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LCA Food 2012 in Saint Malo, France! - Manifestations et colloques ...

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PARALLEL SESSION 1B: TOWARDS LIFE CYCLE SUSTAINABILITY ASSESSMENT 8 th Int. Conference on <strong>LCA</strong> <strong>in</strong> the<br />

Agri-<strong>Food</strong> Sector, 1-4 Oct <strong>2012</strong><br />

Life cycle cost<strong>in</strong>g of farm milk production – cost assessment of carbon<br />

footpr<strong>in</strong>t mitigation strategies<br />

Anne C. Assel<strong>in</strong>-Balençon * , Olivier Jolli<strong>et</strong><br />

School of Public Health (SPH), University of Michigan, 6622 SPH Tower, 1415 Wash<strong>in</strong>gton Heights, Ann Arbor, Michigan 48109-<br />

2029, United States<br />

Correspond<strong>in</strong>g author. E-mail: aassel<strong>in</strong>@umich.edu<br />

ABSTRACT<br />

One po<strong>in</strong>t of concern with the present Life Cycle Cost<strong>in</strong>g (LCC) approach is the arbitrary choice of the discount rate, which does not<br />

differentiate b<strong>et</strong>ween economic objectives and effective economic performance. Here, we propose an alternate m<strong>et</strong>hodology and<br />

apply it to two examples. A multi-year m<strong>et</strong>hod is used to simultaneously assess cumulated cost and impact variations. On the cost<br />

aspect, our m<strong>et</strong>hod assesses the n<strong>et</strong> present value (NPV) of the <strong>in</strong>vestment, as well as its <strong>in</strong>ternal rate of r<strong>et</strong>urn (IRR). We graphically<br />

compare those values to the cumulated environmental impact over the same period. The case studies focus on two energy sav<strong>in</strong>g<br />

alternatives on the farm and the <strong>in</strong>stallation of a digester. The <strong>in</strong>ternal rate of r<strong>et</strong>urn is a synth<strong>et</strong>ic m<strong>et</strong>ric of economic performance<br />

that avoids the arbitrary choice of a discount rate; this <strong>in</strong>dicator can be compared to an economic objective for decision mak<strong>in</strong>g purposes.<br />

Keywords: life cycle cost<strong>in</strong>g, discount rate, life cycle assessment<br />

1. Introduction<br />

Agriculture is a significant contributor to environmental impacts. A study by the University of Arkansas<br />

showed that 70% of the carbon footpr<strong>in</strong>t of US milk occurs at or before the farm gate (Thoma <strong>et</strong> al. <strong>2012</strong>).<br />

Milk is also a significant contributor to water use and land use, as shown by an on-go<strong>in</strong>g comprehensive milk<br />

life cycle study (University of Michigan, 2011).<br />

For decision mak<strong>in</strong>g, however, environmental impact assessment should be consistently complemented<br />

by an economic assessment. Environmental Life Cycle Cost<strong>in</strong>g (LCC), as described <strong>in</strong> the <strong>in</strong>troduction of<br />

Ciroth <strong>et</strong> al. (2008), comb<strong>in</strong>es environmental and economic assessments over the life cycle of the product:<br />

“Environmental life cycle cost<strong>in</strong>g summarizes all costs associated with the life cycle of a product that are<br />

directly covered by one or more of the actors <strong>in</strong> that life cycle; these costs must relate to real money flows.<br />

[…] A complementary life cycle assessment (<strong>LCA</strong>), with equivalent system boundaries and functional units,<br />

is also required, Environmental LCC is performed on a basis analogous to that of <strong>LCA</strong> […].” One of the<br />

most useful features of a comb<strong>in</strong>ed <strong>LCA</strong> and LCC approach is <strong>in</strong> the assessment of a mitigation scenario<br />

relative to a reference situation, enabl<strong>in</strong>g comparison of both costs and environmental impact b<strong>et</strong>ween these<br />

scenarios.<br />

For products with a life time longer than a year, a multi-year assessment has to be performed. Regard<strong>in</strong>g<br />

the cost part, “the use of discounted cash flows for money flows occurr<strong>in</strong>g at different times with<strong>in</strong> a product<br />

life cycle is commonly applied” (Huppes <strong>et</strong> al., 2008) .<br />

One po<strong>in</strong>t of concern of that approach is the arbitrary choice of the time value for money, also known as<br />

the discount rate, which does not differentiate b<strong>et</strong>ween economic objectives and effective economic performance.<br />

On the other hand, the environmental performance (e.g. 20% CO2 saved) is clearly estimated and<br />

reported <strong>in</strong>dependently from the environmental objective ( e.g. objective of 10% m<strong>in</strong>imum impact reduction).<br />

Huppes <strong>et</strong> al. (2008) acknowledges this fact and recommends sensitivity analysis and peer review.<br />

In this paper, we propose an alternate m<strong>et</strong>hodology to avoid the use of discount rate, focus<strong>in</strong>g on three<br />

ma<strong>in</strong> objectives:<br />

1. Elaborate a cost m<strong>et</strong>ric that is <strong>in</strong>dependent of any arbitrary discount rate,<br />

2. Compare consistently environmental and cost performance cumulated over the lif<strong>et</strong>ime of the<br />

equipment<br />

3. Apply the approach to two case studies to d<strong>et</strong>erm<strong>in</strong>e the carbon footpr<strong>in</strong>t and cost performances of<br />

energy sav<strong>in</strong>g equipment and of an anaerobic digester.<br />

2. M<strong>et</strong>hods<br />

2.1. LCC Actors and perspectives<br />

Life cycle cost<strong>in</strong>g summarizes all the costs of the product. It can bear different po<strong>in</strong>ts of view. If we consider<br />

milk, consumers will be concerned with the product cost <strong>in</strong> the r<strong>et</strong>ail shop, and with the costs associated with<br />

milk storage and preparation (e.g. refrigeration cost). The dairy farmer, on the other hand, will account for<br />

the price of feed, dairy <strong>in</strong>frastructure, and equipment, try<strong>in</strong>g to lower his milk production costs and maximize<br />

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