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Belgium (particularly Flanders) The provision of separate collections of certain household waste streams by the municipality has been required since the 1990s. At the kerbside, separate collection of paper/cardboard, vegetable, fruit and garden waste (VFG), biowaste (including food but excluding meat), glass, plastic bottles, metal packaging, drink cartons, other metals and textiles is the responsibility of the provinces. This provision follows Article 16 in Chapter 4 of the Belgian Decree concerning Prevention and Management of Waste Materials. In addition, one bring bank each for bottles and paper must also be provided for every 20,000 individuals. 640 The householder does not have a legal obligation to separately collect their waste, but is encouraged to do so by the Pay-As- You-Throw system that operates in Belgium, which charges a lower rate for separately-collected recyclables than for residual waste. Czech Republic A recent amendment to Waste Act 127/1997 in the Czech Republic now stipulates that by the end of 2010, municipalities must allow their householders to sourceseparate the following waste materials – paper/cardboard, plastics, glass, drinks cartons and biodegradable waste. 641 Packaging Act 477/2001 previously only encouraged such separation. The collections are organised by the local authority with both financial and public relations support from the Czech Republic’s producer responsibility organisation, Eko-Krom. No legal responsibility is placed on the householder to ensure that they separately collect recyclable materials. However, households and companies are incentivised to recycle, as they receive money for sorting their waste when they otherwise have to pay to dispose of their unsorted waste. 642 Denmark Denmark has employed a minimum recycling policy since 1990, when it introduced the separate collection of packaging glass. In 2004, the separate collection of paper/cardboard via kerbside collection schemes was also made mandatory for those municipalities with private built-up areas of greater than 1,000 inhabitants that were collecting less than 55 % of their total paper/cardboard potential in 2002. In addition, the householder in Denmark has a duty to sort their waste for separate collection. 643 640 H. Fogarty, L. Reid and H. Sprott (2008) International Review of Recycling Policies, Scottish Government Social Research. Available at http://www.scotland.gov.uk/Resource/Doc/231872/0063356.pdf 641 Ministry of the Environment of the Czech Republic (2008) [Online] Amendment to Waste Act- For Better Sorting and Recycling, [Accessed on 26 th September 2008], available at http://www.mzp.cz/__C12571F40024D359.nsf/$pid/mzpjkfohsria 642 Resource Recovery Forum (2006) The Czech Republic – Improvement in Waste Sorting, Second in EU. 643 Waste Centre Denmark (2007) Waste from Households, available at http://www.wasteinfo.dk/waste+and+collection+companies/sources+types+and+fractions/waste+fro m+households 546 29/09/09
England and Wales (United Kingdom) The Household Waste Recycling Act (2003) states that collection authorities in England and Wales must collect at the kerbside any two recyclable materials, either together or individually separated, from the remainder of the household waste stream. In addition, Barnet Borough Council provides one example where, alongside the Household Waste Recycling Act, additional responsibility for recycling is also placed on the householder. Barnet Borough Council introduced a compulsory recycling scheme in 2004, undertaking monitoring of household participation in the scheme and providing further contact and the threat of prosecution to households that failed to participate. This scheme has since been replicated in a number of other local authorities in England, and is discussed further in Section 34.4. Finland The separate collection of materials from the household waste stream is specified for paper and packaging in producer responsibility decrees 883/1998 and 962/1997 respectively. The systems for collection and recovery of paper and packaging are predominantly funded via producers, but provided by municipalities. However, where the separate collection of packaging is not justified from either an environmental or economic standpoint, the municipality also becomes financially responsible for the collection and may levy charges accordingly. Germany Producer responsibility for the separate collection of all types of packaging has been in place in Germany since 1991. The ‘Green Dot Scheme’ funds and provides local collection services for glass, paper/cardboard, plastics, tinplate, aluminium and composites (see Section 14.0). In addition, the Biowaste Ordinance (1998) sets out the requirement for municipalities to provide a separate collection of food and garden waste for householders to ensure that, following composting or fermentation, only material whose content of contaminants and potentially toxic elements is negligibly low can be used as a soil improver / amendment / potting medium. Householders in Germany are not strictly obligated to use the recycling services that are provided, but are encouraged to do so due to the Pay-As-You-Throw system (see Section 9.0). Hungary The separate collection of metals, plastic, paper, glass and food/garden waste from households began in Hungary in 2001. Such collections were linked to the ban on landfilling of organic waste and the environmental taxes (producer responsibility) placed on packaging. The local authority provides the collection service on behalf of the producers, though the majority of collection is via bring sites in Hungary rather than a kerbside collection. Italy Decree 22/97 and more recently Decree 152/06 set out specific targets for the collection of different waste streams in Italy, as well as the re-design of the packaging system towards producer responsibility. The waste streams to which targets apply, and which are thus heading towards mandatory source-separation, are paper/cardboard, glass, plastic, metal, biowaste, waste wood and textiles. In developing Waste Management Regional Plans, Local Administrations must define 547 International Review of Waste Policy: Annexes
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International Review of Waste Manag
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29/09/09
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ii 32.0 Levy on Waste Paints - Inte
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Glossary of Acronyms iv 29/09/09 AB
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vi 29/09/09 MSW Municipal solid was
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WASTE POLICIES - EXISTING FRAMEWORK
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3 departing from the hierarchy wher
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7. The inclusion of measures to pre
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7 Reuse; Reuse; Reuse; for example
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ut both grow. “Absolute decouplin
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1.4 Waste Recycling and Composting
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13 waste from these sources. Member
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Management (Food Waste) Regulations
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17 Such measures may include an acc
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19 � endeavour to reduce the use
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21 the European Union. Apart from l
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23 1. Member States shall set up a
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1.6 The Incineration Directive The
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1.7 The UNECE / Stockholm Conventio
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29 � Lindane to Annex A; � Pent
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2.0 Policy Instruments for Waste Ma
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33 agencies), and occasionally unde
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Mechanisms which operate through th
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identical, but in practice they hav
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39 that firms may still need to be
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41 � Recycling investment tax cre
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43 � Lack of communication betwee
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3.2 Issues with Current Situation I
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47 Greenstar claims that when the l
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3.3 Market Failure Currently in Ire
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51 franchise agreements reduce the
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as set out by the EU is limited in
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The beneficial network effects, or
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3.6 Recommendations What is often d
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59 which was designed to reflect a
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61 1. Whether the private sector ha
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4.0 The Role of Local Authorities 4
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that there have been no significant
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Local authorities have no obvious m
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introduced (and under which, they w
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71 International Review of Waste Po
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statutory waste management plans. I
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Each region has devised, and period
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uneconomic infrastructure and regio
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79 programme of measures to achieve
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Waste referred to in paragraph 1 is
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It is suggested that the regions sh
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6.0 Review of Irish Policy on Preve
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2. High quality data relating to wa
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company linked to the municipality
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infrastructure with a high emphasis
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93 and liaise with local authoritie
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To date the Market Development Grou
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Table 6-1: Generation of Municipal
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No adjustment was made to the proje
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whilst initiatives for unsolicited
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7.0 Pay-By-Use - Ireland 7.1 Outlin
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One of the waste management commitm
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eporting in the Annual National Was
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109 � In the absence of a kerbsid
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in case study areas, and an increas
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shifts/by separate staff, which in
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not reflected in reduced costs to c
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extent to which this compromises an
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and residual waste fee not so great
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121 � Choosing collection schemes
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8.3 Key Organisations Involved in I
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of material generated as waste (sin
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Figure 8-2: Balance of Costs and Be
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counterfactual. This type of approa
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131 � Bin-volume based (i.e. wher
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133 � Sack-based schemes with cha
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Table 8-4: Costs under Flat Rate Fe
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to this type of abuse given a) its
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the effect of certain variables on
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effects are not always verifiable i
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A French study (results shown in Fi
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Therefore, it would seem reasonable
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In many jurisdictions, where the pr
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149 “M&S [Marks & Spencer] sell t
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cost of residual waste treatment is
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eduction in waste quantities. The m
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A useful report on illegal dumping,
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Generally, the view which prevails
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9.0 Pay-by-use - Germany 9.1 Outlin
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Table 9-2: Charges for Residual Was
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163 Environmental Advisors (Sachver
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Figure 9-2: Quantities of Residual
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The bulky waste collections, Figure
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The net effect of these changes for
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the market such as waste sluices (e
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Prior to the system’s introductio
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The case of Schweinfurt is truly ou
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10.1.2 Approaches to Selective Coll
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10.4 Key Organisations Involved in
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FOST-Plus reports the following col
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to recover costs in such a way that
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11.0 Landfill Levy - Ireland 11.1 O
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187 � Landfill operators. Local A
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Table 11-2: Trends in Household Was
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191 • The effects of the Repak Pa
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positive. In 2007, of the €32,398
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11.8 Response from Public and Indus
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When the landfill levy was first in
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12.0 Producer Responsibility, Packa
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Although the European legislation d
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Table 12-1: Distribution of Respons
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205 (v) 15% by weight for wood, sup
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207 Companies that supply packaging
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Data from both Repak and self-compl
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Table 12-3: Average Compound Rate o
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The EEA report identifies the role
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The same study went on to highlight
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217 materials at source, effectivel
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and processors). In terms of the re
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Repak members, and non-major produc
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In their submission of information
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225 a. Direct costs of compliance (
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As noted above, there are differenc
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Directive. The current Regulations
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each year by an Industrial Structur
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generally cheaper to collect as it
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Netherlands Netherlands Netherlands
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Figure 13-1: Packaging Recycling an
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Country Country 241 % % of of colle
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It can be seen that against this me
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Figure 13-4: German License Fees Pa
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This is likely to have been depende
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Table 13-9: Financing Sources for R
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iv) Operational Operational Operati
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Table 14-2: Operators of Dual Syste
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provided by the DSD. Through the DS
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Following a poll in 2004, it became
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packaging has to be licensed by the
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15.0 Producer Responsibility - Flan
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265 � The industrial federations
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used to reimburse (inter)municipali
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Consumers can bring old and expired
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15.3.7 Waste Tyres The implementati
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273 � which treatment facilities
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VALORFRIT reimburses the municipali
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Figure 15-3: Belgian Packaging Wast
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279 � Widespread use of PBU; �
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Figure 15-4: Collection for Recycli
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283 � by January 2015, reuse and
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RECUPEL has continually sampled 5 %
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is currently being performed to ide
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Table 15-7 Green Dot Fees for Packa
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Moreover, the provisions of BEBAT n
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293 • All other types of oil gene
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procedure. It would be considerably
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16.0 Deposit Refund Systems - Inter
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same order as the cost savings from
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Country Country System System Year
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NT$13.01 per kg (US$0.39 at January
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collectors. These super-collectors
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A study in 2002 reviewed the outcom
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315 The existing studies show that
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Figure 16-2: Performance of US Stat
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Figure 16-5: Return Percentages of
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This is not to deny the possibility
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323 in in in packaging, packaging,
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harm caused by plastics in the mari
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327 Deposit containers would be tra
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have to be compared with the costs
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Of particular interest are some of
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Figure 16-7: Economic Cost per Tonn
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One of the concerns within Europe h
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(e.g. brought from Germany) so that
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Another pre-requisite, partly becau
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341 International Review of Waste P
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343 � Council of Environmental Ad
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step towards turning people away fr
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The sectors that profited from the
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349 � Willingness of the industry
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Green-Schools is run by An Taisce f
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18.3 When was the Policy Introduced
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355 � Green Homes: The Green Home
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Figure 18-1: Green Homes Research -
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composter. There are similar saving
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information on the various themes i
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Producers must register with the na
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365 • 2008: The Waste Management
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367 • Approved producer complianc
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the generation of electrical and el
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80% of WEEE primary processing take
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outed to charities and schools to d
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since June 2006 to guide and co-ord
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377 � Category 10 - Automatic dis
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table are the ‘2008 Review of Dir
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National National Register Register
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383 � The financial structures as
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purchased), though some offer it vo
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In order to facilitate their financ
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that product, the risk that the mat
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particular streams of WEEE. For exa
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Table 20-2 gives the amount of each
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demand that the receiving facilitie
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Table 20-3: Range of Total Costs fo
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kg), and a TV (15 kg), finding the
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20.10 Lessons Learned Administrativ
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Historical and ‘orphan’ waste,
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in 2012. Hence, the revision may im
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equipment. Furthermore producers do
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409 � 31 st December 2005: Almost
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411 � Regarding “new” WEEE (e
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ate of WEEE collected after the int
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A serious problem is the illegal ex
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22.0 Producer Responsibility, ELVs
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practice previously resulted in the
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421 of that producer's brand or for
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Ireland would be able to meet the r
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22.6.2 Environmental Benefits Assoc
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According to this paper: 427 � Th
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oth pieces of legislation is to res
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23.0 Producer Responsibility, ELVs
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driven the reclamation industry to
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23.2.7 Country-specific Characteris
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23.2.9 Country-specific Characteris
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In addition to the benefits associa
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key reports highlight the importanc
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Government in the form of additiona
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affected. In any event, the effect
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447 happen and because a reasonable
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24.2 Policy Context and Reason for
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time of writing, though it is under
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24.7 Environmental Benefits The Bat
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24.11 Social and Distributional Con
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25.0 Producer Responsibility, Batte
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459 � The competent authorities s
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1995. 537 This proliferation is pri
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463 � Countries where separate co
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This has been possible under a broa
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specific battery types, they might
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For automotive and industrial batte
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25.6.1.2 Retailer Take-back Schemes
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Table 25-5: Average Cost per Kilogr
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effectively be financed at a cost o
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Collection methods in Europe have p
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26.2 Reasons for the Policy Accordi
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26.3 Key Organisations Involved in
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Figure 26-2: German Battery Composi
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26.11 Evasion and Enforcement The c
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27.0 Plastic Bag Levy - Ireland 27.
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27.5.1 Evaluation Studies Available
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491 � Retailers find the effects
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ags in 2003, compared with 36% in 1
Page 507 and 508: 27.10 Social and Distributional Con
Page 509 and 510: 27.14 Lessons Learned 27.14.1 Gener
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Page 513 and 514: Table 28-2: The Organisation of the
Page 515 and 516: same period of 9.8%. 600 The Danish
Page 517 and 518: that only 8,000-10,000 businesses w
Page 519 and 520: 28.12 Lessons Learned The Danish sc
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Page 525 and 526: Considering the impact on the consu
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Page 529 and 530: and the Minister of Economic Affair
Page 531 and 532: Figure 30-1: Market Data on Single
Page 533 and 534: In order to achieve these targets,
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Page 537 and 538: 31.0 Plastic Bag Bans - Internation
Page 539 and 540: 31.5 Environmental Benefits Environ
Page 541 and 542: 32.0 Levy on Waste Paints - Interna
Page 543 and 544: The report concluded that total emp
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Page 547 and 548: private sector operators incur cost
Page 549 and 550: the organic waste fraction is no mo
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Page 553 and 554: 33.12 Complementary Policies Comple
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Page 557: paper/cardboard, metals (aluminium
Page 561 and 562: householder/small commercial sector
Page 563 and 564: government is responsible for the w
Page 565 and 566: Indeed, there are clearly synergies
Page 567 and 568: strengthened as the increased costs
Page 569 and 570: from 15.4 % in 1994 to 49.2 % in 20
Page 571 and 572: materials. 675 Thus complementary p
Page 573 and 574: 34.9 Effect of the Policy on Pricin
Page 575 and 576: � Strong industrial support via p
Page 577 and 578: municipality) unless it is composte
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Page 581 and 582: waste from manufacturing industries
Page 583 and 584: 36.2.1 Country-specific Characteris
Page 585 and 586: solid pre-requisite for the product
Page 587 and 588: 575 However, pending the adoption o
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Page 593 and 594: Table 36-2 Amount (‘000 tonnes) o
Page 595 and 596: separated kitchen and garden waste,
Page 597 and 598: 36.9 Effect of the Policy on Pricin
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Page 601 and 602: 589 risk of contamination with othe
Page 603 and 604: 37.4 Key Organisations Involved in
Page 605 and 606: 37.6.1 Environmental Benefits - Pre
Page 607 and 608: For proposed new composting facilit
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597 • The contaminated batch and
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Table 38-1: Junk Mail Policies Name
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them to increase efforts at suppres
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Table 38-3: Cost Savings from Junk
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39.0 Review of Irish Policy, Constr
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39.1.2 Recycling of C&D Waste - Gen
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40.3 When was the Policy Introduced
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out in national policy and in the i
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currently working in this area and
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goals that are shared by the Nation
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617 waste minimisation and recyclin
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41.7 Environmental Benefits The rev
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to 2 per cent of the landfill levy,
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623 � the name of the accountable
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625 initiatives. In other words, th
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environmental protection and optimu
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The NCDWC had a high level of suppo
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42.15 Lessons Learned For the purpo
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mandatory to varying degrees in Eng
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Japan 635 � Monitoring and auditi
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Hong Kong Industry surveying and in
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Table 43-1: Estimated Total Cost of
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43.8 Social and Distributional Cons
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short time frame over which it has
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In December 2007, Mr. John Gormley,
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647 of waste recovered at the facil
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44.13 Effect of the Policy on Prici
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implementing and managing the Proto
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46.0 Tax on Aggregates - Internatio
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The UK’s ‘Aggregate Levy’ app
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The following study is a comparison
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The intention to implement a landfi
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has encouraged innovation in recycl
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46.9.1 Quality Standards European S
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665 � if one fails to deregister,
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47.0 Product Standards for Aggregat
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It lays down regulations and standa
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has been recognised that recycled o
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48.0 Minimum Recycling Standards (C
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Companies are obliged to either sep
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Table 48-2: Construction and Demoli
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Construction and demolition project
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Belgium Following Article 16 in Cha
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The UK Environment Agency have buil
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during Construction Work came into
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codes. For example, Korea introduce
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In Japan, the lead contractor is re
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50.0 Minimum Recycling Standards (C
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POLICIES FOR RESIDUAL WASTE 693 Int
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695 advance the Commission of their
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have stabilised over the last six y
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ased instruments, or through regula
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Figure 51-4: Materials Captured (re
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200,000 tonnes, though some of this
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tonnes early in 2010, and as much a
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We discuss the matters further belo
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as was made clear above, the inclus
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51.4.2.3 Comment on Targets A conce
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seem that there is little or no bas
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It acknowledges the role of a numbe
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The proposed minimum pre-treatment
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719 The introduction of this measur
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The growing strength of these inter
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It goes on: 723 fully stabilised wa
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of electricity consumption from ren
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52.0 Policies Aimed at Discouraging
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promote cost effective means of res
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authorities work jointly on a strat
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Table 52-1: Summary of Measures by
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It is illuminating to note that in
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737 implemented to make treatment o
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environmental projects, and 45% is
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enclosure; and ii) municipal waste
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52.2.4.4 Finland In 1993, two years
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The objectives of the waste tax are
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52.2.4.10 Country-specific Characte
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meant to finance the Modernisation
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751 - 1995: Publication of a regula
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esidual treatments, and thus exempt
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incineration facilities produce ele
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There are several bands in this tax
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educe the quantity, or improve the
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761 announced in the November 1995
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52.4 Evaluation Studies Available I
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disposal costs necessarily would le
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discernible change in the trend in
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A report on Finnish waste managemen
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some cases, notably in the foundry
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absence of any form of waste tax. F
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Netherlands and Sweden. One might a
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777 ‘the amount of landfilled was
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consequences of an incineration tax
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52.5.6 Reduction in Incineration As
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environmental performance. The land
Page 797 and 798:
increase of between 30-100%. In Aus
Page 799 and 800:
emaining residual waste separately.
Page 801 and 802:
52.11 Evasion and Enforcement 52.11
Page 803 and 804:
Table 52-7: Summary of Measures by
Page 805 and 806:
� A clear rationale for the propo
Page 807 and 808:
overall costs of household waste ma
Page 809 and 810:
53.7 Effects on Technical Change /
Page 811 and 812:
the costs for disposal in municipal
Page 813 and 814:
801 � Old and expired medication.
Page 815 and 816:
Even with high landfill levies, the
Page 817 and 818:
Figure 54-4: Revenues from Flemish
Page 819 and 820:
54.11 Lessons Learned A complex sys
Page 821 and 822:
forge a genuinely ‘autonomous’
Page 823 and 824:
administrations is deemed to change
Page 825 and 826:
The desire to improve recycling per
Page 827 and 828:
Table 55-2: BMW Landfilled in Engla
Page 829 and 830:
55.6 Implementation Costs The inten
Page 831 and 832:
context of UK waste management wher
Page 833 and 834:
During 2007/08, the Environment Age
Page 835 and 836:
823 � Market-relevant information
Page 837 and 838:
need to consider not just ‘policy
Page 839 and 840:
In the above scenario, with capture
Page 841 and 842:
829 figures include nappies, as is
Page 843 and 844:
of the order 65% would reduce the q
Page 845 and 846:
56.2 Proposed Policies to Deal with
Page 847 and 848:
2) Incineration, Incineration, Inci
Page 849 and 850:
Table 56-1: Levies Proposed in RIA,
Page 851 and 852:
839 dramatically reduced by margina
Page 853 and 854:
4) Combustible waste 5) Waste excee
Page 855 and 856:
843 Ew means annual energy containe
Page 857 and 858:
OTHER POLICIES 845 International Re
Page 859 and 860:
57.2 Benefits of Green Procurement
Page 861 and 862:
what can, and what cannot be done,
Page 863 and 864:
In light of the renewed EU Sustaina
Page 865 and 866:
WRAP WRAP WRAP The greening of serv
Page 867 and 868:
57.4.3 Washington State Recycling a
Page 869 and 870:
ecommendation to do so in 2003 via
Page 871 and 872:
859 environment into public procure
Page 873 and 874:
has created a ‘level playing fiel
Page 875 and 876:
Article 6 of Regulation (EC) No.850
Page 877 and 878:
epresentations in relation to this
Page 879 and 880:
TARGET SETTING 867 International Re
Page 881 and 882:
specific actors, or failing that, t
Page 883 and 884:
policy has not been sufficiently re
Page 885 and 886:
873 ban only ensures the best use o
Page 887 and 888:
ecent reports from PROGNOS, the EEA
Page 889 and 890:
877 � Separate collection at the
Page 891 and 892:
achieves this rate country wide. So
Page 893 and 894:
Figure 59-3: Recycling Rates Around
Page 895 and 896:
Box 2: Recycling Centres in Upper A
Page 897 and 898:
Source: Eunomia (2007) Scoping new
Page 899 and 900:
Figure 59-8: Recycling Rates Achiev
Page 901 and 902:
absolute terms, i.e. in terms of we
Page 903 and 904:
verbrandbaar bouw- en sloopafval”
Page 905 and 906:
Figure 59-10: Flanders Residual Was
Page 907 and 908:
there does appear to have been a sl
Page 909 and 910:
Figure 59-12: Residual Waste per In
Page 911 and 912:
899 • The total ‘better than ta
Page 913 and 914:
GRANT FUNDING 901 International Rev
Page 915 and 916:
NDP 2000-2006 Waste management & wa
Page 917 and 918:
authority projects approved for ass
Page 919 and 920:
previously been available for such
Page 921 and 922:
Table 60-1: Environment Fund Income
Page 923 and 924:
een provided are available in the E
Page 925 and 926:
additional 10% must be met by anoth
Page 927 and 928:
Management Board (CIWMB) provide gr
Page 929 and 930:
in place. This is very often to ena
Page 931 and 932:
However, earmarking reduces flexibi
Page 933 and 934:
60.8 Approach to Evaluating Effects
Page 935 and 936:
There is evidence to suggest that e
Page 937 and 938:
925 � undertaking research on qua
Page 939 and 940:
60.12 Lessons Learned The Flemish P
Page 941 and 942:
929 might be axed in times of fundi
Page 943 and 944:
61.0 Appraisal of Residual Waste Tr
Page 945 and 946:
933 � Biogas for vehicle fuels?
Page 947 and 948:
at landfill and incineration, but a
Page 949 and 950:
handle. The choice of discount rate
Page 951 and 952:
Other key variables of importance i
Page 953 and 954:
treatment may give rise to damages,
Page 955 and 956:
1. As described above (for basic st
Page 957 and 958:
In addition to these UK focused stu
Page 959 and 960:
Table 61-1: Externality Values for
Page 961 and 962:
Transport externalities were incorp
Page 963 and 964:
arrive at a ‘best estimate’ of
Page 965 and 966:
than greenhouse gases. This is hard
Page 967 and 968:
production, but mainly the much low
Page 969 and 970:
Table 61-5: Summary of externality
Page 971 and 972:
The second report, on the potential
Page 973 and 974:
961 also given the fact that the st
Page 975 and 976:
61.4 Concluding Remarks on the Lite
Page 977 and 978:
965 associated with fuel used withi
Page 979 and 980:
kg kg CO2 CO2 eq. eq. 62.1.1.2 Glob
Page 981 and 982:
These results suggest a significant
Page 983 and 984:
kg kg SO2 SO2 eq. eq. The results s
Page 985 and 986:
62.1.2 Summary of Results In additi
Page 987 and 988:
DALY, DALY, kg kg chloroethylene ch
Page 989 and 990:
This is clearly true, not least sin
Page 991 and 992:
979 � We have used two ‘sets’
Page 993 and 994:
981 includes a dose-response model
Page 995 and 996:
983 assessments is that the blanket
Page 997 and 998:
our analysis, as well as those asso
Page 999 and 1000:
Table 63-2: Emissions Avoided Throu
Page 1001 and 1002:
the Swedish ORWARE model for contro
Page 1003 and 1004:
instantaneous collection rates for
Page 1005 and 1006:
etween 0.1 to 5 l CH4/m 2*h, so tha
Page 1007 and 1008:
include up to 150 substances includ
Page 1009 and 1010:
63.2.2.2 Landfill of Pre-treated Wa
Page 1011 and 1012:
63.3.1.1 Energy Use at Incineration
Page 1013 and 1014:
of a thermal efficiency of 84% and
Page 1015 and 1016:
1003 data obtained from plant opera
Page 1017 and 1018:
Table 63-13: Air Quality Externalit
Page 1019 and 1020:
1007 1. Energy used within the trea
Page 1021 and 1022:
1009 � Optimised biofilter; and
Page 1023 and 1024:
Table 63-18: Results with Low Exter
Page 1025 and 1026:
Table 63-19: Emissions Associated w
Page 1027 and 1028:
metal, the production of which cons
Page 1029 and 1030:
The two processes have similar envi
Page 1031 and 1032:
Eunomia. 1263 The principal climate
Page 1033 and 1034:
Figure 63-1: N-balance of a One Ste
Page 1035 and 1036:
It should be noted that bioaerosols
Page 1037 and 1038:
Table 63-27: Summary of Damage Cost
Page 1039 and 1040:
If the biogas is cleaned of impurit
Page 1041 and 1042:
the source of the natural gas, and
Page 1043 and 1044:
Table 63-34: Summary of Damage Cost
Page 1045 and 1046:
64.0 Costs of Household Waste Colle
Page 1047 and 1048:
Within the following section we ass
Page 1049 and 1050:
in place). It is possible to sense-
Page 1051 and 1052:
Table 64-4: Household Annual Collec
Page 1053 and 1054:
Table 64-6: Interpretation of WRAP
Page 1055 and 1056:
1043 � Refuse collected weekly in
Page 1057 and 1058:
The nature of these authorities the
Page 1059 and 1060:
64.5 Collection Modelling for Irela
Page 1061 and 1062:
ignore, however, is that whilst cos
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