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

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PARALLEL SESSION 7A: CONSUMERS 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 />

key socio-demographic param<strong>et</strong>ers for cause and effect relationship tests for WTP option (yes/no) and WTP<br />

value.<br />

3. Results<br />

3.1. Environmental impact of different broiler production systems<br />

Table 1. Life cycle impact assessment of energy use, global warm<strong>in</strong>g potential, acidification potential and<br />

eutrophication potential associated with the production of one tonne live weight of broiler chickens from<br />

three different Malaysian hous<strong>in</strong>g systems. For the impact of each hous<strong>in</strong>g system, the values <strong>in</strong> a row show<br />

the absolute amount followed by, <strong>in</strong> italics, the percentage of the total impact accounted for by that particular<br />

activity<br />

594<br />

Broiler feedrelated<br />

Breeder feedrelated<br />

On-farm <strong>in</strong>puts/<br />

emission<br />

Fertiliser<br />

Credit<br />

Energy use (MJ)<br />

Closed house system 8,946 74.2% 828 6.9% 2,280 18.9% -3,679 8,375<br />

Open house system 10,417 83.42% 1,104 8.9% 908 7.3% -3,945 8,484<br />

Semi-<strong>in</strong>tensive system 12,892 84.9% 1,065 7.0% 1,236 8.1% -4,807 10,386<br />

Global Warm<strong>in</strong>g Potential (kg CO2 eq. on a 100 year timescale)<br />

Closed house system 1,603 82.7% 142 7.3% 192 9.9% -680 1,257<br />

Open house system 1,866 86.7% 190 8.8% 95 4.4% -784 1,367<br />

Semi-<strong>in</strong>tensive system 2,309 87.6% 179 6.8% 148 5.6% -889 1,747<br />

Acidification Potential (kg SO2 eq.)<br />

Closed house system 12.8 67.8% 1.2 6.5% 4.9 25.7% -2.0 16.8<br />

Open house system 14.9 68.5% 1.6 7.5% 5.2 24.0% -2.3 19.4<br />

Semi-<strong>in</strong>tensive system 18.4 70.1% 1.4 5.2% 6.5 24.6% -2.7 23.6<br />

Eutrophication Potential (kg PO4 eq.)<br />

Closed house system 7.9 76.0% 0.7 7.0% 1.8 17.0% -0.3 10.0<br />

Open house system 9.2 76.1% 1.0 8.0% 1.9 15.9% -0.4 11.7<br />

Semi-<strong>in</strong>tensive system 11.4 78.6% 0.7 5.0% 2.4 16.4% -0.4 14.1<br />

After consider<strong>in</strong>g the offs<strong>et</strong> values from manure as fertiliser, the SI system recorded the largest burdens <strong>in</strong><br />

the categories of Energy Use, GWP, AP and EP with 10,386 MJ, 1,747 kg of CO2 eq., 24 kg of SO2 eq. and<br />

14 kg of PO4 eq. respectively (see Table 1). This was followed by the OH system, with the CH system be<strong>in</strong>g<br />

the least environmentally impact<strong>in</strong>g, produc<strong>in</strong>g approximately 14 to 28% lower impacts than the SI system.<br />

Broiler feed-related <strong>in</strong>puts accounted for approximately three quarters of the impact values (with 67.8 to<br />

82.7% for the CH system, 68.5 to 86.7% for the OH system and 70.1 to 87.6% for the SI system), followed<br />

by other on-farm <strong>in</strong>puts and emissions from the manure and chickens, while breeder feed-related <strong>in</strong>puts contributed<br />

the smallest environmental impact. Breeder feed-related <strong>in</strong>puts contributed approximately 5 to 9%<br />

to environmental impacts, with the OH system produc<strong>in</strong>g the highest impacts compared to other systems,<br />

s<strong>in</strong>ce this system required four breeder hens to produce one FU. The CH system required an energy <strong>in</strong>put of<br />

approximately four times that of the SI and OH systems, largely due to heat<strong>in</strong>g and ventilation requirements.<br />

However, the SI system produced much higher burdens from emissions, especially the categories of acidification<br />

and eutrophication potentials, ma<strong>in</strong>ly due to the large amount of manure generated throughout the<br />

extended production cycle of 12 weeks.<br />

3.2. Estimation of consumers’ WTP for chicken-HRE<br />

For the first objective of the CVM survey, respondents were asked to evaluate the relative environmental<br />

impact result<strong>in</strong>g from the six major economic activities of Malaysia. On average 48.1% of respondents considered<br />

the manufactur<strong>in</strong>g sector as be<strong>in</strong>g the major contributor of negative impacts on environmental quality,<br />

followed by the chemical <strong>in</strong>dustry (31.9%), transportation (10.5%), agriculture (5.7%), m<strong>in</strong><strong>in</strong>g (2.9%)<br />

and construction (1.4%). Almost two-thirds of respondents (63.3%) stated that the efforts taken by the both<br />

the Government and the <strong>in</strong>dustry <strong>in</strong> these six economic activities to prevent environmental degradation were<br />

less than their rate of development. Meanwhile, half of respondents stated that quality was the ma<strong>in</strong> factor<br />

<strong>in</strong>fluenc<strong>in</strong>g their decision when purchas<strong>in</strong>g chicken meat, and 40% of respondents believed that saf<strong>et</strong>y and<br />

price were essential <strong>in</strong> their decision. Over half of those surveyed believed that environmental problems<br />

aris<strong>in</strong>g from poultry production were generated from the production stage (<strong>in</strong>clud<strong>in</strong>g hous<strong>in</strong>g system)<br />

whereas only 5% considered that production of feed gave the negative impact.<br />

Total

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