- freely available
Energies 2015, 8(12), 13846-13863; doi:10.3390/en81212399
Abstract: As a relatively mature technology, biomass molded fuel (BMF) is widely used in distributed and centralized heating in China and has received considerable government attention. Although many BFM incentive policies have been developed, decreased domestic traditional fuel prices in China have caused BMF to lose its economic viability and new policy recommendations are needed to stimulate this industry. The present study built a regionalized net present value (NPV) model based on real production process simulation to test the impacts of each policy factor. The calculations showed that BMF production costs vary remarkably between regions, with the cost of agricultural briquette fuel (ABF) ranging from 86 US dollar per metric ton (USD/t) to 110 (USD/t), while that of woody pellet fuel (WPF) varies from 122 USD/t to 154 USD/t. The largest part of BMF’s cost composition is feedstock, which accounts for up 50%–60% of the total; accordingly a feedstock subsidy is the most effective policy factor, but in consideration of policy implementation, it would be better to use a production subsidy. For ABF, the optimal product subsidy varies from 26 USD/t to 57 USD/t among different regions of China, while for WPF, the range is 36 USD/t to 75 USD/t. Based on the data, a regional BMF development strategy is also proposed in this study.
Since it is responsible for more than half of all global energy demand, the heating and cooling sector is a cornerstone of any energy or anti-climate change strategy . As 92% of all renewable heat is produced from biomass, bioenergy will play a key role in reducing the greenhouse gas footprint of this sector . Biomass molded fuel (BMF) is a type of solid fuel made from biomass materials such as agricultural or forestry residues, i.e., straws, cornstalks, peanut shells, wood branches, sawdust, shavings, etc.,  densified by molding machines. Densification of biomass has demonstrated numerous merits in improving the properties of biomass and possesses great potential for heating applications. One of the leading advantages of BMF is the highly increased specific weight. Typical unit densities of biomass pellets can be as high as 1000–1400 kg/m3, and bulk densities are about 700 kg/m3, while the density for grass type biomass ranges from 40 kg/m3 to 150 kg/m3, 150 kg/m3 to 200 kg/m3 for commercial wood chips, and 320–720 kg/m3 for most types of dried hard- and softwoods . This characteristic reduces logistical costs and gives BMF wider application. BMF offers many other advantages such as greater efficiency (less fuel required), lower emissions due to cleaner burning (less health and environmental impacts), easier operation, easier storage of fuel and eliminates the need for further drying of the fuel . An emission savings of 77% can be realized by co-firing torrified pellets with fossil coal .
The global BMF industry has experienced tremendous growth in recent years. In 2006, worldwide wood pellet production (excluding Asia, Latin America and Australia) was between 6 million metric tons and 7 million metric tons, while in 2010 production in the same countries had increased to 14.3 million metric tons . Europe ranks first worldwide in terms of wood pellet production and this advantage is expected to increase further; consumption of pellets in the EU steadily increased from 3.8 million tons in 2005 to 9.8 million tons in 2010 and is expected to reach 24 million tons by 2020, of which 11 million tons will be imported . Similarly, in China, BMF is given great importance as a promising alternative source of renewable energy. In its 12th-five-year plan , China set a target of utilizing 10 million tons of BMF every year; and in the “Medium and Long-Term Development Plan for Renewable Energy in China”, a target was set that by 2020, the annual use of BMF will reach 50 million tons . With the support of a series of incentive policies such as feedstock subsidies and tax credits, the annual BMF output in China has increased rapidly to 6.3 million tons in 2014, 20 times that in 2008.
The techno-economic characteristics of BMF have been studied in many papers. Case studies have been carried out to make economic, environmental and social assessments of BMF in different countries and regions [11,12,13,14,15,16]; biomass briquette fuel systems have been optimized using gain and loss method , grey relational analysis , or mixed integer linear programming . Policy analyses have also been carried out in this field: Doumax et al.  using a computable general equilibrium (CGE) model examined the efficiency of an alternative incentive scheme for biodiesel consumption and found that the 10% biodiesel mandate set by the European Parliament and Council 2009 Renewable Energy Directive (called RED) would not be achieved even if the fixed taxes on diesel reach the same level as those on gasoline; Bernard and Prieur  used a partial equilibrium model based on linear programming to evaluate the marginal revenues of liquid biofuels and calculate the minimum tax exemption; Zhang et al.  evaluated policies for current biomass power generation by calculating net present value (NPV) based on Monte-Carlo simulations. From the literature review we found that most policy analyses have focused on liquid biofuels and biomass power generation, whereas minimal study of BFM has taken place, moreover, most economic assessments of BMF in China have been based on one particular plant or conducted at the national level, with little research occurring at the regional level.
The study aims to address this gap, by evaluating the regional techno-economy for BMF in China and providing suitable policy recommendations for each region. The paper is organized as follows: the current situation is introduced first to provide relevant background; methodologies and data are then presented for understanding our results; regional BFM economic performance and suitable subsidies are calculated and analyzed; and finally, conclusions are drawn.
2. The Current Development Situation of Biomass Molded Fuel in China
In most developed countries, BMF is composed of wood produced from sawdust obtained at sawmills, using a machine with a die block in the shape of a ring . In China, the most commonly used BMF products are from agricultural and forestry residues, and mostly take the form of briquettes, pellets, and sometimes of rods. The technologies and products of BMF used in China are shown in Table 1 and Figure 1. Due to China’s current status as an agricultural country, compared to developed countries, the technologies in China are still immature and vulnerable to various disadvantages: low mechanization level in feedstock collection; friction in the die blocks and rollers; short service life of key components; high energy consumption in the molding process; imperfect matching system; and high content of alkali and chlorine in BMF products, resulting in the slagging and corrosion of biomass boilers.
|Products||Machines types||Diameter||Raw material||Applications|
|Pellet||Ring/flat die pellet mills||<10 mm||Agricultural/forestry residues||Small- and medium-scale distributed heating/exporting|
|Briquette||Ring/flat die briquette machine||10–25 mm||Agricultural/forestry residues||Small- and medium-scale distributed heating|
|Rod||Piston presses machine/screw extruder||>30 mm||Forestry residues||Large scale biomass boilers/exporting|
Although there is still a big gap between the BMF industry in China and that in developed countries, the industry has developed rapidly in China and shown marked progress in its technology R & D, machine manufacturing, formulation and implementation of standards, and service systems. By 2014, there were more than 1000 BMF production plants in China, with an annual output of 6.3 million tons, of which about two-thirds came from agriculture and the remainder from forestry. Figure 2 shows the annual BMF output from 2008 to 2014.
The BMF industry in China has a strong regional character. As a result of China’s agricultural structure, most provinces in central, northern and eastern China, like Henan, Hebei, Shandong, and Anhui, have abundant agricultural residues, so agricultural briquettes fuel (ABF) dominates the BMF market in these areas. However, because of the relatively low economic level, environmental issues are not the primary concern in these areas, and there are no bans on coal in most of these jurisdictions. Since coal is the main fossil fuel being replaced by BMF, the market price of BMF is relatively low in these areas. Meanwhile, in northeastern provinces like Jilin, forestry residues are abundant and cheap; BMF in these regions consists mainly of woody pellet fuels (WPF). Figure 3 gives the regional BMF productions and consumptions.
BMF has attracted worldwide attention as a promising alternative fuel, and many countries have formulated policies to stimulate the development of this industry. In China, the main incentive measures have included the following:
As noted above, in its 12th-five-year plan, China set a target of utilizing ten million BFM every year; and in the “Medium and Long-Term Development Plan for Renewable Energy in China”, an annual BMF use target of 50 million tons was set for 2020.
The “Interim Measures for the Application of Agricultural Briquette as Energy Subsidy” specify that for enterprises with registered capital of more than ten million CNY, with an annual consumption of agricultural straw of more than 10,000 tons (including 10,000 tons), a subsidy of 140 CNY/t (22.58 USD/t) for each ton of agricultural straw would be granted .
The “Interim Management Measures on Renewable Energy Development Special Fund” stipulated that for the projects listed in the directory of the national renewable energy industry development guidance, a subsidized loan would be provided. The subsidized loan period is 1–3 years, with a maximum annual interest rate of 3% (the average loan rate in China during 2014 was 6.55%) .
Value-added tax (VAT) return or refund
The taxpayers who produce items comprehensive products using “the three kinds of residue (forestry logging residue, rough-hew residues and wood industry processing residues) , and the secondary or small fuelwood, agricultural straw, sugar cane bagasse as feedstock” could enjoy an 80% VAT return .
Income tax reduction
Chinese income tax law provides that for enterprises who follow to “Preferential Catalogue of Enterprise. Income Tax on Resource Comprehensive Utilization” (2008 Edition), income tax could be levied based on 90% of its total income .
Equipment subsidies .
In this study we built a regionalized NPV model based on real production process simulation. The model’s framework is as follows: first build a universal production system module, initiating it with equipment parameters; then build a regionalized plant module, which are embedded with the production system module; after inputting the regional operating data and price reference, use NPV method to calculate the price when NPV is zero; use sensitivity analysis to search for the most effective policy; after that, make the regional BMF selling price equal to that of coal and through linear programming method to calculate to what degree the incentive compensation should be in each region. Figure 4 gives the flowchart of the regionalized NPV model.
In order to get the first hand information about BMF in China, we have investigated 117 BMF production companies (78 ABF, 39 WPF) in 31 provinces in China, about their feedstocks, the parameters of their production plants, and how the current incentive policies worked by the means of questionnaires and interviews. In most economic analyses regarding biomass energy in China, a uniform set of data is always used. However, in our nationwide investigation, we have found a major regional imbalance: Although the plant scales, production process and process parameter differences like machine type and power consumption vary little between regions, the operating parameters, such as feedstock price, human labor cost, electricity price, etc. vary greatly, and these operating parameters have resulted in great differences in BMF price. In this study we divided the whole of China into seven regions, i.e., Central, North, South, East, Northeast, Northwest and Southwest, according to the comparability of their geographic and climatic, economic and societal features, as well as the similarity of their biomass resources, market and end-users. Table 2 gives the details of each region and their resource, technological, market characteristics.
3.2. Net Present Value Production Model
An NPV method was employed to study the relationship between production costs and incentive policies such as tax breaks, subsidies and loans, etc., so as to identify the best policy portfolio to promote this industry.
|Central China||Henan; Hubei; Hunan||Rich straw resources, few forestry residues, briquettes/pellets are straw-oriented; Land rent and labor cost are low; low coal price.|
|East China||Shanghai; Anhui; Fujian; Jiangsu; Jiangxi; Shandong; Zhejiang||Rich in agricultural straw and forestry residues; land rent and labor cost are high; high coal price; environmental issues are highly concerned, so BMF can be economically competitive.|
|South China||Guangdong; Hainan; Guangxi; Hong Kong; Macau||Rich in wooden residues, limited in straw; typical scale 20,000 t/a or more; land rent and labor cost are high; coal is in short supply and the price is high, and environmental issues are highly concerned, so BMF can be highly competitive.|
|Southwest China||Chongqing; Guizhou; Sichuan; Yunnan; Tibet||Sufficient raw material and broad sources; land rent and labor cost are low; low coal price.|
|North China||Beijing; Tianjin; Hebei; Shanxi; Inner Mongolia||Sufficient of both straw and wooden material, relatively low price; land rent and labor cost are medium; The price of traditional energy like coal and electricity are low.|
|Northeast China||Heilongjiang; Jilin; Liaoning||Sufficient straw material, relatively low price and broad sources; land rent and labor cost are low; low coal price.|
|Northwest China||Gansu; Qinghai; Shaanxi; Ningxia; Xinjiang||Sparsely populated, rich in straws, while the transportation cost is high; land rent and labor cost are low; low coal price.|
The cost of operation and management is calculated as follows:
The formula for calculating variable operation and management costs is as follows:
3.2.2. Cash Flow
The annual net cash flow is calculated as follows:
3.2.3. Net Present Value and Internal Rate of Return
3.3. Sensitivity Analysis Method
The method used here is single factor sensitivity analysis, which sets variation range for one given policy factor and keeps other factors unchanged:
4. Assumptions, Data and Calculation
4.1. General Assumptions
All prices involved are reported real value and normalized to US dollar in 2015, offsetting inflation. Expected Life span of the production plant is 20 years. For economy of scale the per unit cost of larger BMF plants are usually less than that of smaller ones; this is called the “economy of scale” and the corresponding basic equation is as follows:
4.2. Plant Scale
In the nationwide field investigation, we found that the most popular scales of BMF plants are 10,000–30,000 metric tons per annum (t/a), as 67 out of 117 investigated plants are of this scale, representing a 57% share. Only 33 plants have a production scale beyond 30,000 t/a, and 17 plants are below 10,000 t/a. The average BMF plant scale in the east region is the largest, at about 50,000 t/a, followed by the northeast region, at about 30,000 t/a, the remaining regions have similar average scales, at about 20,000 t/a. The model calculation will be based on regional average scales. Figure 5 and Table 3 lists the details.
|Region||Plant numbers||Average scale|
|<10,000 t/a||10,000–30,000 t/a||>30,000 t/a||Total|
4.3. Feedstock Price
The feedstock prices used in this model are also based on our investigation. They include four parts: in-field cost, collection cost, transport cost and storage cost. The regional feedstock prices are shown in Figure 6.
4.4. Production System Parameters
The BMF production system is composed of four sectors: Drying, chopping, molding, and cooling & screening. The schematic diagram for the system is shown in Figure 7.
Here we take a BMF production plant with the scale of 20,000 t/a as an example. Details of the production system of that scale are listed in Table 4. Such a production system has a moulding rate of about 95%, and it can produce both straw briquette fuel and WPF. For plants with other scales, their system investments and power consumption could be calculated by the economy of scale function in Section 4.1.
|Number||Name||Sets||Power consumption (kW)||Equipment price (USD)|
|I. Drying sector||1||Belt conveyor||3||1.5||4.50||1||4838.71|
|3||Large angle belt conveyer||2||4.00||8.00||2.65||8548.39|
|9||Back material conveyor||3||2.2||6.60||2.21||10,693.55|
|II. Chopping sector||1||Grinder||3||45.00||135.00||10.5||50,806.45|
|5||Bag dust collector||2||3||6.00||3||9677.42|
|III. Moulding sector||1||Scraper conveyer||2||2.2||4.40||2.3||7419.35|
|7||V-type belt conveyor||2||2.2||4.40||1.5||4838.71|
|IV. Cooling sector||1||Large angle belt conveyor||2||4||8.00||3.45||11,129.03|
|4||Centrifugal dust collector||1||0||0||2.95||4758.06|
|8||Drying buffer bin||2||0||0.00||2.2||7096.77|
Data source: field investigation.
4.5. Plant Operating Parameters
The plant module is built based on their regional average scales. Below we take an actual BMF factory with a capacity of 20,000 t/a as an example and the corresponding main parameters are listed in Table 5. The regional parameters such as maintenance and overheads costs could be calculated with the economy of scale function described in Section 4.1.
|1||Construction period||1 year|
|2||Production system costs (fixed cost)||620,967 USD|
|3||Maintenance costs (fixed cost)||5,435.48 USD/a|
|4||Overheads costs (fixed cost)||161,290 USD/a|
|5||Workers needed (variable cost)||30|
|6||Period of depreciation||20 years|
|9||Income tax rate||25% |
|10||Value-added tax (VAT) rate 1||17% |
|11||VAT rate 2||13% |
|12||Base internal rate of return||10%|
|13||Discount rate||13% |
|15||Loan terms||10-year loan at 6.9%|
4.6. Regional Data
Table 6 gives the regional data used in the model. Land & construction costs are calculated based on the regional land rent, the prices for labor and energy are derived from the average value among the provinces in each region, and the source of original data is from National Bureau of Statistics of China  and websites listing coal prices [32,33,34].
|Region||Land & construction||Labor price||Electricity||Fuel coal (5000 kcal, tax included)|
5. Results and Discussion
5.1. Calculated Production Cost
Table 7 shows the calculated BMF production costs in each region. In order to validate these results, we compared that data to the local selling prices of the 117 BMF companies that we investigated. Figure 8 demonstrates that the actual average prices of each region show a high degree of consistency with the simulation results.
Due to its lower energy density, the average cost of ABF is 40 USD/t less than that of WPF. In order to compare different BMFs equitably, we also calculated the regional unit energy cost of ABF and WPF based on one ton standard coal equivalent. Figure 9 gives the results. In most regions, the energy costs of ABF and WPF are almost equal, but in central China, the energy cost of ABF is lower than that of WPF, whereas in northwest China, WPF’s energy cost is lower. For ABF, south China has the highest prices, followed by east, northeast, northwest and southwest China, north and central China have the lowest prices. For WPF, south China again has the highest prices, followed by east, central, northeast, southwest, northwest China, north China has the lowest WPF price.
The reason for this price disparity for BMF in China is the unbalanced regional development. In most regions, BMF is replacing coal for both distributed and centralized heating. However, in developed regions like the south and east, due to a high degree of urbanization, less local feedstock is locally available; in addition, the local governments attach high importance to environmental protection, strictly implementing measures like coal ban regulations. Accordingly, BMF is shipped to these regions to replace natural gas at a higher price. However, natural gas presents only a small part of China’s energy consumption and it will be too expensive to provide natural gas heating all over China. From the prospective of mainstream of heating patterns, coal will continue to be the most commonly used fossil fuel in the long run and thus the main competitive target that BMF will seek to replace in most regions in China. From Figure 9 we can observe that in all regions BMF’s energy cost is higher than that of coal, especially in the current context of decreasing coal prices, so some incentives should be adopted to protect the BMF industry and maintain BMF’s commercial competitiveness.
5.2. Energy Consumption
Figure 10 depicts the relationship between the calculated energy consumption to produce a ton of BMF and the actual values that we obtained from the nationwide investigation. The result shows a high degree of consistency, and that means our assumption of the proportionality factor in economy of scale function is valid. From Figure 10 we also observe that along with the increase of BMF production plant scales, the unit energy consumption represents a decreasing tendency and comes close to some value between 50 kWh/t and 80 kWh/t.
The regional energy consumption for BMF production in each region is shown in Table 8. It is concluded that plants in the east region have the lowest energy consumption to produce a ton of BMF, at about 130 kWh/t, followed by the plants in the northeast region, at about 180kWh/t, while plants in the remaining regions are roughly the same, at about 250 kWh/t. This is because that the energy consumption is mainly related to the plant scales, and east China has more large plants, its integration degree is higher than other regions, and therefore the energy consumption is less.
|Popular plant scale (t/a)||50,000||20,000||20,000||20,000||20,000||30,000||20,000|
|Power consumption (kWh/t)||130.24||247.35||247.35||247.35||247.35||186.23||247.35|
5.3. Cost Structure
According to our simulation results, the regional cost structures show a high degree of similarity. Here we will take BMF in central China as an example, and its cost structure is shown in Figure 11. For ABF, feedstock represents the largest share of the total cost, around 51%, with O & M costs come second at 26%, followed by investment costs at 12%, tax costs at about 7%, and loan interest costs at 4%. The cost structure for WPF is similar to that for ABF, with a slightly higher feedstock share, about 58%, resulting from the higher energy density and higher price of woody feedstocks. O & M costs represent a comparable share as in the ABF case at 24%, the investment costs, tax costs and loan interest costs for WPF are 11%, 5% and 2%, respectively.
Unlike other renewable energies such as PV and wind energy, the initial investment of BMF is not the greatest part of its production cost, it means that it is easier for SMEs to access to this industry because the capital threshold is relatively low.
5.4. Sensitivity Analysis
In order to identify the most effective policy factors, we carried out a sensitivity analysis based on current incentive policies. The results show that sensitivity for AMF and WPF are similar. Taking ABF in the east region as an example, the results are shown in Figure 12. We can see that feedstock subsidies have by far the greatest positive impact on lowering BMF production costs, followed by equipment subsidies. Loan rate, VAT rate and income tax rate changes have a negative impact on lowering BMF production costs. The dramatic impact of feedstock subsidies results from the cost structures. The feedstock subsidies aim at reducing the feedstock costs, while the VAT and income tax credit and the equipment subsidies aim at reducing the tax and investment costs, respectively. However, in ABF cost structure, the sum of the shares of investment, tax and loan interest is 23%, less than the half of the feedstock share, so feedstock subsidies should be considered as the first choice to stimulate this industry.
5.5. Subsidy and Development Strategy for Each Region
As shown in the aforementioned analysis, feedstock subsidies are the most effective policy, but in different regions, the price of BMF and the price of the target energy to be replaced vary, so the current uniform subsidy standard would not be suitable for all regions. Therefore we calculated how much the local government should subsidize BMF in each region in order to sustain its economic viability. Figure 13 gives the results. For ABF, the subsidy in south is the lowest, at about 20 USD/t, followed by 28 USD/t in southwest China, 30 USD/t in central China, 33 USD/t in east China and 37 USD/t in north China; as it can be seen, the required subsidies in the northeast and northwest are the highest, at around 38 USD/t and 44 USD/t, respectively.
For WPF, the subsidy in south is again the lowest, at about 27 USD/t, followed by 40 USD/t in southwest China, 44 USD/t in east China, 49 USD/t in northwest China, 53 USD/t in northeast China, 55 USD/t in north China and 57 USD/t in central China.
These results are caused by both the local fossil energy prices and BMF production costs. The reason why south China has the highest production costs but needs the least subsidies is that this region is short of coal and its coal prices are relatively high due to the expensive transportation expenses (its coal price is two times of that in north China). Another factor is the local feedstock conditions, as some regions, like north and central China, are rich in agricultural feedstock due to the fact they are covered by massive arable plains and have few mountains where trees grow, so their agricultural feedstock is much cheap than woody ones, even when the energy density is factored into the calculations. Therefore in these regions ABF are recommended to be extensively promoted, but WPF are suggested as subordinate products.
However, actual policy implementation is difficult and complex, because it is easy for recipients of the feedstock subsidy to cheat and hard to incentivize BMF consumption. According to our investigation, in order to maximize their subsidy, some plant owners cheat with regard to the total amount of feedstock they purchase, and did not produce as much as BMF they claimed for the subsidy. Therefore, it is better to change the feedstock subsidy to a product-based subsidy, credited only for the BMF actually produced and utilized by consumers. The regional product subsidies are shown in Figure 14: For ABF, the product subsidies are 26 USD/t, 36 USD/t, 39 USD/t, 42 USD/t, 48 USD/t, 49 USD/t and 57 USD/t in the south, southwest, central, east, north, northeast and northwest regions, respectively; for WPF, the product subsidies are 36 USD/t, 52 USD/t, 58 USD/t, 65 USD/t, 69 USD/t, 72 USD/t and 75 UDS/t in south, southwest, east, northwest, northeast, north and central China, respectively.
Also from the subsidy results we can sketch a desired development strategy for BMF in each region. A high subsidy requirement means that it is not economical to develop BMF in that region, Table 9 indicates which regions should develop each type of BMF and at what level: ABF should be developed with priority in the south region, then in the southwest, central, east, north region, and is not recommended in the northeast, northwest; WPF should be developed first in the south, southwest region, then in the east, northwest and northeast region, and is not recommended in the north and central regions.
|BMF||Priority development||Modest development||Not recommended|
|ABF||South||Southwest, Central, East, North||Northeast, Northwest|
|WPF||South, Southwest||East, Northwest, Northeast||North, Central|
At present, there are mainly two kinds of BMF in China: agricultural briquette fuel (ABF) and WPF, and their production costs vary remarkably across China’s regions. The cost of ABF varies from 86 USD/t to 110 USD/t between the regions, while WPF’s production cost ranges from 122 USD/t to 154 USD/t. The largest part of BMF’s cost composition is feedstock, which represents between 50% and 60% of the total cost.
For the foreseeable future, coal will be the main target fossil fuel the BMF will seek to replace, but the energy costs for both ABF and WPF are significantly higher than those of coal in each region. Incentive policies should be adopted to protect this industry and maintain BMF’s commercial viability.
Feedstock subsidies are the most effective policy option, but the current uniform subsidy standard is not appropriate for each region. Due to feasibility considerations related to policy implementation, it would be better to replace the current feedstock-based subsidy with a product-based subsidy. The optimal subsidies are calculated for each region: for ABF, the product subsidies vary from 26 USD/t to 57 USD/t between regions, while for WPF, the range is from 36 USD/t to 75 USD/t.
Based on the calculation of production costs, coal prices and optimal subsidy amounts, a regional BMF development strategy is also proposed. ABF should be targeted for priority development in south China, then in the southwest, central, east, north regions, and is not recommended in the northeast or northwest regions; priority WPF development should occur in the south and southwest regions, and then in the east, northwest and northeast regions, and is not recommended in the north or central regions. Moreover, in China’s most developed and wealthiest regions, it is recommended to use BMF to replace natural gas first.
The study is supported by the Renewable Energy Efficiency and Energy Partnership (REEEP Project ID: 108030134) the United Nations Development Programme (UNDP: 00068721-CPR/13/304), the National Natural Science Foundation of China (No.71203119) and the Guangdong Industry-Academia-Research Project (No. 2012B090400025).
Jie Xu performed the techno-economic analysis, built the Bioethanol Plant-Gate Price Assessment Model (BPAM) adapted to China, and collected most of the data for the analysis; Shiyan Chang help to build the NPV module; Zhenhong Yuan and Longlong Ma guide development of study methodology of the study and the writing of this paper; Yang Jiang and Weizhen Li provided key technical parameters of the technology analyzed in the paper; Shuna Liu helped about the industry investigation. All authors contributed to the editing and reviewing of the document.
Conflicts of Interest
The authors declare no conflict of interest.
- Cullen, J.M.; Allwood, J.M. The efficient use of energy: Tracing the global flow of energy from fuel to service. Energy Policy 2010, 38, 75–81. [Google Scholar] [CrossRef]
- Alakangas, E.; Asikainen, A.; Grammelis, P.; Hämäläinen, J.; Haslinger, W.; Janssen, R.; Kallner, P.; Lehto, J.; Mutka, K.; Rutz, D.; et al. Biomass Technology Roadmap; Renewable Heating and Cooling (RHC-Platform): Brussels, Belgium, 2014. [Google Scholar]
- Chen, W.H.; Peng, J.; Bi, X.T. A state-of-the-art review of biomass torrefaction, densification and applications. Renew. Sustain. Energy Rev. 2015, 44, 847–866. [Google Scholar] [CrossRef]
- Stelte, W.; Holm, J.K.; Sanadi, A.R.; Barsberg, S.; Ahrenfeldt, J.; Henriksen, U.B. Fuel pellets from biomass: The importance of the pelletizing pressure and its dependency on the processing conditions. Fuel 2011, 90, 3285–3290. [Google Scholar] [CrossRef]
- Pa, A.; Bi, X.T.; Sokhansanj, S. Evaluation of wood pellet application for residential heating inbritish columbia based on a streamlined life cycle analysis. Biomass Bioenergy 2013, 49, 109–122. [Google Scholar] [CrossRef]
- Agar, D.; Gil, J.; Sanchez, D.; Echeverria, I.; Wihersaari, M. Torrefied versus conventional pellet production—A comparative study on energy and emission balance based on pilot-plant data and EU sustainability criteria. Appl. Energy 2015, 138, 621–630. [Google Scholar] [CrossRef]
- Castellano, J.M.; Gómez, M.; Fernández, M.; Esteban, L.S.; Carrasco, J.E. Study on the effects of raw materials composition and pelletization conditions on the quality and properties of pellets obtained from different woody and non woody biomasses. Fuel 2015, 139, 629–636. [Google Scholar] [CrossRef]
- PellCert, Intelligent Energy Europe. Industrial Wood Pellets Report. 2012. Available online: http://ec.europa.eu/energy/intelligent/projects/sites/iee-projects/files/projects/documents/pellcert_report_on_pellets_for_power_use.pdf (accessed on 31 August 2015). [Google Scholar]
- Notice on the Issue of National 12th Five-Year Plan for Renewable Energy. Available online: http://www.sxdrc.gov.cn/xxlm/xny/zhdt/201212/t20121213_67157.htm (accessed on 31 August 2015).
- Medium and Long-Term Development Plan for Renewable Energy in China. Available online: http://www.martinot.info/China_RE_Plan_to_2020_Sep-2007.pdf (accessed on 31 August 2015).
- Feng, C.; Yu, X.; Tan, H.; Liu, T.; Hu, T.; Zhang, Z.; Qiu, S.; Chen, L. The economic feasibility of a crop-residue densification plant: A case study for the city of jinzhou in china. Renew. Sustain. Energy Rev. 2013, 24, 172–180. [Google Scholar] [CrossRef]
- Karkania, V.; Fanara, E.; Zabaniotou, A. Review of sustainable biomass pellets production—A study for agricultural residues pellets’ market in greece. Renew. Sustain. Energy Rev. 2012, 16, 1426–1436. [Google Scholar] [CrossRef]
- Hu, J.; Lei, T.; Wang, Z.; Yan, X.; Shi, X.; Li, Z.; He, X.; Zhang, Q. Economic, environmental and social assessment of briquette fuel from agricultural residues in china—A study on flat die briquetting using corn stalk. Energy 2014, 64, 557–566. [Google Scholar] [CrossRef]
- Mansuy, N.; Thiffault, E.; Lemieux, S.; Manka, F.; Paré, D.; Lebel, L. Sustainable biomass supply chains from salvage logging of fire-killed stands: A case study for wood pellet production in eastern Canada. Appl. Energy 2015, 154, 62–73. [Google Scholar] [CrossRef]
- Pirraglia, A.; Gonzalez, R.; Saloni, D.; Denig, J. Technical and economic assessment for the production of torrefied ligno-cellulosic biomass pellets in the US. Energy Convers. Manag. 2013, 66, 153–164. [Google Scholar] [CrossRef]
- Stolarski, M.J.; Szczukowski, S.; Tworkowski, J.; Krzyżaniak, M.; Gulczyński, P.; Mleczek, M. Comparison of quality and production cost of briquettes made from agricultural and forest origin biomass. Renew. Energy 2013, 57, 20–26. [Google Scholar] [CrossRef]
- Lee, S.M.; Lee, J.W. Optimization of biomass torrefaction conditions by the gain and loss method and regression model analysis. Bioresour. Technol. 2014, 172, 438–443. [Google Scholar] [CrossRef] [PubMed]
- Wang, Z.; Lei, T.; Chang, X.; Shi, X.; Xiao, J.; Li, Z.; He, X.; Zhu, J.; Yang, S. Optimization of a biomass briquette fuel system based on grey relational analysis and analytic hierarchy process: A study using cornstalks in China. Appl. Energy 2015, 157, 523–532. [Google Scholar] [CrossRef]
- Pantaleo, A.M.; Giarola, S.; Bauen, A.; Shah, N. Integration of biomass into urban energy systems for heat and power. Part I: An milp based spatial optimization methodology. Energy Convers. Manag. 2014, 83, 347–361. [Google Scholar] [CrossRef]
- Doumax, V.; Philip, J.M.; Sarasa, C. Biofuels, tax policies and oil prices in France: Insights from a dynamic CGE model. Energy Policy 2014, 66, 603–614. [Google Scholar] [CrossRef]
- Bernard, F.; Prieur, A. Biofuel market and carbon modeling to analyse french biofuel policy. Energy Policy 2007, 35, 5991–6002. [Google Scholar] [CrossRef]
- Shi-long, Z.M.L. Economic benefitanalysis and policy choice of biomass power generation project. J. Hangzhou Dianzi Univ. 2013, 9, 36–41. [Google Scholar]
- Richard Sikkema, M.S.; Martin, J.; Wolfgang, H. Las Report on Producers, Traders and Consumers of Wood Pellets; HFA Holzforschung Austria: Vienna, Austria, 2009. [Google Scholar]
- Interim Measures for the Application of Agricultural Briquette as Energy Subsidy. Available online: http://www.mof.gov.cn/zhengwuxinxi/caizhengwengao/caizhengbuwengao2008/wengao200811qi/200903/t20090304_118500.html (accessed on 31 August 2015).
- Renewable Energy Law of the People’s Republic of China. Available online: http://www.gov.cn/fwxx/bw/gjdljgwyh/content_2263069.htm (accessed on 31 August 2015).
- Notice on Adjusting and Perfecting the Policy of Comprehensive Utilization of Resources and Value Added Tax; Ministry of Finance: Beijing, China, 2011.
- Guidance Suggestion on Agricultural Equipment Purchase Subsidies. Available online: http://www.moa.gov.cn/govpublic/CWS/201501/t20150129_4356487.htm (accessed on 31 August 2015).
- Qiang, Y.R.F. Tax System of China, 1st ed.; Tsinghua University Press: Beijing, China, 2011. [Google Scholar]
- Detailed Rule for the Implementation of the Provisional Regulation of the People’s Republic of China on Value-Added Tax; Ministry of Finance: Beijing, China, 1993.
- Li, X. Parameter & Data 2011 Sinopec Project Feasibility Study Technical Economy; SINOPEC Economic Research Institute: Beijing, China, 2011; pp. 1–97. [Google Scholar]
- Electricity Price. Available online: http://www.stats.gov.cn/english/ (accessed on 31 August 2015).
- China Coal Resource. Available online: http://en.sxcoal.com/ (accessed on 31 August 2015).
- Coal Prices. Available online: http://www.coal.com.cn/Market/dongbei.aspx (accessed on 31 August 2015).
- Coal Price in Provinces. Available online: http://www.chinaccm.com/ (accessed on 31 August 2015).
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