Evaluating the Economic Feasibility of Plant Factory Scenarios That Produce Biomass for Biorefining Processes
Abstract
:1. Introduction
1.1. Knowledge Gap in Literature
1.2. Research Aim and Structure
- What are the main drivers and variables to consider during an economic feasibility evaluation of plant factory projects that produce feedstocks for biorefining processes?
- What is the economic feasibility for the use of plant factories to produce biomass feedstocks for the biorefining industry?
2. Literature
2.1. Literature Review of Existing Plant Factory Knowledge
2.2. Literature Review for the Establishment of a Plant Factory System Boundary
3. Methodology
3.1. Plant Factory Scenario Descriptions
3.1.1. Crop Selection
3.1.2. Market and Product Selection
3.1.3. Technology and Integration Selection
3.2. Economic Modelling of Plant Factory Scenarios
3.2.1. Data Acquisition
3.2.2. Data Processing
Capital Expenditure (CAPEX) Calculations
Operating Expenditure (OPEX) Calculations
Economic Feasibility Calculations
4. Results
4.1. Plant Factory Scenario Cultivation Conditions
4.2. Plant Factory Scenario CAPEX Results
4.3. Plant Factory Scenario OPEX Results
4.4. Plant Factory Scenario Revenue Results
4.4.1. Tomato-Based Plant Factory Revenue Results
4.4.2. Lettuce-Based Plant Factory Revenue Results
4.4.3. Tobacco-Based Plant Factory Revenue Results
4.4.4. Cannabis-Based Plant Factory Revenue Results
5. Discussion
5.1. Tomato-Based Plant Factory Scenarios
5.2. Lettuce-Based Plant Factory Scenarios
5.3. Tobacco and Cannabis Plant Factory Scenarios
5.4. Economic Feasibility of Plant Factory Scenarios
5.5. Implications and Limitations
- Exploring how the plant factory system boundary can be conceptualised to show dependencies within the greater economy;
- Contributing to the debate around the use of plant factories by providing a new perspective to the applicability of the plant factory concept within the greater biorefining industry.
- The initial review of the plant factory literature in Section 2 alluded to the fact that crop yield data were not easily available for crops grown in plant factories. Directly comparable results of crop yields and cultivation conditions under varying degrees of CEA were even more scarce. This paper had to use best-available crop data to populate the economic model, which approximated the crop growth rates under specific cultivation conditions. Future research can include the standardised cultivation of various crops to draw a clear correlation between crop growth performance and the level of environmental control provided by CEA structures.
- The economic feasibility analysis of this paper considered the costs associated with operating plant factories within the defined scenarios. The revenue potential of these scenarios was based on the revenue potential of the final products which would be produced within the cultivated biomass in each plant factory. This paper calculated capital for uncertainty to put the economic indexes of each scenario in the context of the omitted expenses of the economic model. Future research can include the expansion of the economic feasibility analysis to include the downstream processing steps which were omitted from the analysis. This will lead to a more detailed techno-economic analysis which includes the extraction and purification costs of value-added compounds from host plants.
- The economic feasibility analysis also only considered monocultures within a specific scenario. Future research can include the investigation of contract farming within plant factories and the simultaneous cultivation of different crops to produce a variety of products for multiple markets.
6. Conclusions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Article Type | Objective | Selected Crops | References |
---|---|---|---|
Economic modelling | Design of an economically feasible modular vertical farm | Lettuce and tomatoes | [7] |
Assessing financial risk of vertical farms using imprecise probability | Lettuce | [18] | |
Development of a decision support framework to help design and operate urban farming systems | Leafy greens | [8] | |
Development of a vegetable supply chain in the urban environment using plant factories | Leafy greens | [9] | |
Resource/ technology reviews | Quantify and compare resource requirements of greenhouses and plant factories | Lettuce | [14] |
Review of technology options available to greenhouses and plant factories | Lettuce and tomatoes | [11] | |
Review of Internet of Things (IoT) solutions to monitor edible crop growth in vertical farms | Edible biomass, mostly leafy greens | [13] | |
Review of differences in energy efficiencies between plant factory technology solutions | Edible biomass | [5] | |
Review of controlled environment agriculture case studies in terms of challenges and opportunities | Leafy greens | [19] | |
Review of the resource use efficiencies within plant factories | Leafy greens, highlights lack of larger crop growth data | [20] | |
Plant factory integration | Evaluating the industrial symbiosis of plant factories with surrounding industries | Leafy greens and herbs | [21] |
Evaluating the industrial symbiosis of plant factories with surrounding industries based on environmental impact measurements | Leafy greens and herbs | [16] | |
Evaluating the integration of plant factories with on-site composting infrastructure | Lettuce | [22] | |
Plant factory assessments | Assessing the environmental, economic and social impacts of urban agriculture | Edible biomass | [23] |
Assessing the role of IoT technology within a plant factory case study | Lettuce | [24] | |
Assessing the environmental impact of the constituent elements which make up a plant factory structure and business | Edible biomass | [25] |
Key Research Themes | References |
---|---|
CEA/Plant factory design and operation | [1,2,8,11,28,29,30,31,32,33,34] |
Supply chain under uncertainty | [9,26,27,35,36,37,38,39,40,41] |
Biorefining markets | [27,42,43,44,45,46,47,48,49,50,51,52] |
Plant Factory Component | Space Breakdown (%) | References |
---|---|---|
Germination and nursery | 15 | [54] |
Growth phase bottom layer | 60 | [18,53] |
Harvest, packaging, and storage | 15 | [30] |
Walkways, offices, and ancillary spaces | 10 | Assumed |
Total | 100 | - |
Scenario | Plant Factory Structure | Market | Products |
---|---|---|---|
Tomato—food (TF) | High-wire | Food | Edible tomatoes |
Tomato—miraculin (TM) | Vertical farm (five levels) | Food/ biopharmaceutical | Miraculin accumulated in tomatoes |
Lettuce—food (LF) | Vertical farm (five levels) | Food | Edible lettuce |
Lettuce—miraculin (LM) | Vertical farm (five levels) | Food/ biopharmaceutical | Miraculin accumulated in lettuce |
Lettuce—renewable— integrated (LRI) | Vertical farm (five levels) | Food | Edible lettuce, with solar panels and alternative fertiliser considered |
Tobacco—conventional (TC) | Vertical farm (five levels) | Biopharmaceutical/ bio-based products | Tobacco biomass, accumulated artemisinin, biodiesel, and biomethane |
Tobacco—PHB (TPHB) | Vertical farm (five levels) | Bio-based products | Polyhydroxybutyrate (PHB) polymer accumulated in tobacco |
Tobacco—transgenic (TT) | Vertical farm (five levels) | Biopharmaceutical | Hepatitis B virus (HBV) antibodies accumulated in tobacco |
Tobacco—transgenic—dwarf (TTD) | Vertical farm (five levels) | Biopharmaceutical | HBV antibodies accumulated in dwarf tobacco |
Cannabis—conventional (CC) | Vertical farm (three levels) | Medicinal/recreational | Value in cannabidiol (CBD) content |
Modelling Method | Objective | References |
---|---|---|
Monte Carlo | Economic risk assessment of biofuel technologies | [81] |
Monte Carlo | Biomass supply chain development for biofuel production | [82] |
Monte Carlo and System Dynamics | Review of greenhouse modelling techniques | [29] |
Monte Carlo | Assessing economic viability of hydroponic cultivation in emerging markets | [83] |
Probability bound analysis | Assessing financial risk of vertical farms using imprecise probability | [18] |
Monte Carlo | Life cycle assessment (LCA) of biodiesel production from tobacco seeds | [65] |
Monte Carlo | Sustainability assessment of bio-based aviation fuel | [84] |
Growing Area | Planting Density | Biomass Yield per Plant | PPFD | Average Temperature | CO2 Concentration | Photoperiod | Cultivation Period | |
---|---|---|---|---|---|---|---|---|
(m2) | (Plant/m2) | (g Fresh Weight/Plant) | (µmol/m2/s) | (°C) | (ppm) | (h) | (Days) | |
Scenario | ||||||||
TF | 1020 | 2.5–2.8 | 20,320–30,480 | 600 | 22.5 | 1000 | 12 | 90–110 |
TM | 2720 | 27–44 | 171–250 | 400 | 22.5 | 1000 | 12 | 70–90 |
LF | 2720 | 32–66 | 80–200 | 200 | 17 | 1000 | 16 | 30–42 |
LM | 2720 | 32–66 | 80–200 | 200 | 17 | 1000 | 16 | 30–42 |
LRI | 2720 | 32–66 | 80–200 | 200 | 17 | 1000 | 16 | 30–42 |
TC | 2720 | 3.6–4.8 | ~1700 | 275 | 27.5 | 750 | 13 | 100–130 |
TPHB | 2720 | 32–44 | 67–101 | 275 | 27.5 | 750 | 13 | 90–110 |
TT | 2720 | 26–39 | 43–59 | 275 | 27.5 | 750 | 13 | 74–84 |
TTD | 2720 | 36–53 | 35–44 | 275 | 27.5 | 750 | 13 | 74–84 |
CC | 1632 | 10–30 | 83–373 | 500 | 26 | 950 | 16 | 70–80 |
Quantity | Unit Price (R) | Total Component Price (R) | Depreciation Cost per Year (R/Year) | |
---|---|---|---|---|
Panel (455 W rating) | 500 | 3334 | 1,666,925 | - |
Inverter (8 kW) | 22 | 43,413 | 955,075 | - |
Installation | - | - | 428,000 | - |
Total CAPEX | 3,050,000 | 122,000 |
Scenarios | Cost (R) | Lifespan (Years) | Depreciation per Year (%) | Depreciation Cost per Year (R/Year) | |||
---|---|---|---|---|---|---|---|
Construction | |||||||
Structure | TF | 6,745,000 | 30 | 3.33 | 224,833 | ||
TM | |||||||
LF, LM, LRI | |||||||
TC, TPHB, TT, TTD | |||||||
CC | |||||||
Equipment | |||||||
Plant factory module | TF | 3,430,353 | 25 | 4 | 137,214 | ||
TM | 17,151,765 | 25 | 4 | 686,071 | |||
LF, LM, LRI | 17,151,765 | 20,201,765 a | 25 | 4 | 686,071 | 808,071 a | |
TC, TPHB, TT, TTD | 17,151,765 | 25 | 4 | 686,071 | |||
CC | 10,291,059 | 25 | 4 | 441,642 | |||
Lift and transport car | TF | 100,000 | 15 | 6.67 | 6667 | ||
TM | |||||||
LF, LM, LRI | |||||||
TC, TPHB, TT, TTD | |||||||
CC | |||||||
Fertigation system | TF | 328,720 | 10 | 10 | 32,872 | ||
TM | |||||||
LF, LM, LRI | |||||||
TC, TPHB, TT, TTD | |||||||
CC | |||||||
Monitor and control system | TF | 997,577 | 10 | 10 | 99,758 | ||
TM | 2,497,801 | 10 | 10 | 249,780 | |||
LF, LM, LRI | 2,497,801 | 10 | 10 | 249,780 | |||
TC, TPHB, TT, TTD | 2,497,801 | 10 | 10 | 249,780 | |||
CC | 1,546,739 | 10 | 10 | 154,674 | |||
HVAC system | TF | 836,595 | 10 | 10 | 83,660 | ||
TM | |||||||
LF, LM, LRI | |||||||
TC, TPHB, TT, TTD | |||||||
CC | 511,105 | 10 | 10 | 51,110 | |||
Total CAPEX | TF | 12,438,245 | - | - | 585,003 | ||
TM | 27,659,880 | - | - | 1,283,882 | |||
LF, LM, LRI | 27,659,880 | 30,709,880 a | - | - | 1,283,882 | 1,405,882 a | |
TC, TPHB, TT, TTD | 27,659,880 | - | - | 1,283,882 | |||
CC | 19,522,622 | - | - | 881,799 |
Scenarios | |||
OPEX component | Unit | TF | TM |
Fixed cost | |||
Indirect labour | R/year | 1,499,273–1,820,279 | 1,499,904–1,819,928 |
Variable (COGS) cost | |||
Direct labour | R/year | 44,831–102,254 | 67,267–153,381 |
Electricity | R/year | 2,493,606–3,474,307 | 4,990,472–7,031,889 |
Water | R/year | 27,762–56,661 | 74,026–151,092 |
Fertiliser | R/year | 85,232–249,538 | 227,221–665,379 |
Grow media | R/year | 28,556–41,144 | 190,344–331,501 |
Seeds | R/year | 1,081–1,559 | 938,925–1,629,663 |
CO2 | R/year | 190,498–260,537 | 507,981–694,757 |
Total COGS | R/year | 3,026,155–4,033,157 | 7,649,327–9,904,036 |
Scenarios | ||||
---|---|---|---|---|
OPEX component | Unit | LF | LM | LRI |
Fixed cost | ||||
Indirect labour | R/year | 1,496,505–1,821,113 | ||
Variable (COGS) cost | ||||
Direct labour | R/year | 67,263–153,384 | ||
Grid electricity | R/year | 3,969,748–5,569,269 | 3,509,923–4,955,137 | |
Water | R/year | 61,100–114,189 | ||
Fertiliser | R/year | 184,864–502,663 | ||
Grow media | R/year | 522,790–1,064,527 | 71,693–136,903 | |
Seeds | R/year | 59,815–120,663 | ||
CO2 | R/year | 677,290–926,297 | ||
Total COGS | R/year | 6,059,818–7,815,184 | 5,596,623–7,207,506 (panels) 5,454,366–7,112,600 (grains) 4,990,546–6,499,481 (combined) |
Scenarios | |||||
---|---|---|---|---|---|
OPEX component | Unit | TC | TPHB | TT | TTD |
Fixed cost | |||||
Indirect labour | R/year | 1,498,525–1,825,671 | |||
Variable (COGS) cost | |||||
Direct labour | R/year | 67,257–153,381 | |||
Electricity | R/year | 4,452,982–6,392,575 | |||
Water | R/year | 69,922–163,230 | |||
Fertiliser | R/year | 219,298–719,451 | |||
Grow media | R/year | 16,655–26,054 | 173,400–268,689 | 185,156–294,406 | 253,819–399,207 |
Seeds | R/year | 32,634–50,817 | 340,188–526,262 | 361,714–573,686 | 497,917–784,409 |
CO2 | R/year | 550,339–752,628 | |||
Total COGS | R/year | 5,816,197–7,840,108 | 6,393,465–8,434,953 | 6,435,846–8,488,624 | 6,692,149–8,737,868 |
Scenario | ||
---|---|---|
OPEX component | Unit | CC |
Fixed cost | ||
Indirect labour | R/year | 1,498,023–1,822,495 |
Variable (COGS) cost | ||
Direct labour | R/year | 44,828–102,261 |
Electricity | R/year | 4,664,240–6,433,889 |
Water | R/year | 72,977–98,105 |
Fertiliser | R/year | 216,546–427,402 |
Grow media | R/year | 222,168–557,353 |
Seeds | R/year | 7,572,613–18,710,626 |
CO2 | R/year | 406,384–555,778 |
Total COGS | R/year | 14,152,192–25,731,525 |
Scenarios | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
Unit | TF | TM | LF | LM | LRI | TC | TPHB | TT | TTD | CC | |
Revenue | R/year | 1,010,876–1,635,218 (producer price) 4,195,270–10,599,920 (hydroponic price) | 3,204,000,000–7,066,000,000 (miracle berry) 14,652,953–31,506,451 (sugar equivalent) | 729,257–1,996,895 (producer price) 10,945,263–28,962,000 (hydroponic price) | 1,081,285–3,011,150 (sugar equivalent) | 729,257–1,996,895 (producer price) 10,945,263–28,962,000 (hydroponic price) | 2,235,798–3,329,928 (producer price) 19,982–36,106 (methane) 4314–6521 (biodiesel) 26,086–120,392 (artemisinin) | 12,564–19,870 (polypropylene price) 49,878–86,110 (PHB price) | 25,231,351–48,806,539 (HBV antibody) | 27,519,590–51,613,595 (HBV antibody) | 50,999,614–225,340,789 |
Cost of Cultivation a | R/year R/kg/year | 5,247,052–6,308,527 35–53 | 10,596,485–12,867,671 108–184 | 8,988,2645–10,783,088 40–101 | 8,988,2645–10,783,088 N/A | 8,643,900–10,298,222 (panels) 8,389,501–10,065,881 (grains) 8,042,543–9,582,324 (combined) 38–97 (panels) 37–96 (grains) 35–91 (combined) | 8,743,519–10,795,692 147–203 | 9,325,878–11,383,441 N/A | 9,371,340–11,435,940 N/A | 9,620,235–11,701,874 N/A | 16,702,559–28,286,586 455–1,480 (whole plant) 1,516–4,935 (leaves and inflorescences) |
ROI | % | −36 (producer price) 11 (hydroponic price) | 17,600 (miracle berry) 37 (sugar equivalent) | −31 (producer price) 31 (hydroponic price) | −29 | 29 (panels) 33 (grains) 31 (combined) | N/A | N/A | 93 | 101 | 508 |
Payback Period b | years | 9 (hydroponic price) | 0.006 (miracle berry) 3 (sugar equivalent) | 3.23 (hydroponic price) | N/A | 3.45 (panels) 3.03 (grains) 3.23 (combined) | N/A | N/A | 1.1 | 1.0 | 0.20 |
Capital for uncertainty | R/year | −1,624,654–4,871,751 (hydroponic price) | 3,031,137–19,655,509 (sugar equivalent) | 1,194,202–18,899,854 (hydroponic price) | N/A | 1,633,439–19,341,092 (panels) 1,738,310–19,692,730 (grains) 2,160,251–20,086,477 (combined) | N/A | N/A | 14,870,937–38,352,675 | 16,888,055–41,009,508 | 31,597,483–199,523,749 |
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Pesch, H.; Louw, L. Evaluating the Economic Feasibility of Plant Factory Scenarios That Produce Biomass for Biorefining Processes. Sustainability 2023, 15, 1324. https://doi.org/10.3390/su15021324
Pesch H, Louw L. Evaluating the Economic Feasibility of Plant Factory Scenarios That Produce Biomass for Biorefining Processes. Sustainability. 2023; 15(2):1324. https://doi.org/10.3390/su15021324
Chicago/Turabian StylePesch, Heino, and Louis Louw. 2023. "Evaluating the Economic Feasibility of Plant Factory Scenarios That Produce Biomass for Biorefining Processes" Sustainability 15, no. 2: 1324. https://doi.org/10.3390/su15021324
APA StylePesch, H., & Louw, L. (2023). Evaluating the Economic Feasibility of Plant Factory Scenarios That Produce Biomass for Biorefining Processes. Sustainability, 15(2), 1324. https://doi.org/10.3390/su15021324