Submitted:
18 September 2024
Posted:
19 September 2024
You are already at the latest version
Abstract
Keywords:
1. Introduction
1.1. Sustainable Whisky Production
1.2. Analytical Hierarchy Process model used for Risk Assessment
2. Materials and Methods
2.1. Qualitative Analysis – Identify Common Risk Factors from Case Studies
2.2. Quantitative Analysis – Using AHP Model to Assess Risks in Whisky Industry
2.2.1. Step 1. Hierarchy Construction
2.2.2. Step 2. Pairwise Comparison
- means that Criterion 1 is moderately more important than Criterion 2.
- means that Criterion 2 is less important than Criterion 1.
2.2.3. Step 3. Checking the Consistency Ratio
3. Results
- (a) The sub-criteria with the highest environmental risk were determined to be climate change affecting ingredients availability (0.558), and water usage (0.186), while the lowest environmental risk was biodiversity risk (0.041). Waste management (0.116) and energy consumption (0.098) are very closely ranked. These findings explain the extensive focus in research literature to developing new technological alternatives that mitigate these risks. The CR value of 0.074 (the highest among to other risk categories results from this study) implies that the prioritization may change, depending on the unique context under which certain distilleries may operate.
- (b)In the operational risk class, supply chain disruption (0.507) is perceived to hold highest impact towards sustainable whisky production, followed by equipment failure leading to production delays (0.263), and non-compliance with technological parameters during manufacturing phases (0.152). Based on the experts’ experience, unqualified personnel (0.078) had the lowest perceived contribution to operational risk. The consistency ration CR of 0.004 indicates excellent consensus on the impact and priority of the sub-risks that were assessed.
- (c) The weights of the sub-criteria in the technological innovation risk category have been determined to be frequent technological updates (0.591) and intellectual property risks related to new technologies (0.333). Since the distilleries that participated in this study are built after 2000s, majority of them rely on newer technology and adhere to ISO guidelines. Therefore, the sub-risk lack of investment in circular technologies (0.075) is ranked relatively low for the selected target group. However, there are many frequent technological advances that can be adopted to address water usage, waste management and other environmental risks. The intellectual property implication of such solutions are often the driving factors of successful marketing strategies that satisfy customer preferences for reduced carbon footprint technologies, increase brand awareness of being sustainable and help distilleries gain competitive advantage. The consistency ration CR of 0.014 indicates consensus on the impact and priority of the sub-risks that were assessed.
- (d) In the economic risk class, inefficient use of resources (0.461) is by far the most important sub-criteria impacting sustainable whisky production, closely followed by the cost of implementing sustainable practices (0.305) and financial penalties for non-compliance with standards and regulations (0.187). The cost of innovation (0.046) is ranked lower than other economic sub-criteria, since the sample population have less of an innovation and technological gap to address compared to traditional whisky distilleries that, for example, would need to buy equipment to modernize their production facilities. The consistency ration CR of 0.016 indicates consensus on the impact and priority of the sub-risks that were assessed.
- The main food safety risk associated with sustainable whisky production are chemical risks (0.671) such as contamination of grains – raw material with mycotoxins, pesticides, residual chemical from cleaning processes, followed by physical risks (0.265) – entry of foreign objects during technological process and biological risks (0.063) –contamination of grains with bacteria, fungi, etc. Biological risk has the lowest weight because of the nature of alcoholic beverage production, as the pathogenic microorganisms cannot survive the high alcohol content (min. 40% alc. vol.) present in whiskies . The consistency ration CR of 0.030 indicates consensus on the impact and priority of the sub-risks that were assessed.
4. Discussion
4.1. Limitations of the AHP Research
4.2. Recommendations for Future Research
5. Conclusions
6. Patents
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Country | Year Opened | Whisky type (Grain Type) |
Production (liters) |
|---|---|---|---|
| Austria | 2009 | Single Malt Whisky (Barley) | ~90,000 |
| Belgium | 2004 | Single Malt Whisky (Barley) | ~60,000 |
| Czech Republic | 2008 | Single Malt Whisky (Barley) | ~70,000 |
| Estonia | 2015 | Single Malt Whisky (Barley) | ~30,000 |
| Finland | 2014 | Rye Whisky (Rye) | ~100,000 |
| France | 2015 | Malt Whisky (Barley), and Experimental (various grains) | ~100,000 |
| Germany | 2016 | Single Malt Whisky (Barley) | ~200,000 |
| Hungary | 2002 | Malt Whisky (Barley) | ~30,000 |
| Italy | 2012 | Malt Whisky (Barley), Rye Whisky | ~90,000 |
| Lithuania | 2010 | Grain Whisky (Rye, Wheat) | ~50,000 |
| Luxembourg | 2004 | Single Malt Whisky (Barley) | ~20,000 |
| Netherlands | 2000 | Single Malt Whisky (Barley), Rye Whisky, and Corn Whisky (Maize) | ~150,000 |
| Norway | 2014 | Single Malt Whisky (Barley) | ~30,000 |
| Poland | 2005 | Single Malt Whisky (Barley) | ~50,000 |
| Portugal | 2018 | Malt Whisky (Barley) | ~20,000 |
| Slovakia | 2001 | Grain Whisky (Corn, Wheat, Barley) | ~100,000 |
| Spain | 2002 | Malt Whisky (Barley) | ~100,000 |
| Switzerland | 2005 | Single Malt Whisky (Barley) | ~100,000 |
| Intensity scale | Definition |
|---|---|
| 1 | indicates equal importance |
| 3 | indicates moderate importance |
| 5 | indicates strong importance |
| 7 | indicates very strong importance |
| 9 | indicates extreme importance |
| 2,4,6,8 | intermediate values between the two adjacent judgments. |
| Size of matrix (n) | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 |
| Random Average CI (RI) | 0 | 0 | 0.52 | 0.89 | 1.11 | 1.24 | 1.35 | 1.40 | 1.45 | 1.49 |
| Main risk | Local Weight (LW) |
Sub-criteria | Local Weight (LW) | Global Weight (GW) | Rank |
|---|---|---|---|---|---|
| Environmental (E) | 0.369 | (E1) Climate change1 | 0.558 | 0.247 | 1 |
| (E2) Biodiversity loss | 0.041 | 0.018 | 13 | ||
| (E3) Water usage | 0.186 | 0.082 | 4 | ||
| (E4) Energy consumption | 0.098 | 0.044 | 8 | ||
| (E5) Waste management | 0.116 | 0.051 | 7 | ||
| Operational (O) | 0.253 | (O1) Supply chain disruption | 0.507 | 0.139 | 2 |
| (O2) Equipment failure2 | 0.263 | 0.072 | 5 | ||
| (O3) Non-compliance3 | 0.152 | 0.041 | 9 | ||
| (O4) Unqualified personnel | 0.078 | 0.021 | 12 | ||
| Technological innovation (TI) | 0.181 | (TI1) Lack of investment4 | 0.075 | 0.015 | 15 |
| (TI2) Intellectual property risks5 | 0.333 | 0.065 | 6 | ||
| (TI3) Frequent technological updates | 0.592 | 0.115 | 3 | ||
| Economical (Ec) | 0.101 | (Ec1) Cost of innovation | 0.047 | 0.003 | 18 |
| (Ec2) Cost of implementing sustainable practices | 0.305 | 0.017 | 14 | ||
| (Ec3) Financial penalties6 | 0.187 | 0.010 | 16 | ||
| (Ec4) Inefficient use of resources | 0.461 | 0.025 | 10 | ||
| Food safety (FS) | 0.096 | (FS1) Physical risk7 | 0.265 | 0.009 | 17 |
| (FS2) Chemical risk8 | 0.672 | 0.023 | 11 | ||
| (FS3) Biological risk9 | 0.063 | 0.002 | 19 |
| Main risk categories | Λmax | CI | CR | Decision (CR≤0.1) |
|---|---|---|---|---|
| Environmental (E) | 5.334081 | 0.083520 | 0.074270 | Consistent |
| Operational (O) | 4.013335 | 0.004445 | 0.004888 | Consistent |
| Technological innovation (TI) | 3.014153 | 0.007077 | 0.014767 | Consistent |
| Economical (Ec) | 4.044563 | 0.014854 | 0.016333 | Consistent |
| Food safety (FS) | 3.029071 | 0.014536 | 0.030330 | Consistent |
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