(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 ...
71 The basic system is composed of a top roller that presses down on to two bottom rollers
72 within solution under the influence of an electrical field,
- 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 and 78: 66 The sorting of recyclables may b
- Page 79 and 80: 68 4.5. Mechanical and</str
- Page 81: 70 glass breakage on the tipping fl
- 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
- Page 129 and 130: 118 process treats the wastes as co
- Page 131 and 132: 120 consumption is about 0.7 x106 k
71<br />
The basic system is composed of a top roller that presses down <strong>on</strong> to two<br />
bottom rollers <str<strong>on</strong>g>and</str<strong>on</strong>g> the drums rotate to facilitate the passage of the material <strong>on</strong><br />
a c<strong>on</strong>veyor belt (Orsat et al., 1999). This system is well adapted to combining<br />
with electroosmotic dewatering. larger groove angles can help to further reduce<br />
the moisture c<strong>on</strong>tent during roller pressing of sugar cane bagasse.<br />
Screw press dewatering<br />
In a screw press, the material is introduced in a perforated chamber where an<br />
endless screw forces the material al<strong>on</strong>g the length of the chamber towards the<br />
discharge. The pressure force of the screw drives the water out through the<br />
perforati<strong>on</strong>s of the holding chamber. For this type of dewatering process, the<br />
<strong>waste</strong> feed must have a certain particle size large enough not to clog the<br />
perforati<strong>on</strong>s of the holding system <str<strong>on</strong>g>and</str<strong>on</strong>g> to flow through without excessive<br />
resistance.<br />
Rotary <str<strong>on</strong>g>and</str<strong>on</strong>g> centrifugal presses<br />
A centrifugal dewatering system c<strong>on</strong>sists of a basket or a solid bowl <str<strong>on</strong>g>and</str<strong>on</strong>g> a<br />
c<strong>on</strong>veyor, both of which can rotate at high speed. As the bowl rotates, the<br />
heavier solids gravitate to the bowl wall where they accumulate. The separati<strong>on</strong><br />
of solids from the liquid depends <strong>on</strong> the G-force, time <str<strong>on</strong>g>and</str<strong>on</strong>g> permeability of the<br />
<strong>waste</strong> mass (Leung., 1998).<br />
Membrane filter press<br />
A membrane filter press comprises a stack of filter plates held tightly closed by<br />
pressure. The filter plates have a filtrati<strong>on</strong> drainage surface that supports a filter<br />
media, in most cases a polypropylene filter cloth held in place by a more rigid<br />
polypropylene structure. The mixed solid–liquid <strong>waste</strong> is pumped into the<br />
chambers under pressure. The filtered liquid passes through the filter cloth,<br />
against the drainage surface of the plates, <str<strong>on</strong>g>and</str<strong>on</strong>g> is directed towards discharge<br />
collectors. The pressure gradient between the cake <str<strong>on</strong>g>and</str<strong>on</strong>g> the filter material<br />
provides the driving force for the flow. Solids are retained <strong>on</strong> the filter cloth<br />
forming a filter cake. The filter plates are separated <str<strong>on</strong>g>and</str<strong>on</strong>g> the filter cake is<br />
discharged. At this stage a vacuum step may be introduced to further reduce<br />
the moisture c<strong>on</strong>tent. In a study by (El-Shafey et al. 2004), brewer’s spent<br />
grain was dewatered to a low moisture level of 20–30% when combining<br />
membrane filter pressing (500 kPa) with vacuum drying.<br />
Electroosmotic dewatering<br />
Electroosmosis is caused by the electrical double layer that exists at the<br />
interface of suspended particles subjected to an applied voltage across a solid–<br />
liquid mixture. In <strong>waste</strong> slurries, the solid particles possess a slight electric<br />
charge known as the zeta potential. Hence, when exposed to an electric field,<br />
the charged particles <str<strong>on</strong>g>and</str<strong>on</strong>g> the liquid fracti<strong>on</strong> are entrained to move in opposite<br />
directi<strong>on</strong>s: <strong>on</strong>e towards the anode, the other towards the cathode (Orsat et al.,<br />
1996). On the <strong>on</strong>e h<str<strong>on</strong>g>and</str<strong>on</strong>g>, electrophoresis is the movement of charged particles