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Sustainable Food Production, Consumption, and the Generation of

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The amount <strong>of</strong> packaging waste sent to l<strong>and</strong>fills has gained considerable prominence as<br />

an environmental issue in Canada as a result <strong>of</strong> <strong>the</strong> 1990 National Protocol on Packaging (Labatt,<br />

2004). This protocol recommended specific packaging waste reduction targets for<br />

manufacturing sectors <strong>and</strong> was fur<strong>the</strong>r extended in 1995 to include regulations to enforce<br />

compliance with <strong>the</strong>se regulations. The goals outlined in <strong>the</strong> protocol include reducing<br />

packaging waste by 50 percent by 2000 through source reduction <strong>and</strong> exp<strong>and</strong>ed reuse (25<br />

percent) <strong>and</strong> recycling (25 percent). The National Task Force on Packaging, appointed by <strong>the</strong><br />

Canadian Council <strong>of</strong> Ministers <strong>of</strong> <strong>the</strong> Environment, indicates that packaging stewardship is <strong>the</strong><br />

“principle by which industries assume responsibility for <strong>the</strong> environmental impacts caused by <strong>the</strong><br />

packaging that <strong>the</strong>y introduce to <strong>the</strong> marketplace” (Sinclair & Fenton, 1996). The protocol <strong>and</strong><br />

its principles have not yet been formalized in Canadian legislation that creates obligations on<br />

businesses, <strong>and</strong> m<strong>and</strong>atory take-back provisions at <strong>the</strong> national level do not exist under <strong>the</strong><br />

protocol. Emphasis has been to require packaging stewards to contribute to <strong>the</strong> cost <strong>of</strong> municipal<br />

recycling programs (Hall, 2004), <strong>and</strong> in some provinces m<strong>and</strong>atory deposits on beverage<br />

containers has encouraged <strong>the</strong> take-back <strong>of</strong> containers (Sinclair & Fenton, 1996). The protocol<br />

does not impose specific waste-prevention performance obligations, but does focus on wastereduction<br />

as a primary goal. A Canadian Code <strong>of</strong> Packaging Practice has been developed as a<br />

guideline, ranging from no packaging, to reusable <strong>and</strong> recyclable packaging. Life cycle analysis<br />

is also included in <strong>the</strong> protocol, developed to identify <strong>the</strong> environmental impacts <strong>of</strong> packaging at<br />

all stages <strong>and</strong> to prepare action plans to minimize environmental impacts <strong>of</strong> <strong>the</strong> packaging. The<br />

Code <strong>of</strong> Preferred Canadian Packaging Practices was published in 1994 as a guide for industry in<br />

<strong>the</strong> design <strong>of</strong> products <strong>and</strong> <strong>the</strong> selection <strong>of</strong> packaging (Sinclair & Fenton, 1996). Despite <strong>the</strong>se<br />

guidelines <strong>and</strong> goals <strong>the</strong> National Packaging Protocol lacks <strong>the</strong> necessary stewardship policy <strong>of</strong><br />

industry obligation to reduce <strong>the</strong> impact <strong>of</strong> packaging on <strong>the</strong> environment.<br />

Since adopting <strong>the</strong> waste reduction goal <strong>of</strong> 50 percent, <strong>the</strong> Capital Regional District has<br />

commissioned four studies to assess <strong>the</strong> composition <strong>of</strong> <strong>the</strong> waste stream to <strong>the</strong> Hartl<strong>and</strong><br />

L<strong>and</strong>fill. The objectives <strong>of</strong> <strong>the</strong> l<strong>and</strong>fill study are to determine <strong>the</strong> overall waste composition by<br />

material type, characterizing <strong>the</strong> waste by sector, <strong>and</strong> reviewing trends from different areas <strong>of</strong> <strong>the</strong><br />

CRD. The most recent study, conducted in May 2005, revealed that approximately 30 percent <strong>of</strong><br />

<strong>the</strong> waste stream is composed <strong>of</strong> paper <strong>and</strong> plastic products (paper <strong>and</strong> paperboard 15.8 percent;<br />

plastics 13.8 percent). Although <strong>the</strong>se materials have not been identified to be solely coming<br />

from food products, it is highly suggestive that a significant amount derives from food packaging<br />

(Sperling, 2005). The composition study also identified waste disposal rates, revealing that each<br />

person within <strong>the</strong> CRD was responsible for 429 kg <strong>of</strong> l<strong>and</strong>filled waste in 2004 (CRD, 2005). A<br />

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