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

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GROUP 5, SESSION B: FOOD PRODUCTS 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 />

136. Analysis of material and energy flow associated with food<br />

production and consumption <strong>in</strong> Japan<br />

Naoki Yoshikawa 1,* , Koji Amano 1 , Koji Shimada 2<br />

1 Ritsumeikan University, College of Science and Eng<strong>in</strong>eer<strong>in</strong>g, Kusatsu, Japan, 2 Ritsumeikan University,<br />

College of Economics, Kusatsu, Japan, Correspond<strong>in</strong>g author. E-mail: n-yoshik@fc.ritsumei.ac.jp<br />

The potential load on the environment due to food systems has been discussed for years. In the exist<strong>in</strong>g research<br />

(Sh<strong>in</strong>do <strong>et</strong> al., 2010; Oda, 2006) on food systems, nitrogen accumulation <strong>in</strong> Japan is attributed to <strong>in</strong>crease<br />

<strong>in</strong> food import, <strong>in</strong>crease <strong>in</strong> chemical fertiliser <strong>in</strong>put, and changes <strong>in</strong> food consumption patterns. Life<br />

cycle th<strong>in</strong>k<strong>in</strong>g plays an important role <strong>in</strong> understand<strong>in</strong>g the comprehensive flow of energy, carbon, water,<br />

and other important materials associated with the systems for food production/consumption and biomass<br />

(food waste) utilisation. Such evaluation is required for estimat<strong>in</strong>g the comprehensive effect of future<br />

changes <strong>in</strong> consumption patterns, biomass policy, and agricultural technologies.<br />

In this study, the material flow associated with food systems, <strong>in</strong>clud<strong>in</strong>g waste treatment and recycl<strong>in</strong>g, is<br />

evaluated. In particular, we focus on the energy flow, <strong>in</strong>clud<strong>in</strong>g some <strong>in</strong>dicators that reflect the energy effectiveness<br />

of food systems and the utilisation level of biomass and food waste.<br />

The energy flows <strong>in</strong>vestigated <strong>in</strong> this study are related to the follow<strong>in</strong>g types of energy:<br />

1. Cumulative non-renewable energy<br />

2. Feedstock energy related to food and biomass<br />

3. Nutritionist's calories of food<br />

In this study, we evaluated 47 commodities of food. They were evaluated on the basis of the follow<strong>in</strong>g <strong>in</strong>dicators:<br />

a. Effectiveness of utilisation of food waste and co-products (EF-w)<br />

EP AE EC FSE2<br />

( EF w)<br />

<br />

FSE1<br />

Here, FSE1: Feedstock energy before treatment/utilisation of food waste and co-products; EP: Energy production<br />

via utilisation of food waste/co-products; AE: Alternative effect of material recycl<strong>in</strong>g; EC: Energy<br />

consumption dur<strong>in</strong>g treatment/utilisation of food waste and co-products; FSE2: Feedstock energy after treatment/utilisation<br />

of food waste and co-products.<br />

b. Energy effectiveness of food supply/consumption (EF-f)<br />

FE<br />

( EF f ) <br />

TI EP AE<br />

Here, TI: Cumulative non-renewable energy used; FE: Total energy <strong>in</strong>take for a food system<br />

The data perta<strong>in</strong><strong>in</strong>g to material flow and food transportation are collected from statistics, reports, and experts.<br />

The data perta<strong>in</strong><strong>in</strong>g to energy consumption dur<strong>in</strong>g food production are collected from papers or calculated<br />

from production-cost data.<br />

Fig. 1 shows the material flow of food products <strong>in</strong> Japan <strong>in</strong> 2005. The amount of <strong>in</strong>put from crop farm<strong>in</strong>g to<br />

animal farm<strong>in</strong>g is roughly the same as that to that from food manufactur<strong>in</strong>g. The flow from food manufactur<strong>in</strong>g<br />

to animal farm<strong>in</strong>g denotes the flow of rice and wheat bran. The <strong>in</strong>ternal flow related to crop farm<strong>in</strong>g consists<br />

of the <strong>in</strong>corporation of residues. The comprehensive approach employed <strong>in</strong> this study can be used to<br />

evaluate the effect of active utilisation (for example, bio<strong>et</strong>hanol production or compost<strong>in</strong>g of straw) by consider<strong>in</strong>g<br />

alternatives for organic materials used <strong>in</strong> farmlands and future change <strong>in</strong> gra<strong>in</strong> consumption, which<br />

are necessary for decid<strong>in</strong>g long-term policies.<br />

References<br />

Sh<strong>in</strong>do J., Okamoto K., Kawashima H., Konohira E, 2010. Nitrogen flow associated with food production<br />

and consumption and its effect on water quality <strong>in</strong> Japan from 1961 to 2005. Soil Sci. Plant Nutr., 55(4),<br />

pp. 532-545<br />

Oda K., 2006. Trends <strong>in</strong> nitrogen flow s<strong>in</strong>ce the 1980s <strong>in</strong> the food and feed system <strong>in</strong> Japan. Jpn. J. Soil Sci.<br />

Plant Nutr., 77, pp. 517-524 (<strong>in</strong> Japanese with an English abstract)<br />

861

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