(best examples and good practices) on household organic waste ...
(best examples and good practices) on household organic waste ... (best examples and good practices) on household organic waste ...
197 tool of Regional (
198 The encouragement of rational organization
- Page 157 and 158: 146 distributed either through gas
- Page 159 and 160: 148 mentioned in earlier. (Chemical
- Page 161 and 162: 150 Picture 39.: Public fuelling st
- Page 163 and 164: 152 The pumpable organic waste is b
- Page 165 and 166: 154 purchased by AGA and</s
- Page 167 and 168: 156 Picture 43.: Paper bag with hou
- Page 169 and 170: 158 (Table 8.): The Ljungsjöverket
- Page 171 and 172: 160 Figure 46.: Schematic operation
- Page 173 and 174: 162 9. United Kingdom The British S
- Page 175 and 176: 164 9.2. Waste quantities 2008 The
- Page 177 and 178: 166 9.3. Best practices</st
- Page 179 and 180: 168 The partners collect around 840
- Page 181 and 182: 170 Figure 51.: Quantity of waste c
- Page 183 and 184: 172 The company recycles wood, meta
- Page 185 and 186: 174 (26,650) of all households acro
- Page 187 and 188: 176 Recycling Bins which are emptie
- Page 189 and 190: 178 distance path. Since 1981, the
- Page 191 and 192: 180 The scheme in operation in Wye
- Page 193 and 194: 182 The method of composting the ga
- Page 195 and 196: 184 such as: Waste, Management (of
- Page 197 and 198: 186 heterogeneous in composition <s
- Page 199 and 200: 188 2000 2004 2005 2006 Total 63,24
- Page 201 and 202: 190 All domestic waste/recycling co
- Page 203 and 204: 192 The end product is made into a
- Page 205 and 206: 194 10.4.4. The Moerdijk incinerati
- Page 207: 196 11. Greece The Greeks Strategy
- Page 211 and 212: 200 Picture 55.: Panoramic View of
- Page 213 and 214: 202 Four (4) ballistic separators
- Page 215 and 216: 204 Picture 58.: View of Composting
- Page 217 and 218: 206 Picture 59.: Refinery Unit at A
- Page 219 and 220: 208 Unit for Treatment of Air Emiss
- Page 221 and 222: 210 Picture 60.: Chania MBT plant (
- Page 223 and 224: 212 A biological stabilization is t
- Page 225 and 226: 214 Picture 66.: Prototype composti
- Page 227 and 228: 216 Picture 69.: Psitallia sewage s
- Page 229 and 230: 218 Figure 56.: Process description
- Page 231 and 232: 220 Since ARTI-TZ started dissemina
- Page 233 and 234: 222 Picture 74.: Construction of AD
- Page 235 and 236: 224 biodegradables be isolated <str
- Page 237 and 238: 226 Picture 77.: The physical separ
- Page 239 and 240: 228 solution are fermented (e.g., s
- Page 241 and 242: 230 Picture 78.: Transportation of
- Page 243 and 244: 232 Picture 80.: Loofen company’s
- Page 245 and 246: 234 The interior parts of both the
- Page 247 and 248: 236 Figure 61.: Coway high capacity
- Page 249 and 250: 238 13.3.1. Coway model (WM05-A) In
- Page 251 and 252: 240 13.3.3. Coway model (WM03) The
- Page 253 and 254: 242 13.5. DUO Enterprise Ltd Food g
- Page 255 and 256: 244 References: Beyea, J., J. Cook,
- Page 257 and 258: 246 Flaga A., 2003 Sludge Drying, I
197<br />
tool of Regi<strong>on</strong>al (<str<strong>on</strong>g>and</str<strong>on</strong>g> Inter-regi<strong>on</strong>al) Waste Management Plan<br />
as the operati<strong>on</strong>al tool for <strong>waste</strong> management planning,<br />
determines the obligati<strong>on</strong>s of the management authorities <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
the Regi<strong>on</strong>s, regulates the permits of <strong>waste</strong> management<br />
operators <str<strong>on</strong>g>and</str<strong>on</strong>g> sets a time limit for the eradicati<strong>on</strong> of<br />
unc<strong>on</strong>trolled dumping.<br />
‣ Joint Ministerial Decisi<strong>on</strong> 29407/3508/2002 <strong>on</strong> sanitary l<str<strong>on</strong>g>and</str<strong>on</strong>g>fill<br />
of <strong>waste</strong>, transposing Council Directive 99/31 <strong>on</strong> l<str<strong>on</strong>g>and</str<strong>on</strong>g>fill of<br />
<strong>waste</strong>. The Decisi<strong>on</strong> inter alia sets strict operati<strong>on</strong>al guidelines<br />
for Sanitary L<str<strong>on</strong>g>and</str<strong>on</strong>g>fill Sites; m<str<strong>on</strong>g>and</str<strong>on</strong>g>atory processing of <strong>waste</strong> both<br />
at a nati<strong>on</strong>al <str<strong>on</strong>g>and</str<strong>on</strong>g> at L<str<strong>on</strong>g>and</str<strong>on</strong>g>fill Site level, establishes targets for<br />
reducing the amount of <strong>waste</strong> deposited by l<str<strong>on</strong>g>and</str<strong>on</strong>g>fill <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
provides for planning <str<strong>on</strong>g>and</str<strong>on</strong>g> licensing.<br />
‣ Law 2939/2001 <str<strong>on</strong>g>and</str<strong>on</strong>g> associated Presidential Decrees for the<br />
recycling of packaging <strong>waste</strong>, transposing Council Directive<br />
94/62/EC <strong>on</strong> packaging <strong>waste</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> related Directives <strong>on</strong> other<br />
<strong>waste</strong>s (used tires, end of life vehicles, <strong>waste</strong> oils, electrical <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
electr<strong>on</strong>ic <strong>waste</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> batteries). Quantitative targets are set for<br />
recovery <str<strong>on</strong>g>and</str<strong>on</strong>g> their enactment is primarily an implementati<strong>on</strong> of<br />
the ‘polluter pays’ principle, since producers of products <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
producers of <strong>waste</strong> are obligatorily involved in the set up <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
management of relevant Alternative Management Systems.<br />
(MEEC.,2010)<br />
It must be emphasized that Greeks policy does not have complete <strong>waste</strong><br />
management plan for green garden <strong>waste</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> kitchen <strong>waste</strong>. The instruments<br />
policy focuses in the use of l<str<strong>on</strong>g>and</str<strong>on</strong>g>fills for <strong>waste</strong> disposal <str<strong>on</strong>g>and</str<strong>on</strong>g> some recycling for a<br />
small part of the recyclable <strong>waste</strong> stream. The recycling centers though are very<br />
little in Greece today <str<strong>on</strong>g>and</str<strong>on</strong>g> this is a great difficulty for the public that has the will<br />
to participate. It must be also noted that incinerati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> anaerobic digesti<strong>on</strong><br />
are not widely used today in Greece for the treatment of <strong>waste</strong><br />
11.2.Greece policy objectives<br />
Al<strong>on</strong>g with the measure of Article 3 <str<strong>on</strong>g>and</str<strong>on</strong>g> 5 of the Directive, which they appear in<br />
the Directive, the 2003 Joint Ministerial Decisi<strong>on</strong> adds:<br />
The envir<strong>on</strong>mentally acceptable <str<strong>on</strong>g>and</str<strong>on</strong>g> safe disposal of <strong>waste</strong> that<br />
is not subject to recovery <str<strong>on</strong>g>and</str<strong>on</strong>g> <strong>waste</strong> remnants processing, with<br />
the aim of sustainability,