Techno-Economic and Life Cycle Cost Analysis through the Lens of Uncertainty: A Scoping Review
Abstract
:1. Introduction
- What are the main sources of uncertainty in TEA and LCCA?
- Which methods/tools were used to cope with these uncertainties?
- Which probability distribution functions were used to define the uncertainties?
2. Background
2.1. Techno-Economic Analysis
2.2. Life Cycle Cost Analysis
2.3. Uncertainty
3. Methodology
- Analyzing the scope, range, and nature of the study,
- An assessment of the feasibility of conducting a comprehensive systematic review,
- Sharing and summarizing findings, and
- Knowledge gaps identification
3.1. Searching Procedure
- Three main research questions were defined (stage 1).
- A preliminary search was conducted in two scientific databases, Scopus and ScienceDirect (stage 2), using the following search strings. These search strings are:For Scopus:TITLE-ABS-KEY ((techno-economic OR (life AND cycle AND cost*)) AND(uncertainty))For ScienceDirect:(techno-economic OR life cycle cost) AND uncertaintyThe initial search was not limited at this level. Titles, abstracts, and keywords were searched across the selected databases. Thus, 3635 and 680 documents (in all categories) were indexed in Scopus and ScienceDirect, respectively.
- The main interest was to study the most recent studies. Therefore, the studies conducted in the last 5 years were chosen (2017–April 2022). As a result of applying this limit, the number of documents decreased to 1777 for Scopus and 470 for ScienceDirect, respectively (stage 2).Figure 2. Overall research process scheme based on PRISMA adapted from [14].
- In the next step, the language of the studies was also limited to English. Consequently, only a few documents were removed from Scopus. The remaining studies were indexed in Scopus and ScienceDirect as 1741 and 470, respectively (stage 2 continued).
- Limiting the search strings only to the title (stage 2 continued), the number of articles dropped significantly (63 and 35 for Scopus and ScienceDirect).
- All the documents obtained from ScienceDirect were repeated in the Scopus list. Therefore, in this step, by trimming the list and removing duplicates, 63 documents remained (stage 3). The remaining articles were listed in Excel to perform the necessary investigation.
- A full-text screening was conducted to determine the eligibility of the studies. Accordingly, three studies were deemed non-relevant and were eliminated from the list (stage 3 continued). The list contained 60 publications at this stage.
- To obtain more credible results, the results were limited to only journal papers, and book chapters and conference papers were eliminated. All in all, the final list included 47 studies.
- The Bolographic information was extracted and reported (stages 4 and 5), including the title, country of origin, year of publication, the study’s aim and scope, methodology, barriers and challenges, and other observations.
3.2. Limitation
4. Results and Discussion
4.1. Descriptive Analysis
4.1.1. Number of Publications
4.1.2. The Origin of Studies
4.1.3. Publications by Document Type
4.1.4. Publications by Subject Area
4.2. Content-Based Analysis
5. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
Nomenclature
ANN | Artificial Neural Network | NPB | Non-Parametric Bootstrapping |
ANOVA | Analysis of Variance | PM | Pedigree Matrix |
ARIMA | Auto-Regressive Integrated Moving Average | PN | Petri Net |
DNN | Deep Neural Networks | Probability Distribution Function | |
FOATSE | First Order Analysis Taylor Series Expansion | PA | Profitability Analysis |
GA | Genetic Algorithm | RO | Robust Optimization |
GBM | Geometric Brownian Motion | SAA | Sample Average Approximation |
GABCAO | Global Artificial Bee Colony Algorithm Optimization | ScA | Scenario Analysis |
GSA | Global Sensitivity Analysis | SFA | Seismic Fragility Assessment |
LIDRA | Low Impact Development Rapid Assessment | SPA | Semi-Probabilistic Approach |
MRJD | Mean -Reversion and Jump-Diffusion | SA | Sensitivity Analysis |
MCS | Monte Carlo Simulation | SIM | Sobol’s Indices Methodology |
MLFD | Multi-Level Factorial Design | SPCE | Sparse Polynomial Chaos Expansion |
MOO | Multi-Objective Optimization | SRA | System Reliability Analysis |
MMO | Multiple Model Optimization | SUA | System Uncertainty Analysis |
MSO | Multi-Scenario Optimization | UA | Uncertainty Analysis |
N/A | Not applicable | HOM | Hazard Occurrence Model |
NIPCE | Non-Intrusive Polynomial Chaos Expansion |
Appendix A
Definition | Reference |
---|---|
“The evaluation of the technic performance or potential and the economic feasibility of a new technology that aims to improve the social or environmental impact of a technology currently in practice, and which helps decision-makers in directing research and development or investments.” | [17] |
“The techno-economic evaluation incorporates results from both investment and performance analysis to select the most cost-efficient solution for a certain scenario and performance requirements.” | [18] |
“Iterative process illustrating the valorization of potential technologies. It adopts design techniques to estimate costs and revenues aimed at identifying profitability. Next, risk analysis is performed in support of risk reduction strategies.” | [19] |
“Techno-economic modelling methods are typically used to evaluate the economic feasibility of new technologies and services. Techno-economic modelling combines forecasting network design and investment analysis methods, typically utilizing the spreadsheet-based tool.” | [81] |
“TEA is a methodology framework to analyse the technical and economic performance of a process, product or service and includes studies on the economic impact of research, development, demonstration, and deployment of technologies, quantifying the cost of manufacturing and market opportunities.” | [82] |
“The TEA model is an integrated model, with direct linkages between the economic and technological parts. The dynamic character of TEA, where a change in one parameter directly affects all output indicators, is key to identifying the most influencing parameters for a feasible technology.” | [83] |
“The techno-economic analysis (TEA) involves evaluating a process/technology through a process simulation approach.” | [84] |
Definition | Reference |
---|---|
In an LCCA, all the significant net expenditures arising during the ownership of an asset are identified and quantified in order to optimize the total cost of asset ownership. | [85] |
The life cycle cost of a product (LCCA) involves the total cost throughout its entire lifespan. | [86] |
As a result of LCCA analysis, an estimate of the total incremental costs associated with developing, producing, using, and retiring a particular product can be determined | [87] |
A conventional life cycle cost analysis assesses all costs associated with the life cycle of a product that are directly borne by the main producer or user | [88] |
The LCCA is a type of investment calculus that incorporates a life-cycle perspective beyond that offered by traditional investment calculus. As well as considering investment costs, it also considers operating costs over the product’s expected lifetime. | [89] |
The LCCA methodology enables comparisons of costs over a given period, taking into account relevant integral economic factors | [90] |
In LCCA, all present and future costs essential to a system are summed together in present value during a given life cycle. | [91] |
A life cycle cost assessment is a method of evaluating life-cycle costs in a systematic manner. It can examine a project’s entire life cycle, a selected period of time, or a selected stage in its life cycle | [92] |
Appendix B
Reference | Sources of Uncertainty | |
---|---|---|
1 | [56] | The grid electricity and diesel price, grid electricity’s greenhouse gas emissions, energy consumption, annual solar irradiance, average ambient temperature, inflation rate, economic and environmental parameters |
2 | [9] | Variations in the feedstock, plant capacities, manufacturing parameters, and capital and operating costs |
3 | [63] | Syngas and transportation fuel prices, biomass quality, supply and pricing |
4 | [64] | Main indicators of profitability such as internal rate of return, cost of goods, and performance forecast variables, such as product purity and annual throughput) |
5 | [66] | Input variables of biodiesel production, profitability indicators |
6 | [7] | Different input parameters, including feed grade, kinetic coefficients, and metal price |
7 | [68] | Input parameters such as electricity selling price and cost of Ca(OH)2 |
8 | [93] | Economic parameters |
9 | [94] | A historical time series of wind directions and speeds in the years between 2000–2019, mean wind speeds, power density, most probable wind speeds, maximum energy carrying speeds, and predominant wind directions in wind passes are presented in this section |
10 | [95] | Feedstock composition, HTL yield model, aqueous-phase product treatment, utility consumption, and equipment sizing and costing |
11 | [96] | Biodiesel production input variables and profitability indicators |
12 | [97] | Process parameters such as materials and energy demands, production costs, and unit production costs |
13 | [98] | Various distributed energy resources (DERs) data, wind, solar and electric vehicles (EVs) |
14 | [99] | Wide range of system parameters (Electrolyzer, PV, and economic parameters) |
15 | [3] | Review |
16 | [100] | Coefficients of cost correlation and parameters of scenarios |
17 | [101] | System parameters including electrolyzer, PV, H2 tank, battery bank, fuel cell) and economic parameters |
18 | [102] | Solvent property uncertainties on a rate-based absorb model (density, viscosity, solubility, surface tension, equilibrium between vapor and liquid, chemical reaction kinetics, heat of reaction, specific heat capacity) |
19 | [103] | Several geological and structural parameters are uncertain, including the stress field, the location and orientation of natural fractures and faults, the temperature distribution, and the pressure distribution within the reservoir |
20 | [104] | Model parameters |
21 | [105] | Technical and financial parameters |
22 | [106] | The price of energy, technological uncertainty regarding internal combustion, hybrid, plug-in hybrid, battery, and fuel cell electric under various progress scenarios for 2035 and 2050 |
23 | [107] | Parameters of the PV-electrolyzer system from a technical and economic perspective |
24 | [108] | The uncertainty of bio-crude yields, quality, utility consumption, and efficiency, as well as key economic indicators |
25 | [109] | Process and economic variables |
26 | [110] | Process and economic variables |
27 | [111] | Economic key factors |
30 | [112] | Economic key factors |
31 | [113] | Economic key factors |
32 | [114] | Number of people inside the room |
33 | [115] | Estimate feedstock requirements, costs, life-cycle energy usage, greenhouse gas emissions for grower payments and field operations, and major parameters associated with the transportation of corn stover feedstock |
34 | [116] | Technical and economic parameters |
35 | [117] | Technical parameters and environmental uncertainties |
36 | [118] | Price of biodiesel and feedstock, the efficiency of biodiesel conversion, and operating costs |
37 | [119] | Post-combustion CO2 capture techno-economic parameters |
38 | [69] | Technical, economic, and environmental parameters (electricity and heat loads, wind and PV generation, EE unit factors for EE evaluation) |
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Type | Source | Ref. |
---|---|---|
Variability | An unpredictable result of changes in systems (involving time, space, or other variables) | [38] |
Systematic errors | Bias in sampling procedures or measuring equipment | [38] |
Measurement error | Errors that appear random due to imperfections in the measurement equipment and observational methods | [38] |
Random errors | A measurement error caused by varying factors between measurements | Oxford definition |
Parameter uncertainty | Measurement errors, sampling errors, variability, and surrogate data contribute to incomplete knowledge of parameters | [39] |
Model uncertainty | Our limitations in representing physical systems may result in uncertainty when we approximate a model in order to solve a problem. | [38] |
Scenario uncertainty | A level of uncertainty associated with specifying an exposure scenario that is consistent with the purpose and scope of the exposure assessment | [40] |
Exposure factor Uncertainty | Contributes to the specification of numerical values for human exposure | [40] |
Uncertainty due to choices | Different choices of partitioning methods, etc. | [41] |
Spatial variability | The phenomenon occurs when the value of a quantity is different at different spatial locations. A descriptive spatial statistic such as the range can be used to assess spatial variability. | [42] |
Temporal variability | A measure of the frequency and magnitude of fluctuations in ecosystem structure such as standing stocks of resources and species abundance | [43] |
Data uncertainty | This type of data contains noise that causes it to deviate from the correct or original values. | [44] |
Completeness uncertainty | Like modeling uncertainties, completeness uncertainties occur at the beginning of the probabilistic risk analysis process. In probabilistic risk analysis, there is uncertainty as to whether all significant phenomena and significant relationships have been considered. | [45] |
Aleatory uncertainty | Samples and parameters are intrinsically random | [38] |
Epistemic uncertainty | An insufficient understanding of fundamental phenomena | [38] |
Ambiguity | Being open to multiple interpretations | Oxford definition |
Volitional uncertainty | Whether or not an individual will follow through on an individual’s commitment | [46] |
Statistical variation | A measure of how widely distributed a group of data is | [47,48] |
Subjective judgment | A lack of certainty in the interpretation of data or the estimations of experts | [38] |
Linguistic imprecision | Depends on the utterance alternatives available to the speaker in the context | [49] |
Inherent randomness | Resulting from the irreducibility of a system to a deterministic system | [38] |
Disagreement | Lack of consensus or approval, inconsistency or correspondence | Oxford definition |
Approximation | Nearly accurate but not exactly correct value or quantity | Oxford definition |
Semantic uncertainty | Occurs when humans give names to things, especially when those things are mapped as geographic data | [50] |
Interpretational uncertainty | Occurs when interpreters use inconsistent decoding methodologies to extract information from data or models. | Helmholtz dictionary |
Engineering | 27% |
Energy | 22% |
Environmental Science | 19% |
Chemical Engineering | 7% |
Chemistry | 5% |
Earth and Planetary Sciences | 4% |
Agricultural and Biological Sciences | 3% |
Materials Science | 2% |
Physics and Astronomy | 2% |
Biochemistry, Genetics, and Molecular Biology | 2% |
Business, Management, and Accounting | 2% |
Computer Science | 2% |
Social Sciences | 1% |
Decision Sciences, Economics and Finance, Mathematics | 1% |
Techno-economic analysis (TEA) | 33 |
Life cycle cost analysis (LCCA) | 13 |
Techno-economic-environmental analysis (TEEA) | 1 |
Model/Tool | Trials | Application | ||
---|---|---|---|---|
1 | UQ by SPCE | N/A | Uniform | Heavy-duty transport (Bus) |
2 | SA By MCS | 1000 | Mostly Uniform and a Triangular | Economic feasibility of cross-laminated timber |
3 | MCS | Probability distributions | Biomass gasification | |
4 | MCS | 20,000 and 60,000 | Normal, Triangular, Logistic, Scaled beta | Field-grown bioproducts manufacturing |
5 | MCS, SA | 100,000 | Normal | Bio-catalyzed biodiesel production |
6 | SAA by MCS SA | uniform, normal, and lognormal | Cell-Based Flotation Circuits | |
7 | SA, UA by MCS | 10,000 | Normal | Anaerobic digestion of Cuban sugarcane vinasses |
8 | MCS, SA | 10,000 | Triangular | Cooking oil to jet fuel production |
9 | ScA | N/A | Weibull distribution | Wind energy potential in selected sites |
10 | MCS | 10,000 | Normal, Triangular, Logistic, Lognormal, | Wet waste hydrothermal liquefaction (HTL) |
11 | MCS, SA | 30,000 | Normal | Biodiesel production from palm kernel oil |
12 | MCS | 100,000 | Normal | Technologies for the extraction of crude anthocyanin powder |
13 | GABCAO | N/A | N/A | Distribution network |
14 | MCS | 50,000 | Two-half-Lognormal | An off-grid stand-alone photovoltaic system for hydrogen electrolysis |
15 | Review | N/A | CO2 Capture and Storage (CCS) technologies | |
16 | MCS, SA | Biorefineries | ||
17 | GSA, MCS, RO by (MCS + GA) | Uniform, Weibull, Beta | Design of remote micro-grid | |
18 | MCS, SIM | 10,000 | Normal, | Performances of a CO2 Absorber |
19 | MMO | N/A | Enhanced Geothermal System (EGS) | |
20 | MOM | N/A | Hybrid harmonic filter planning | |
21 | SUA | N/A | Ship power and propulsion concepts | |
22 | ScA, SA | N/A | Fuel cell vehicles | |
23 | GSA by MCS + SIM | 100,000 | Normal | Directly coupled photovoltaic-electrolyzer system |
24 | MCS | 10,000 | Normal, Pareto, Lognormal, Triangular, Maximum extreme | Algal-derived bio-crude via hydrothermal liquefaction |
25 | ANN + MCS | Uniform, Normal | Power to gaseoxy-fuel boiler hybrid system | |
26 | MCS | 10,000 | Triangular, Boot-strapped, Uniform, Linear | Incorporating microbial oil production into the concept of a biorefinery |
27 | MCS, SA, PA | Triangular | A distributed hydrogen refueling station using glycerol steam reforming | |
28 | NIPCE | N/A | Directly coupled photovoltaic-electrolyzer system | |
29 | GBM, ARIMA, and MRJD | N/A | Normal, | Profitability assessment of offshore wind energy |
30 | MCS, SA | 1,000,000 | Normal | Biomass-to-liquid systems for the production of transportation fuels |
31 | NLOA, SA | N/A | Interval Uncertainties | Biodiesel Production |
32 | NIPCE, MCS | Normal | CO2 capture from enclosed environments | |
33 | SA | N/A | Normal, Uniform, Lognormal, Triangular | Butanol production from corn stover |
34 | SA | N/A | N/A | Very early stage CO2 capture technologies |
35 | SA, PM, MCS | 3000 | Normal, Lognormal | Producing high-value propylene glycol from low-value biodiesel glycerol |
36 | MCS, SA | Uniform | biodiesel production | |
37 | PM, SA | N/A | Very early stage CO2 capture technologies | |
38 | MCS | 1000 | Normal | Gas and electricity network integration and storage |
Reference | Sources of Uncertainty | |
---|---|---|
1 | [71] | Deterioration, hazards and the hazard responses of assets, costs volatility |
4 | [73] | Electricity prices, renewable energy sources, and load uncertainties |
5 | [74] | Model parameter and scenario uncertainties |
6 | [75] | Measurement sensors which provide the state information; activated dampers, which produce reactive forces and provide additional damping; and controllers, which control actuator outputs based on state measurements. |
9 | [76] | Energy price and electrical demand, wind speed |
12 | [77] | Capital and operating costs |
13 | [2] | |
14 | [78] | Uncertainties in the cost calculation |
17 | [79] | Energy price and electrical demand |
19 | [34] | Review |
22 | [80] | Uncertainty in the input data |
Model/Tool | Trials | Probability Distribution Function | Application | |
---|---|---|---|---|
1 | DNN | N/A | Different PDFs | Infrastructure asset management |
2 | SPA by MCS | 100,000 | Uniform | The service life of a viaduct (a bridge) |
3 | MCS | Slab track mono-block sleeper system for Indonesian urban metro railway | ||
4 | MSO | N/A | Normal, Weibull, Beta | Optimal reinforcement framework for distribution system |
5 | MCS, NPB | 1000 | Uniform | HDPE pipe alternatives |
6 | MCS | binomial, Uniform | High-performance control systems | |
7 | SFA, HOM by MCS | Four-story modern ductile reinforced concrete building in Los Angeles | ||
8 | ScA | N/A | Railway turnouts | |
9 | MSO | N/A | Normal, Beta, Weibull | Distribution system planning |
10 | MCS | Normal, Uniform, Lognormal, Triangular, Weibull | Uncertainty in LCCA | |
11 | FOTSE | N/A | Normal, Uniform, Lognormal | Highway bridge structures |
12 | ScA | N/A | Lignocellulose biomass solvent liquefaction and sugar fermentation to ethanol | |
13 | Review | N/A | Financial variables within the infrastructure | |
14 | LIDRA by MCS | Triangular | Green infrastructure | |
15 | ScA | N/A | Deep extra heavy oil green field | |
16 | MOO with RA | N/A | Normal | Maintenance for bridges |
17 | MOO | N/A | Normal | Distribution systems reinforcement |
18 | MCS | Normal, Triangular | Buildings’ energy efficiency measures | |
19 | Review | N/A | Long-range infrastructure | |
20 | MCS | 1000 | Uniform, Lognormal | Pavement industry |
21 | SA by MLFD + n-way ANOVA | N/A | Bridge | |
22 | PN + MCS | Weibull, Exponential, Lognormal, Normal | Real-time condition monitoring in railways |
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Barahmand, Z.; Eikeland, M.S. Techno-Economic and Life Cycle Cost Analysis through the Lens of Uncertainty: A Scoping Review. Sustainability 2022, 14, 12191. https://doi.org/10.3390/su141912191
Barahmand Z, Eikeland MS. Techno-Economic and Life Cycle Cost Analysis through the Lens of Uncertainty: A Scoping Review. Sustainability. 2022; 14(19):12191. https://doi.org/10.3390/su141912191
Chicago/Turabian StyleBarahmand, Zahir, and Marianne S. Eikeland. 2022. "Techno-Economic and Life Cycle Cost Analysis through the Lens of Uncertainty: A Scoping Review" Sustainability 14, no. 19: 12191. https://doi.org/10.3390/su141912191
APA StyleBarahmand, Z., & Eikeland, M. S. (2022). Techno-Economic and Life Cycle Cost Analysis through the Lens of Uncertainty: A Scoping Review. Sustainability, 14(19), 12191. https://doi.org/10.3390/su141912191