Sampath Gunukula,
Ivan C. Lee and
Dat T. Tran*
CCDC Army Research Laboratory, FCDD-RLS-DE, Adelphi, MD 20783, USA. E-mail: dat.t.tran4.civ@mail.mil
First published on 11th September 2019
It is necessary to advance the development of compact energy systems for making energy from biomass like wood or switchgrass, as an alternative to the construction of highly capital-intensive large scale biorefineries. Compact energy systems consist of four individual components: a biomass preparation unit, a biomass converter, a fuel processor, and a powered engine. The individual unit processes within each component and the possible types of compact energy systems with different biomass converter technologies like fermentation, pyrolysis, and gasification are presented. The size, weight, and energy efficiency of upgrading biomass to energy using a compact energy system with various gasification technologies has been estimated. A compact energy system with a hydrogen fuel cell as a powered-engine component, processing 10 kg of dry biomass per day, generates a net energy (kW h) of −7.5, −30, 18.7, 13.1, and 11.7 with the super-critical, microwave assisted, catalytic, steam, and conventional gasification technologies as biomass converter technologies, respectively. The low yields of super-critical gasification and low efficacy of converting electric energy to heat via electromagnetic waves with microwave assisted gasification result in negative net energy with the respective compact energy system. Finally, the challenges and opportunities with the development of low weight, small size, and highly energy efficient compact energy systems built around gasification are discussed.
It has been expected that the biomass conversion technologies must be deployed at large-scale bio-refineries with a feedstock processing capacity of several hundred dry metric tons per day in order to compete with the petroleum derived fuels on a cost basis.2,3 The construction of such large scale biorefineries, however, require capital investments of around one half-billion dollars.2,3 The high capital risk and a low return on investment have limited the construction of biorefinery plants. Additionally, procuring large amounts of biomass to meet the feedstock demand of a biorefinery creates logistic issues as the bulk density of biomass is inherently very low.4 It is recently shown that the biomass densification using palletization, torrefaction, and pyrolysis to overcome the logistic issues is not economically viable.5
The limitations of fuel production in a large scale biorefinery facility can be addressed by developing compact energy systems with an arbitrary biomass processing capacity ranging anywhere between 1 kg and 100 kg per day. The biomass to make fuels using compact energy systems can be obtained from household generated food, yard, and plastic wastes. Compact energy systems would thus eliminate the difficulty of transporting large quantities of biomass to bio refinery locations. Furthermore, these compact energy systems can be manufactured by smaller specialized shops and thus the construction of large scale biorefineries would no longer be required. Additionally, the use of the food and plastic waste as a feedstock eliminates the costs of collecting, transporting, and landfilling these wastes. Compact energy systems can be used as an in-built (or on-board) power source for manned and unmanned vehicles or as an independent power source for recharging purposes. In both applications, the net available energy of a compact energy system, which is defined as the specific higher heating value of the fuel product minus the sum of total energy input to upgrade biomass to the fuel product, must be positive. Moreover, the physical dimensions of compact energy systems for on-board applications must meet the weight and footprint (volume) requirements of manned and unmanned vehicles.
The development of a compact energy system dates to the World War II.6 During the wartime, several European nations produced a wood gas vehicle with an on-board fuel generation system. These on-board fuel generation systems gasified wood to make energy. After World War II, on-board fuel generation technology fell into oblivion because of its heavy weight, low energy efficiency, and large size (footprint). In recent times, a great amount of research has been dedicated towards the development of a wide range of new biomass conversion pathways as well as compact thermoelectric devices like Stirling engine and electrochemical devices like fuel cells. Such research efforts will enable us to build new compact energy systems with a small size, low weight, and high energy efficiency.
There are 15 different types of compact energy systems that can be built using gasification as a biomass conversion pathway (refer to Sections 2 and 3 of this study). Likewise, many compact energy systems can be built with fermentation and pyrolysis as the biomass conversion pathway (refer Section 2 of this study). To avoid potential losses to the research and development (R&D) costs and to accelerate the commercialization of compact energy systems, R&D efforts must be directed towards the development of feasible compact energy systems that can provide positive net available energy and meet the size and weight requirements. To this end, in this study, modeling analysis is performed to evaluate the feasibility of developing compact energy systems built around the biomass gasification pathway. Further, the challenges and research opportunities in the development of these types of compact energy systems are discussed.
The possible sub-components of the biomass preparation component include, but are not limited to, any of these unit processes: mechanical screening, drying, grinding, and the physical, chemical, and mechanical pretreatment of a biomass. The mechanical screening of incoming biomass removes unwanted coarse particles. A dryer reduces the biomass moisture to the target level by evaporating water. The biomass size can be reduced with hammer mill type grinders. The lignocellulosic structure of a biomass can be disrupted by means of physical, chemical, and mechanical biomass pretreatment technologies so that the enzymes can access cellulose and hemicellulose of a biomass to produce fuel intermediates.7 It must be noted that the increase in number of unit processes within the biomass preparation component increases the total weight and volume of a compact energy system and decrease its energy efficiency.
Like gasification, pyrolysis involves simple heating of a biomass. Pyrolysis, however, heats the biomass at lower temperatures without the presence of oxygen. Pyrolysis is further classified to auto pyrolysis, fast pyrolysis, catalytic fast pyrolysis, slow pyrolysis, and microwave assisted pyrolysis.10 The major product of biomass slow pyrolysis operating at a temperature between 300 to 350 °C, 1 atm, and a residence time of several hours is bio-char.10 Unlike slow pyrolysis, the other pyrolysis processes involve heating biomass to a higher temperature at a high rapid rate. Pyrolyzing biomass at a temperature between 500 to 550 °C, 1 atm, and a residence time of less than 30 seconds produces bio-oil as a major product.10
The microbial technologies can synthesize liquid as well as gaseous fuels from carbohydrates, CO2, and organic wastes. The sugars derived from the decomposition of cellulose, hemicellulose, and starch can be transformed to a range of molecules including ethanol, acetone, propanol, and butanol using biosynthetic pathways in microorganisms like Saccharomyces cerevisiae and Escherichia coli.11,12 Contrary to carbohydrate fermentation, algae can make biodiesel (alkyl esters of long chain fatty acids) by fixing CO2 from the atmosphere.12 The methanogenic decomposition of organic wastes can produce biogas, a mixture of CH4 and CO2.12
The choice of a biomass converter technology influences the selection of sub-components of the biomass preparation unit as the biomass must meet certain specifications like size and moisture content specific to the biomass upgrading technology. If, for instance, a microbial technology is selected as a biomass converter, the biomass preparation unit must have sub-components to process incoming biomass to fermentable sugars. The biomass preparation component must reduce the size of incoming biomass to 2 mm if gasification and pyrolysis technologies are deployed in the biomass converter.
Feedstock | Biomass prep. | Biomass converter | Fuel processor | Powered-engine |
---|---|---|---|---|
Lignocellulose/organic waste | Dryer and grinder | Fast, auto, catalytic, or microwave assisted pyrolysis | Steam refining and char separations | Compressed tank and fuel cell |
Lignocellulose/organic waste | Dryer and grinder | Fast, auto, catalytic, or microwave assisted pyrolysis | Steam refining and char separations | Gas engine or Stirling engine |
Lignocellulose/organic waste | Dryer and grinder | Slow pyrolysis | Combustion | Gas engine or Stirling engine |
Lignocellulose/organic waste | Dryer and grinder | Slow pyrolysis | Direct carbon fuel cell | |
Lignocellulose/organic waste | Dryer and grinder | Fast, auto, catalytic, or microwave assisted pyrolysis | Blue whirl combustion and separations | Gas engine or Stirling engine |
Lignocellulose/organic waste | Dryer and grinder | Fast, auto, catalytic, or microwave assisted pyrolysis | Solid oxide fuel cell |
Feedstock | Biomass preparation component | Biomass converter | Fuel processor | Powered-engine |
---|---|---|---|---|
a Gasification can be conventional, steam, catalytic, supercritical, and microwave assisted. | ||||
Lignocellulose | Dryer and grinder | Conventional gasification | Steam refining and separations | Compressed tank and fuel cell |
Lignocellulose | Grinder | Steam gasification | Steam refining and separations | Compressed tank and fuel cell |
Organic (food) waste | Grinder | Supercritical water gasification | Steam refining and separations | Compressed tank and fuel cell |
Lignocellulose | Dryer and grinder | Catalytic gasification | Steam refining and separations | Compressed tank and fuel cell |
Lignocellulose | Dryer and grinder | Microwave assisted catalytic gasification | Steam refining and separations | Compressed tank and fuel cell |
Lignocellulose and/or food waste | Dryer and/or grinder | Gasificationa | Gas engine or Stirling engine |
Feedstocks | Biomass prep. | Biomass converter | Fuel processor | Powered-engine |
---|---|---|---|---|
Lignocellulose and/or food waste | Grinder | Enzymatic hydrolysis and fermentation to make biofuel | Steam refiner and separations | Compressed tank and fuel cell |
Lignocellulose and/or food waste | Grinder | Enzymatic hydrolysis and fermentation to make ethanol | Ethanol or solid oxide fuel cell | |
Lignocellulose and/or food waste | Grinder | Enzymatic hydrolysis and fermentation to make biofuel | Blue whirl combustion and separations | Gas engine or Stirling engine |
Developing and deploying compact energy systems requires answering the following engineering and science questions:
(1) What are the ideal combinations of biomass preparation, biomass converter, fuel processor, and powered-engine technologies that are optimize energy efficiency, volume, and weight for the desired application?
(2) How does the target energy demand and potential application influence ideal combinations?
(3) What are the major technological barriers in developing the ideal compact energy system?
(4) In which form (solid biomass, liquid fuel intermediate like bio-oil and ethanol, or gaseous hydrogen) must the energy be stored in for potential use?
(5) What are the best types of biomass feedstocks that are suitable for compact energy systems?
(6) How much energy is required to acquire biomass feedstock and process it using different types of compact energy systems?
(7) How adaptable are these compact energy systems for the feedstock uncertainty?
In this study, we addressed most of these questions for compact energy systems built around gasification (Table 2) through a system modeling approach.
Biomass converter technology | Conventional gasification | Catalytic gasification | Steam gasification | Supercritical gasification | Microwave assisted gasification | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Powered-engine | G | S | F | G | S | F | G | S | F | G | S | F | G | S | F |
Food waste | X | X | X | ||||||||||||
Lignocellulose | X | X | X | X | X | X | X | X | X | X | X | X | |||
Grinder | X | X | X | X | X | X | X | X | X | X | X | X | X | X | X |
Dryer | X | X | X | X | X | X | X | X | X | X | X | X | |||
Air compressor | X | X | X | X | X | X | X | X | X | X | X | X | |||
PSA for air purification | X | X | X | X | X | X | X | X | X | ||||||
Gasifier | X | X | X | X | X | X | X | X | X | X | X | X | X | X | X |
Steam reformer | X | X | X | X | X | X | X | X | X | X | X | X | |||
Heat exchanger | X | X | X | X | X | X | X | X | X | X | X | X | X | X | X |
Coarse filter | X | X | X | X | X | X | X | X | X | X | X | X | X | X | X |
PSA for syngas purification | X | X | X | X | |||||||||||
Pd-membrane | X | X | X | X | X | ||||||||||
Compact energy system type | T1 | T2 | T3 | T4 | T5 | T6 | T7 | T8 | T9 | T10 | T11 | T12 | T13 | T14 | T15 |
Compact energy system type | Wet biomass processed (kg d−1) | Dry biomass processed (kg d−1) | Hydrogen (H)/producer (P) gas produced (kg d−1) | Net total energy (kW h) | Net powera (kW) | Weight (kg) | Volume (L) |
---|---|---|---|---|---|---|---|
a Net power is calculated assuming operational time of 24 hours. | |||||||
T1 | 14 | 10 | 16.5 (P) | 9.9 | 0.41 | 8.2 | 45 |
T2 | 14 | 10 | 16.5 (P) | 10.7 | 0.45 | 15 | 37 |
T3 | 14 | 10 | 1 (H) | 13.3 | 0.56 | 8 | 5 |
T4 | 19 | 10 | 23 (P) | 9.2 | 0.38 | 6.3 | 39 |
T5 | 19 | 10 | 23 (P) | 9.9 | 0.41 | 13 | 43 |
T6 | 19 | 10 | 1.4 (H) | 18.7 | 0.78 | 14.5 | 4 |
T7 | 24 | 10 | 23.5 (P) | 6.9 | 0.29 | 7 | 33 |
T8 | 24 | 10 | 23.5 (P) | 7.4 | 0.31 | 14 | 32 |
T9 | 24 | 10 | 1.2 (H) | 11.7 | 0.49 | 7.35 | 5 |
T10 | 70 | 10 | 60 (P) | −15.5 | −0.65 | 14 | 59 |
T11 | 70 | 10 | 60 (P) | −14 | −0.58 | 24 | 44 |
T12 | 70 | 10 | 0.3 (H) | −7.5 | −0.31 | 12 | 11 |
T13 | 14 | 10 | 16.5 (P) | −63 | −2.62 | 9.8 | 48 |
T14 | 14 | 10 | 16.5 (P) | −65 | −2.7 | 16.6 | 40 |
T15 | 14 | 10 | 1 (H) | −30 | −1.25 | 9.1 | 8 |
The use of food waste cannot be used in compact energy systems built around gasification. Given the high moisture content of food waste, only supercritical gasification seems a viable technology for the conversion of food waste to hydrogen or producer gas, as there is no need to evaporate a large quantity of water. However, the energy analysis has shown that the net energy generation is negative in compact energy systems built around supercritical gasification (T10, T11, and T12 in Table 3). Such high energy inefficiency is attributed to the low hydrogen yield with the T12 compact energy system and a low gross calorific value of producer gas with T10 and T12 systems. The size and weight requirements of compact energy systems built around supercritical gasification processes are found to be comparable to that of other types of compact energy systems.
The energy efficiency analysis of compact energy systems built around microwave assisted gasification (T13, T14, and T15) has indicated that the energy generated from biomass is not enough to meet the energy demand of upgrading biomass to hydrogen or producer gas. This is due to the low efficiency of converting electric energy to heat via electromagnetic waves. The efficiency of converting from electrical energy to electromagnetic waves (microwaves) using magnetrons built into the microwave reactor is about 50%.2 An absorbent must be placed in a microwave reactor to absorb heat from electromagnetic waves generated by the magnetron.1 The efficiency of converting microwaves to heat depends on the dielectric properties of adsorbent materials.3,4,7
In this study, silicon carbide material was employed as the adsorbent for the microwave assisted catalytic gasification.7 The critical efficiency of converting microwaves to thermal energy using silicon carbide adsorbent material was predicted using a dielectric constant of 34%.3,4 With reference to the weight and volume of compact energy systems built around conventional gasification, the addition of a magnetron to the gasification reactor increases the weight and volume by 5% and 10% respectively. The weight and volume dimensions of a magnetron can be found in Obata et al.8
The comparison of amounts of hydrogen and producer gas delivered by different compact energy system types (T1 to T9) indicates that high hydrogen/producer gas yield per unit of dry biomass can be varied with the type of biomass gasification technology. The variance is attributed to the different carbon, hydrogen, and oxygen compositions of the biomass (Table S1†), different gasification operating conditions like temperature (Table S2†), hydrogen production yields in the gasifier, and the amount of moisture present in the biomass at the gasification reactor stage.
Among the compact energy system types T1 to T9, the net available energy in terms of kilowatt-hours produced by the compact energy system with a fuel cell as a power engine component is higher than that of gas and Stirling engines (Table 5). This is because the fuel cell efficiency of converting hydrogen to net available energy compared to the efficiency of converting hot gas to net available energy in Stirling engines is much higher (Table S3†). The weight and volume of compact energy systems with a Stirling or gas engines is found to be higher than that of a compact energy system with a fuel cell as the power engine component (Table 3). For the same reasons, high fuel efficiency, easy separation of hydrogen, and low specific power and power density, the compact energy system with a hydrogen fuel cell component is found to have a high specific power (W kg−1) and volumetric power density (W L−1) compared to a gasoline or Stirling engine (Fig. 3).
Fig. 3 The comparison of volumetric power density and specific power of different compact energy system types. |
Fig. 4 The weight (kg) of compact energy system built around gasification for the target power (kW) and operational time (h). |
Fig. 4 shows that for a given power requirement, the weight of a compact energy system increases with operational time. Similarly, for a given operational time, the weight of compact energy systems increases with the target power output. Such an increase in the weight of compact energy systems is attributed to the increase in the biomass flow rate. Fig. 4 or Table S4† can be used to determine the viability of deploying compact energy systems built around gasification to supply target power for the manned and unmanned ground vehicles. For instance, the Clearpath's Husky Unmanned Ground Vehicle has a power requirement of 1 kW with an operational time of 3 hours. These requirements can be met with the compact energy system types of T3, T6, and T9 with a weight of 4.4 kg. Since the maximum payload of the Husky Unmanned Ground Vehicle is about 70 kg, it is viable to deploy compact energy systems built around catalytic gasification for providing system power.
The steam reformed syngas consists of significant trace amounts of impurities. These impurities include water, carbon monoxide, carbon dioxide, and H2S. These impurities can be removed, and hydrogen, with a purity of >99%, can be produced using the pressure swing adsorption followed by the Pd-membrane separation. The hydrogen purification system weight can be reduced, and the energy efficiency can be improved through process intensification, i.e. by combining two-unit processes to one-unit process. We propose such process intensification for hydrogen purification using the compact Pd-membrane process. In this compact process, the traditional Pd-membrane is modified by having a layer of zeolite (aluminosilicate framework Al2O3/SiO2) with an activated carbon deposition on top of the Pd-membrane. The deposited carbon can adsorb water and the silica zeolite can adsorb H2S and CO. Research is necessary to create a compact Pd-membrane process for studying its performance in purifying hydrogen from the steam reformed syngas.
In this study, we assumed that the biomass moisture can be removed by supplying heat via hot syngas using a compact heat exchanger (refer ESI† for more information about modeling details). Compact heat exchangers for the heat transfer between gas–gas, gas–liquid, as well as liquid–liquid mediums have been used in real-life applications.21 Although implemented commercially, compact heat exchangers for heat transfer between solid biomass and hot gas need to be further developed for industrial applications. Additionally, further research is needed to identify materials with a high enough specific heat conductivity to withstand temperatures greater than 1000 °C for use as tube material.
The individual components of compact energy system types T3, T6, and T9 were demonstrated at various scales independently. However, the compact unit processes within each component as individual components have not yet been integrated to one holistic system to produce energy. Further work is necessary to build a prototype that integrates individual components and their respective unit processes. The development of the prototype should progress through several design iterations, implementing inexpensive materials. Like the compact energy systems with the gasification as the biomass converter technology, future work is necessary to determine the feasibility of developing compact energy systems listed in Tables 1 and 3. Additionally, the unit processes within the individual components of compact energy systems listed in Tables 1 and 3 must be studied to reduce the size and weight of the process equipment and improve the energy efficiency. For instance, the blue whirl combustion technology listed in Tables 1 and 3 is still at the technology readiness level of one and it is currently studied to understand the physical and chemical aspects responsible for the formation of blue whirl for the transition of this new combustion technology to a higher technology readiness level.22
Innovations for process intensification for syngas separation and purification processes can further reduce the size and increase the energy efficiency of systems built around gasification. The successful integration of the individual components of compact energy systems with biomass gasification as the upgrading pathway can increase the energy security, operation, and reduce the environmental impacts associated with the production of petroleum derived energy. Furthermore, successful integration can reduce capital risks and logistic challenges associated with the production of energy in a large scale biorefinery with a dry biomass processing capacity on the order of 100 to 103 metric tons per day. Like this study, system analysis of compact energy systems with fermentation and pyrolysis as biomass upgrading pathways must be performed to determine the viability of respective compact energy systems for power applications.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c9ra06039a |
This journal is © The Royal Society of Chemistry 2019 |