Submitted:
05 October 2023
Posted:
09 October 2023
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Abstract

Keywords:
1. Introduction
2. Contextualising about the importance of intangibles in sustaining smallholder family-based broiler production
3. Material and Methods
3.1. Mainstream economic cost model

3.2. Alternative economic cost model: Emergy synthesis as a way to include the intangibles
3.2.1. Estimative of cultural information transformity based on the Emergy theory
3.2.2. Transformity assessment for the broiler smallholder service with and without cultural information
3.2.3. Estimative of a holistic view-based payment for the broiler smallholder by their services

4. Results and Discussion
4.1. Valuing cultural information
| Solar | Em$Value | |||||
|---|---|---|---|---|---|---|
| Energy | Transformity | EMERGY | (emdollar/yr) | |||
| Item | Unit | (units/yr) | (sej/unit) | (sej/yr) | in millions | |
| Annual Flow | ||||||
| 1 | Renewable resource | J | 5.60 | 23,769.10 | ||
| 2 | Human metabolism | J | 2.71 | 2.06 | 5.60 | 23,769.10 |
| 3 | Information flow | J | 2.71 | 2.06 | 5.60 | 23,769.10 |
| Steady-state Storage | ||||||
| (sej) | (sej/J) | ( sej) | (emdollar) | |||
| in millions | ||||||
| 4 | Population | J | 2.02 | 9.13 | 1.85 | 784,380.31 |
| 5 | Culture information | J | 2.02 | 2.77 | 5.60 | 2,376,910.02 |
- 1 The Emergy of renewable resources for Santa Catarina State was obtained from data previously published by Demétrio [36].
- 2 Human metabolism.
- 3 Information flow:
- 4 Population:.
- 5 Culture information:.
4.2. Emergy synthesis of broiler smallholders
4.3. The impact of culture information on the broiler production Emergy indicators
4.4. The imbalance between the estimated economic-based and environmental-based payments
4.5. General insights into quantifying the value
- Market valuation: This form of valuation involves the analysis of prices and recent transactions of similar products or assets on the market. The idea is to use concrete data from real transactions to establish a value based on market conditions.
- Valuation by cost: This method aims to determine value based on production costs, including materials, labour, depreciation, operating expenses and other expenses. In the industry, the cost of production is a good indicator of the value of the product.
- The valuation of environmental costs based on Emergy (without services or information) uses only a physical inventory of the resources used in its accounting. This type of valuation takes into account the energy embodied in natural resources and considers their quantity and quality; Emergy makes it possible to assess the environmental costs associated with production. The Emergy valuation approach (without services and information) can be useful especially when the focus is on analysing the physical resources, production technologies and geographical aspects (such as rainfall and land use) involved in a given production system.
- The valuation of the environmental cost in Emergy with services (including the money paid in environmental accounting) offers a more comprehensive view and may be more appropriate when it is desired to understand the social, economic and environmental impacts of the organisation in a more complete and integrated way.
- Evaluating the “(eco)cost” in Emergy by including information can take into account scientific knowledge, technology, intellectual capital and culture, which are essential to the operation and functioning of production systems. Including information in the estimation of Emergy aims to reflect the contribution of these elements and allows for a more comprehensive assessment of the efficiency and sustainability of the production system. This approach is highly relevant in Emergy-based environmental accounting as it recognises that production depends not only on tangible physical resources but also on the knowledge, skills and information available. Therefore, Emergy-based environmental accounting that includes information seeks to understand and quantify both the physical and intangible aspects involved in the production and functioning of economic and ecological systems.
5. Conclusions
References
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| Solar | Em$ | |||||||
|---|---|---|---|---|---|---|---|---|
| Data | Transformity | EMERGY | Value (sej/$.yr) | |||||
| Item | Unit | (units/yr) | (sej/unit) | ( sej/yr) | 2018 | % | ||
| ENVIRONMENT RESOURCES (considering kinetic wind and Earth cycle Emergy contrib.; Emergy per person) | ** | 0.37 | 1.55 | 0.00 | ||||
| RESOURCES CONSUMPTION | 19,828.42 | 84,161.36 | 78.20 | |||||
| Food | J | 3.06 | 1.52 | a | 46.45 | 197.15 | 0.18 | |
| Electric power | J | 1.12 | 6.45 | b | 0.07 | 0.31 | 0.00 | |
| Fuel | J | 2.92 | 1.41 | c | 411.73 | 1,747.58 | 1.62 | |
| Natural gas | J | 9.66 | 2.90 | b | 0.28 | 1.19 | 0.00 | |
| Ethanol | J | 2.12 | 1.41 | c | 2.99 | 12.70 | 0.01 | |
| Information | ||||||||
| Cultural information | J | 5.77 | 2.77 | Table 1 | 15,961.45 | 67,748.08 | 62.95 | |
| Educational information | J | 9.84 | 3.46 | b | 3,405.45 | 14,454.36 | 13.43 | |
| MONETARY FLOW | ||||||||
| Wage | USD | 2.22 | 2.36 | e | 5,228.87 | 22,193.86 | 20.62 | |
| PRODUCED WASTE | ||||||||
| Solid waste treatment | J | 1.30 | 2.29 | f | 298.31 | 1266.19 | 1.18 | |
| OUTPUTS* | ||||||||
| Product | ||||||||
| Work | J | 1.47 | 1.73 | 25,355.97 | 107,622.96 | 100.00 | ||
| Coproducts | ||||||||
| Sleep | J | 5.50 | 4.61 | 25,355.97 | ||||
| Leisure | J | 3.82 | 6.64 | 25,355.97 | ||||
| w/ Ci | w/o Ci | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Name of Index | Expression | Unit | Total | Agroindustry | Producer | Total | Agroindustry | Producer | ||||
| Emergy | R+N+F | sej/yr | 1.29 | 9.22 | 3.66 | 1.13 | 9.22 | 2.07 | ||||
| Broiler UEV | Y / Ep | J | 4.72 | 3.38 | 1.34 | 4.14 | 3.38 | 7.58 | ||||
| Litter (as fertilizer) UEV | Y / Ep | J | 3.68 | 2.64 | 1.05 | 3.23 | 2.64 | 5.91 | ||||
| Renewable resource from nature | (R) / (R+N+F) | % | 18% | 22% | 6% | 20% | 22% | 11% | ||||
| Non-renewable resource from nature | N/(R+N+F) | % | 0% | 0% | 0% | 0 | 0% | 0% | ||||
| Non-renewable purchase resources | (F)/(R+N+F) | % | 82% | 78% | 94% | 80% | 78% | 89% | ||||
| Environmental Loading Ratio | (N+FN)/(R+FR) | sej/sej | 4.65 | 3.49 | 15.01 | 3.95 | 3.49 | 8.04 | ||||
| Emergy Investment Ratio | (F) / (N + R) | sej/sej | 5,496.66 | - | 1,562.05 | 4,815.69 | - | 881.08 | ||||
| Emergy Yield Ratio | Y / (FN) | sej/sej | 1.22 | 1.29 | 1.07 | 1.25 | 1.29 | 1.12 | ||||
| Emergy Sustainability Index | EYR / ELR | sej/sej | 0.26 | 0.37 | 0.07 | 0.32 | 0.37 | 0.14 | ||||
| Emergy Exchange Ratio | Y / ($) (sej/$) | sej/sej | 2.08 | 1.49 | 0.59 | 1.82 | 1.49 | 0.33 | ||||
| Emergy Exchange Ratio (producer) | Yproducer / ($/bird) (sej/$) | 1.00 | 1.00 | |||||||||
| if EER = 1.0 | USD/bird | 1.61 | 0.91 | |||||||||
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