(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 ...
105 already recycled a relatively large proportion of municipal waste
106 has been specified only for some product types such as packaging
- Page 65 and 66: 54 pulled through an induced draft
- Page 67 and 68: 56 the non-biodegradables a
- Page 69 and 70: 58 3.3.8. Bioreactor land</
- Page 71 and 72: 60 4. Materials Sorting Processes 4
- Page 73 and 74: 62 Plastics Plastics (Fiqure.32) po
- Page 75 and 76: 64 separate containers. There are a
- Page 77 and 78: 66 The sorting of recyclables may b
- Page 79 and 80: 68 4.5. Mechanical and</str
- Page 81 and 82: 70 glass breakage on the tipping fl
- Page 83 and 84: 72 within solution under the influe
- Page 85 and 86: 74 material, and t
- Page 87 and 88: 76 changing pole configuration or w
- Page 89 and 90: 78 4.7. Mechanical Biological Treat
- Page 91 and 92: 80 Biological processing compartmen
- Page 93 and 94: 82 equivalence considerations <stro
- Page 95 and 96: 84 5.2. Waste streams considered in
- Page 97 and 98: 86 Figure 27.: Percentage of munici
- Page 99 and 100: 88 6.Italy The Italian strategy Ita
- Page 101 and 102: 90 Italy also set targets for colle
- Page 103 and 104: 92 (Figure 30.). The quality of com
- Page 105 and 106: 94 a controlled environment with wa
- Page 107 and 108: 96 Picture 11.: The Corteolona plan
- Page 109 and 110: 98 The building in the foreground h
- Page 111 and 112: 100 compost their garden waste. The
- Page 113 and 114: 102 The total amount of waste produ
- Page 115: 104 7. Germany 7.1. Waste managemen
- Page 119 and 120: 108 7.3. Best practices</st
- Page 121 and 122: 110 The installation has different
- Page 123 and 124: 112 The sludge is placed into a lar
- Page 125 and 126: 114 Picture 22.: Air mixing mechani
- Page 127 and 128: 116 Finally the dried sludge is bee
- Page 129 and 130: 118 process treats the wastes as co
- Page 131 and 132: 120 consumption is about 0.7 x106 k
- Page 133 and 134: 122 Picture 30.: The heat exchanger
- Page 135 and 136: 124 used for the construction of l<
- Page 137 and 138: 126 International’. In the Drum D
- Page 139 and 140: 128 Picture 34.: Delivery crane in
- Page 141 and 142: 130 industrial processes, where <st
- Page 143 and 144: 132 industry, mixes the waste <stro
- Page 145 and 146: 134 8. Sweden The Swedish strategy
- Page 147 and 148: 136 joint committee or local govern
- Page 149 and 150: 138 upon the number of collected fr
- Page 151 and 152: 140 2004 2005 2006 2007 2008 Hazard
- Page 153 and 154: 142 Anaerobic digestion also produc
- Page 155 and 156: 144 Hässleholm 12,300 10,120 Karls
- 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
105<br />
already recycled a relatively large proporti<strong>on</strong> of municipal <strong>waste</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> l<str<strong>on</strong>g>and</str<strong>on</strong>g>filled<br />
approximately 40 %.(EEA Report No 7/.,2009)<br />
German <strong>waste</strong> policy follows the EU’s <strong>waste</strong> hierarchy, with preventi<strong>on</strong> as the<br />
first priority, followed by material recovery <str<strong>on</strong>g>and</str<strong>on</strong>g> energy recovery, depending <strong>on</strong><br />
which is better for the envir<strong>on</strong>ment. Objectives for managing municipal <strong>waste</strong><br />
also focus <strong>on</strong> avoiding c<strong>on</strong>taminati<strong>on</strong> of <strong>waste</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> ensuring treatment <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
l<str<strong>on</strong>g>and</str<strong>on</strong>g>filling of <strong>waste</strong> that is not recovered. (EEA Report No 7/.,2009)<br />
The two most important fracti<strong>on</strong>s of <strong>waste</strong> are (paper <str<strong>on</strong>g>and</str<strong>on</strong>g> bio<strong>waste</strong>). Am<strong>on</strong>g<br />
the most efficient acti<strong>on</strong>s for the treatment of these types of <strong>waste</strong>, are:<br />
composting or anaerobic biological treatment; <str<strong>on</strong>g>and</str<strong>on</strong>g> limiting the <strong>organic</strong> c<strong>on</strong>tent<br />
of l<str<strong>on</strong>g>and</str<strong>on</strong>g>filled <strong>waste</strong>. (EEA Report No 7/.,2009)<br />
Germany set a target in 1999 for stopping l<str<strong>on</strong>g>and</str<strong>on</strong>g>filling <str<strong>on</strong>g>and</str<strong>on</strong>g> treating residues by<br />
2020. This is an ambitious <str<strong>on</strong>g>and</str<strong>on</strong>g> very difficult to achieve objective <str<strong>on</strong>g>and</str<strong>on</strong>g> includes,<br />
recovering <strong>waste</strong> incinerati<strong>on</strong> residues <str<strong>on</strong>g>and</str<strong>on</strong>g> further developing treatment<br />
technologies such as sorting <str<strong>on</strong>g>and</str<strong>on</strong>g> MBT. (EEA Report No 7/.,2009)<br />
Except for recycling targets for packaging <strong>waste</strong>, very few quantitative targets<br />
have been set at federal levels. Those that exist generally apply to paper <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
cardboard. In additi<strong>on</strong> to the targets of the 2004 Packaging Directive, the paper<br />
industry has committed itself to recycle around 80 % of <strong>waste</strong> paper in a<br />
voluntary agreement. (EEA Report No 7/.,2009)<br />
7.2. The German policy<br />
Germany is a federal republic made up of sixteen federal states (Bundesländer).<br />
Resp<strong>on</strong>sibility for <strong>waste</strong> management <str<strong>on</strong>g>and</str<strong>on</strong>g> envir<strong>on</strong>mental protecti<strong>on</strong> is shared<br />
between the nati<strong>on</strong>al government, the federal states <str<strong>on</strong>g>and</str<strong>on</strong>g> the local authorities.<br />
The nati<strong>on</strong>al Ministry of Envir<strong>on</strong>ment sets priorities, participates in the<br />
enactment of laws <str<strong>on</strong>g>and</str<strong>on</strong>g> oversees strategic planning, informati<strong>on</strong> <str<strong>on</strong>g>and</str<strong>on</strong>g> public<br />
relati<strong>on</strong>s <str<strong>on</strong>g>and</str<strong>on</strong>g> defines requirements for <strong>waste</strong> facilities. Each federal state adopts<br />
its own <strong>waste</strong> management act c<strong>on</strong>taining supplementary regulati<strong>on</strong>s to the<br />
nati<strong>on</strong>al law, e.g. c<strong>on</strong>cerning regi<strong>on</strong>al <strong>waste</strong> management c<strong>on</strong>cepts <str<strong>on</strong>g>and</str<strong>on</strong>g> rules <strong>on</strong><br />
requirements for disposal. There is no nati<strong>on</strong>al <strong>waste</strong> management planning in<br />
Germany. Instead, each federal state develops a <strong>waste</strong> management plan for its<br />
area. (EEA Report No 7/.,2009)<br />
According to the producer resp<strong>on</strong>sibility principle, which is a core tenet of<br />
German <strong>waste</strong> legislati<strong>on</strong>, the producer of a product generally still has<br />
resp<strong>on</strong>sibility for the product when it becomes <strong>waste</strong>. However, this principle