3 h at 60ºC with the frequency of 25 kHz and under mechanical stirring at 500 rpm. After timing the transesterification reaction, the glycerol and biodiesel layers were separated by centrifugation (200 rpm, 10 min). The mixture was settled for 12 h and the biodiesel layer was washed several times with distilled water to subtract the remaining catalyst, methanol, and soap. Afterward, the washed biodiesel was heated (107 °C, 1 h) to eliminate the remaining water and methanol. The following formula was applied to identify the biodiesel yield [52]:

$$Yield\left(\text{\%}\right)=\frac{{W}_{biodiesel}}{{W}_{mutton-oil}}\times 100,$$
(1)

where Wbiodisel and Wmutton-oil are the weight of biodiesel and the weight of mutton oil, respectively.

Experimental design

The RSM was applied to examine the impacts of catalyst type, catalyst concentration, and M/O on the transesterification process. The numerical form of independent variables can be created as Eq. (2) [53]:

$$Y=F\left({X}_{1},{X}_{2},{X}_{3},\dots ,{X}_{n}\right)\pm c,$$
(2)

where Y is the response (e.g., the yield), F stands for the function, c stands for the experimental deviation, and X1,X2,X3, …,Xn represent independent variables.

If the response (y) is matched by a linear function of the independent variable, Eq. (2) could be rewritten as Eq. (3):

$$ Y = \beta_{0} + \beta_{1} X_{1} + \beta_{2} X_{2} + \cdots + \beta_{n} X_{n} \pm c. $$
(3)

Here, the type of catalyst was represented as a discrete variable and the M/O as well as the catalyst concentration were considered the continuous variables. The continuous variables were selected in 5 levels. A mathematical equation can be written using an RSM of 20 experiments. Table 1 lists the coded and not-coded independent variables (Xi) and levels for CCD applied to Design-Expert software.

Table 1 Factors and their levels for central composite design

The experimental data were analyzed by the second-order polynomial regression model (Eq. (4)) [54]:

$$ Y = \beta_{0} + \,\sum\nolimits_{i = 1}^{n} {\,\beta_{i} } X_{i} \, + \,\sum\nolimits_{i = 1}^{n} {\beta_{ii} X_{i}^{2} \, + \,\sum\nolimits_{i = 1}^{n} {\sum\nolimits_{j = 1}^{i - 1} {\beta_{ij} X_{i} X_{j} } } } , $$
(4)

where i, j, n, Y, X and β0 are the linear coefficient, quadratic coefficient, the number of independent factors, the response factor (biodiesel yield), the independent factor and the regression coefficient, respectively.

Biodiesel characteristics

The biodiesel characteristics are measured by the following devices/techniques.

Fatty acid methyl ester content

To reveal the fatty acid methyl ester (FAME) composition of the biodiesel, a gas chromatograph 5973 (GC, Agilent Technologies) with a VF-1 (Agilent Technologies) capillary column (30 m × 0.25 mm × 0.25 μm) was utilized.

Kinematic viscosity

A Canon-Fenske Routine Viscometer (Canon USA Inc., State College, PA) was utilized to measure the viscosity of the biodiesel sample based on the ASTM D 92–85 method [55].

Density

The ASTM D 4052–91 was applied to estimate the density of biodiesel. The sample was poured into a graduated cylinder (100 ml) at a specific temperature (25 °C) and a hydrometer was used to determine the sample gravity [56].

Acid value

The KS M ISO 6618 (Korean standard association) was used to measure acid value. Initially, 10 g of the sample was poured into a flask with a 250-ml capacity. Afterward, 100 mL of ethanol and ether solution with a volume ratio of 1:2 was mixed with three drops of phenolphthalein and injected into the sample. The solution was titrated against 0.1 N KOH solution. The endpoint was determined based on pink color persistency (10 s). The acid value could be obtained by Eq. (5) as follows [57]:

$$AV=\frac{A\times N\times 5.611}{W},$$
(5)

where AV represents the acid value (mg KOH/g), A stands for the consumption of N/10 KOH (mL), N represents the titer of N/10 KOH (-), and W stands for the sample volume (mL).

Saponification value

Saponification value refers to short chains in alkyl groups of biodiesel fatty acids [56]. To measure the saponification value (SV), AOCS CD3 titration method was used. 1 g of mutton bone biodiesel was mixed with 25 ml of 0.5 N KOH solution. Besides, 4 ml of ethanol and ether solution with a volume ratio of 1:2 solution was introduced to the sample. The mixture is refluxed for 30 min. After cooling to 25 °C, a few drops of phenolphthalein were added to the solution as pH indicator and the endpoint was signaled by the appearance of the pink color. The solution was titrated in the presence of 0.5 N HCI solution till the pink color was eliminated. Besides, a blank titration on the water was done in the same quantity of KOH solution under the same condition and time. The saponification value (SV) could be calculated as follows [56]:

$$SV=56.1\times \frac{N\times \left({V}_{a}-{V}_{b}\right)}{M},$$
(6)

where M is the weight of biodiesel (g), Va is the HCl volume Volume (ml) used in the test, Vb is the HCl volume (ml) used in blank and N is the Normality of HCL.

Iodine value

The level of unsaturation of biodiesel is evaluated by calculating the iodine value. One gram of biodiesel was dissolved in 10 ml of chloroform. Besides, 25 ml of Hanus solution was settled for 30 min in a dark space. Afterward, 10 ml of 15% KI (15 g KI dissolved in 100 ml) and the Hanus solution were added to the solution (biodiesel and chloroform). The prepared solution was titrated with 0.1 N Na2S2O3 until the yellow color of the solution turned into a transparent yellow color [58]. The iodine value could be calculated by Eq. (7):

$$IV=\frac{{M}_{1}\times \left({V}_{b}-{V}_{t}\right)}{{M}_{2}},$$
(7)

where IV is iodine value (g I2/100 g amostra, Vt is Na2S2O3 solution volume (mL) for the sample, Vb is Na2S2O3 solution volume for the blank (mL), M1 is mass of the biodiesel sample (g) and M2 is the molar mass of iodine.

Higher heating value

The empirical equations were used to determine the higher heating value (HHV). An increase in IV leads to a decrease in the heat content of a sample. Thus, Eq. (8) could be used to calculate the HHV (MJ/kg) of the biodiesel [59]:

$$HHV=49.43-\left[\frac{0.041\times SV+0.015\times IV}{{M}_{2}}\right].$$
(8)

Cetane number

The diesel quality testing by ASTM D613 was used to determine the cetane number (CN). The cetane number could be correlated as a function of IV and SN [60]:

$$CN=46.3+\left(\frac{5458}{SV}\right)-0.225\times IV.$$
(9)

Results and discussion

Response surface methodology

The effect of M/O, catalyst concentration and catalyst type on biodiesel yield was studied by using five-level three-factor CCD. Table 2 lists the input variables, the coded values and the experimental results for biodiesel yield introduced to Design-Expert software.

Table 2 Input variables, the coded values and the experimental results for biodiesel yield

Evaluation of regression model for the mutton biodiesel yield

The coefficients of the second-order polynomial equation (Eq. (4)) were determined and their significance was tested based on the regression analysis. The fitting model supported the significance of three linear coefficients (X1, X2, X3), three quadratic coefficients (X21; X22; X23), and three cross-product coefficients (X1X2, X1X3, X2X3) (Tables 1, 2). The results of the analysis of variance (ANOVA) for the response surface model are listed in Table 3.

Table 3 Results of the analysis of variance (ANOVA) for mutton bone biodiesel

Moreover, the model coefficients are examined. As shown in Table 3, the p-values of the linear coefficients are major compared to the other terms. Still, to diminish error, all the coefficients were taken into account. Based on Table 3, a small deficiency in fitting was observed; the model represents the appropriate relationship between the parameters. It was found that the X3 (linear effect of catalyst type), \({X}_{1}^{2}\) (quadratic effect of M/O), \({X}_{2}^{2}\) (quadratic effect of catalyst concentration), X1X3 (the interaction effect of M/O and catalyst type) and X2X3 (the interaction effect of catalyst concentration and catalyst type) have a significant effect on the biodiesel yield. The final estimate response model equation (based on the experimental data) for mutton biodiesel is as follows:

$$Y=79.41-0.16{X}_{1}-0.68{X}_{2}+1.59{X}_{3}+5.63{X}_{1}\times {X}_{3}+6.19{X}_{2}\times {X}_{3}-1.33{X}_{1}^{2}-{2.12X}_{2}^{2},$$
(10)

where Y represents the response factor, i.e., FAME content (% (w/w)) and X1, X2, and X3 stand for the quantities of the independent variables as indicated in Table 2. The coefficient estimates and probability values of the model are listed in Table 4.

Table 4 The coefficient estimates and significance of the response surface model

Model accuracy check

According to the ANOVA results, the quadratic polynomial model could demonstrate the actual relationship of FAME yield and the model variables. In Table 5, the statistical summary of variance analysis for the proposed model is shown. The coefficients of determination (R2 = 0.9437 and R2adj = 0.9028) for the obtained correlation are near unity, which shows the excellent significance of the proposed model.

Table 5 Statistical summary of variance analysis for the proposed model

Figure 1 illustrates a unit slope line that shows the zero deviation between the predicted and observed values. As can be seen, all the points are close to the line of the perfect fit. The figure approves the model’s accuracy. Therefore, the proposed correlation (Eq. (10)), is capable of predicting experimental outcomes.

Fig. 1
figure 1

The predicted versus observed values for biodiesel yield (R2 = 0.9437 and R.2adj = 0.9028)

Effect of process variables on biodiesel synthesis

Figure 2 illustrates the effect of M/O, KOH concentration and their reciprocal interaction on mutton bone biodiesel synthesis. The biodiesel yield is moderately influenced by the M/O at low catalyst concentration. This could be happen as increasing in the catalyst concentration could enhance the rate of the unwanted saponification reaction. On the other hand, at high catalyst concentration, a rise in M/O elevates the rate of transesterification reaction and compensates the effect of saponification reaction. Therefore, the impact of M/O is considerable at high catalyst concentration. The maximum acquisition of FAME content is achieved with a high M/O and 2.5 wt% catalyst concentration.

Fig. 2
figure 2

The effect of M/O, KOH concentration and their reciprocal interaction on mutton bone biodiesel synthesis at 60 °C, 3 h, and 500 rpm

The influence of NaOH catalyst concentration and M/O on mutton bone biodiesel synthesis is shown in Fig. 3. Similar trend was observed for NaOH catalyst. The FAME content increases with a decrease in catalyst concentration and M/O. The highest content of methyl ester is achieved with a catalysis level of 1.5% (w/w) and M/O of 1:9.

Fig. 3
figure 3

The effect of NaOH catalyst amount, M/O, and their reciprocal interaction on mutton bone biodiesel synthesis at 60 °C, 3 h, and 500 rpm

By considering the desirability function approach, the optimum value of the response surface, catalyst concentration, and M/O was obtained as presented in Fig. 4. The results approved that the maximum yield of 90.087% could be obtained with KOH catalyst concentration of 2.5 wt%; and M/O of 15:1.

Fig. 4
figure 4

Desirability ramp of yield at 60 °C, 3 h, and 500 rpm

To check the validity of the results obtained in Fig. 4, an experiment was set under these conditions. The experimental yield of mutton bone biodiesel was estimated as 90.0524%, which was in good consistency with the desirability function result (90.087%).

(In each figure, more explanation and description are necessary. The current version only lists what can be shown.)

Characterization of the biodiesel sample

The analyzing methods for evaluating the characterization of the mutton bone biodiesel sample are previously discussed in Sect. 2–5. The GC/MS chromatogram analysis of biodiesel is shown in Fig. 5. The results indicate that biodiesel contains a variety of fatty acid methyl esters from C14 to C20, which include mostly palmitic acid (C16:0), stearic acid (C18:0) and oleic acid (C18:1). The FAME composition of the produced biodiesel from mutton bone oil is listed in Table 6. To make comparison possible, the FAME composition of the biodiesels generated from soybean oil, lard oil, chicken fat oil, and mutton fat oil are also listed in this table. It could be seen that the produced biodiesels from animal wastes are high in oleic acid (22–45%), palmitic acid (~ 17–23%) and stearic acid (~ 6–27%). However, the biodiesel generated from plant source lipid (soybean oil) most has Linoleic fatty acid. Furthermore, as a result of Table 6 and the analysis of the previous literature studies, the mutton bone biodiesel and mutton fat biodiesel feature notably higher stearic contents in comparison to chicken fat biodiesel.

Fig. 5
figure 5

The GC/MS chromatogram analysis of mutton bone biodiesel

Table 6 The comparison of the FA composition (wt %) of the mutton bone biodiesel with the other biodiesels

The comparison between the standard values with the experimental results is also tabulated in Table 7. The following 5 features admit the engine's good performance of biodiesel fuel prepared from mutton bone oil:

  1. 1.

    Flashpoint is the temperature at that a flame appears when the fuel is exposed to fire. This is a key characteristic of fuel in terms of the safety of storing and shipping fuel. This parameter is a function of fuel’s volatility, which is a key factor for engine start and warming function [67]. As listed in Table 7, the pure biodiesel obtained from mutton fat has a higher flashpoint compared to diesel. Therefore, biodiesel is considerably safer than diesel for storage. A low flashpoint of liquid fuel may inhibit auto explosion and risks at elevated temperatures.

  2. 2.

    Another key characteristic of fuel is its viscosity which influences the flow behavior. In the case of mutton bone biodiesel, the kinematic viscosity was higher than that of the ASTM standard (Table 7). The higher clearly, the kinematic viscosity values change depending on the type of FAME. For instance, higher quantities of saturated FAs along with bigger carbon chains lead to an increase in kinematic viscosity [68].

  3. 3.

    The presence of unsaturated FAs in biodiesel is needed to a specific extent to ensure no fuel solidification [67]. On the other hand, the high level of unsaturated FAs may lead to the formation of irreversible polymerized condensation products. As listed in Table 7, the iodine value of the obtained biodiesel was 36.54 grI2/100 ml of oil. The maximum iodine value of 120 grI2/100 ml was advised by EN-14214 [60], which admits the good performance of the produced biodiesel as a fuel.

  4. 4.

    The heating value referred to the enthalpy releases during the perfect ignition of fuel at constant volume. The greater the heating value of the fuel, the lesser the fuel volume needed to achieve the same power output for an engine [69]. It has been reported that the higher heating values (HHVs) of biodiesels are in the range of 39–41 MG/kg, which is moderately less than those of gasoline (46 MJ/kg), petrodiesel (43 MJ/kg), or petroleum (42 MK/kg) [56]. Therefore, the HHV of the produced biodiesel (40.0265 MJ/kg) gives an appropriate value.

  5. 5.

    In general, a higher CN value for diesel fuel means a shorter ignition delay and combustion duration, fewer knocking, and fewer nitrogen oxides (NOx) [70, 71]. The CN value for the mutton bone biodiesel (63.37) is higher than that of the diesel (47–55) (Table 7). This makes the mutton bone biodiesel more attractive than diesel fuel. Furthermore, it could be used as a cetane enhancer in petroleum diesel fuels.

Table 7 Fuel properties of biodiesel from mutton bone oil

Modeling of methanol + mutton bone fat mixture for biodiesel production in a membrane reactor system

In this part, a membrane system with a recycle stream is proposed to compensate for the long residence time of the biodiesel production process from methanol + mutton bone fat mixture. The recycled stream could improve the transesterification rate and product yield. On the other hand, the membrane system is applied for purifying biodiesel.

Determination of the reaction kinetics

The following reaction could be considered for biodiesel production from methanol + mutton bone fat mixture [72, 73]:

$$TG+3M\to P+G,$$
(11)

where [TG], [M], [P] and [G] denote the triglyceride, methanol, FAME and glycerol concentrations.

The impact of ultrasonic waves on reactants (TG and M) are not the same. Therefore, Eq. 12 is proposed for the rate equation to consider individual reaction rate orders [72]:

$${r}_{P}=\frac{d\left[P\right]}{dt}=k{\left[TG\right]}^{\alpha }{\left[M\right]}^{\beta }.$$
(12)

The linearization equation is obtained from Eq. (12):

$$ln\left({r}_{P}\right)=ln\left(k\right)+\alpha \times ln\left(\left[TG\right]\right)+\beta \times ln\left(\left[M\right]\right).$$
(13)

Experimental data were curve-fitted in Eq. 13. The results are shown in Table 8.

Table 8 Reaction kinetic constants for the proposed model (T = 60 °C)

Mathematical modeling of the membrane reactor system

Figure 6 shows a membrane system proposed by biodiesel production. The reactants including methanol + mutton bone fat oil mixture are fed to the fully mixed reactor system. The products are then directed to a membrane system. The biodiesel (FAME) is permeated through the membrane and the retentate is recycled to the reactor. Therefore, the biodiesel purification and reaction rate enhancement will take place simultaneously. In this study, a Filtanium ceramic membrane (TAMI, Nyons, France) constructed of a titanium oxide support and the active layer was selected based on the work prepared by Cao et al. [48].

Fig. 6
figure 6

Schematic of the membrane reactor system used for the biodiesel production

For finding the kinetics of mutton bone oil biodiesel with an ultrasonic bath the following assumptions are considered:

  • 1-The recycled stream is fully mixed which is equivalent to the statement that all the properties of this stream (e.g., temperature and concentration are uniforms.

  • 2-The feed mass flow rate is assumed to equal to the product mass flowrate.

  • 3-Triglyceride is not presented in the reactor outlet stream.

  • 4-Two distinct phases were formed: methanol, glycerol and FAME are presented in a single mobile phase and triglyceride is formed in another phase in the reactor.

  • 5-Only FAME can permeate through the membrane.

Equation (14) could be obtained by the mentioned assumptions [49]:

$$ \mathop {\text{V}}\limits^{.}_{{{\varvec{out}}}} = \frac{{_{{\mathop {\text{m}}\limits^{.}_{{{\varvec{Total}} - {\varvec{in}}}} }} }}{{\rho_{out} }} = \frac{{F_{Methanol - in} \times MW_{Methanol} + F_{TG - in} \times MW_{TG} }}{{\rho_{out} }}. $$
(14)

In Eq. (14), \(\mathop {\text{V}}\limits^{.}_{out}\)\(,\boldsymbol{ }\boldsymbol{ }\boldsymbol{ },\boldsymbol{ }{F}_{Methanol-in},\boldsymbol{ }{F}_{TG-in}\boldsymbol{ }\mathrm{and}\boldsymbol{ }{MW}_{TG},\boldsymbol{ }{\rho }_{out}\) are permeate flow rate of the (lit/min), mass flow rate of the feedstock, methanol molar rate in the feed stream (mol/min), Triglyceride molar rate in the feed stream (mol/min), Triglyceride molecular weight (g/mol) and product density (g/mlit), respectively.

The components molar balances are illustrated in the following:

$$\frac{d(Methanol)}{dt}={F}_{Methanol-in}+{r}_{Methanol}{\times V}_{0},$$
(15)
$$\frac{d(TG)}{dt}={F}_{TG-in}+{r}_{TG}\times {V}_{0},$$
(16)
$$\frac{d(FAME)}{dt}={r}_{FAME}{\times V}_{0}-{F}_{FAME-out},$$
(17)
$$\frac{d(G)}{dt}={r}_{G}{\times V}_{0,}$$
(18)

where

$$ F_{FAME - out} = \left[ {FAME} \right]_{out} \mathop {\text{V}}\limits^{.} \times_{out} . $$
(19)

The volume of the mobile phase (Vmobile) can be calculated by Eq. (20):

$${V}_{mobile}={V}_{0}-\frac{\left[TG\right]\times {V}_{0}\times {MW}_{TG}}{{\rho }_{TG}}.$$
(20)

The concentration of the FAME in the mobile phase passing through the membrane could be obtained from Eq. 21:

$${\left[FAME\right]}_{out}=\frac{{V}_{0}\times \left[FAME\right]}{{V}_{mobile}}=\frac{\left[FAME\right]}{\left(1-\frac{\left[TG\right]\times {MW}_{TG}}{{\rho }_{TG}}\right)}.$$
(21)

In Eqs. (15) to (21), V0, [x], r, t, Fx-in and Fx-out are reactor volume (lit), concentration of component x (mol/lit), reaction rate (mol/(lit.min)), time (t), flowrate of component x in feed and product streams (mol/min), respectively. The modeling was performed by MATLAB 2016a software. The modified Rosenbrock method (ode23s) was used to solve the set of stiff ordinary differential equations (ODEs).

Model validation

At first, the mathematical modeling results were compared with experimental data obtained from Cao et al.’s work [48]. They produced biodiesel from canola oil using a 6-L membrane reactor system [48]. Figure 7 shows the comparison of experimental and calculated FAME concentration variation in the membrane reactor.

Fig. 7
figure 7

The comparison of experimental and calculated FAME concentration variation in the membrane reactor

The proposed membrane system for biodiesel generation from methanol + mutton bone fat mixture

Table 9 presents the system specifications for the membrane system. The system conditions are similar to those used for experimental tests.

Table 9 The operating parameters of the membrane reactor system

The membrane system performance for biodiesel production is investigated. Figure 8 shows the methanol and FAME concentrations in the membrane system at optimum condition (Fig. 4). As can be seen, after 30 min, a significant amount of FAME has been produced, which indicates the high efficiency of the proposed membrane system. It means that the reaction time in the membrane system (30 min) is 6 times shorter than the conventional method (3 h).

Fig. 8
figure 8

Methanol and FAME concentrations at reactor outlet, T = 60 °C, reactor volume = 80 lit

The biodiesel yield, the TG and the methanol conversion rates are shown in Fig. 9. A comparison between the biodiesel yield with Fig. 4 shows that the yield of the proposed system is equivalent to a single batch reactor with a reaction time of 3 h. Therefore, the membrane system has significantly improved the reaction rate.

Fig. 9
figure 9

Methanol conversion, TG conversion and FAME yield

Conclusions

The application of methanol for biodiesel production from mutton bone was examined experimentally. Two homogenous catalysts (KOH and NaOH) are used in an ultrasound-assisted system to perform the transesterification process. A response surface design methodology was assisted to evaluate the effects of M/O, type of alkali catalyst and catalyst concentration on biodiesel yield at the frequency of 25 kHz and temperature of 60 °C. Optimization of the process of biodiesel production was achieved by five-level-three-factors CCD using RSM. A second-order model was found to calculate the mutton bone yield as a function of the process variable. The optimum conditions were obtained as a methanol/oil of 15:1 and KOH concentration of 2.5 wt%. Under these conditions, the conversion rate exceeds 90% in three hours.

The analysis of density, acid value, saponification value, iodine value, kinematic viscosity and combustion properties showed the good performance of mutton bone biofuel generated through methanol in comparison with fossil fuels. The obtained biodiesel met the quality standards of American Communities. Finally, a mathematical model of biodiesel production in a membrane system is developed. The reaction rate constant is calculated as a function of ultrasonic frequency. Compared with the conventional method, the membrane system has significantly improved the reaction rate.

Data availability statement

No data are associated with this article.

References

  1. Modi DN. Biodiesel production using supercritical methanol. 2010.

  2. Chapman A, Itaoka K. Curiosity, economic and environmental reasoning: public perceptions of liberalization and renewable energy transition in Japan. Energy Res Soc Sci. 2018;37:102–10.

    Article  Google Scholar 

  3. Zhang Y. Design and economic assessment of biodiesel production from waste cooking oil. M.S. thesis. Ottawa, Canada: University of Ottawa; 2002.

    Google Scholar 

  4. Murugesan A, Umarani C, Subramanian R, Nedunchezhian N. Bio-diesel as an alternative fuel for diesel engines—a review. Renew Sustain Energy Rev. 2009;13(3):653–62.

    Article  CAS  Google Scholar 

  5. Knothe G. Dependence of biodiesel fuel properties on the structure of fatty acid alkyl esters. Fuel Process Technol. 2005;86(10):1059–70.

    Article  CAS  Google Scholar 

  6. Mythili R, Venkatachalam P, Subramanian P, Uma D. Production characterization and efficiency of biodiesel: a review. Int J Energy Res. 2014;38(10):1233–59.

    Article  Google Scholar 

  7. Boakye P. Biodiesel production from selected non-edible feedstocks using unsupported potassium carbonate. Master of science in chemical engineering, Kwame Nkrumah University of Science and Technology. 2013;10.

  8. Sivakumar P, Sindhanaiselvan S, Gandhi NN, Devi SS, Renganathan S. Optimization and kinetic studies on biodiesel production from underutilized Ceiba Pentandra oil. Fuel. 2013;103:693–8.

    Article  CAS  Google Scholar 

  9. Rashid U, Anwar F. Production of biodiesel through optimized alkaline-catalyzed transesterification of rapeseed oil. Fuel. 2008;87(3):265–73.

    Article  CAS  Google Scholar 

  10. Fadhil AB, Abdulahad WS. Transesterification of mustard (Brassica nigra) seed oil with ethanol: purification of the crude ethyl ester with activated carbon produced from de-oiled cake. Energy Convers Manage. 2014;77:495–503.

    Article  CAS  Google Scholar 

  11. Abd Rabu R, Janajreh I, Honnery D. Transesterification of waste cooking oil: process optimization and conversion rate evaluation. Energy Convers Manage. 2013;65:764–9.

    Article  CAS  Google Scholar 

  12. Dorado M, Ballesteros E, De Almeida J, Schellert C, Löhrlein H, Krause R. An alkali-catalyzed transesterification process for high free fatty acid waste oils. Transactions of the ASAE. 2002;45(3):525.

    Article  CAS  Google Scholar 

  13. Freedman B, Pryde E, Mounts T. Variables affecting the yields of fatty esters from transesterified vegetable oils. J Am Oil Chem Soc. 1984;61(10):1638–43.

    Article  CAS  Google Scholar 

  14. Sarantopoulos I, Chatzisymeon E, Foteinis S, Tsoutsos T. Optimization of biodiesel production from waste lard by a two-step transesterification process under mild conditions. Energy Sustain Dev. 2014;23:110–4.

    Article  CAS  Google Scholar 

  15. Vicente G, Martınez M, Aracil J. Integrated biodiesel production: a comparison of different homogeneous catalysts systems. Biores Technol. 2004;92(3):297–305.

    Article  CAS  Google Scholar 

  16. Wyatt VT, Hess MA, Dunn RO, Foglia TA, Haas MJ, Marmer WN. Fuel properties and nitrogen oxide emission levels of biodiesel produced from animal fats. J Am Oil Chem Soc. 2005;82(8):585–91.

    Article  CAS  Google Scholar 

  17. Srinivasan GR, Palani S, Jambulingam R. Biodiesel production from waste animal fat using a novel catalyst HCA immobilized AuNPS amine grafted SBA-15. J Eng Sci Technol. 2018;13(8):2632–43.

    Google Scholar 

  18. Stavarache C, Vinatoru M, Maeda Y. Aspects of ultrasonically assisted transesterification of various vegetable oils with methanol. Ultrason Sonochem. 2007;14(3):380–6.

    Article  CAS  Google Scholar 

  19. Wu H, Zong M-h. Effect of ultrasonic irradiation on enzymatic transesterification of waste oil to biodiesel. Washington: ACS Publications. 2007.

  20. Parkar PA, Choudhary HA, Moholkar VS. Mechanistic and kinetic investigations in ultrasound assisted acid catalyzed biodiesel synthesis. Chem Eng J. 2012;187:248–60.

    Article  CAS  Google Scholar 

  21. Kalva A, Sivasankar T, Moholkar VS. Physical mechanism of ultrasound-assisted synthesis of biodiesel. Ind Eng Chem Res. 2009;48(1):534–44.

    Article  CAS  Google Scholar 

  22. Ji J, Wang J, Li Y, Yu Y, Xu Z. Preparation of biodiesel with the help of ultrasonic and hydrodynamic cavitation. Ultrasonics. 2006;44:e411–4.

    Article  Google Scholar 

  23. Stavarache C, Vinatoru M, Maeda Y, Bandow H. Ultrasonically driven continuous process for vegetable oil transesterification. Ultrason Sonochem. 2007;14(4):413–7.

    Article  CAS  Google Scholar 

  24. Wu P, Yang Y, Colucci JA, Grulke EA. Effect of ultrasonication on droplet size in biodiesel mixtures. J Am Oil Chem Soc. 2007;84(9):877–84.

    Article  CAS  Google Scholar 

  25. Stavarache C, Vinatoru M, Nishimura R, Maeda Y. Fatty acids methyl esters from vegetable oil by means of ultrasonic energy. Ultrason Sonochem. 2005;12(5):367–72.

    Article  CAS  Google Scholar 

  26. Kelkar MA, Gogate PR, Pandit AB. Intensification of esterification of acids for synthesis of biodiesel using acoustic and hydrodynamic cavitation. Ultrason Sonochem. 2008;15(3):188–94.

    Article  CAS  Google Scholar 

  27. Mahamuni NN, Adewuyi YG. Optimization of the synthesis of biodiesel via ultrasound-enhanced base-catalyzed transesterification of soybean oil using a multifrequency ultrasonic reactor. Energy Fuels. 2009;23(5):2757–66.

    Article  CAS  Google Scholar 

  28. Deng X, Fang Z, Liu Y-h. Ultrasonic transesterification of Jatropha curcas L oil to biodiesel by a two-step process. Energy Convers Manage. 2010;51(12):2802–7.

    Article  CAS  Google Scholar 

  29. Gole VL, Gogate PR. Intensification of synthesis of biodiesel from nonedible oils using sonochemical reactors. Ind Eng Chem Res. 2012;51(37):11866–74.

    Article  CAS  Google Scholar 

  30. Choudhury HA, Goswami PP, Malani RS, Moholkar VS. Ultrasonic biodiesel synthesis from crude Jatropha curcas oil with heterogeneous base catalyst: mechanistic insight and statistical optimization. Ultrason Sonochem. 2014;21(3):1050–64.

    Article  CAS  Google Scholar 

  31. Khan O, Khan ME, Yadav AK, Sharma D. The ultrasonic-assisted optimization of biodiesel production from eucalyptus oil. Energy Sour Part A Recovery Utilization Environ Eff. 2017;39(13):1323–31.

    Article  CAS  Google Scholar 

  32. Fayyazi E, Ghobadian B, Najafi G, Hosseinzadeh B, Mamat R, Hosseinzadeh J. An ultrasound-assisted system for the optimization of biodiesel production from chicken fat oil using a genetic algorithm and response surface methodology. Ultrason Sonochem. 2015;26:312–20.

    Article  CAS  Google Scholar 

  33. Haghighi SFM, Parvasi P, Jokar SM, Basile A. Investigating the effects of ultrasonic frequency and membrane technology on biodiesel production from chicken waste. Energies. 2021;14(8):2133.

    Article  CAS  Google Scholar 

  34. He C, Mei Y, Zhang Y, Liu L, Li P, Zhang Z, Jing Y, Li G, Jiao Y. Enhanced biodiesel production from diseased swine fat by ultrasound-assisted two-step catalyzed process. Biores Technol. 2020;304:123017.

    Article  CAS  Google Scholar 

  35. Othman R, Mohammad AW, Ismail M, Salimon J. Application of polymeric solvent resistant nanofiltration membranes for biodiesel production. J Membr Sci. 2010;348(1–2):287–97.

    Article  CAS  Google Scholar 

  36. Shuit SH, Ong YT, Lee KT, Subhash B, Tan SH. Membrane technology as a promising alternative in biodiesel production: a review. Biotechnol Adv. 2012;30(6):1364–80.

    Article  CAS  Google Scholar 

  37. Sokač T, Gojun M, Tušek AJ, Šalić A, Zelić B. Purification of biodiesel produced by lipase catalysed transesterification by ultrafiltration: Selection of membranes and analysis of membrane blocking mechanisms. Renew Energy. 2020;159:642–51.

    Article  Google Scholar 

  38. Naderi A, Chung T-S, Weber M, Maletzko C. High performance dual-layer hollow fiber membrane of sulfonated polyphenylsulfone/polybenzimidazole for hydrogen purification. J Membr Sci. 2019;591:117292.

    Article  CAS  Google Scholar 

  39. Roosta A. New group interaction parameters of the UNIFAC model for the solubility of water in fatty acid methyl esters and biodiesel. Fuel. 2018;220:339–44.

    Article  CAS  Google Scholar 

  40. Bagnato G, Sanna A. Process and techno-economic analysis for fuel and chemical production by hydrodeoxygenation of bio-oil. Catalysts. 2019;9(12):1021.

    Article  CAS  Google Scholar 

  41. Ghavami S, Gregory A, Webb J, Bayat M, Denis M, Kumar V, Milbrand TA, Larson AN, Fatemi M, Alizad A. Ultrasound radiation force for the assessment of bone fracture healing in children: an in vivo pilot study. Sensors. 2019;19(4):955.

    Article  Google Scholar 

  42. Atadashi I, Aroua M, Aziz AA. Biodiesel separation and purification: a review. Renew Energy. 2011;36(2):437–43.

    Article  CAS  Google Scholar 

  43. Alamsyah R, Loebis EH. Design and technical testing for crude biodiesel reactor using dry methods: comparison of energy analysis. Energy Procedia. 2014;47:235–41.

    Article  CAS  Google Scholar 

  44. Atadashi I. Purification of crude biodiesel using dry washing and membrane technologies. Alex Eng J. 2015;54(4):1265–72.

    Article  Google Scholar 

  45. Alves MJ, Nascimento SM, Pereira IG, Martins MI, Cardoso VL, Reis M. Biodiesel purification using micro and ultrafiltration membranes. Renew Energy. 2013;58:15–20.

    Article  CAS  Google Scholar 

  46. Noriega MA, Narváez P, Habert AC. Biodiesel separation using ultrafiltration poly (ether sulfone) hollow fiber membranes: improving biodiesel and glycerol rich phases settling. Chem Eng Res Des. 2018;138:32–42.

    Article  CAS  Google Scholar 

  47. Noriega MA, Narváez P, Habert AC. Simulation and validation of biodiesel production in liquid-liquid film reactors integrated with PES hollow fibers membranes. Fuel. 2018;227:367–78.

    Article  CAS  Google Scholar 

  48. Cao P, Dubé MA, Tremblay AY. High-purity fatty acid methyl ester production from canola, soybean, palm, and yellow grease lipids by means of a membrane reactor. Biomass Bioenerg. 2008;32(11):1028–36.

    Article  CAS  Google Scholar 

  49. Cao P, Dubé MA, Tremblay AY. Methanol recycling in the production of biodiesel in a membrane reactor. Fuel. 2008;87(6):825–33.

    Article  CAS  Google Scholar 

  50. Cao P, Tremblay AY, Dubé MA. Kinetics of canola oil transesterification in a membrane reactor. Ind Eng Chem Res. 2009;48(5):2533–41.

    Article  CAS  Google Scholar 

  51. Talaghat M, Jokar S, Modarres E. Mathematical modeling of methyl ester concentration distribution in a continuous membrane tubular reactor and comparison with conventional tubular reactor. Heat Mass Transf. 2017;53(10):3099–108.

    Article  CAS  Google Scholar 

  52. Fadhil AB, Ahmed KM, Dheyab MM. Silybum marianum L. seed oil: a novel feedstock for biodiesel production. Arab J Chem. 2017;10:S683–90.

    Article  CAS  Google Scholar 

  53. Sandhya K, Abinandan S, Vedaraman N, Velappan K. Extraction of fleshing oil from waste limed fleshings and biodiesel production. Waste Manage. 2016;48:638–43.

    Article  CAS  Google Scholar 

  54. Ezekannagha CB, Ude CN, Onukwuli OD. Optimization of the methanolysis of lard oil in the production of biodiesel with response surface methodology. Egypt J Pet. 2017;26(4):1001–11.

    Article  Google Scholar 

  55. ASTM A. Standard specification for biodiesel fuel (B100) blend stock for distillate fuels. Annual book of ASTM standards. 2008.

  56. Getahun E, Gabiyye N. Experimental investigation and characterization of biodiesel production from leather industry fleshing wastes. Int J Renew Sustain Energy. 2013;2(3):120–9.

    CAS  Google Scholar 

  57. Jeong G-T, Yang H-S, Park D-H. Optimization of transesterification of animal fat ester using response surface methodology. Biores Technol. 2009;100(1):25–30.

    Article  CAS  Google Scholar 

  58. Horwitz W. Official methods of analysis of AOAC International. Volume I, agricultural chemicals, contaminants, drugs/edited by William Horwitz. Gaithersburg, Maryland: AOAC International, 1997; 2010.

    Google Scholar 

  59. Cocks LV, Rede CV. (1966). Laboratory handbook for oil and fat analysts. Laboratory handbook for oil and fat analysts.

  60. Fadhil AB, Al-Tikrity ET, Albadree MA. Biodiesel production from mixed non-edible oils, castor seed oil and waste fish oil. Fuel. 2017;210:721–8.

    Article  CAS  Google Scholar 

  61. Bhatti HN, Hanif MA, Qasim M. Biodiesel production from waste tallow. Fuel. 2008;87(13–14):2961–6.

    Article  CAS  Google Scholar 

  62. Damanik N, Ong HC, Chong W, Silitonga A. Biodiesel production from Calophyllum inophyllum—palm mixed oil. Energy Sour Part A Recovery Utilization Environ Eff. 2017;39(12):1283–9.

    Article  CAS  Google Scholar 

  63. Mohamad M, Ngadi N, Wong S, Jusoh M, Yahya N. Prediction of biodiesel yield during transesterification process using response surface methodology. Fuel. 2017;190:104–12.

    Article  CAS  Google Scholar 

  64. Sakthivel R, Ramesh K, Purnachandran R, Shameer PM. A review on the properties, performance and emission aspects of the third generation biodiesels. Renew Sustain Energy Rev. 2018;82:2970–92.

    Article  CAS  Google Scholar 

  65. Cunha A Jr, Feddern V, Marina C, Higarashi MM, De Abreu PG, Coldebella A. Synthesis and characterization of ethylic biodiesel from animal fat wastes. Fuel. 2013;105:228–34.

    Article  CAS  Google Scholar 

  66. Kubendran D, Salma Aathika AR, Amudha T, Thiruselvi D, Yuvarani M, Sivanesan S. Utilization of leather fleshing waste as a feedstock for sustainable biodiesel production. Energy Sour Part A Recovery Utilization Environ Eff. 2017;39(15):1587–93.

    CAS  Google Scholar 

  67. Amani MA, Davoudi MS, Tahvildari K, Nabavi SM, Davoudi MS. Biodiesel production from Phoenix dactylifera as a new feedstock. Ind Crops Prod. 2013;43:40–3.

    Article  CAS  Google Scholar 

  68. Reyes JF, Sepulveda M. PM-10 emissions and power of a diesel engine fueled with crude and refined biodiesel from salmon oil. Fuel. 2006;85(12–13):1714–9.

    Article  CAS  Google Scholar 

  69. Monyem A, Van Gerpen JH. The effect of biodiesel oxidation on engine performance and emissions. Biomass Bioenerg. 2001;20(4):317–25.

    Article  CAS  Google Scholar 

  70. Alptekin E, Canakci M. Optimization of pretreatment reaction for methyl ester production from chicken fat. Fuel. 2010;89(12):4035–9.

    Article  CAS  Google Scholar 

  71. Krisnangkura K. A simple method for estimation of cetane index of vegetable oil methyl esters. J Am Oil Chem Soc. 1986;63(4):552–3.

    Article  CAS  Google Scholar 

  72. Elizabeth Grant G, Gnaneswar Gude V. Kinetics of ultrasonic transesterification of waste cooking oil. Environ Prog Sustain Energy. 2014;33(3):1051–8.

    Article  CAS  Google Scholar 

  73. Singh AK, Fernando SD. Reaction kinetics of soybean oil transesterification using heterogeneous metal oxide catalysts. Chem Eng Technol. 2007;30(12):1716–20.

    Article  CAS  Google Scholar 

Download references

Acknowledgements

The authors would like to express their gratitude to the Iran National Science Foundation (INSF) for supporting this work.

Author information

Authors and Affiliations

Authors

Contributions

Ali Farokhnia provided the experiments and drafting the article. Seyyed Mohammad Jokar provided the main idea; wrote the main manuscript text and approved of the final version to be submitted Payam Parvasi modeled the membrane reactor and wrote the main manuscript text. Albert S. Kim revised the manuscript critically for important intellectual content.

Corresponding author

Correspondence to Payam Parvasi.

Ethics declarations

Competing interests

The authors declare no competing interests.

Additional information

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Farokhnia, A., Jokar, S.M., Parvasi, P. et al. A novel design for biodiesel production from methanol + mutton bone fat mixture. Biotechnol Biofuels 15, 130 (2022). https://doi.org/10.1186/s13068-022-02229-4

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s13068-022-02229-4

Keywords