(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 ...
67 Picture 6.: Typical
68 4.5. Mechanical
- Page 27 and 28: 16 The duration of the composting p
- Page 29 and 30: 18 Figure 7.: Principal emissions f
- Page 31 and 32: 20 2.2 Anaerobic Digestion (AD) 2.2
- Page 33 and 34: 22 4. Finally, methanogenic organis
- Page 35 and 36: 24 If the proper conditions cannot
- Page 37 and 38: 26 Considerations such as the desig
- Page 39 and 40: 28 to the viscosity of the feed, th
- Page 41 and 42: 30 The Netherlands
- Page 43 and 44: 32 Heavy metals in digestate usuall
- Page 45 and 46: 34 3. Large scale biodegradable was
- Page 47 and 48: 36 power and 1,200
- Page 49 and 50: 38 filtration or electrostatic prec
- Page 51 and 52: 40 acceptable range, but reduce the
- Page 53 and 54: 42 Rotary kiln furnaces Rotary kiln
- Page 55 and 56: 44 It has been processed an
- Page 57 and 58: 46 Heavy metals can be grouped into
- Page 59 and 60: 48 choices for a commercial plant w
- Page 61 and 62: 50 Gasification (Figure.19) using o
- Page 63 and 64: 52 AC plasma CO2 plasma arc Microwa
- 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: 66 The sorting of recyclables may b
- 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 and 116: 104 7. Germany 7.1. Waste managemen
- Page 117 and 118: 106 has been specified only for som
- 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
68<br />
4.5. Mechanical <str<strong>on</strong>g>and</str<strong>on</strong>g> Manual Operati<strong>on</strong><br />
There are two types of sorting processes which are used today in <strong>waste</strong> recovery<br />
facilities. The Manual sorting, which produce higher quality product from the<br />
mixed <strong>waste</strong> stream, but is not so efficient because of the very slow processing<br />
rates. Manual sorting also yields more rejected materials <str<strong>on</strong>g>and</str<strong>on</strong>g> misses a<br />
c<strong>on</strong>siderable porti<strong>on</strong>, for example HDPE <str<strong>on</strong>g>and</str<strong>on</strong>g> PET plastics <strong>waste</strong> stream due to<br />
the inability to target certain c<strong>on</strong>tainer shapes. If a plastic substance cannot be<br />
distinguished with the naked eye, it cannot be efficiently manually sorted <str<strong>on</strong>g>and</str<strong>on</strong>g><br />
will therefore not be separated. Furthermore, it is extremely difficult for a<br />
sorter to distinguish between PVC <str<strong>on</strong>g>and</str<strong>on</strong>g> PET plastics, but these resins can be<br />
separated more quickly <str<strong>on</strong>g>and</str<strong>on</strong>g> accurately with the use of automated systems.<br />
(Dubanowitz., 2000) The same happens to kitchen <strong>waste</strong> which cannot be<br />
separated from the mixed <strong>waste</strong> stream as easy as in source separati<strong>on</strong>.<br />
When there are bulky items such as (appliances, furniture, etc.) <str<strong>on</strong>g>and</str<strong>on</strong>g> specified<br />
c<strong>on</strong>taminants (e.g., hazardous <strong>waste</strong>) must be separated prior to mechanical<br />
separati<strong>on</strong> process in order for the further treatment of these materials to be<br />
efficient. Manual separati<strong>on</strong> is also applicable to the removal of c<strong>on</strong>taminants<br />
from source-separated materials. (C<strong>on</strong>taminants refers to comp<strong>on</strong>ents other<br />
than the materials specified for separate collecti<strong>on</strong>.). (Tchobanoglous <str<strong>on</strong>g>and</str<strong>on</strong>g> Kreith.,<br />
2002)<br />
manual separati<strong>on</strong> (Picture 7.) of materials usually includes a sorting belt or<br />
maybe a table, which c<strong>on</strong>tains the mixed <strong>waste</strong> stream. Workers are stati<strong>on</strong>ed<br />
at the right <str<strong>on</strong>g>and</str<strong>on</strong>g> at the left of the belt for the materials separati<strong>on</strong>. Hoppers or<br />
other receptacles for receiving removed items are positi<strong>on</strong>ed within easy reach<br />
of the sorters.<br />
Picture 7.: Manual Waste Sorting<br />
(Portal of Prague., 2010)