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International Review of Waste Management Policy - Department of ...

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DIFTAR charges are intended to replace part <strong>of</strong> the municipal taxation on income, as<br />

well as a flat rate municipal waste tax. Low income individuals <strong>of</strong>ten do not pay<br />

income taxes so it is possible that waste associated costs may be increased for this<br />

section <strong>of</strong> society. However, social correction mechanisms have been introduced by<br />

different municipal authorities to reduce disproportionate effects. Specific exclusions<br />

apply for families with newborn children to account for diaper waste (the use <strong>of</strong><br />

reusable diapers is only marginally introduced in Flanders). Low income families and<br />

families with newborn children usually get a number <strong>of</strong> residual waste bags for free,<br />

e.g. 20 to 40 bags per year.<br />

Ideologically, DIFTAR ought to replace an equal income generated from surtaxes or<br />

municipal waste taxes. However, several municipalities have introduced DIFTAR and<br />

only partially reduced municipal taxes, thus leading to a general increase in the<br />

revenue take from households. This diminishes the social acceptance <strong>of</strong> DIFTAR and,<br />

more generally, <strong>of</strong> environmental taxation.<br />

10.10 Complementary Policies<br />

DIFTAR systems should be combined with policy measures that ensure alternative<br />

avenues for individual materials. These alternatives need to be easily accessible for<br />

individuals. Minimal standards for separate collection have been deemed necessary<br />

in Flanders, ensuring that when DIFTAR schemes are introduced, households’<br />

propensity to resort to fly tipping is minimised. <strong>Waste</strong> minimisation (and ease <strong>of</strong><br />

recycling) policy measures need also to be targeted at producers and distributors.<br />

DIFTAR ought also to be combined with initiatives to enhance the home treatment <strong>of</strong><br />

biowaste. One way <strong>of</strong> doing this, which is used in many Flemish authorities, is the<br />

introduction <strong>of</strong> charging for the biowaste container. Home treatment can be realised<br />

by promoting home composting or ‘chicken projects’. Several municipalities in<br />

Flanders actively promote the ownership <strong>of</strong> chickens because they eat leftover<br />

biowaste. An average consumption <strong>of</strong> 150g/day kitchen waste or 50 kg/year can be<br />

reached. The Animal By-Product Regulation needs to be observed when feeding<br />

chickens with kitchen waste. The material is not considered to be waste, as it is not<br />

discarded, and it is in principle fit for human consumption. However, three important<br />

principles needs to be respected:<br />

182<br />

� The food chain has to be controlled through to the end consumer;<br />

� Cannibalism must be avoided; and<br />

� Feeding with animal products is forbidden.<br />

The effects on the private chicken owner are that no meat, fish or meat products may<br />

be given to the chicken, and no kitchen waste with meat (like spaghetti sauce). The<br />

eggs and the meat <strong>of</strong> the chicken are only destined for private consumption.<br />

Policies that make residual waste more expensive help to encourage diversion <strong>of</strong><br />

material up the waste hierarchy.<br />

10.11 Effect <strong>of</strong> the <strong>Policy</strong> on Pricing <strong>of</strong> Resources / Services<br />

In principle, waste charging policies ought to be financially neutral for the government<br />

or municipality, as long as PBU systems replace existing flat fee taxation. The aim is<br />

29/09/09

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