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What is often reported in the literature is the cost of the producer responsibility scheme, sometimes referred to as the ‘financing need’, but the reality is that the costs of collection, sorting and reprocessing have to be shouldered by somebody, and the manner of implementation of producer responsibility, whilst it may affect the costs of implementation, probably has the most significant effect on the distribution of these costs across households / local authorities / businesses (those who pay for the collection of waste) and the obligated companies (those whose responsibility it is to demonstrate compliance). In essence, whatever the costs of the system, those which are not borne by ‘producers’ will have to be borne by other actors. The key financial actors are the waste collector and the producer responsibility organisation (representing the packaging manufacturers and ‘users’). In the German example, the waste collection is wholly paid for by the producer responsibility organisation (based on the fees charged to the manufacturers and users). The DSD’s 18,560 members paid 540 million Euros (£377.6 million) in 2003. With DSD receiving Green Dot fees for 4,495,692 tonnes of packaging waste, this makes for an average of over €120 per tonne. This figure includes the income from recycled material. Costs (licence fees) payable to DSD for packaging produced or sold in Germany are shown in Figure 13-4. In schemes such as the Japanese one, the collection is done at a cost to the municipality and a share of the recycling cost is borne by the producer responsibility organisation (to bridge the gap between the cost of the recycling process and the value of the recyclate). In schemes such as that operated in the UK, the vast majority of the cost of household collection is borne by taxpayers, whilst obligated companies contribute a fraction of the cost of collecting, sorting and reprocessing the material. The Table 13-7 shows the fees levied by material in some of the Green Dot schemes in Europe, all expressed in Euros per tonne. Where the producer responsibility scheme pays 100% of the collection and sorting of household waste there are generally higher fees to pay for these efforts. In addition, one notes that the fees tend to follow the relative costs of collection. Plastics, being a low bulk density material, and typically requiring post-collection sorting, are relatively more expensive to collect, even taking into account the relatively high revenues which can be obtained from sales of sorted polymers. In all countries shown, the fees for plastic are high, whereas the fees for glass are much lower, reflecting the lower costs, and in many parts of Europe, the reduced necessity for colour sorting and / or the potential to collect high proportions of glass through bring schemes. 244 29/09/09
Figure 13-4: German License Fees Payable to the Governing Authority per Tonne of Packaging Produced (effective 2007) Licence fee per tonne (euro) 245 1400 1200 1000 800 600 400 200 0 Plastic Other composites Beverage cartons Aluminium Tin-plate Paper and cardboard International Review of Waste Policy: Annexes Material Natural materials Glass Table 13-7: Fees by Material for Green Dot schemes in Europe (Euros per tonne) Material Material Belgium Belgium (2008) (2008) Germany Germany (2007) (2007) (2007) Austria Austria (2007) (2007) France France (2007) (2007) Spain Spain (2008) (2008) Greece Greece Greece (2005) (2005) (2005) * Glass 29.30 74 61 3.6 - 10 Plastics 159.40 1296 610 177.80 278-329 62 Steel 18.80 - - 22.60 61 20 Aluminium 33.90 733 370 45.30 102 8 Paper/card 15.70 175 105 122.10 51 50 *Plus a fee of 0.4 Euro cents per item Source: Pro Europe, 2008 This can be contrasted with the UK scheme where the fluctuation in PRN price is driven by the closeness to balance of supply and demand for PRNs as ‘evidence’. The fluctuating value of PRNs is shown in Figure 13-5. This shows, for example, how for most materials, following the end of the 2001 compliance year, PRN prices for most materials made no upward movement in the period to the end of 2003 as Government did not change the level of the targets from 2001 to 2003 (and everyone knew they would be met). In 2004, material specific rates were introduced, and the overall recovery requirement was much more closely aligned with the recycling requirement. This meant that energy recovery PRNs lost a considerable amount of their value, although those for recovery of energy from wood have remained somewhat higher. What
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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
Page 205 and 206: positive. In 2007, of the €32,398
Page 207 and 208: 11.8 Response from Public and Indus
Page 209 and 210: When the landfill levy was first in
Page 211 and 212: 12.0 Producer Responsibility, Packa
Page 213 and 214: Although the European legislation d
Page 215 and 216: Table 12-1: Distribution of Respons
Page 217 and 218: 205 (v) 15% by weight for wood, sup
Page 219 and 220: 207 Companies that supply packaging
Page 221 and 222: Data from both Repak and self-compl
Page 223 and 224: Table 12-3: Average Compound Rate o
Page 225 and 226: The EEA report identifies the role
Page 227 and 228: The same study went on to highlight
Page 229 and 230: 217 materials at source, effectivel
Page 231 and 232: and processors). In terms of the re
Page 233 and 234: Repak members, and non-major produc
Page 235 and 236: In their submission of information
Page 237 and 238: 225 a. Direct costs of compliance (
Page 239 and 240: As noted above, there are differenc
Page 243 and 244: Directive. The current Regulations
Page 245 and 246: each year by an Industrial Structur
Page 247 and 248: generally cheaper to collect as it
Page 249 and 250: Netherlands Netherlands Netherlands
Page 251 and 252: Figure 13-1: Packaging Recycling an
Page 253 and 254: Country Country 241 % % of of colle
Page 255: It can be seen that against this me
Page 259 and 260: This is likely to have been depende
Page 261 and 262: Table 13-9: Financing Sources for R
Page 263 and 264: iv) Operational Operational Operati
Page 267 and 268: Table 14-2: Operators of Dual Syste
Page 269 and 270: provided by the DSD. Through the DS
Page 271 and 272: Following a poll in 2004, it became
Page 273 and 274: packaging has to be licensed by the
Page 275 and 276: 15.0 Producer Responsibility - Flan
Page 277 and 278: 265 � The industrial federations
Page 279 and 280: used to reimburse (inter)municipali
Page 281 and 282: Consumers can bring old and expired
Page 283 and 284: 15.3.7 Waste Tyres The implementati
Page 285 and 286: 273 � which treatment facilities
Page 287 and 288: VALORFRIT reimburses the municipali
Page 289 and 290: Figure 15-3: Belgian Packaging Wast
Page 291 and 292: 279 � Widespread use of PBU; �
Page 293 and 294: Figure 15-4: Collection for Recycli
Page 295 and 296: 283 � by January 2015, reuse and
Page 297 and 298: RECUPEL has continually sampled 5 %
Page 299 and 300: is currently being performed to ide
Page 301 and 302: Table 15-7 Green Dot Fees for Packa
Page 303 and 304: Moreover, the provisions of BEBAT n
Page 305 and 306: 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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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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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
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27.10 Social and Distributional Con
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27.14 Lessons Learned 27.14.1 Gener
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499 � Higher rates of recycling;
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Table 28-2: The Organisation of the
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same period of 9.8%. 600 The Danish
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that only 8,000-10,000 businesses w
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28.12 Lessons Learned The Danish sc
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a government body, the revenue is
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511 � Lubricating oil; � Antifr
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Considering the impact on the consu
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30.0 Product Taxes - Belgium 30.1 O
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and the Minister of Economic Affair
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Figure 30-1: Market Data on Single
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In order to achieve these targets,
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ecycling targets is partly linked t
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31.0 Plastic Bag Bans - Internation
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31.5 Environmental Benefits Environ
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32.0 Levy on Waste Paints - Interna
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The report concluded that total emp
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33.0 Circular WPPR 17/08 - Ireland
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private sector operators incur cost
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the organic waste fraction is no mo
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investments are utilised, will be i
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33.12 Complementary Policies Comple
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34.0 Minimum Recycling Standards (H
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paper/cardboard, metals (aluminium
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England and Wales (United Kingdom)
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householder/small commercial sector
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government is responsible for the w
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Indeed, there are clearly synergies
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strengthened as the increased costs
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from 15.4 % in 1994 to 49.2 % in 20
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materials. 675 Thus complementary p
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34.9 Effect of the Policy on Pricin
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� Strong industrial support via p
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municipality) unless it is composte
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City of Portland, Oregon (USA) The
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waste from manufacturing industries
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solid pre-requisite for the product
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575 However, pending the adoption o
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where the abovementioned statutory
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36.5 Environmental Benefits The env
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Table 36-2 Amount (‘000 tonnes) o
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separated kitchen and garden waste,
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36.9 Effect of the Policy on Pricin
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product, especially when bioactive
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589 risk of contamination with othe
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37.6.1 Environmental Benefits - Pre
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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
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increase of between 30-100%. In Aus
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emaining residual waste separately.
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52.11 Evasion and Enforcement 52.11
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Table 52-7: Summary of Measures by
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� A clear rationale for the propo
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overall costs of household waste ma
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53.7 Effects on Technical Change /
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the costs for disposal in municipal
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801 � Old and expired medication.
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Even with high landfill levies, the
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Figure 54-4: Revenues from Flemish
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54.11 Lessons Learned A complex sys
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forge a genuinely ‘autonomous’
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administrations is deemed to change
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The desire to improve recycling per
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Table 55-2: BMW Landfilled in Engla
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55.6 Implementation Costs The inten
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context of UK waste management wher
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During 2007/08, the Environment Age
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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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