Как выбрать гостиницу для кошек
14 декабря, 2021
Vegetable oils are the main feedstock for the production of first generation biofuels, which can offer several CO2 benefits and limit the consumption of fossil fuels. Raw vegetable oils consist of fatty acid triglycerides, the consistency of which depends on their origin (i. e. plant type) as shown in Table 2. Their production, however, is competing for the cultivated areas that were originally dedicated for the production of food and feed crops. As a result the production and utilization of vegetable oils for biofuels production has instigated the "food vs. fuel" debate. For this reason traditional energy crops (soy, cotton, etc) with low oil yield per hectare are being substituted by new energy crops (eg. jatropha, palm, castor etc).
C8:0 |
C10:0 |
C12:0 |
C14:0 |
C16:0 |
C16:1 |
C18:0 |
C18:1 |
C18:2 |
C18:3 |
C20:0/ C22:0 |
C20:1/ C22:1 |
||
Rapeseed oil |
0.0 |
0.0 |
0.0 |
0.0 |
3.5 |
1.0 |
1.5 |
12.5 |
15.0 |
7.5 |
9.0 |
50.0 |
|
D Ш |
Soybean oil |
0.0 |
0.0 |
0.0 |
0.3 |
8.2 |
0.5 |
4.5 |
25.0 |
49.0 |
5.0 |
7.5 |
0.0 |
Sunflower oil |
0.0 |
0.0 |
0.0 |
0.0 |
6.0 |
0.0 |
4.2 |
18.8 |
69.3 |
0.3 |
1.4 |
0.0 |
|
Corn oil |
0.0 |
0.0 |
0.0 |
1.0 |
9.0 |
1.5 |
2.5 |
40.0 |
45.0 |
0.0 |
0.0 |
1.0 |
|
Palm oil |
0.0 |
0.0 |
0.0 |
3.5 |
39.5 |
0.0 |
3.5 |
47.0 |
6.5 |
0.0 |
0.0 |
0.0 |
|
D Ш |
Peanut oil |
0.0 |
0.0 |
0.0 |
0.5 |
8.0 |
1.5 |
3.5 |
51.5 |
27.5 |
0.0 |
7.5 |
0.0 |
0 c |
Canola oil |
0.0 |
0.0 |
0.1 |
0.1 |
4.7 |
0.1 |
1.6 |
65.9 |
21.2 |
5.2 |
1.2 |
0.0 |
Castor oil |
0.0 |
0.1 |
0.2 |
10.6 |
1.4 |
9.5 |
29.7 |
29.7 |
41.3 |
3.3 |
3.8 |
0.0 |
Table 2. Fatty acid composition of most common vegetable oils [14][15] |
Catalytic hydrotreatment was explored for conversion of vegetable oils in the early 90’s. The investigation of the hydrogenolysis of various vegetable oils such as maracuja, buritimtucha and babassu oils over a Ni-Mo/y-Al2O3 catalyst as well as the effect of temperature and pressure on its effectiveness was firstly investigated [16][17]. The reaction products included a gas product rich in the excess hydrogen, carbon monoxide, carbon dioxide and light hydrocarbons as well as a liquid organic product of paraffinic nature. In more detail these studies showed the conversion of triglycerides into carboxyl oxides and then to high quality hydrocarbons via decarboxylation and decarbonylation reactions. Rapeseed oil hydroprocessing was also studied in lab-scale reactor for temperatures 310° and 360°C and hydrogen pressures of 7 and 15 MPa using three different Ni-Mo/alumina catalysts [18]. These products contained mostly n-heptadecane and n-octadecane accompanied by low concentrations of other n-alkanes and i-alkanes [19].
3.2. Waste cooking oils conversion to paraffinic biofuels
Even though vegetable oils are the main feedstock for the production of first generation biofuels, soon their production has troubled the public opinion due to their abated sustainability and to their association with the food vs. fuel debate. As a result the technology has shifted towards the exploitation of both solid and liquid residual biomass. Waste Cooking Oils (WCOs) is a type of residual biomass resulting from frying with typical vegetable frying oils (e. g. soybean-oil, corn-oil, olive-oil, sesame-oil etc). WCOs have particular problems regarding their disposal. In particular grease may result in coating of pipelines within the residential sewage system and is one of the most common causes of clogs and sewage spills. Furthermore, in the cases that sewage leaks into the environment, WCOs can cause human and environmental health problems because of the pathogens contained. It has been estimated that by disposing 1 lit of WCO, over 1,000,000 of liters of water can be contaminated, which is estimated as the average demand of a single person for 14 years.
Catalytic hydroprocessing of WCO was studied as an alternative approach of producing 2nd generation biofuels [20—24]. Initially catalytic hydrocracking was investigated over commercial hydrocracking catalysts leading not only to biodiesel but also to lighter products such as biogasoline [20], employing a continuous-flow catalytic hydroprocessing pilot-plant with a fixed-bed reactor. During this study several parameters were considered including hydrocracking temperature (350-390°C) and liquid hourly space velocity or LHSV (0.5-2.5 hr-1) under high pressure (140 bar), revealing that the conversion is favoured by high reaction temperature and low LHSV. Lower and medium temperatures, however, were more suitable for biodiesel production while higher temperatures offered better selectivity for biogasoline production. Furthermore, heteroatom removal (S, N and particularly O) was increased while saturation of double bonds was decreased with increasing hydrocracking temperature, indicating the necessity of a pre-treatment step.
However catalytic hydrotreatment was later examined in more detail as a more promising technology particularly for paraffinic biodiesel production (Figure 1). The same team has studied the effect of temperature (330-398°C) on the product yields and heteroatom removal [21]. The study was conducted in the same pilot plant utilizing a commercial NiMo/Al2O3 hydrotreating catalyst over lower pressure (80 bar). According to this study, the hydrotreating temperature is the key operating parameter which defines the catalyst effectiveness and life. In fact lower temperatures (330°C) favour diesel production and selectivity. Sulfur and nitrogen removal were equally effective at all temperatures, while oxygen removal and saturation of double bonds were favoured by hydrotreating temperature. The same team also studied the effect of the other three operating parameters i. e. pressure, LHSV and H2/WCO ratio [22]. Moreover they also studied the hydrocarbon content of the products [23] qualitatively via two-dimensional chromatography and quantitatively via Gas Chromatography with Flame Ionization Detector (GC-FID), which indicated the presence of C15-C18 paraffins. Interestingly this study showed that as hydrotreating temperature increases, the content of normal paraffins decreases while of iso-paraffins increases, revealing that isomerization reactions are favoured by temperature.
Figure 7. Catalytic hydrotreatment of WCO to 2nd generation biodiesel
The total liquid product of WCO catalytic hydrotreatment was further investigated in terms of its percentage that contains paraffins within the diesel boiling point range (220-360°C) [24]. The properties of WCO, hydrotreated WCO (total liquid product) and the diesel fraction of the hydrotreated WCO are presented in Table 3. Based on this study the overall yield of the WCO catalytic hydrotreatment technology was estimated over 92%v/v. The properties of the new 2nd generation paraffinic diesel product indicated a high-quality diesel with high heating value (49MJ/kg) and high cetane index (77) which is double of the one of fossil diesel. An additional advantage of the new biodiesel is its oxidation stability (exceeding 22hrs) and negligible acidity, rendering it as a safe biofuel, suitable for use in all engines. The properties and potential of the new biodiesel were further studied [25], for evaluating different fractions of the total liquid product and their suitability as an alternative diesel fuel.
1 |
WCO |
Hydrotreated WCO |
Final biodiesel |
|
Density |
gr/cm3 |
0.896 |
0.7562 |
0.7869 |
C |
wt% |
76.74 |
84.59 |
86.67 |
H |
wt% |
11.61 |
15.02 |
14.74 |
S |
wppm |
38 |
11.80 |
1.54 |
N |
wppm |
47.42 |
0.77 |
1.37 |
O |
wt% |
14.57 |
0.38 |
0 |
Recovery 0% |
°C |
431.6 |
195.6 |
234.1 |
Recovery 10% |
°C |
556.4 |
287.4 |
294.1 |
Recovery 30% |
°C |
599 |
304.0 |
296.8 |
Recovery 50% |
°C |
603.2 |
314.4 |
298.3 |
Recovery 70% |
°C |
609 |
319.0 |
300 |
Recovery 90% |
°C |
612.4 |
320.4 |
298.3 |
Recovery 100% |
°C |
727.2 |
475.4 |
306.2 |
Table 3. Basic properties of waste cooking oil, hydrotreated waste cooking oil and final biodiesel |