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14 July 2022

Multi-Product Productions from Malaysian Oil Palm Empty Fruit Bunch (EFB): Selection for Optimal Process and Transportation Mode

,
,
and
1
Faculty of Chemical and Process Engineering Technology, Universiti Malaysia Pahang, Gambang, Pahang 26300, Malaysia
2
Centre for Sustainability of Ecosystem & Earth Resources, Universiti Malaysia Pahang, Gambang, Pahang 26300, Malaysia
3
Faculty of Civil Engineering Technology, Universiti Malaysia Pahang, Gambang, Pahang 26300, Malaysia
4
Department of Industrial Engineering and Management Systems, University of Central Florida, Orlando, FL 32816, USA

Abstract

In Malaysia, palm oil industries have played significant roles in the economic sectors and the nation’s developments. One aspect of these industries that is gaining growing interest is oil palm residue management and bio-based product generations. EFB has been identified to be a feasible raw material for the production of bio-energy, bio-chemicals, and bio-materials. In this paper, our previous deterministic mathematical programming model was extended to include decisions for selecting optimal transportation modes and processes at each level of the processing stage in the supply chain. The superstructure of alternatives was extended to show states of produced products whether solid, liquid, or gaseous, and for which truck, train, barge, or pipeline would be possible modes of transportation. The objective function was to maximize profit which accounts for associated costs including the emission treatment costs from production and transportation. The optimal profit was USD 1,561,106,613 per year for single ownership of all facilities in the supply chain.

1. Introduction

Palm oil industries have played significant roles in the socio-economic developments in Malaysia. Since 1960, Malaysia has been one of the major producers and exporters of palm oil [1]. Statistics have shown that the palm oil sector has contributed 12% of total Malaysia’s export, and this percentage was equivalent to RM 80.4 billion [2] or about USD 18.26 billion in current currency conversion. In terms of social and rural improvements, the establishment of the Federal Land Development Authority (FELDA) in 1956 has carried out landless resettlements mainly for palm oil plantations in the country that benefited almost 113,000 low-income families [3]. This effort has not only alleviated poverty in the country but also reduced economic imbalances between urban and rural populations [4].
As palm oil is one of the most important sources of vegetable oils, the demand for it is increasing with the proliferative growth of the human population globally. Interestingly, significant uses of palm oils for cooking and manufacturing oleo-chemicals have been annexed with the production of biodiesel recently. In this context, Malaysia’s Ministry of Plantation Industries and Commodities intends to mandate 20% blending of palm-based biodiesel with petro-based diesel instead of 5% blending before November 2014. This move has further increased the economic gains of palm oil, especially in situations where petroleum prices are unduly high.
Palm oil plantations also produce agricultural biomass such as EFB. Although it was once considered a low-value residue, technological advances started to convert this biomass into numerous types of bio-based products. The scenario has created considerable amounts of enterprising companies to venture into these waste-to-wealth businesses throughout the country. However, to plan and operate any EFB utilization project successfully, the supply chain that includes optimal decisions for process and transportation is one of the key considerations. With numerous alternatives available, selecting the best processing route for producing a product is an important decision to make because of several associated factors such as the product’s competitiveness, the viability and status of technology, the social and environmental impacts, and so on. In this regard, Figure 1 depicts technological and resource-to-product selection dilemmas that typically occur in any biomass supply chain. Furthermore, the figure also has options to sell the produced products directly or to further refine them as shown by the dash lines.
Figure 1. Selection dilemmas in the biomass supply chain.
The optimal decisions concerning transportation amounts and modes are meanwhile influencing the overall economic profitability as well as biomass accessibility and mobility. Questions may about arise whether to use a truck, train, barge or pipeline for transporting biomass and derived products from processing facilities to the desired destinations in the most economical way. Based on these reasons, the development of an optimization model with the decision is imperative and would be a focus of this study. The classification for this type of modeling is Mixed Integer Programming (MIP), which could be linear or non-linear.
Previous studies about MIP modeling of the biomass supply chain have been published by several authors. Recently, [5] had reviewed the optimization biomass supply chain optimization model streamed to the formulation gaps. These include modeling off biomass sources for energy purposes through combustion [6]; a hybrid of gasification and fermentation processes of agricultural residues and dedicated crops for bio-ethanol production [7]; bio-ethanol production from agricultural residues and municipal solid wastes by considering policy standards and conversion technologies [8]; agricultural residues for bioethanol production via a bio-chemical route only by considering enzymatic hydrolysis and acidic hydrolysis [9]; multi-objective optimization for gasoline and bio-diesel productions by using combinations of forestry residues, agricultural residues, and dedicated crops [10]; and oil seed crop for the productions of energy products such as biodiesel, heat, power, and syngas [11]. In recent studies, [12] have modeled the biofuel supply chain from corn stover by using a fast pyrolysis process. They have considered different biomass supplies and demands with biofuel supply shortage penalty and storage costs in the model. [13] have optimized a biofuel supply chain model that integrates strategic and tactical planning decisions. Key strategic decisions were numbers, locations, capacities, and distribution patterns for biomass and ethanol, while biomass production and delivery were among the tactical decisions. [14] have developed an optimization model of the supply chain for bioelectricity production from forest residues in Portugal. The objective function has minimized the total supply chain cost and optimally selected biomass amounts and sources. For recent studies, [15] developed a model that provides and considers options in a biomass-to-bioproducts supply chain to produce multiple products. [16] had integrated a multi-objective optimization model with a fuzzy-Analytic Hierarchy process in their palm oil mill biomass supply chain model, while [17] had extended the palm oil mill biomass cogeneration supply chain into operation and maintenance consideration in their optimization model. Some of the authors have expanded into stochastic modeling [18].
The above-mentioned studies have modeled the biomass supply chain problem as Mixed Integer Linear Programming (MILP) models, while the present paper considers nonlinearities in the problem which will lead to a Mixed Integer Non-linear Programming (MINLP) model. Thus, this research implication was revealed through the attainment of a method to linearize certain nonlinear models. According to [19] the optimization modeler keeps exploring the linearization method of the complex optimization problem to reduce the modeling time. A new method for linearization of certain nonlinear constraints in the linear optimization model was developed by [20]. The model in this study is an extension of our previous model [21] to make it more comprehensive and extensive. In this model, the objective was to maximize the profit of EFB’s supply chain for multi-product productions which would provide optimal decisions regarding biomass amounts, process and production levels, the product’s direct sales or further refinements, transportation modes at each processing stage, as well as environmental considerations from both productions and transportations. The rationale behind conducting this extended optimization model is directed towards the prosperous biomass industry. This study is pursued to develop a comprehensive decision-making tool for future investments in palm oil biomass projects that require decisive selection of those mentioned considerations. One of the optimization model implications is to motivate industrial player to invest in a biomass project such as a palm oil mill-based cogeneration system. It also acts as a tool for energy policy makers to support biomass utilization in some countries that have abundant resources of biomass such as Malaysia and Indonesia.

2. Materials and Methods

To model and optimize the EFB’s supply chain, a methodology that is shown in Figure 2 was followed. This study has extended the previous optimization model from [21] to include integer variables for important decisions related to selections of best processes and transportation modes. Each decision was effective for each processing stage (pre-processing, main processing, further processing 1, and further processing 2) in the supply chain.
Figure 2. Methodology for EFB’s supply chain with optimal processing route and transportation mode.
Figure 3 shows the modified superstructure of EFB’s supply chain. Each segment of transportation was assigned with relevant modes of transportation. Solid biomass and product transportations to the next processing stages would utilize either truck, train, or barge, while transportation of liquid or gaseous products would use the pipeline automatically. Square shapes in the superstructure represent processing facilities while storages are represented by the oval shapes. The black solid arrows show processing sequences while the black dash lines give indications to sell the products from storage directly to the customers. The curve arrows represent option for selling of the products at i, k and m. The extraction process was divided into three (extraction 1–3), acid hydrolysis into two (acid hydrolysis 1 and 2), enzymatic process into two (enzymatic hydrolysis 1 and 2), bio-oil upgrading into two (bio-oil upgrading 1 and 2), and lastly FTL production into two (FTL production 1 and 2).
Figure 3. Superstructure of EFB’s supply chain for selecting optimal processing routes and transportation modes.
These divisions are shown with a square shape in Figure 3 with more than one product except for power production with the products (electricity, MP steam, and LP steam) produced from a single unit process. The reason behind these divisions was to ensure the model could decide on the optimal processing routes and their transportation modes, as well as to ensure the explanations could be established clearly. Similar to the previous superstructure, the extended superstructure shows competitive utilizations and routes for EFB, cellulose, hemicellulose, pellet, torrefied pellet, glucose, xylose, bio-syngas, and bio-oil. In addition, it assumed homogenous blending of EFBs from different collection points.
Overall, there were four stages of processing (h, j, l, and n) and four segments of transportations (g to h, h to j, j to l, and l to n). Table 1 contains lists of the indices such as g, h, j, l, and p, which will be used in the model’s formulations and lists of further aspects for each of the indices.
Table 1. List of indices and descriptions for the model’s formulations.

3. Mathematical Model for the Optimal Selections

Formulations of the mathematical model to optimize the EFB’s supply chain were written by the following equations, which are each explained in Table 2 and Table 3.
Maximize Profit = Maximize (Sales of products − Biomass cost − Transportation operating cost −
Production cost − Emission treatment cost)
S a l e s   o f   p r o d u c t s = p = 1 P Q p P r o d u c t s   s e l l i n g   p r i c e
B i o m a s s   c o s t = g G F g E F B   C o s t
Transportation operating cost = Truck, train, and barge transportation operating cost +
pipeline transportation operating cost
T r u c k ,   t r a i n ,   a n d   b a r g e   t r a n s p o r t a t i o n   o p e r a t i n g   c o s t = t T ( ( O P C O S T M t g G h H F T F T g , h , t 2 D G H g , h ) + ( O P C O S T M t h H j J F T H T h , j , t 2 D H I J h , j ) + ( O P C O S T M t j J s 2 S 2 F T J T S j , s 2 , t 2 D J K L S j , s 2 )
P i p e l i n e   t r a n s p o r t a t i o n   o p e r a t i n g   c o s t = z Z ( ( O P C O S T P z j J l g 2 L G 2 F T J T _ L G j , l g 2 , z D J K L _ L G j , l g 2 ) + ( O P C O S T P z l g 2 L G 2 n N F T L T l g 2 , n , z D L M N l g 2 , n )
Table 2. Description of formulations (1) to (58).
Table 3. Descriptions of terms used in formulations (1) to (58).
The values of operating cost factors for each transportation mode were obtained from studies by [22]. This cost might include the salaries and wages, fuel, maintenance, etc., while the exact values in USD per tonne per km are much dependent on the types and densities of the transported products. Operating costs for solid transportation using truck, train, and barge were calculated for return trips, while for liquid and gas transportation through the pipeline were not. Further, Formulations (7)–(11) detail the loads for transportations.
t T F T F T g , h , t = F T F g , h
t T F T H T h , j , t = i I F T H h , i , j
t T F T J T _ S s 1 s 2 = k K F T J _ S s 1 , k , s 2
z Z F T J T L G l g 1 , l g 2 , z = k K F T J _ L G l g 1 , k , l g 2
z Z F T L T l g 2 , n , z = m M F T L l g 2 . m . n
Production cost and emission treatment cost were also included in the model, described mathematically by (12) to (23). The production cost was the result of multiplication between flowrate and production cost factor. Production cost factor was the cost in USD to produce one unit capacity of product. Approximation of values for these factors were done in every processing unit in the processing facilities because they were difficult to be obtained in exact values. The costs for treating emissions from transportation and production activities in the supply chain have indicated that the environmental performances were considered simultaneously. It used USD 40 per tonnes of CO2 equivalent for emission cost as per the previous model. Equations (16)–(23) represent the mass balances for the emissions that were written in tonnes CO2 equivalent per year.
P r o d u c t i o n   c o s t = h H i I F P H h , i   P R O C H h , i + i I j J k K F P J i , j , k P R O C J i , j , k   + k K s 2 S 2 m M F P L _ S k , s 2 , m P R O C L _ S k , s 2 , m + l g 2 L G 2 m M F P L _ L G k , l g 2 , m P R O C L _ L G k , l g 2 , m + ( m M n N o O F P N m , n , o     P R O C N m , n , o )
E m i s s i o n   t r e a t m e n t   c o s t = e m i s s i o n   t r e a t m e n t   c o s t   f r o m   p r o d u c t i o n + e m i s s i o n   t r e a t m e n t   c o s t   f r o m   p r o d u c t i o n
E m i s s i o n   t r e a t m e n t   c o s t   f r o m   p r o d u c t i o n = [ ( h H i I F E V H h , i ) + i I j J k K F E V J i , j , k + k K s 2 S 2 m M F E V L _ S k , s 2 , m + ( l g 2 L G 2 m M F E V L _ L G k , l g 2 , m ) + ( m M n N o O F E V N m , n , o ) ]   E T _ c o s t
E m i s s i o n   t r e a t m e n t   c o s t   f r o m   t r a n s p o r t a t i o n = [ g G h H t T F T F T E g , h , t + h H j J t T F T H T E h , j , t + ( j J s 2 S 2 t T F T J T E _ S j , s 2 , t ) ] E T _ c o s t
F E V H h , i = F P H h , i E N V H h , i
F E V J i , j , k = F P J i , j , k E N V J i , j , k
F E V L _ S k , s 2 , m = F P L _ S k , s 2 , m E N V L _ S k , s 2 , m
F E V L _ L G k , l g 2 , m = F P L _ L G k , l g 2 , m E N V L _ L G k , l g 2 , m
F E V N m , n , o = F P N m , n , o E N V N m , n , o
F T F T E g , h , t = F T F T g , h , t E M F A C t D G H g , h
F T H T E h , j , t = F T H T h , j , t E M F A C t D H I J h , j
F T J T E _ S j , s 2 , t = F T J T _ S j , s 2 , t E M F A C t D J K L _ S j , s 2
The amount of EFB feedstock at location g must not exceed the total availability. This has considered the leftovers of EFBs in the fields. In addition, the demands for each of the products p that were produced must be met. These are described by the following constraints:
g G F g   B i o m a s s   A v a i l a b i l i t y
F i v e   p e r c e n t   o f   W o r l d   D e m a n d s Q p B i o p r o d u c t s   D e m a n d
The other mass balances were represented by (26) to (40) which comprise an inequality and equalities. Multiplications of continuous and discrete (binary) variables for (27), (29), (31), (32), and (41) to (45) have caused the model to be MINLP [23]. High computational time is the typical issue with this type of programming. Methods for solving MINLP models have been reported by [24] that included branch and bound method, generalized benders decomposition, outer approximation, LP/NLP-based branch and bound, and extended cutting plane method. For this study, however, the optimization solver Branch-And-Reduce Optimization Navigator (BARON) that is available in GAMS was used for solving the MINLP.
h H F T F g , h   F g
g G F T F g , h   C O N V H h , i   Y 1 h , i = F P H h , i
F P H h , i = j J F T H h , i , j + F S H h , i
h H F T H h , i , j   C O N V J i , j , k   Y 2 i , j , k = F P J i , j , k
i I F P J i , j , k = F S J j , k + s 2 S 2 F T J _ S j , k , s 2 + l g 2 L G 2 F T J _ L G j , k , l g 2
j J F T J _ S j , k , s 2   C O N V L _ S k , s 2 , m   Y 3 a k , s 2 , m = F P L _ S k , s 2 , m  
j J F T J _ L G j , k , l g 2   C O N V L _ L G k , l g 2 , m   Y 3 b k , l g 2 , m = F P L _ L G k , l g 2 , m
k K F P L _ S k , s 2 , m = F S L _ S s 2 , m
k K F P L _ L G k , l g 2 , m = F S L _ L G l g 2 , m + n N F T L l g 2 , m , n  
l g 2 L G 2 F T L l g 2 , m , n C O N V N m , n , o = F P N m , n , o
m M F P N m , n , o = F S N n , o
h H F S H h , i =   Q i
j J F S J j , k =   Q k  
s 2 S 2 F S L _ S s 2 , m + l g 2 L G 2 F S L _ L G l g 2 , m     =   Q m
n N F S N n , o = Q o
F T F T g , h , t T M A X C t Y G H g , h , t X 1 t
F T H T h , j , t T M A X C t Y H J h , j , t X 2 t
F T J T _ S s 1 , s 2 , t T M A X C t Y J L _ S s 1 , s 2 , t X 3 t
F T J T _ L G l g 1 , l g 2 , z P M A X C t Y J L _ L G l g 1 , l g 2 , z Z Z 1 z
F T L T l g 2 , n , z P M A X C t Y L N l g 2 , n , z Z Z 2 z
Binary variables will produce either 1 for selection or 0 for not. Formulations (46)–(50) would be for selecting the transportation mode, while (50)–(54) would be for the processing route.
t T Y G H g , h , t 1
t T Y H J h , j , t 1  
t T Y J L s 1 , s 2 , t 1
z Z Y J L _ L l g 1 , l g 2 , z 1
z Z Y L N l g 2 , n , z 1
i I Y 1 h , i 1
k K Y 2 i , j , k 1
m M Y 3 a k , s 2 , m 1
m M Y 3 b k , l g 2 , m 1
It was an intention in this paper to assign the modes of transportation according to the physical state of the products, which in turn depends closely on the stage of processing. Stage h would only produce solid products, stages j and l would produce solid, liquid, and gaseous products, and stage n would produce only gaseous products. Therefore, transportation from g to h would involve only solids; from h to j would again involve only solids; from j to l would involve solids, liquids, and gases; from l to n would involve liquids and gas; and lastly there is no transportation required after n. In addition, the model has not considered transportation for every direct-sales product. Equations (55) and (56) represent the assignments between the transportation mode and the products’ states based on fractions. In other words, they fractionally distribute transportation capacities according to the products’ states.
S u m   o f   X = X 1 t + X 2 t + X 3 t = 1
S u m   o f   Z = Z Z 1 z + Z Z 2 z = 1
The following equations set the range of capacities for transportation modes at each processing route.
0 T M A X C t 500 , 000
0 P M A X C z 50 , 000

Model Parameters

Parameters such as the products’ selling prices, demands, and availability of EFB were the same as in the previous model [21], while the other parameters are presented here. Table A1, Table A2, Table A3, Table A4 and Table A5 in the Appendix A recorded the distances between the four stages of processing facilities as shown in the superstructure so that the model could determine the transportation costs. All these distances were obtained by using Google Maps. Furthermore, distances from j to l were tabulated according to the products’ states. The data acquisition such as the operating cost factor and emission factor were acquired from [22] and [25] for each of the transportation modes. It was assumed that there was no emission from the pipeline transportation.
The production cost factors, conversion factors, and emission factors from productions were tabulated accordingly in Table A6, Table A7, Table A8, Table A9, Table A10, Table A11, Table A12, Table A13, Table A14, Table A15, Table A16, Table A17, Table A18, Table A19, Table A20 and Table A21 in the Appendix A. Particularly at l, depending on the states of products from j, separate tables have shown the related parameters clearly. Approximation of parameters was done due to the difficulties in obtaining real data for this model. The parameters were sufficient to prove the model’s practicality, and they were independent of scales, configurations, feedstock conditions, etc.

4. Results and Discussions

The model formulation as shown above were implemented in GAMS Rev. 149 and solved by using the BARON Rev 8.1.1 in AMD A10-4600M APU processor. With the given parameters, the optimal value of overall net profit was obtained to be USD 1,561,106,613 per year, which could be gained by single ownership for all facilities in the supply chain. The model’s statistics have shown that it has 66 blocks of equations, 55 blocks of variables, 6540 single equations, and 10,900 single variables, and it took 4 min to solve. Figure 4a shows the superstructure with processing routes (red dash arrows) and processing units (red dash lines) that would be eliminated prior to optimization, while Figure 4b shows the optimal one. The curve arrows represent option for selling of the products (i, k, m, o).
Figure 4. (a) Optimization process for processing routes and processing unit. (b) Final superstructure of EFB supply chain with optimal processing routes.
The superstructure optimization has eliminated processing routes and units. EFBs from collection point 1 (Johore) would be sent for pre-processing to all facilities except extraction 3 at the amounts of 3,147,894.737 tonnes per year. EFBs from collection point 2 (Pahang) would be utilized at the amount of 2,717,543.860 tonnes per year and be sent to DLF production, extraction 1, extraction 2, extraction 3, pelletization, and torrefied pelletization. EFBs from collection point 3 (Perak) would be consumed at the amount of 2,447,368.421 tonnes per year in DLF production, extraction 1, extraction 2, pelletization, and torrefied pelletization. If the supplies of the EFBs at a single collection point were not sufficient, homogenous blending by using EFBs from other collection points would be conducted. To produce all the products, 8,373,235.36 tonnes per year of EFBs would be utilized at the cost of USD 6 per tonne. Table 4 shows optimal production levels of all products after optimal selections have been implemented.
Table 4. Optimal production level of products.
Based on Figure 4a,b, from i, hemicellulose would no longer be sent to acid hydrolysis 2 but would only be consumed at enzymatic hydrolysis 2 to produce xylose. As a result, the processing route from hemicellulose to xylose through acid hydrolysis 2 has been eliminated in the optimal superstructure. Briquette and pellet were not sent to boiler combustion. Instead, the boiler combustion has only utilized torrefied pellet for producing HP steam. Fast pyrolysis has only one feed that came from pellet and is no longer using torrefied pellet as a feed.
From k, the processing route from xylose to produce bio-gas through anaerobic digestion has been eliminated. Instead, there was only one optimal processing route to produce bio-gas through anaerobic digestion, which used portions of glucose. Xylose also was no longer an input to fermentation to produce bio-ethanol. In addition, since all of the produced bio-oil would be sold directly to the customer, related further processing routes and units that should utilize this product were dismissed. Specifically, steam reforming, bio-upgrading 1 and 2 at l were removed from the optimal superstructure. Bio-gasoline and bio-diesel were only produced from FTL production 1 and FTL production 2, respectively. Bio-hydrogen was meanwhile generated from bio-syngas through separation.
Optimal results for transportation modes at each processing route and emissions from such transportation activities are tabulated in Table 5, Table 6, Table 7 and Table 8. Emission values were negligible for transportations that used pipeline and transportations that involved very close distances between two processing facilities. Furthermore, the optimal results have assigned 97.9% of barges’ capacities to serve for solid transportations between g and h, and the remaining capacities for transportations between h and j. For trains, 84.6% of their capacities have been used for transportations between h and j, and the remaining for solids transportations between j and l. For trucks, 86.1% of their capacities were utilized for solids transportations between g to h, and the remaining capacities were between h and j. For liquid and gaseous products, 97.2% of pipeline capacities were used for transportations from j to l, and the balances were assigned from l to n.
Table 5. Optimal results for transportations between EFB collection points, g and pre-processing facilities, h.
Table 6. Optimal results for transportations between pre-processing facilities, h and main processing facilities, j.
Table 7. Optimal results for transportations between main processing facilities, j and further processing 1 facilities, l (s2 and l2).
Table 8. Optimal results for transportations between further processing 1 facilities, l and further processing 2 facilities, n.
Table 9, Table 10, Table 11 and Table 12 show the optimal results for productions of every processing facility with their respective emission levels. The optimal production rates in tonnes per year for all products have considered the constraint for which the annual demands must at least be met. In order to know what portion of the products needs to be sent for further processing, one could find the difference between the production rate and amounts to be sold directly to the customers.
Table 9. Optimal results for productions at pre-processing facilities, h.
Table 10. Optimal results for productions at main processing facilities, j.
Table 11. Optimal results for productions at further processing 1 facilities, l (s2 and l2).
Table 12. Optimal results for productions at further processing 2 facilities, n.

Sensitivity Analysis

The optimal results that included the selections of optimal processing routes, transportation modes and decision variables which have been presented are subject to have differences depending on the parameters that were used. Uncertainties in economic and technological factors are among the influential issues in a deterministic modeling. Hence, investigations need to be done to find important parameters that could affect large variations to the optimal results. In this section, simultaneous considerations for multi-parameters were done. Even though a myriad of simultaneous perturbations is possible, the sensitivity analysis here has only considered ammonia’s selling price, conversion factor and production cost factor for demonstration purposes. The changes in these parameters were carried out by classifying them into three scenarios as shown in Table 13. Both original selling price and production cost factor were increased until 50%, and the conversion factor was set until 0.95. The overall profits have shown non-linear patterns with the increased values of the three parameters. In the pursuit to find the most important parameter for the developed model, more thorough sensitivity analysis might be required.
Table 13. Sensitivity analysis for some parameters related to ammonia.

5. Conclusions and Future Work

The developed optimization model has extended the previous one by adding integer decision for best processing routes and transportation modes for the multi-product productions from Malaysia’s EFBs in the context of supply chain. The previous superstructure was modified to divide several processing units so that the model could select the optimal ones. It also added the classifications of processing routes and products according to whether their states were solid, liquid, or gas, which would help to determine the best assignments for transportation modes. In addition, environmental considerations have been included in the model in the form of emission treatment costs from both production and transportation activities. Since the model contains approximated parameters due to the issues of availabilities and uncertainties, sensitivity analysis has been done to demonstrate those changes in the objective function. Such parameter approximations were however still sufficient to show the model’s practicality to solve a large and complex biomass supply chain like in this one. The single owner of the EFB supply chain could now have a better judgement in prioritizing the prospective manufacturing investments.
For future works, the model could be further developed by considering stochastic behaviors of the economics and financial planning that are related to the biomass supply chain.

Author Contributions

Writing—original draft, conceptualization, and methodology, A.A.; writing—review and editing and publication, R.Z.; visualization and investigation, M.E.; supervision, A.E. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Universiti Malaysia Pahang under the research grant of PDU213003-2. The APC is discounted using author voucher discount code (cc9cc19ff5e51e21).

Institutional Review Board Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The first author would like to acknowledge Universiti Malaysia Pahang (UMP) for financial support under research grant PDU213003-2.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Table A1. Distances for transporting EFB feedstock between g to h in km, ( D G H g , h ) .
Table A1. Distances for transporting EFB feedstock between g to h in km, ( D G H g , h ) .
EFB Sources Locations, gPre-Processing Facilities, hDistance (km)
EFB Collection 1Aerobic Digestion On Site0
EFB Collection 1DLF Production 271
EFB Collection 1Extraction Plant 1322
EFB Collection 1Extraction Plant 2322
EFB Collection 1Extraction Plant 3322
EFB Collection 1Briquetting Plant 271
EFB Collection 1Pelletization Mill 287
EFB Collection 1Torrefied Pelletization Mill 208
EFB Collection 1Alkaline Activation (Activated Carbon) Plant 208
EFB Collection 2Aerobic Digestion On Site0
EFB Collection 2DLF Production 165
EFB Collection 2Extraction Plant 1230
EFB Collection 2Extraction Plant 2230
EFB Collection 2Extraction Plant 3230
EFB Collection 2Briquetting Plant 165
EFB Collection 2Pelletization Mill 195
EFB Collection 2Torrefied Pelletization Mill 224
EFB Collection 2Alkaline Activation (Activated Carbon) Plant 224
EFB Collection 3Aerobic Digestion On Site0
EFB Collection 3DLF Production 274
EFB Collection 3Extraction Plant 1486
EFB Collection 3Extraction Plant 2486
EFB Collection 3Extraction Plant 3486
EFB Collection 3Briquetting Plant 274
EFB Collection 3Pelletization Mill 289
EFB Collection 3Torrefied Pelletization Mill 346
EFB Collection 3Alkaline Activation (Activated Carbon) Plant 346
Table A2. Distances for transporting pre-processed feedstock between h and j in km, ( D H I J h , j ) .
Table A2. Distances for transporting pre-processed feedstock between h and j in km, ( D H I J h , j ) .
Pre-Processing Facilities, hMain Processing Facilities, jDistance (km)
Extraction Plant 1CMC Production 0
Extraction Plant 1Acid Hydrolysis 1546
Extraction Plant 1Enzymatic Hydrolysis 1315
Extraction Plant 2Acid Hydrolysis 2546
Extraction Plant 2Enzymatic Hydrolysis 2315
Extraction Plant 3Resin Production 386
DLF Production Bio-composite Production 33
Briquetting Plant Boiler Combustion 83
Pelletization Mill Boiler Combustion 88
Pelletization Mill Gasification 17
Pelletization Mill Fast Pyrolysis 0
Pelletization Mill Slow Pyrolysis 345
Torrefied Pelletization Mill Boiler Combustion 23
Torrefied Pelletization Mill Gasification 78
Torrefied Pelletization Mill Fast Pyrolysis 86
Table A3. Distances for transporting solid intermediate products l between j and s2(l) in km, ( D J K L _ S j , s 2 ) .
Table A3. Distances for transporting solid intermediate products l between j and s2(l) in km, ( D J K L _ S j , s 2 ) .
Main Processing Facilities, jFurther Processing 1 Facilities, s2(l)Distance (km)
Acid Hydrolysis 2 Xylitol Production 0
Acid Hydrolysis 1Anaerobic Digestion Plant 338
Enzymatic Hydrolysis 1Anaerobic Digestion Plant 37
Enzymatic Hydrolysis 2Xylitol Production 379
Table A4. Distances for transporting liquid and gaseous intermediate products 1 between j and lg2(l) in km, ( D J K L _ L G j , l g 2 ) .
Table A4. Distances for transporting liquid and gaseous intermediate products 1 between j and lg2(l) in km, ( D J K L _ L G j , l g 2 ) .
Main Processing Facilities, jFurther Processing 1 Facilities, lg2(l)Distance (km)
Boiler CombustionPower Production0
Boiler CombustionMP Steam Production 0
Boiler CombustionLP Steam Production0
Acid Hydrolysis (1 and 2)Fermentation Plant (1 and 2)327
Enzymatic Hydrolysis (1 and 2)Fermentation Plant (1 and 2)65
Gasification Separation Plant0
Gasification Methanol Production404
Gasification FTL Production (1 and 2)19
Fast PyrolysisBio-oil Upgrading (1 and 2)94
Fast PyrolysisSteam Reforming Plant0
Table A5. Distances for intermediate product 2 between lg2(l) and n in km, ( D L M N l g 2 , n ) .
Table A5. Distances for intermediate product 2 between lg2(l) and n in km, ( D L M N l g 2 , n ) .
Further Processing 1 Facilities, lg2(l)Further Processing 2 Facilities, nDistance (km)
Steam Reforming PlantAmmonia Production361
Separation PlantAmmonia Production367
Methanol ProductionFormaldehyde Production686
Fermentation Plant (1 and 2)Bio-ethylene316
Table A6. Operating cost factor and emission factor for transportation mode.
Table A6. Operating cost factor and emission factor for transportation mode.
Transportation ModeOperating Cost Factor (USD per Tonne per km)Emission Factor (Tonnes CO2 Equivalent per Tonne per km)
Truck0.16410.000062
Train0.03330.000022
Barge0.01360.000015
Pipeline0.0500-
Table A7. Approximated production cost factor at h in USD per tonne.
Table A7. Approximated production cost factor at h in USD per tonne.
Biomass Type, gPre-Processing, hPre-Processed Product, iUSD/TonneReference
Blended EFBsDLF ProductionDry Long Fiber85[26]
Blended EFBsAerobic DigestionBio-compost10[27]
Blended EFBsAlkaline ActivationActivated Carbon144[28]
Blended EFBsExtraction 1Cellulose125[29]
Blended EFBsExtraction 2Hemicellulose130[29]
Blended EFBsExtraction 3Lignin135[29]
Blended EFBsBriquettingBriquette50[30]
Blended EFBsPelletizationPellet60[31]
Blended EFBsTorrefied PelletizationTorrefied Pellet70[31]
Table A8. Approximated conversion factor at h.
Table A8. Approximated conversion factor at h.
Biomass Type, gPre-Processing, hPre-Processed Product, iConversion FactorReference
Blended EFBsDLF ProductionDry Long Fiber0.37[32]
Blended EFBsAerobic DigestionBio-compost0.95[33]
Blended EFBsAlkaline ActivationActivated Carbon0.50[34]
Blended EFBsExtraction 1Cellulose0.70Assumed value based on hemicellulose and lignin conversion factor
Blended EFBsExtraction 2Hemicellulose0.15[35]
Blended EFBsExtraction 3Lignin0.15[36]
Blended EFBsBriquettingBriquette0.38[32]
Blended EFBsPelletizationPellet0.38[32]
Blended EFBsTorrefied PelletizationTorrefied Pellet0.38[32]
Table A9. Approximated CO2 emission factor at h.
Table A9. Approximated CO2 emission factor at h.
Biomass Type, gPre-Processing, hPre-Processed Product, iCO2 Emission Factor (Tonnes CO2 Equivalent/Tonnes of Product Produced)Reference
Blended EFBsDLF ProductionDry Long Fiber0.0041[37]
Blended EFBsAerobic DigestionBio-compost0.0200[38]
Blended EFBsAlkaline ActivationActivated Carbon0.0176[39]
Blended EFBsExtraction 1Cellulose0.0590[29]
Blended EFBsExtraction 2Hemicellulose0.0650[29]
Blended EFBsExtraction 3Lignin0.0620Assumed value based on values for cellulose and hemicellulose
Blended EFBsBriquettingBriquette0.0500Assumed value
Blended EFBsPelletizationPellet0.0500Assumed value
Blended EFBsTorrefied PelletizationTorrefied Pellet0.0805[40]
Table A10. Approximated production cost factor at j in USD per tonne.
Table A10. Approximated production cost factor at j in USD per tonne.
Pre-Processed Feedstock, iMain Processing, jIntermediate Product 1, kUSD/TonneReference
Dry Long FiberBio-composite ProductionBio-composite107.0[41]
CelluloseCMC ProductionCMC2500.0[42]
CelluloseAcid Hydrolysis 1Glucose73.4[29]
CelluloseEnzymatic Hydrolysis 1Glucose85.7[29]
HemicelluloseAcid Hydrolysis 2Xylose168.7[29]
HemicelluloseEnzymatic Hydrolysis 2Xylose83.1[29]
LigninResin ProductionBio-resin1900.0[43]
Briquette Boiler CombustionHP Steam20.7[44]
PelletBoiler CombustionHP Steam20.7[44]
PelletGasification Bio-syngas300.0Assumed value based on 50% of Bio-syngas price
PelletFast PyrolysisBio-oil1003[45]
PelletSlow PyrolysisBio-char111.5[46]
Torrefied PelletBoiler CombustionHP Steam20.7[44]
Torrefied PelletGasification Bio-syngas300.0Assumed value based on 50% of Bio-syngas price
Torrefied PelletFast PyrolysisBio-oil1003[45]
Table A11. Approximated conversion factor at j.
Table A11. Approximated conversion factor at j.
Pre-Processed Feedstock, iMain Processing, jIntermediate Product 1, kConversion FactorReference
Dry Long FiberBio-composite ProductionBio-composite0.75[47]
CelluloseCMC ProductionCMC0.86[48]
CelluloseAcid Hydrolysis 1Glucose0.37[29]
CelluloseEnzymatic Hydrolysis 1Glucose0.47[29]
HemicelluloseAcid Hydrolysis 2Xylose0.91[28]
HemicelluloseEnzymatic Hydrolysis 2Xylose0.88[29]
LigninResin ProductionBio-resin0.95[49]
Briquette Boiler CombustionHP Steam0.20[50]
PelletBoiler CombustionHP Steam0.25[50]
PelletGasification Bio-syngas0.70[51]
PelletFast PyrolysisBio-oil0.60[52]
PelletSlow PyrolysisBio-char0.50[53]
Torrefied PelletBoiler CombustionHP Steam0.30[50]
Torrefied PelletGasification Bio-syngas0.80[51]
Torrefied PelletFast PyrolysisBio-oil0.60[54]
Table A12. Approximated CO2 emission factor at j.
Table A12. Approximated CO2 emission factor at j.
Pre-Processed Feedstock, iMain Processing, jIntermediate Product 1, kCO2 Emission Factor (Tonnes CO2 Equivalent/Tonnes of Product Produced)Reference
Dry Long FiberBio-composite ProductionBio-composite7.481 [55]
CelluloseCMC ProductionCMC0.097Assumed value
CelluloseAcid Hydrolysis 1Glucose0.097[29]
CelluloseEnzymatic Hydrolysis 1Glucose0.085[29]
HemicelluloseAcid Hydrolysis 2Xylose0.075[29]
HemicelluloseEnzymatic Hydrolysis 2Xylose0.082[29]
LigninResin ProductionBio-resin2.500[56]
Briquette Boiler CombustionHP Steam0.750[57]
PelletBoiler CombustionHP Steam0.750Assumed value
PelletGasification Bio-syngas0.680[58]
PelletFast PyrolysisBio-oil0.580[52]
PelletSlow PyrolysisBio-char0.580[52]
Torrefied PelletBoiler CombustionHP Steam0.750Assumed value
Torrefied PelletGasification Bio-syngas0.680[58]
Torrefied PelletFast PyrolysisBio-oil0.580[52]
Table A13. Approximated production cost factor at s2(l) in USD per tonne.
Table A13. Approximated production cost factor at s2(l) in USD per tonne.
Intermediate Product 1, kFurther Processing 1, s2(l)Intermediate Product 2, mUSD/Tonne Reference
GlucoseAnaerobic DigestionBio-gas199.0Assumed value for 50% less of the bio-gas price
XyloseAnaerobic DigestionBio-gas199.0Assumed value for 50% less of the bio-gas price
XyloseXylitol ProductionXylitol2100.0Assumed value for 50% less of the xylitol price
Table A14. Approximated production cost factor at lg2(l) in USD per tonne or per MWh.
Table A14. Approximated production cost factor at lg2(l) in USD per tonne or per MWh.
Intermediate Product 1, kFurther Processing 1, lg2(l)Intermediate Product 2, mUSD/Tonne or MWhReference
Bio-oilSteam ReformingBio-hydrogen455.0[59]
Bio-oilBio-oil Upgrading 1Bio-gasoline1089.0[60]
Bio-oilBio-oil Upgrading 2Bio-diesel918.0 [60]
Glucose Fermentation 1Bio-ethanol98.2[29]
XyloseFermentation 2Bio-ethanol98.2[29]
HP SteamPower ProductionElectricity58.9/MWh[50]
HP SteamPower ProductionMP Steam12.0Assumed valued based on the steam price
HP SteamPower ProductionLP Steam7.0Assumed valued based on the steam price
Bio-syngasMethanol ProductionBio-methanol83.6[29]
Bio-syngasSeparationBio-hydrogen112[61]
Bio-syngasFTL Productions 2Bio-diesel167.3[29]
Bio-syngasFTL Productions 1Bio-gasoline519.8[60]
Table A15. Approximated conversion factor at s2(l).
Table A15. Approximated conversion factor at s2(l).
Intermediate Product 1, kFurther Processing 1, s2(l)Intermediate Product 2, mConversion FactorReference
GlucoseAnaerobic DigestionBio-gas0.70[33]
XyloseAnaerobic DigestionBio-gas0.70[33]
XyloseXylitol ProductionXylitol0.70[62]
Table A16. Approximated conversion factor at lg2(l).
Table A16. Approximated conversion factor at lg2(l).
Intermediate Product 1, kFurther Processing 1, lg2(l)Intermediate Product 2, mConversion FactorReference
Bio-oilSteam ReformingBio-hydrogen0.84[63]
Bio-oilBio-oil Upgrading 1Bio-gasoline0.40[64]
Bio-oilBio-oil Upgrading 2Bio-diesel0.20[64]
Glucose Fermentation 1Bio-ethanol0.33[29]
XyloseFermentation 2Bio-ethanol0.33[29]
HP SteamPower ProductionElectricity0.30 MWh/tonne of steam[65]
HP SteamPower ProductionMP Steam0.35[32]
HP SteamPower ProductionLP Steam0.35[32]
Bio-syngasMethanol ProductionBio-methanol0.41[29]
Bio-syngasSeparationBio-hydrogen0.46 [29]
Bio-syngasFTL Productions 2Bio-diesel0.71 [51]
Bio-syngasFTL Productions 1Bio-gasoline0.29Assumed value from bio-diesel conversion factor
Table A17. Approximated CO2 emission factor at s2(l).
Table A17. Approximated CO2 emission factor at s2(l).
Intermediate Product 1, kFurther Processing 1, s2(l)Intermediate Product 2, mCO2 Emission Factor (Tonnes CO2 Equivalent/Tonnes of Product Produced)Reference
GlucoseAnaerobic DigestionBio-gas0.250 [66]
XyloseAnaerobic DigestionBio-gas0.250 [66]
XyloseXylitol ProductionXylitol0.082Assumed value based on value of xylose
Table A18. Approximated CO2 emission factor at lg2(l).
Table A18. Approximated CO2 emission factor at lg2(l).
Intermediate Product 1, kFurther Processing 1, lg2(l)Intermediate Product 2, mCO2 Emission Factor (Tonnes CO2 Equivalent/Tonnes of Product Produced)Reference
Bio-oilSteam ReformingBio-hydrogen16.930[52]
Bio-oilBio-oil Upgrading 1Bio-gasoline13.000[52]
Bio-oilBio-oil Upgrading 2Bio-diesel13.000[52]
Glucose Fermentation 1Bio-ethanol0.098[29]
XyloseFermentation 2Bio-ethanol0.098[29]
HP SteamPower ProductionElectricity0.050Assumed value
HP SteamPower ProductionMP Steam0.050Assumed value
HP SteamPower ProductionLP Steam0.050Assumed value
Bio-syngasMethanol ProductionBio-methanol0.083[29]
Bio-syngasSeparationBio-hydrogen0.090[29]
Bio-syngasFTL Productions 2Bio-diesel0.067[29]
Bio-syngasFTL Productions 1Bio-gasoline0.639[29]
Table A19. Approximated production cost factor at n in USD per tonne.
Table A19. Approximated production cost factor at n in USD per tonne.
Intermediate Product 2, mFurther Processing 2, nFinal Product, pUSD/TonneReference
Bio-hydrogenAmmonia ProductionAmmonia377[67]
Bio-methanolFormaldehyde ProductionFormaldehyde232[68]
Bio-ethanolBio-ethylene ProductionBio-ethylene1200[46]
Table A20. Approximated conversion factor at n.
Table A20. Approximated conversion factor at n.
Intermediate Product 2, mFurther Processing 2, nFinal Product, pConversion FactorReference
Bio-hydrogenAmmonia ProductionAmmonia0.80 [67]
Bio-methanolFormaldehyde ProductionFormaldehyde0.97 [69]
Bio-ethanolBio-ethylene ProductionBio-ethylene0.99 [46]
Table A21. Approximated CO2 emission factor at n.
Table A21. Approximated CO2 emission factor at n.
Intermediate Product 2, mFurther Processing 2, nFinal Product, pCO2 Emission Factor (Tonnes CO2 Equivalent/Tonnes of Product Produced)Reference
Bio-hydrogenAmmonia ProductionAmmonia1.694[70]
Bio-methanolFormaldehyde ProductionFormaldehyde0.083Assumed value
Bio-ethanolBio-ethylene ProductionBio-ethylene1.400[46]

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