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Incorporating Life-Cycle Economic and Environmental Factors in Managerial Decision-Making

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Sustainable Supply Chains

Part of the book series: International Series in Operations Research & Management Science ((ISOR,volume 174))

Abstract

Recent environmental trends, including (1) an expansion of existing command and control directives, (2) the introduction of market-based policy instruments, and (3) the adoption of extended producer responsibility, have created a need for new tools to help managerial decision-making. To address this need, we develop a nonlinear mathematical programming model from a profit-maximizing firm’s perspective, which can be tailored as a decision-support tool for firms facing environmental goals and constraints. We typify our approach using the specific context of diesel engine manufacturing and remanufacturing. The approach allows the incorporation of traditional operations planning considerations—in particular, capacity, production, and inventory—together with environmental considerations that range from product design through production to product end of life. A current hurdle to implementing such a model is the availability of input data. We therefore highlight the need to involve all departments within businesses and for industrial ecologists and business managers to work together to implement meaningful decision models that are based on accurate and timely data and can have positive economic and environmental impact.

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Notes

  1. 1.

    that is, convex/linear/concave, and increasing/decreasing.

  2. 2.

    However, there is a sense that customers in developing markets are now gravitating towards similar preferences as customers in developed markets.

  3. 3.

    A reason mentioned by one of the managers interviewed is that customers in developed markets value uptime and the comparable performance afforded by remanufactured engines, while in developing markets where uptime is less critical and labor costs are low, repair is preferred as a less expensive alternative to buying a remanufactured engine.

  4. 4.

    A positive value of IP itn or IP itr indicates inventory on hand whereas a negative value indicates a backordered quantity.

  5. 5.

    An alternative way by which the companies interviewed influence the returns of cores is through an upfront “core charge” at the time of sale, which is refunded when the core is returned after use. This is analogous to a deposit-refund system, which has been successfully employed by various countries to encourage the recycling of products such as beverage containers and automotive batteries.

  6. 6.

    For expositional convenience, we assume that in any given period, only cores sold τ i periods ago will return for remanufacture, where τ i is the economic life of product i. A more general formulation could allow for core returns from sales in any prior period. We also noted from the interviews that there is limited difference in the economic lives of new and remanufactured versions of an engine, although there is an upper bound on the number of times a core can be remanufactured. For over the road truck engines, it is common to remanufacture a core up to five times.

  7. 7.

    Company B is not constrained by the market availability of allowances and also does not face a mandated limit on CO2 emissions. However, under the ETS, all CO2 emissions have to be accounted for by allowances that have market value. From our model, the shadow price associated with the voluntary emissions constraint can be used to assess the impact on profitability of voluntarily limiting CO2 emissions. The model can be easily adapted to accommodate a mandated limit and/or constrained market availability of allowances, if applicable.

  8. 8.

    AMPL® stands for “A Modeling Language for Mathematical Programming” (Fourer 2003). Demo versions of AMPL and MINOS are available at http://www.ampl.com

  9. 9.

    A core may return several times for remanufacture.

  10. 10.

    The emissions constraint is active in both cases.

  11. 11.

    Again, the emissions constraint is again active in cases.

  12. 12.

    When the design choice of remanufacturability equals zero for product i, the level of remanufacturability is just the inherent level Θ iB , implying that a remanufactured product i is almost entirely rebuilt.

  13. 13.

    The companies interviewed do not currently face mandated product take-back. Therefore disposal costs are only incurred for the non-remanufacturable portions of only those cores that return for remanufacture.

References

  • Bloemhof-Ruwaard JM, van Beek P, Hordijk L, Van Wassenhove LN (1995) Interactions between operational research and environmental management. Eur J Oper Res 85:229–243

    Article  Google Scholar 

  • EC (European Commission) (2001) Green paper on integrated product policy

    Google Scholar 

  • EC (European Commission) (2011) Policies. Retrieved from http://ec.europa.eu/environment/policy_en.htm. Accessed 30 Jan 2011

  • EPA (Environmental Protection Agency), United States (2005) Acid Rain Program: 2004 Progress Report

    Google Scholar 

  • Environmental Resources Management (2005) Study and assessment of available information for a pilot project on a teak garden chair: final report. Oxford, UK

    Google Scholar 

  • Fourer R, Gay DM, Kernighan BW (2003) AMPL: A modeling language for mathematical programming. Brooks/Cole-Thomson Learning, California

    Google Scholar 

  • Fourer R (2011) Nonlinear programming frequently asked questions. Retrieved from http://158.193.150.10/nonlinear-programming-faq.html. Accessed 30 Jan 2011

  • NEOS (Network-Enabled Optimization System) (2011) Optimization software guide. Retrieved from http://www.neos-guide.org/NEOS/index.php/Optimization_Software_Guide. Accessed 30 Jan 2011

  • Nokia Corporation (2005) Integrated product policy pilot project\!: life cycle environmental issues of mobile phones. Espoo, Finland

    Google Scholar 

  • Scheer D, Rubik F (eds) (2005) Governance of integrated product policy: in search of sustainable production and consumption. Greenleaf Publishing Ltd., Sheffield, UK

    Google Scholar 

  • Smith VM, Keoleian GA (2004) The value of remanufactured engines: life-cycle environmental and economic perspectives. J Ind Ecol 8(1–2):193–221

    Google Scholar 

  • Tukker A (2006) Identifying priorities for environmental product policy. J Ind Ecol 10(3):1–4

    Article  Google Scholar 

  • Tukker A, Jansen B (2006) Environmental impacts of iroducts: a detailed review of studies. J Ind Ecol 10(3):159–182

    Article  Google Scholar 

Download references

Acknowledgements

This chapter is a summarized version of: Subramanian, R, B. Talbot, S. Gupta. 2010. An Approach to Integrating Environmental Considerations within Managerial Decision Making. Journal of Industrial Ecology 14(3) 378–398.

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Correspondence to Ravi Subramanian .

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Appendices

Appendix 1: Product Features Assumed in the Base Data

Following is a brief overview of the characteristics of products 1 and 2 assumed in the numerical illustration:

  • Product 2 is more “complex” and requires more manufacturing and remanufacturing capacity per unit than product 1.

  • Fixed and variable costs of manufacturing and remanufacturing are respectively higher for product 2 than for product 1. Also, holding and backordering costs are higher for product 2.

  • Overall, customers of product 2 are less price sensitive and more quality conscious than customers of product 1. Customers of product 1 are less sensitive to the credit offered to induce core returns.

  • The market sizes for both new and remanufactured product 1 are respectively larger than those for product 2.

  • Emissions attributable to manufacturing and remanufacturing are respectively higher for product 2 than for product 1.

  • The performance standard is higher for product 2.

Appendix 2: Illustrative Results

Fig. 14.3
figure 3

Effect of environmental factors on product mix decision\(\left( \begin{aligned} \text{Plotted Values}&=\frac{\sum\nolimits_{t=1}^{10}{{{X}_{1t}}}}{\sum\nolimits_{i=1}^{2}{\sum\nolimits_{t=1}^{10}{({{X}_{it}}+{{Y}_{it}})}}},\,\frac{\sum\nolimits_{t=1}^{10}{{{X}_{2t}}}}{\sum\nolimits_{i=1}^{2}{\sum\nolimits_{t=1}^{10}{({{X}_{it}}+{{Y}_{it}})}}}, \nonumber\\& \frac{\sum\nolimits_{t=1}^{10}{{{Y}_{1t}}}}{\sum\nolimits_{i=1}^{2}{\sum\nolimits_{t=1}^{10}{({{X}_{it}}+{{Y}_{it}})}}},\,\frac{\sum\nolimits_{t=1}^{10}{{{Y}_{2t}}}}{\sum\nolimits_{i=1}^{2}{\sum\nolimits_{t=1}^{10}{({{X}_{it}}+{{Y}_{it}})}}}\end{aligned} \right)\)

Fig. 14.4
figure 4

Effect of environmental factors on design choice of performance \(\text{(Plotted Values}={{Q}_{10}},{{Q}_{20}})\)

Fig. 14.5
figure 5

Effect of environmental factors on design choice of remanufacturability \(\text{(Plotted Values}={{\Theta }_{10}},{{\Theta }_{20}})\)

Fig. 14.6
figure 6

Effect of environmental factors on core credit decision \(\left( \text{Plotted Values}=\frac{1}{10}\sum\nolimits_{t=1}^{10}{{{\Psi }_{1t}}},\,\frac{1}{10}\sum\nolimits_{t=1}^{10}{{{\Psi }_{2t}}} \right)\)

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Subramanian, R. (2012). Incorporating Life-Cycle Economic and Environmental Factors in Managerial Decision-Making. In: Boone, T., Jayaraman, V., Ganeshan, R. (eds) Sustainable Supply Chains. International Series in Operations Research & Management Science, vol 174. Springer, New York, NY. https://doi.org/10.1007/978-1-4419-6105-1_14

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