Total number of cryopreserved straws contained sperm from bulls, boars, and male inobuta in the evacuation zone of the Fukushima Daiichi Nuclear Plant.
\r\n\t
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On 22 April 2011, the evacuation zone was set to a 20-km radius surrounding the FNPP, leaving approximately 3,400 cows, 31,500 pigs, and 630,000 chickens behind within the zone. On 12 May 2011, the Government of Japan ordered Fukushima prefectural government to euthanize unleashed livestock within the evacuation zone. Abandoned animals now have formed an invaluable model for studying the effects of chronic radionuclide intake. A comprehensive assessment of the effect of long-term exposure to internally deposited radionuclides on surviving domestic animals in the evacuation area is therefore urgently needed for the benefit of the livestock industry, as well as for human health. Radiobiological data from the FNPP accident could help to develop a set of internationally harmonized measures to protect domestic animals in the event of a future nuclear or radiological emergency.
Exposure to a large dose of ionizing radiation can cause irreparable damages to multiple organ systems, particularly those with highly proliferative cells, such as the skin, the hematopoietic and gastrointestinal system [3]. The testis and ovary are relatively radiosensitive organs [4], composed of a series of spermatogenic cells such as stem cells, spermatogonia, spermatids, spermatocytes, sperm, and oogonium, primary oocyte, secondery oocyte and ovum, respectively. These different types of germ cells differ remarkably in their susceptibility to radiation-induced effects according to their level of reproductive activity [5]. The effect on reproductive organs and behaviour by chronic exposure to radionuclides is one of major concerns. Furthermore, radiation-induced genomic changes, occurring in germ cells may have hereditary effects, including carcinogenesis, congenital malformation and growth retardation in offsprings. A germ cell is the only cell that can produce next-generation. Therefore, greater use of cryopreservation of germ cells provide an essential resource to preserve their genetics and foetuses obtained by fertilization using those of the freezing sperm and oocytes for further studies on the effect of ionizing radiation on the next generations.
We have collected and cryopreserved the sperm and oocytes from three spices of domestic animals in the FNPP evacuation zone between 27 September 2011 and 31 March 2013. In this chapter, we introduce approaches to cryopreserve germ cells from the cattle, the pig, and the inobuta which is a mongrel of the wild boar and the pig for further research of radiobiology.
Data used for estimating the risk associated with exposure to ionizing radiation have been primarily obtained from epidemiological studies of survivors of the atomic bombing of Hiroshima and Nagasaki [6], the Chernobyl nuclear accident [7], and some complementary animal experiments [8–10]. However, reports of the effect of chronic low-dose radiation on livestock animals are limited.
Direct radiation injury to animals was reported only in local areas within the 30-km exclusion zone in Chernobyl nuclear power plant [11]. In some cases, chronic dose rates may have reduced the fertility of some animal species inside the zone. Recently, review of Russian language studies on radionuclide behavior in agricultural animals has been published [12, 13]. There are several important animal pathways for radionuclide transfer to the diet of humans. The important for many contamination scenarios for radiologically important radionuclides (90Sr, 131I and 137Cs) is muscle (meat) consumption. The information presented this review has reported values are for Cs due to the Chernobyl accident in cattle, sheep, goat, rabbits, and chicken.
On the other hand, irradiation damages the ovaries and testes as direct effects of radiation, and indirectly affect through hormonal disruption. In human and wild animals, several studies of the functional changes in the reproductive tract have been made as a result of Chernobyl accident, abnormalities in spermatozoa and reproductive failures have been described [7]. Additionally, Weinberg et al. reported some genetic changes of unclear importance in offspring of Chernobyl accident liquidators [14, 15]. Although there are some claim that its changes is caused by the psychological factors (stressful conditions), it does not yet have enough information to explain all of the serious changes.
The Japanese government ordered Fukushima prefecture to euthanize cattle in the evacuation zone on 12 May 2011 to prevent radio-contaminated livestock products from entering the human food chain. We obtained testes and ovaries from the euthanized cattle, pigs and inobutas collected by the combined unit of veterinary doctors belonging to the Livestock Hygiene Service Center of Fukushima prefecture.
Almost bulls and boars were castrated. Therefore, we could only collect testes from 11 euthanized Japanese black beef bulls, 3 boars, and 1 male inobuta between 29 August 2011 and 28 February 2013 (Figure 1). Testes were collected in Kawauchi village located 15 km southwest of FNPP: the air dose rate was 0.5 μSv/h, Naraha town located 17 km south of FNPP: the air dose rate was 2 μSv/h, Tomioka town located 7 km south of FNPP: the air dose rate was 20 μSv/h.
Animals in the evacuation zone of the Fukushima Daiichi Nuclear Plant. A: Japanease black beef cattle B: Pig C: Inobuta
In bull, sperm from two caudae epididymides were collected. Immediately after collection, sperm were diluted with a Triladyl freezing extender containing egg yolk at natural temperature (Mini Tube, Germany). The tubes containing sperm were transferred to the Niigata University within 6-8 h after collection. Semen samples were cooled to 5-10°C during transferring. Aliquots of 0.5 ml of sperm suspension were individually placed in straws and ends were sealed. The straws were then placed in liquid nitrogen vapor for 10 min and then plunged directly into liquid nitrogen. In boars and male inobuta, freezing protocol was performed as described above. The semen extender, Modena extender containing egg yolk was used for freezing epididymal sperm. Total number of frozen sperm was 507 straws from bulls, 160 straws from boars and 83 straws from inobutas (Table 1).
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t
\n\t\t\t\t | \n\t\t\t11 | \n\t\t\t507 | \n\t\t
\n\t\t\t\t | \n\t\t\t3 | \n\t\t\t160 | \n\t\t
\n\t\t\t\t | \n\t\t\t1 | \n\t\t\t83 | \n\t\t
Total number of cryopreserved straws contained sperm from bulls, boars, and male inobuta in the evacuation zone of the Fukushima Daiichi Nuclear Plant.
Oogenesis is associated closely with folliculogenesis in mammals. Oogenesis begins in the fetal ovary when the primordial germ cells arrive in the gonad of a genetic female and become oogonia. These cells proliferate via mitosis during fetal development. When proliferation ceases and the cells enter meiosis either before birth (human, cows, sow) or shortly thereafter (mice, rats, hamster) [16, 17], they are defined as primary oocytes arrested in the first meiotic prophase. Primordial follicles are formed in which the primary oocytes are surrounded by single layer of flattened granulose cells. Although the primordial follicles remain in this state of suspended animation for long time, oocytes and follicle resume the development near the time of ovulation. When follicles enter the development phase, they develop into primary and subsequent secondly follicles, along with proliferation of granulose cells and the oocytes growth. Primary and secondly follicle have cuboidal single layer and multiple layers of granulose cells, respectively. During the next phase, a fluid-filled cavity is formed adjacent to the oocyte in the follicle defined as antral follicle. Finally, one follicle growth rapidly and become the ovulatory follicle (maturation). In most mammals, the oocytes resume and complete the first meiotic division at ovulation.
Ionizing radiation may affect infertility or genetic disorders in subsequent generation induced by DNA damage in the germ cells and follicular cells. Many experiments have shown that radiosensitivity of follicle/oocyte varies widely according to the developmental stage of them and species [18]. In mice, the genetic sensitivity of oocyte in early stages of follicle development is a relatively high, and which decreases during the last week before ovulation. However, the sensitivity increases around the time of ovulation again. In contrast, oocytes in primordial follicle show a very low genetic sensitivity, and which increase with follicle development thereafter in guinea pigs. However, the knowledge in livestock is limited. In order to reveal the affect of exposure to low-dose of radiation on germ cells, it is necessary to study carefully at long term, including the influences on subsequent generations.
The aim of our studies is to examine of development of female germ cells in livestock within the evacuation zone and to preserve of female gametes for future studies. We collected ovaries from 36 cows, 12 sows, and 2 female inobutas. In cows, collected ovaries were washed and stored at 20°C in physiological saline containing antibiotics, and were transported to the laboratory within 7 h after the collection. Cattle cumulus-oocyte complexes (COCs) were aspirated from small ovarian follicles and incubated in
\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t\t\n\t\t\t\t | \n\t\t
Caw | \n\t\t\t9 | \n\t\t\tBlastocyst | \n\t\t\t40 | \n\t\t
Sow | \n\t\t\t12 | \n\t\t\tMetaphase II | \n\t\t\t371 | \n\t\t
Inobuta | \n\t\t\t2 | \n\t\t\tMetaphase II | \n\t\t\t64 | \n\t\t
Total number of cryopresearved oocytes and embryos from caws, sows, and female inobutas in the evacuation zone of the Fukushima Daiichi Nuclear Plant.
Germ cells in the testis show one of the highest mitotic activities of any tissue in the body, so that in the human adult about 100 million new cells are produced each day [20]. Spermatogenesis is highly regulated, starting with spermatogonial stem cells and ending with differentiated, motile spermatozoa. The testis is one of the most radiosensitive tissues, with very low doses of radiation causing significant impairment of function. It is well known that immature cells are more radiosensitive to doses as low as 0.1 Gy, causing morphological and quantitative changes to the spermatogonia in human testis. Doses of 2–3 Gy result in overt damage to spermatocytes, leading to a reduction in the spermatid numbers. At doses of 4–6 Gy, the numbers of spermatozoa significantly decrease, implying damage to the spermatids. A recent study in mice showed that low-dose-rate radiation exposure (3.49 mGy/h) did not cause adverse effects at dose levels of ≤2 Gy, but the testis weight, sperm count and motility decreased at a dose of 2 Gy [21].
We needed to overcome a number of obstacles while working in the evacuation area, that is, dissections under the sun in the summer and snow in the winter, gathering the dissectors, as well as drive 400 miles a day. We also had restrictions on the time that we were allowed to stay in the area and the radiocontaminated materials to bring out of the area. We recently reported radionuclide deposition in organs of abandoned cattle following the FNPP accident. The deposition occurred in an individual radionuclide and in an organ-specific manner, and radioactive Cs was detected in all the organs examined [22]. Discharge of 134Cs and 137Cs that emit γ-and β-rays is of primary concern, because they were released in a large amount and have a long half-lives [23]. Furthermore, we have investigated the effect of chronic radiation exposure on bull testes to 134Cs and 137Cs associated with the FNPP accident. Adverse radiation-induced effects, so far, have not been observed in bull testes following chronic exposure to the above levels of radiation for up to 10 months [24].
The paternal and maternal genomes are not equivalent and both are required for mammalian development. The difference between the parental genomes is believed to be due to gamete-specific differential modification, a process known as genomic imprinting, suggesting that DNA methylation may play a role in genomic imprinting. Lie et al, have examined the expression of these three imprinted genes in mutant mice that are deficient in DNA methyltransferase activity [25]. Results demonstrate that a normal level of DNA methylation is required for controlling differential expression of the paternal and maternal alleles of imprinted genes. Few animal studies have investigated the possible link between paternal exposures and effects on genomic imprinting. Chronic treatment of male rats with 5-azacytidine, a drug that alters DNA methylation resulted in abnormalities in male germ cells and early embryo development but no increase in the incidence of congenital malformations [26]. This is an important area with potential consequences for the offspring of exposed males, and warrants further study [27].
In addition, questions regarding the effect of log-term exposure to radiation on the genetic damage to next generation are now being raised, but no clear evidence for this has been reported, except laboratory animals. Genetic analysis of foetuses obtained by fertilization using cryopreserved sperm and oocytes from cattle in the evacuation zone, is underway in our laboratory.
In conclusion, cryopreservation of germ cells has potential applications not only for production of next generations of animals but also for general reproductive biology including the field of radiation biology.
We express our gratitude to the Iwaki Livestock Hygiene Service Centre in Fukushima Prefecture, especially to DVM. Yuji Kobayashi and livestock farmers in the 20-km FNPP evacuation zone. This work was partly supported by a grant for Manabu Fukumoto of the Japan Society for the Promotion of Science, and the Emergency Budget for the Reconstruction of Northeastern Japan, MEXT, Japan, Discretionary Expense of the President of Tohoku University and Nippon Life Insurance Foundation supported this study. This work was also supported by the Programme for Promotion of Basic and Applied Researches for Innovations in Bio-oriented Industry.
Decarbonizing the transportation sector is the highest priority to reduce global warming, air pollution and associated health hazards. There is a need to develop ultra-low carbon or carbon-negative fuels which can be produced from renewable sources like waste, organic substances, plants and trees etc. DME is a low cost, low carbon and zero soot and PM chemical stock that can be used on CI engines. DME can be produced from various feedstocks such as wood, methanol, wastes, biomass etc. Its use as a substitute for diesel fuel is due to high cetane number of 55–60 and superior combustion characteristics. It is a colorless, non-toxic, mildly narcotic and easily inflammable gas at normal temperature and pressure similar to LPG.
Many CI engine manufacturers like Isuzu, Nissan, Mitsubishi, Volvo have developed DME fueled CI engine powered vehicles. DME vehicle’s reliability have been validated in the field with running tests of 100,000 Km or more. DME fueled CI engines exhibit higher combustion efficiency and soot free combustion in comparison to corresponding diesel engines.
Diesel engines are used widely in power generation industry. Expansion of the power generation sector is fueling the growth of diesel engine production. Global diesel power engine market is estimated to grow at a CAGR of more than 3.5% during the period from 2021 to 2026. Demand for reliable electricity due to the industrial expansion, development of commercial infrastructure, electrification of human habitats, and uninterrupted power supply is the major cause for the growth of diesel engine power market [1]. Therefore, there is a valid case for developing these engines to operate on DME.
Figure 1 presents the global energy consumption from 1971 to 2019 in Exajoules (1018 J). World energy consumption has been increasing steadily from 1971 (176.8 EJ) to 2019 (418 EJ), an increase of 136% [2]. Largest increase has been in oil and electricity consumption. It is expected that the increase in these two sources will continue in the future. With the development of new battery technologies and solar PVs, increase in rate of electricity consumption including that generated from renewables will increase further.
World total energy consumption by source (1971–2019) [
Figure 2 gives the world energy consumption history and projections. Figure 2(a) shows that increase in industrial energy consumption is expected to be the largest followed by the transportation sector although growth in residential and commercial sectors is also expected at a relatively moderate rate. Figure 2(b) gives the world energy consumption on the basis of fuel. Use of petroleum and other liquids are anticipated to increase till 2050 and will be about 250 quadrillion Btu. Renewables, during the same period, are expected to rise to 40 quadrillion Btu. Therefore, the share of petroleum and other liquids will be around six times that of renewables. In the heavy-duty sector diesel-based compression ignition engines are the preferred power source. Therefore, there is a sound future for the CI engines in all sectors, i.e., power generation, transportation, industry etc. Conversion of CI engines to use DME will lead to reduction in fossil fuel consumption and prevent degradation of environment.
World energy consumption, history and projections [
Among the petroleum fuels, diesel is a critical fuel for transportation especially heavy-duty vehicles, agricultural vehicles, construction and earth moving equipment. Power generation is another important area where diesel is used. Figure 3 shows the end-use of diesel fuel in the USA, Japan and India, countries which are the one of the largest consumers of diesel fuel. In all three countries transport sector is the major consumer of mineral diesel. Conversion of trucks and busses to DME will lead to major reduction of fossil fuel and associated emissions.
End-use of diesel fuel in USA, Japan and India [
IMARC group has categorized the global diesel engine market as shown in Figure 4.
Categorization of the diesel engine market based on power rating and end-user [
Power rating of the diesel engines varies from 0.5 MW to more than 5 MW used in automotive and non-automotive applications all over the world. Figure 4 illustrates that development of engine technology to utilize DME in diesel engines will have a positive effect in all sectors and across continents. Thus, a concentrated effort by different OEMs to come out with DME conversion kits or even new DME engine designs will not only reduce fossil fuel consumption and environmental deterioration but also has a firm economic viability. All sectors are expected to exhibit increase in use of diesel engines, however highest growth is expected from the power generation sector, trucks and busses and industrial sector. The global diesel engine market reached a value of US$ 212.4 billion in 2021 [7]. It has been predicted that the demand for diesel engines including all sectors and sizes should increase to US$ 240 billion in the year 2025 registering a compound annual growth rate of over 3% from 2020 to 2025 [8].
Top Key producers of Dimethyl Ether (DME) include: a) Akzo Nobel, b) Shell, c) The Chemours Company, d) China Energy, e) Mitsubishi Corporation, f) Ferrostal GmbH, g) Grillo Werke, h) Jiutai Energy Group, i) Oberon fuels and j) Zagros. In Japan several large scale DME plants have been set-up [9]. China is the bulk producer of DME from Chinese coal and production plants have also been set-up in Trinidad and Tabago, North America, Indonesia and Uzbekistan. First bio DME production plant was constructed in Sweden. Global production of DME at present is roughly 9 million tons per year [10]. Different feedstocks can be used in the production of DME. These are natural gas, coal, waste from pulp and paper mills, forest products, agricultural by-products, municipal waste and dedicated fuel crops e.g., switch grass. Methanol dehydration is the main process for production of DME currently. Synthetic gas can however be produced by gasification of coal, biomass, natural gas reforming [11].
There are three pathways to produce DME: a. Two-step process, b. One-step process, c. Liquid-one-step process called as bio reforming. Typically, DME is produced through a two-step process with syngas the feedstock (Table 1). Methanol is first produced from Syngas, followed by dehydration of methanol into DME (Eqs. 1–4) (Table 1, Figure 5) [12].
Equation | Process Desc | Eq. |
---|---|---|
CO + 2H2 → CH3OH | Methanol formation | (1) |
2CH3OH → CH3OCH3 + H2O | Methanol dehydration with solid-acid catalyst | (2) |
H2O + CO → CO2 + H2 | Water gas shift reaction | (3) |
3H2 + 3CO → CH3OCH3 + CO2 | Net reaction | (4) |
Two-step synthesis process of DME [12].
Two-step process for synthesis of DME [
In Japan, Korea and China single-step process is used most commonly (Eq. 5–6) (Table 2 and Figure 6). In this process, the methanol formation, methanol dehydration and water-gas shift reaction are merged. Different feedstocks can be used in this process such as methane, scrubbed bio-gas, syngas, etc. In case of methane feedstock methane-dry-reforming is done before the single-step process. Japan Steel Company has reached production capacity of 100 t DME/day by this process (Olah, et al. 2009). Mass balance shows that for every gm DME produced 1.43 gm of CO2 is used in the process. In overall reaction, CO2 sequestration is 0.48 gm per gram of DME.
Eq. (2) | Process Desc | Eq. |
---|---|---|
3CH4 + 3CO2 → 6CO + 6H2 | Methane-dry-reforming | (5) |
6CO + 6H2 → 2CH3OCH3 + 2CO2 | DME synthesis | (6) |
3CH4 + CO2 → 2CH3OCH3 | Net | (7) |
Single-step synthesis of DME [12].
Single-step process for DME synthesis [
Third process for DME production is bio-reforming (Table 3, Eq. 8–12). For optimized process to produce methanol Metgas is used, which is 2:1 H2:CO ratio syngas. Two processes to produce Metgas are methane-steam-reforming and methane-dry-reforming step. Next steps are methanol formation and DME synthesis by dehydration of Methanol. Water produced during the dehydration of methanol is used in the methane-steam-reforming process. CO2 consumed during per gm formation of DME is 0.48 gm. There are no emissions of CO2 during bio-reforming process, however there will be CO2 emissions regarding process’s energy requirements.
Equation | Process Desc | Eq. |
---|---|---|
2CH4+ 2H2O → 2CO + 6H2 | Methane-steam reforming | (8) |
CH4 + CO2 → 2CO + 2H2 | Methane-dry-reforming step | (9) |
4CO + 8H2 → 4CH3OH | Methanol formation | (10) |
4CH3OH → 2CH3OCH3 + 2H2 | Methanol dehydration | (11) |
3CH4 + CO2 → 2CH3OCH3 | Net | (12) |
Bio-reforming process for production of DME [12].
Both one-step and two-step DME production process are mature technologies. There are many companies which have developed single-step process for producing DME. Notable among these are Haldor-Topsoe A/S Denmark, JFE Holdings, Japan, Korea Gas Company, S. Korea, Air Products USA, NKK Japan, Oberon Fuels USA etc. Two-step DME production process has been developed by companies like Toyo Japan, Mitsubishi Gas Company Japan, Lurgi Germany, Udhe Germany. Several companies have developed novel processes and technologies for production of DME.
World’s first bio-DME demonstration plant in Sweden (started in 2010) uses black liquor (waste from paper and pulp industry) to produce high-quality syngas which is used for synthesis of DME (Figure 7).
Bio-DME production plant in Sweden [
Oberon Fuels has developed proprietary skid-mounted, small-scale production units that convert methane and carbon dioxide to DME from various feedstocks, such as biogas from dairy manure and food waste. These small-scale plants are affordable as compared to a large plant, do not require large infrastructure and permits etc. for operation. These small-scale production units can produce 10,000 gallons (37854.12 liters) of DME per day to cater to the regional fuel markets [14].
Schematic of the plant is shown in Figure 8, consists of SMR, make-up syngas compressors, methanol synthesis reactors, pre-cut column and DME column and DME storage tanks.
Schematic of a small size DME production plant developed by Oberon fuels [
The Oberon Fuels methane-gas-to-DME process has the following three major steps:
Syngas production
Methanol synthesis
Simultaneous DME synthesis and separation via catalytic distillation.
First two steps are common in large scale industrial application. Catalytic synthesis of DME with purification has been investigated in detail and has been demonstrated industrially by Oberon Fuels at Brawley California. In this plant, all production, storage, piping, tanks and valves are overground. DME produced from un-scrubbed (60% methane) HSAD (High Solid Anaerobic Digestion) of food waste, yard waste, bio-waste is called as Bio-DME. Chemically Bio-DME and DME are chemically same, Bio-DME uses biogas (typically produced from anaerobic digester), whereas DME is produced from pipeline natural gas.
Table 4 shows the boiling points of propane, butane and DME.
Table 4 illustrates that the boiling point of DME is in between that of propane and butane and all three are gas at room temperature of 15°C. The storage and handling facilities for LPG can therefore be repurposed for DME at a low cost. LPG storage and handling infrastructure is widespread in many countries including India. In addition to the use of existing LPG facilities new installations need to be created for DME. In the existing LPG installations changes will be needed for seals, valves, pressure regulators, gaskets, pumps to handle DME.
Storage, handling and transport of DME is as a liquid under pressure similar to LPG. DME is compressed to 5 bar pressure for liquefaction at room temperature. Material compatibility of DME with the seals and gaskets in stationary and moving parts has to be established. ASTM specification D7901 gives directions on safety and handling of DME, which includes elastomer selection for gaskets and seals (to avoid their failure). Also, all equipment for DME storage and handling have necessarily to be overground. Table 5 provides compatibility of different elastomers with DME as per ASTM D7901. Rubber and plastics swell and deteriorate easily on contact with DME as compared to LPG. Nitrile rubber seals (NBR) and fluoro rubber seals (FKM) are used with LPG but swell in contact with DME and therefore cannot be used with DME.
Propane (C3H8) | DME(CH3OCH3) | Butane(C2H6) | |
---|---|---|---|
Boiling point (°C) | −42°C | −24°C | −1°C |
Boiling points of propane, DME and butane [15].
Elastomer | Compatibility rating for use of DME |
---|---|
Natural Rubber (NR), Isoprene, Butadiene Styrene (SBR, Buna S), Butadiene (BR), Butyl (HR), Ethylene Propylene (EPR, EPDM, EP), Polyacrylate (ACM), Fluor elastomer – Di polymer, Fluor elastomer – Terpolymer | 4 |
Polychloroprene (Neop rene, CR), Chlorosulfonated Polyethylene (CSM) | 3 |
Polysulfide (T) | 2 |
Silicone (VMQ), Fluor silicone (FVMQ), Perfluoro elastomer (FFKM), Polytetrafluoroethylene (PTFE), Nitrile (NBR, BUNA-N), Hydrogenated Nitrile Butadiene Rubber (HNBR) | 1 |
Rating Legend (at room temperature) 1 = Little or minor effect, 0 to 5% volume swell, 2 = Minor to moderate effect, 5 to 10% volume swell, 3 = Moderate to severe effect, 10 to 20% volume swell, 4 = Not recommended for DME use |
Compatibility of DME with elastomers as per ASTM D7901 [12].
Cylinder tanks for DME fuel will be similar to LPG, will be fabricated structure consisting of cylindrical shell and panel with filling valve, outlet valve, return valve, safety valve, overfill prevention device, quick coupling and fluid level gauge.
A pressurized fuel injection system for DME is an essential requirement. Thus, the tank, fuel pumps, fuel piping and the fuel injector have to be kept under suitable pressure. Fuel pumps have to pressurize the fuel circuit to a pressure which is higher than the saturation vapor pressure of DME at the operating temperature. This will prevent the DME fuel to vaporize and cause cavitation in the fuel circuit before the fuel injection into the cylinder. Temperature of the fuel inside the fuel injector reaches to 80°C and the pressure of the fuel circuit after the fuel pumps has to be increased accordingly. A pressure higher than 30 bar is considered adequate for keeping the DME in liquified form even at higher temperatures encountered during operation of the engine. Feed-pumps will be able to pressurize the fuel to the required pressure.
ASTM standard range for viscosity of liquid fuels has a range of 1.39 to 4.2 cSt at 40°C whereas viscosity of DME is within 0.185 cSt and 0.23 cSt. Low viscosity of DME will result in leakages past clearances used for sealing like plungers and barrels, seals and gaskets and pump gears etc. Low lubricity will result in high wear and seizure of the moving parts in fuel injection system. Viscosity and lubricity enhancing additives are added to the DME to overcome these problems.
Bulk modulus of DME is less than diesel by an order of magnitude. This implies that DME is much more compressible than diesel. High compressibility of DME will result in delay in the injection timings. Injection lag will be higher as compared to diesel and therefore the ECU has to be programmed accordingly. The compression work of DME in the fuel pumps and injectors is much higher than diesel fuel and the parasitic power for pumping of fuel is higher. Large compressibility of DME also results in injection instability and this problem can be overcome by modifying the nozzle design and control of fuel temperature.
Table 6 compares the chemical and physical properties of DME, diesel fuel and LPG (propane, butane). Diesel properties are compared to DME to understand the similarity between the two in compression-based ignition, whereas comparison of DME to LPG is required to know about the similarity in fuel handling of the two fuels.
Property | DME | Diesel | Propane | Property | DME | Diesel | Propane |
---|---|---|---|---|---|---|---|
CH3-O-CH3 | — | C3H8 | 3.4–18.6 | 0.6–7.5 | 2.1–10.1 | ||
46 | 170 | 44.097 | 52.2 | 86.0 | 82 | ||
27.6 | 42.5 | 46.3 | 13.0 | 14.0 | 18 | ||
667 | 831 | 500 | 34.8 | 0 | 0 | ||
> 55 | 40–55 | — | 400 | 708 | 369.9 | ||
9.0 | 14.6 | 15.8 | 5.37 | 3.00 | 4.301 | ||
235 | 250 | 470 | 259 | — | 220 | ||
−20 | 180/ 370 | −42 | <1 | 3 | 4.29 | ||
460 (−20°C) | 250 | 372 | 0.012 | 0.027 | 0.007 | ||
100–1000 MPa Depend on Temp. & Press. | 1400 Mpa | 220 MPa | 530 | ≪10 | 580 |
Table 6 shows that auto-ignition temperature of DME is lower than diesel at pressure higher than atmospheric. Also, the cetane number of DME is higher than that of diesel. Thus, DME fuel is suitable in CI engines and has high potential to replace diesel fuel. At the same time, boiling point of DME is close to propane below Zero °C and the handling, storage and distribution of DME is similar to LPG. World over, LPG is used as cooking fuel and also for transport, therefore there is adequate experience in handling and storage of LPG. Use of LPG storage and handling facilities for DME with modifications to the seals, gaskets and certain metallic parts can be done with lower efforts and cost.
DME is an oxygenated fuel with an oxygen percentage of nearly 35%. Higher Cetane number results in lower ignition delays and smaller pre-mixed combustion phase, lower peak cylinder pressures and lower NOx formation. Absence of C-C bonds leads to sootless combustion. In the DME molecule each carbon atom is bound to three hydrogen atoms on one side and oxygen atom on the other. Bond energy of C-H is 414 kJ/mol and that of C-O bond is 359.0 kJ/mol. Higher C-H bond energy is responsible for shorter ignition delays and higher cetane number of DME.
LHV of DME is almost half that of diesel, therefore to obtain the same horsepower, flow rate of DME is about 1.7 times that of diesel. This means larger storage tanks for DME, higher diameter pipes and tubes for fuel flow, higher flow capacity of the DME pumps and the fuel injectors. Duration of Injection (DOI) of DME will be longer than diesel and the Start of Injection (SOI) has to be advanced accordingly. Lower boiling point of DME translates into faster vaporization of injected fuel in the combustion chamber. This along with lower critical temperature of DME results in superheated vapor in the combustion chamber, adequate air-fuel mixing is ensured. Large heat of vaporization also lowers the in-cylinder temperatures and lower NOx emissions.
Chain combustion reaction is possibly through one of the following competing pathways [12]:
C–O bond fission (pyrolysis mechanism):
Hydrogen abstraction (oxidation mechanism):
As the C-O bond energy is smaller than C-H bond, distortion of the C-O bonds in the DME molecule weakens the bonding strength and the breakage of the C-O bonds earlier. Pyrolysis is more likely to start the chain reaction at relatively low temperatures, showing as lower auto-ignition temperature.
Change of piston and cylinder heads in the existing diesel engines may not be required other than design of the fuel injection nozzle to suit the volumetric flow rate and existing piston profile. However, in order to have an optimum design of combustion chamber to suit the spray characteristics of DME changes to the piston bowl and re-location of piston rings may be needed. For best performance of the engine valve timings may also need to be modified resulting in design and development of new camshafts. For modifying existing diesel engines, it becomes necessary to retrofit a new fuel injection system right from the fuel tank, feed pumps, pressure pumps, common rails and fuel injectors.
DME is similar to LPG in terms of safety. Vapor of DME is heavier than air and settles to the ground similar to LPG. Sufficient ventilation is necessary in locations where DME is being used whether for stationary installations or transport. Ignition limit of DME is 3.4% - 18.6% by volume and therefore necessary precautions have to be implemented which will be similar to LPG. Global Warming Potential (GWP) of a molecule is its adverse effect on climate change. GWP includes both the molecules lifetime and ability to absorb radiation. DME is atmospherically not dangerous and does not contribute to global warming.
Common rail fuel injection systems have been developed for DME fueled CI engines and these engines have demonstrated good engine performances and efficiency along with significant reduction in harmful exhaust emissions. This has been made possible by having a good control of the fuel injection characteristics and temperature. The common rail concept for DME fuel have also proven effective in simple and safe fuel handling. Figure 9(a) illustrate a comparison of the concepts use for DME fueled diesel engines, figure is self-explanatory. Figure 9(b) shows a schematic of the DME fuel storage and distribution system on engine.
Fuel injection system and injection characteristics of a DME fueled engine [
Figure 9(c) presents a comparison of the simulated injection characteristics of diesel and DME digital hydraulic operating system (DHOS) injectors. Piston lifts in both the cases are similar, whereas the fuel injection pressure for diesel injector is about 1200 bar and for the DME injector it is around 800 bar. Duration of injection (DOI) for the DME injector is higher as compared to the diesel injector and similar trend is reflected in the period of needle lift of the injector. The injection rate of fuel for the DME case is higher than diesel all along the injection and the DOI is higher as can be seen in the bottom-most figure. Higher volume of fuel flow for DME vis-a-vis diesel can be seen in the figure due to lower density and LHV of DME compared to diesel.
Stoichiometric combustion of DME in air yields 1.91 m of CO2. This is equivalent to 66 gm of CO2 per MJ (LHV) of combusted DME.
DME combustion in air | (16) |
Stoichiometric combustion of one gram of diesel
Diesel combustion in air | (17) |
Combustion of one gm of DME in air emits less CO2 than combustion of one gm of Diesel, difference being 1.25 gm less CO2. Experimental investigations have brought out that there is substantial reduction in particulate matter (PM), NOx and combustion noise when DME is used as a fuel in CI engines. Combustion efficiency (BSFC) of DME fuel in a CI engine is similar to diesel (Figure 10) and so fuel consumption can be similar on an energy basis. Also shown in Figure 10 are comparison of the road load emissions of NOx, CO, HC and Smoke (PM) on a DME and diesel fueled engine. Smoke is undetectable and NOx, CO, HC are lower in DME engine fitted with an oxidation catalyst.
Comparative analysis of emission data from neat DME & mineral fueled CI engine [
Figure 11 gives the NOx emission data vs. engine efficiency for a 1.15 MW diesel power generation unit engine fueled with DME and with different levels of EGR. As the DME fueled engine does not produce any soot and ultra-low PM emissions, higher EGR levels can be used on the engine to reduce the NOx emissions. Against a 950 ppm NOx regulation, as the EGR is increased, very low NOx levels of 30 ppm can be achieved albeit with an engine efficiency penalty of 3%.
NOx emission data from a DME-fueled 1.15 MW diesel power generation unit [
Figure 12 shows emission results on 6-cylinder 7 liter turbocharged/intercooled heavy-duty diesel engine operating in Japanese D13 mode driving cycle. NOx and CO2 emissions can be reduced with DME fueled engine vis-a-vis diesel engine at comparable fuel economy. In addition, combustion noise of DME fueled engines are lesser than their diesel counterparts.
Comparison of fuel consumption (BSFC), NOx and CO2 emissions on a 6-cylinder 7 liter turbocharge/intercooled heavy-duty diesel engine operating in Japanese D13 mode [
In many countries research and development of DME fueled CI engines has been carried out and commercial trails done successfully. Japan, Europe, North America, China and South Korea are the leaders in development of DME fueled engines. A brief summary of the development of DME engines is presented in Table 7.
Region/Country | Details |
---|---|
Europe |
|
North America |
|
Japan |
|
China |
|
S. Korea |
|
Life cycle studies are used to compare the effect of different fuels/energy sources/ transport technologies. Life-cycle analysis consists of Well-to-Pump (WTP) and Pump-to-Wheel (PTW) estimation of energy consumption and emission of pollutants and GHG impact of these pollutions. WTP path consists of a) recovery and transport of raw material, b) production of the fuel, c) transportation of fuel, and d) distribution. PTW is the vehicle operation part of the pathway. Figure 13 shows a schematic to illustrate the Well-to-Wheel cycle for different fuel/transport technology combinations.
Well-to-wheel cycle for transportation fuels [
Many studies on life cycle energy consumption and emissions for DME fuel have been carried out globally. Lee et al. have investigated Well-to-Wheels emissions of greenhouse gases and air pollutants of di-methyl ether from natural gas and renewable feedstocks in comparison with petroleum gasoline and diesel in the United States and Europe. For this purpose they have used Greenhouse gases, Regulated Emissions and Energy use in Transportation (GREET) model developed by Argonne National Laboratory (ANL). They have used five pathways to calculate the WTW by use of DME as fuel, these are 1) fossil NG with large-scale DME plants, 2) methanol from fossil NG with large-scale plants for both methanol and DME (separately), 3) land-fill-gas (LFG) with small-scale DME plants, 4) manure-based biogas with small-scale DME plants, 5) methanol from black liquor gasification with small-scale DME plants. They have studied DME production and use in the US and Europe in two class of vehicles (light-duty (LDV) and heavy-duty vehicles (HDV). Their studies show that WTW consumption of fossil energy and emission of GHG emissions in production and use of DME fuel is very low as compared to diesel and gasoline vehicles. Five pathways used in the production of DME are shown in Figure 14.
Five pathways for production of DME [
In this study a small DME production plant is assumed to have a capacity of 25 MTPD (metric ton per day) and a large-scale plant is one with a capacity of 3600 MTPD. Case NG uses the fossil NG to produce DME directly in a large scale DME production plant. NG is supplied to the DME production plant through a pipeline. In case MeOH fossil NG is first converted to methanol and thence to DME. In this case the methanol production plant is close to the source of NG and methanol is transported to the DME production units by rail. Biogas from two sources has been considered, i.e., a) landfill gas (LFG) and b) during production and treatment of manure (MANR). Both are taken as renewable alternatives. Biogas is made up of CH4 and CO2 and is generated by anaerobic digestion (AD) of organic wastes. In both cases DME plant are small scale plants co-located with the source of biogas. Before the biogas can be fed into the DME plant it has to be cleaned in separate reactors where impurities like Sulfur compounds etc. are removed and the biogas is upgraded to the required composition.
Figure 15(a) depicts the WTW energy consumption for DME production through different pathways. DME production seems to consume more energy per MJ of fuel produced as compared to gasoline and diesel in both US and EU. This is because the conversion efficiency of raw material to DME is significantly lesser than gasoline and diesel. Although, conversion of fossil NG to DME directly or through MeOH is lesser than gasoline and diesel, however, this may also be due to scale of operation and size of plants which are much bigger and established for gasoline and diesel. Also, production of DME from renewable sources will result in zero or negligible consumption of fossil fuel.
WTW energy consumption and emissions for DME produced through different pathways. (a) Comparison of WTW energy consumption for DME production vis-a-vis gasoline and diesel production in US and EU [
Figure 15(b) shows the GHG emissions from DME production gasoline and diesel consumption and MeOH production. The emissions consist of the following components, a) For preparation and transportation of feedstock, b) Production of fuel and its transport, c) Avoided combustion and non-combustion emissions, d) biogenic CO2 in fuel and e) Fuel combustion. In the case of DME produced from bio-gas, avoided combustion and non-combustion are a major portion of the emissions inventory and in reducing the WTW emissions to very low/negative values. Thus, WTG GHG for LFG and manure based bio-gas are 6 and − 1 gCO2 e/MJ respectively and are 93% and 101% lower than US diesel. In the EU LFG and manure based bio-gas to DME process shows 6 and 12 gCO2 e/MJ of GHG emissions respectively which are 92% and 87% lower than EU diesel. If, however, regional electricity is used for production of DME then the WTW GHG emissions in the US will increase to 25 and 1 gCO2 e/MJ for LFG and manure bio-gas respectively. In the EU, the corresponding figures for DME production are 19 and 13 gCO2e/MJ from LFG and manure biogas respectively. Thus, it can be seen that the energy mix of the process has a strong impact on the WTW emissions as well.
In Figure 16, WTW GHG emissions vs. WTW vehicle energy consumption are plotted for some alternative fuels and petroleum-based gasoline and diesel. Figure 17 plots the results for synthetic diesel from farmed wood, synthetic diesel from waste wood and black liquor, ethanol from sugarcane (Brazil) and DME from waste wood and black liquor. WTW GHG emissions of DME produced from waste wood and black liquor are the lowest of all the fuels studied. WTW energy consumption (MJ/100 Km) for DME is second lowest after petroleum fuels. This may be due to the established production process of petroleum fuels and well-optimized engine and vehicle technologies for petroleum-based fuels. It is possible the life cycle energy consumption of DME fuel will reduce as the production technology for DME is matured and CIDI engines are designed specifically for DME fuel.
Well-to-wheel GHG emissions & vehicle energy consumption for some alternate fuels [
Different type of coal gasifiers [
Annual consumption of diesel fuel in India is more than 100 billion liters [25]. Relative consumption of diesel fuel by different type of vehicles in the transport sector in India is shown in Figure 17. In the transport sector, Trucks (HCV/LCV) are the major consumers of diesel fuel (40%) followed by private cars/ SUVs (19%) and Busses/State Transport Undertakings (14%).
Transport sector, use of diesel sector (India) [
Thus, a concentrated effort to convert diesel trucks and busses to use DME as fuel will have a major effect on reduction of GHG in India. Conversion of private diesel vehicles will be difficult as these vehicles are powered by different types and make of diesel engines. Figure 19 displays the details of the Industrial sector regarding consumption of diesel fuel. In this sector, equipment such as construction, boring, drilling, earth-moving etc. are the largest users of diesel fuel (38%) followed by Industry (29%) and Gensets (24%). It may not be possible to take up conversion of the construction and earth moving equipment diesel engines to operate on DME due to the nature of the work involved or diesel use in furnaces etc., however conversion of gensets to DME can be taken up and will have a positive effect on the GHG emissions and the reduction of use of fossil diesel.
Use of diesel fuel by industrial sector in India [
Conversion of diesel engines in the agricultural sector (13% consumption of diesel fuel) to DME will also be beneficial for India in terms of reduction of GHG and diesel fuel. Agriculture equipment like tractors, diesel pumps, agricultural implements, tillers, harvesters, thrashers etc. operate in limited areas and the provision of DME dispensation facilities to cater to the demands of a particular area may be economically feasible.
Decarbonizing of the transport and other engineering sectors has become an urgent necessity to stop further global warming. Electrification of power trains by using batteries, fuel cells, electric transmission etc. promise to drastically reduce and even reverse the global warming trend. Battery and fuel cell technologies are however still in the evolution phase and for them to match the power density, energy density, low-cost and the reliability of liquid fuels-based IC engines is expected to take at least another two to three decades. Meanwhile the IC engines technology has reached a high level of maturity, sophistication, knowledge and economy of scale. IC engines-based power trains will continue to dominate the transportation, industrial, power generation and other sectors for next three decades. Therefore, it is imperative that solutions are found to make IC engines-based power trains clean and energy efficient. Compression Ignition (CI) engines with diesel fuel are used in many heavy-duty applications like long-distance trucks, busses, agricultural equipment, earth moving and construction equipment. Conversion of these diesel engines to use an alternative clean fuel like DME will aid in protecting the environment and conservation of energy. Primarily this will involve development of a pressurized fuel injection system and matching the fuel injection parameters to the physical and chemical properties of DME. Sufficient developments have been done in the past in development of fuel injection systems for DME fueled CI engines, therefore with the collaboration of the engine OEMs and the fuel equipment manufacturers diesel engines conversion to DME can be taken up in an economical way and in a time-bound manner. Impact of such conversions will be seen in the form of reduction of WTW energy consumption and harmful emissions.
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L. Motta, C. C. P. Andrade and M. H. A. Santana",authors:[{id:"29669",title:"Prof.",name:"Maria Helena",middleName:null,surname:"Santana",slug:"maria-helena-santana",fullName:"Maria Helena Santana"},{id:"154939",title:"Dr.",name:"Fernanda",middleName:null,surname:"Motta",slug:"fernanda-motta",fullName:"Fernanda Motta"},{id:"165676",title:"Dr.",name:"Cristiane",middleName:null,surname:"Andrade",slug:"cristiane-andrade",fullName:"Cristiane Andrade"}]},{id:"31331",doi:"10.5772/31355",title:"Digestate: A New Nutrient Source - Review",slug:"digestate-a-new-nutrient-source-review",totalDownloads:7735,totalCrossrefCites:45,totalDimensionsCites:101,abstract:null,book:{id:"1323",slug:"biogas",title:"Biogas",fullTitle:"Biogas"},signatures:"Marianna Makádi, Attila Tomócsik and Viktória Orosz",authors:[{id:"86724",title:"Ms.",name:"Marianna",middleName:null,surname:"Makádi",slug:"marianna-makadi",fullName:"Marianna Makádi"}]},{id:"20063",doi:"10.5772/16454",title:"Detoxification of Lignocellulosic Hydrolysates for Improved Bioethanol Production",slug:"detoxification-of-lignocellulosic-hydrolysates-for-improved-bioethanol-production",totalDownloads:11886,totalCrossrefCites:8,totalDimensionsCites:90,abstract:null,book:{id:"448",slug:"biofuel-production-recent-developments-and-prospects",title:"Biofuel Production",fullTitle:"Biofuel Production - Recent Developments and Prospects"},signatures:"Anuj K. Chandel, Silvio Silvério da Silva and Om V. Singh",authors:[{id:"25160",title:"Prof.",name:"Om",middleName:"V",surname:"Singh",slug:"om-singh",fullName:"Om Singh"},{id:"51540",title:"Dr.",name:"Silvio",middleName:null,surname:"Silva",slug:"silvio-silva",fullName:"Silvio Silva"},{id:"76898",title:"Dr.",name:"Anuj",middleName:null,surname:"Chandel",slug:"anuj-chandel",fullName:"Anuj Chandel"}]}],mostDownloadedChaptersLast30Days:[{id:"59269",title:"Gasification of Municipal Solid Waste",slug:"gasification-of-municipal-solid-waste",totalDownloads:3654,totalCrossrefCites:19,totalDimensionsCites:30,abstract:"Gasification of municipal solid waste (MSW) is an attractive alternative fuel production process for the treatment of solid waste as it has several potential benefits over traditional combustion of MSW. Syngas produced from the gasification of MSW can be utilized as a gas fuel being combusted in a conventional burner or in a gas engine to utilize the heat or produce electricity. Also, it can be used as a building block for producing valuable products such as chemicals and other forms of fuel energy. This book chapter covers the properties of MSW, gasification mechanism, chemistry, operating conditions, gasification technologies, processes, recovery system, and most importantly by reviewing the environmental impacts of MSW gasification. As one of recent advanced technologies, a case study of pilot-scale MSW gasification is introduced, which could be one of the most efficient pathways to utilize the technology to produce electricity with a newly developed gasification process by reducing tar and pollutant emission.",book:{id:"6349",slug:"gasification-for-low-grade-feedstock",title:"Gasification for Low-grade Feedstock",fullTitle:"Gasification for Low-grade Feedstock"},signatures:"Yong-Chil Seo, Md Tanvir Alam and Won-Seok Yang",authors:[{id:"213854",title:"Prof.",name:"Yong-Chil",middleName:null,surname:"Seo",slug:"yong-chil-seo",fullName:"Yong-Chil Seo"},{id:"213857",title:"Mr.",name:"Md Tanvir",middleName:null,surname:"Alam",slug:"md-tanvir-alam",fullName:"Md Tanvir Alam"},{id:"222321",title:"Dr.",name:"Won-Seok",middleName:null,surname:"Yang",slug:"won-seok-yang",fullName:"Won-Seok Yang"}]},{id:"52687",title:"Methods of Estimating Forest Biomass: A Review",slug:"methods-of-estimating-forest-biomass-a-review",totalDownloads:3448,totalCrossrefCites:9,totalDimensionsCites:14,abstract:"Forest plays a special role in carbon sequestration and thus mitigating climate change. However, the large uncertainty in biomass estimation is unable to meet the requirement of the accurate carbon accounting. The use of a suitable and rigor method to accurately estimate forest biomass is significant. Moreover, the world is increasingly facing the conflicting pressures of economic growth and environmental protection. Improving energy structure and vigorously developing biomass energy has become the development trend of energy utilization in the future. As energy plant is characterized by a large net accumulation of biomass. Therefore, the scientific evaluation of the size and potential of energy from plant also requires a suitable method for estimating biomass. Here, we reviewed the estimate methods, including allometric equation, mean biomass density, biomass expansion factor, geostatistics, etc. For each method, we will present background, rational, applicability, as well as estimation procedure by exemplifying a case. In this chapter, we argued that the new developed technique such as geo-statistics and remote sensing technique (e.g. LIDAR) would be the key tools to improve forest biomass estimation accuracy. However, prior to this, spatial variation of forest biomass at various levels should be explored using multi-source data and multi-approaches.",book:{id:"5393",slug:"biomass-volume-estimation-and-valorization-for-energy",title:"Biomass Volume Estimation and Valorization for Energy",fullTitle:"Biomass Volume Estimation and Valorization for Energy"},signatures:"Lei Shi and Shirong Liu",authors:[{id:"187616",title:"Associate Prof.",name:"Lei",middleName:null,surname:"Shi",slug:"lei-shi",fullName:"Lei Shi"},{id:"194544",title:"Prof.",name:"Shirong",middleName:null,surname:"Liu",slug:"shirong-liu",fullName:"Shirong Liu"}]},{id:"52751",title:"Biomass Compositional Analysis for Conversion to Renewable Fuels and Chemicals",slug:"biomass-compositional-analysis-for-conversion-to-renewable-fuels-and-chemicals",totalDownloads:2882,totalCrossrefCites:14,totalDimensionsCites:30,abstract:"As the world continues to deplete its nonrenewable resources, there has begun a shift toward using renewable materials for the production of fuels and chemicals. Terrestrial biomass, as well as municipal solid wastes, provides renewable feedstocks for fuel and chemical production. However, one of the major challenges to using biomass as a feedstock for fuel and chemical production is the great amount of innate variability between different biomass types and within individual biomass species. This inconsistency arises from varied growth and harvesting conditions and presents challenges for conversion processes, which frequently require physically and chemically uniform materials. This chapter will examine intrinsic biomass compositional characteristics including cellulose, hemicellulose, lignin, extractives/volatiles, and ash for a wide array of biomass types. Additionally, extrinsic properties, such as moisture content and particle grind size, will be examined for their effect on biomass conversion to fuels using four major conversion processes: direct combustion, pyrolysis, hydrothermal liquefaction, and fermentation. A brief discussion on recent research for the production of building block chemicals from biomass will also be presented.",book:{id:"5393",slug:"biomass-volume-estimation-and-valorization-for-energy",title:"Biomass Volume Estimation and Valorization for Energy",fullTitle:"Biomass Volume Estimation and Valorization for Energy"},signatures:"C. Luke Williams, Rachel M. Emerson and Jaya Shankar Tumuluru",authors:[{id:"95803",title:"Dr.",name:"Jaya Shankar",middleName:null,surname:"Tumuluru",slug:"jaya-shankar-tumuluru",fullName:"Jaya Shankar Tumuluru"},{id:"187715",title:"Dr.",name:"C. Luke",middleName:null,surname:"Williams",slug:"c.-luke-williams",fullName:"C. Luke Williams"},{id:"194456",title:"MSc.",name:"Rachel M.",middleName:null,surname:"Emerson",slug:"rachel-m.-emerson",fullName:"Rachel M. Emerson"}]},{id:"52891",title:"Advances in the Application of Spectroscopic Techniques in the Biofuel Area over the Last Few Decades",slug:"advances-in-the-application-of-spectroscopic-techniques-in-the-biofuel-area-over-the-last-few-decade",totalDownloads:2642,totalCrossrefCites:1,totalDimensionsCites:2,abstract:"Guided by the instability of the oil market, as well as limited availability of and, especially, the environmental impacts of fossil fuels, the needs of the market for environmental-friendly energy sources have increased. However, as with any other product that is intended to place on the market, it is essential to ensure the quality of the fuel for successful marketing and acceptance by consumers. Spectroscopic techniques have been widely used for different purposes in the literature for the past decades, from biological applications to the measurement of the elemental composition of planets. From studies focused on biodiesel, bioethanol, biomass and biofuel in general, different spectroscopic techniques have also been applied in the area. The focus of this chapter is to elucidate what has been published in the last few decades over the subject, detailing the basic concepts of the main spectroscopic techniques applied and showing the results and developments over biofuel. The aim of the chapter is to achieve a set of information that can be used as a bigger compile of information of the state of the art regarding the theme.",book:{id:"5509",slug:"frontiers-in-bioenergy-and-biofuels",title:"Frontiers in Bioenergy and Biofuels",fullTitle:"Frontiers in Bioenergy and Biofuels"},signatures:"João Cajaiba Da Silva, Alex Queiroz, Alline Oliveira and Vinícius\nKartnaller",authors:[{id:"107106",title:"Prof.",name:"João",middleName:null,surname:"Cajaiba Da Silva",slug:"joao-cajaiba-da-silva",fullName:"João Cajaiba Da Silva"},{id:"192636",title:"MSc.",name:"Alex",middleName:null,surname:"Queiroz",slug:"alex-queiroz",fullName:"Alex Queiroz"},{id:"192637",title:"MSc.",name:"Alline",middleName:null,surname:"Oliveira",slug:"alline-oliveira",fullName:"Alline Oliveira"},{id:"192638",title:"M.Sc.",name:"Vinicius",middleName:null,surname:"Kartnaller",slug:"vinicius-kartnaller",fullName:"Vinicius Kartnaller"}]},{id:"62959",title:"Biogas for Clean Energy",slug:"biogas-for-clean-energy",totalDownloads:1690,totalCrossrefCites:2,totalDimensionsCites:8,abstract:"This chapter demonstrates a biogas renewable energy resource potential study for electric power generation from easily available biogas feedstock materials in four selected case study sites. Under this study, the site used in the model is a rural Kebele in Jama Woreda at 10.548° N, 39.33° E. The common biogas feedstocks considered under this study are animal slurry, human feces and jatropha byproducts whereas the biodiesel is considered from jatropha seed.",book:{id:"6839",slug:"anaerobic-digestion",title:"Anaerobic Digestion",fullTitle:"Anaerobic Digestion"},signatures:"Demsew Mitiku Teferra and Wondwosen Wubu",authors:[{id:"259485",title:"Mr.",name:"Demsew Mitiku",middleName:null,surname:"Teferra",slug:"demsew-mitiku-teferra",fullName:"Demsew Mitiku Teferra"}]}],onlineFirstChaptersFilter:{topicId:"763",limit:6,offset:0},onlineFirstChaptersCollection:[],onlineFirstChaptersTotal:0},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:8,limit:8,total:0},allSeries:{pteSeriesList:[{id:"14",title:"Artificial Intelligence",numberOfPublishedBooks:9,numberOfPublishedChapters:89,numberOfOpenTopics:6,numberOfUpcomingTopics:0,issn:"2633-1403",doi:"10.5772/intechopen.79920",isOpenForSubmission:!0},{id:"7",title:"Biomedical Engineering",numberOfPublishedBooks:12,numberOfPublishedChapters:104,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2631-5343",doi:"10.5772/intechopen.71985",isOpenForSubmission:!0}],lsSeriesList:[{id:"11",title:"Biochemistry",numberOfPublishedBooks:32,numberOfPublishedChapters:318,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2632-0983",doi:"10.5772/intechopen.72877",isOpenForSubmission:!0},{id:"25",title:"Environmental Sciences",numberOfPublishedBooks:1,numberOfPublishedChapters:12,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2754-6713",doi:"10.5772/intechopen.100362",isOpenForSubmission:!0},{id:"10",title:"Physiology",numberOfPublishedBooks:11,numberOfPublishedChapters:141,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-8261",doi:"10.5772/intechopen.72796",isOpenForSubmission:!0}],hsSeriesList:[{id:"3",title:"Dentistry",numberOfPublishedBooks:8,numberOfPublishedChapters:129,numberOfOpenTopics:2,numberOfUpcomingTopics:0,issn:"2631-6218",doi:"10.5772/intechopen.71199",isOpenForSubmission:!0},{id:"6",title:"Infectious Diseases",numberOfPublishedBooks:13,numberOfPublishedChapters:113,numberOfOpenTopics:3,numberOfUpcomingTopics:1,issn:"2631-6188",doi:"10.5772/intechopen.71852",isOpenForSubmission:!0},{id:"13",title:"Veterinary Medicine and Science",numberOfPublishedBooks:11,numberOfPublishedChapters:106,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2632-0517",doi:"10.5772/intechopen.73681",isOpenForSubmission:!0}],sshSeriesList:[{id:"22",title:"Business, Management and Economics",numberOfPublishedBooks:1,numberOfPublishedChapters:19,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2753-894X",doi:"10.5772/intechopen.100359",isOpenForSubmission:!0},{id:"23",title:"Education and Human Development",numberOfPublishedBooks:0,numberOfPublishedChapters:5,numberOfOpenTopics:1,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100360",isOpenForSubmission:!0},{id:"24",title:"Sustainable Development",numberOfPublishedBooks:0,numberOfPublishedChapters:15,numberOfOpenTopics:5,numberOfUpcomingTopics:0,issn:null,doi:"10.5772/intechopen.100361",isOpenForSubmission:!0}],testimonialsList:[{id:"13",text:"The collaboration with and support of the technical staff of IntechOpen is fantastic. 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Dr. Bobek is a member of the editorial boards of six international journals and a member of the Strategic Council of the Minister of Foreign Affairs of the Republic of Slovenia. He has a long history in academia, consulting, and entrepreneurship. His own consulting firm, Palemid, has managed twenty significant projects, such as Cooperation Program Interreg V-A (Slovenia-Austria) and Capacity Building for the Serbian Chamber of Enforcement Agents. He has also participated in many international projects in Italy, Germany, Great Britain, the United States, Spain, Turkey, France, Romania, Croatia, Montenegro, Malaysia, and China. Dr. Bobek is also a co-founder of the Academy of Regional Management in Slovenia.",institutionString:"Universities of Applied Sciences FH Joanneum, Austria",institution:null},editorTwo:{id:"293992",title:"Dr.",name:"Tatjana",middleName:null,surname:"Horvat",slug:"tatjana-horvat",fullName:"Tatjana Horvat",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002hXb0hQAC/Profile_Picture_1642419002203",biography:"Tatjana Horvat works as a professor for accountant and auditing at the University of Primorska, Slovenia. She is a Certified State Internal Auditor (licensed by Ministry of Finance RS) and Certified Internal Auditor for Business Sector and Certified accountant (licensed by Slovenian Institute of Auditors). At the Ministry of Justice of Slovenia, she is a member of examination boards for court expert candidates and judicial appraisers in the following areas: economy/finance, valuation of companies, banking, and forensic investigation of economic operations/accounting. At the leading business newspaper Finance in Slovenia (Swedish ownership), she is the editor and head of the area for business, finance, tax-related articles, and educational programs.",institutionString:null,institution:{name:"University of Primorska",institutionURL:null,country:{name:"Slovenia"}}},editorThree:null},{id:"87",title:"Economics",coverUrl:"https://cdn.intechopen.com/series_topics/covers/87.jpg",isOpenForSubmission:!0,editor:{id:"327730",title:"Prof.",name:"Jaime",middleName:null,surname:"Ortiz",slug:"jaime-ortiz",fullName:"Jaime Ortiz",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y00002zaOKZQA2/Profile_Picture_1642145584421",biography:"Dr. Jaime Ortiz holds degrees from Chile, the Netherlands, and the United States. He has held tenured faculty, distinguished professorship, and executive leadership appointments in several universities around the world. Dr. Ortiz has previously worked for international organizations and non-government entities in economic and business matters, and he has university-wide globalization engagement in more than thirty-six countries. He has advised, among others, the United Nations Development Program, Inter-American Development Bank, Organization of American States, Pre-investment Organization of Latin America and the Caribbean, Technical Cooperation of the Suisse Government, and the World Bank. Dr. Ortiz is the author, co-author, or editor of books, book chapters, textbooks, research monographs and technical reports, and refereed journal articles. He is listed in Who’s Who in the World, Who’s Who in America, Who’s Who in Finance and Business, Who’s Who in Business Higher Education, Who’s Who in American Education, and Who’s Who Directory of Economists. Dr. Ortiz has been a Fulbright Scholar and an MSI Leadership Fellow with the W.K. Kellogg Foundation. His teaching interests revolve around global economies and markets while his research focuses on topics related to development and growth, global business decisions, and the economics of technical innovation.",institutionString:null,institution:{name:"University of Houston",institutionURL:null,country:{name:"United States of America"}}},editorTwo:null,editorThree:null},{id:"88",title:"Marketing",coverUrl:"https://cdn.intechopen.com/series_topics/covers/88.jpg",isOpenForSubmission:!0,editor:{id:"203609",title:"Associate Prof.",name:"Hanna",middleName:null,surname:"Gorska-Warsewicz",slug:"hanna-gorska-warsewicz",fullName:"Hanna Gorska-Warsewicz",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bSD9pQAG/Profile_Picture_2022-06-14T11:58:32.jpeg",biography:"Hanna Górska-Warsewicz, Ph.D. is Associate Professor at Warsaw University of Life Sciences and Head of Department of Food Market and Consumption Research. She specializes in the subject of brands, brand equity, and brand management in production, service, and trade enterprises. She combines this subject with marketing and marketing management in both theoretical and practical aspects. Prof. Hanna Górska-Warsewicz also analyzes brands in the context of trademarks, legal regulations and the protection of intangible. She is an author or co-author of over 200 publications in this field, including 8 books. 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