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

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

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PLENARY SESSION 1: FOOD 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 />

116<br />

Compar<strong>in</strong>g environmental impacts of end-of-life treatments of food<br />

waste<br />

Carbotech AG, environmental consult<strong>in</strong>g, 4002 Basel, Switzerland<br />

Correspond<strong>in</strong>g author. E-mail: m.zschokke@carbotech.ch<br />

Mischa Zschokke * , Thomas Kägi, Fredy D<strong>in</strong>kel<br />

The goal of this study was to compare the environmental burden of landfill<strong>in</strong>g food waste with three alternative biowaste treatments<br />

“compost<strong>in</strong>g”, “anaerobic digestion” and “municipal solid waste <strong>in</strong>c<strong>in</strong>eration”. The life cycle <strong>in</strong>ventories for anaerobic digestion and<br />

compost<strong>in</strong>g <strong>in</strong>cludes a new approach to account for benefits <strong>in</strong> us<strong>in</strong>g biowaste as a fertiliser substitute. Depend<strong>in</strong>g on the impact<br />

assessment m<strong>et</strong>hod used, the rank<strong>in</strong>g of the different treatment m<strong>et</strong>hods tend to vary. But tak<strong>in</strong>g <strong>in</strong>to account the range of uncerta<strong>in</strong>ty<br />

the three exam<strong>in</strong>ed treatment m<strong>et</strong>hods show comparable environmental impacts. Landfill<strong>in</strong>g of food waste <strong>in</strong> contrast results <strong>in</strong> a<br />

much higher environmental impact compared to the other three treatment m<strong>et</strong>hods. As all <strong>in</strong>vestigated treatment m<strong>et</strong>hods show similar<br />

results, the decision on which technique to use can be based on other factors such as economics, available <strong>in</strong>frastructure or even<br />

on the composition and nature of the food waste because different m<strong>et</strong>hods are favourable for treatment.<br />

Keywords: biowaste, benefits of biowaste, <strong>in</strong>c<strong>in</strong>eration, compost<strong>in</strong>g, anaerobic digestion<br />

1. Introduction<br />

Every year huge quantities of edible food end up <strong>in</strong> landfills worldwide (e.g. 7 million tonnes <strong>in</strong> the<br />

United K<strong>in</strong>gdom and 34 million tonnes <strong>in</strong> the United States (Eunomia 2006, WRAP 2007a and 2007b, EPA<br />

2011). Roughly one third orig<strong>in</strong>ates from producers/supply cha<strong>in</strong>, one third from r<strong>et</strong>ail and the f<strong>in</strong>al third<br />

from regular households (Sibrián <strong>et</strong> al., 2006, Parfitt <strong>et</strong> al., 2010,).<br />

In addition to the costs for disposal, these landfills generate large amounts of greenhouse gases. Landfill<br />

gas emissions are one of the largest anthropogenic sources of m<strong>et</strong>hane especially because of food waste<br />

(Adhikari 2006). In the United States food waste now represents the s<strong>in</strong>gle largest component of municipal<br />

solid waste reach<strong>in</strong>g landfills and <strong>in</strong>c<strong>in</strong>erators, and generates more than 16 percent of all m<strong>et</strong>hane emissions<br />

<strong>in</strong> that country (EPA <strong>2012</strong>). Not only could the direct emissions from landfills be decreased by reduc<strong>in</strong>g the<br />

amount of landfilled food waste but the use of alternate m<strong>et</strong>hods for treatment of food waste could further<br />

reduce the environmental impact.<br />

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

2.1 Goal and Scope<br />

The goal of this study was to compare the environmental burden of landfill<strong>in</strong>g food waste with three alternative<br />

biowaste treatments “compost<strong>in</strong>g”, “anaerobic digestion” and “municipal solid waste <strong>in</strong>c<strong>in</strong>eration”<br />

(MSWI) as described <strong>in</strong> D<strong>in</strong>kel <strong>et</strong> al., (2011).<br />

The functional unit used <strong>in</strong> the presented study is 1 kg of treated food waste. The applied <strong>in</strong>ventory m<strong>et</strong>hodology<br />

is derived from the eco<strong>in</strong>vent version 2.2 guidel<strong>in</strong>es (Frischknecht R. and Jungbluth N., 2007). Data<br />

for the <strong>in</strong>vestigated m<strong>et</strong>hods of treatment are based on exist<strong>in</strong>g eco<strong>in</strong>vent version 2.2 processes and were<br />

extended and updated with new values <strong>in</strong> the follow<strong>in</strong>g fields:<br />

emissions from anaerobic digestion: updated values for N2O, CO2, CH4 and NH3 <strong>in</strong> the digestion<br />

process and from spread<strong>in</strong>g digestate<br />

emissions from compost<strong>in</strong>g: updated values for N2O, CO2, CH4 and NH3<br />

TCDD-2,3,7,8-emissions <strong>in</strong> municipal solid waste <strong>in</strong>c<strong>in</strong>eration were adjusted to account for the current<br />

regulatory values<br />

the heat<strong>in</strong>g value of biowaste was adapted accord<strong>in</strong>g to own calculations to be suitable to model <strong>in</strong>c<strong>in</strong>eration<br />

<strong>in</strong> municipal solid waste <strong>in</strong>c<strong>in</strong>eration plants<br />

2.2 Inventory data<br />

In particular, the emissions for compost<strong>in</strong>g and anaerobic digestion were updated by field measurements<br />

and generally show lower values than previously reported. The m<strong>et</strong>hane emissions <strong>in</strong> the current version of<br />

eco<strong>in</strong>vent are overestimated by about 5 times.<br />

The used values for the biological treatment m<strong>et</strong>hods are summarised <strong>in</strong> the follow<strong>in</strong>g tables:

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