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17<br />

5. Humificati<strong>on</strong> indicators – measurement of humic substances, especially<br />

humic acid carb<strong>on</strong> to fulvic acid carb<strong>on</strong> ratio, may provide an effective measure<br />

of stabilizati<strong>on</strong>. Humic acid c<strong>on</strong>tent increases as composting progresses.<br />

6. Molecular size determinati<strong>on</strong> – molecular sizes rise as humic substances<br />

are formed. This test requires specialized equipment <str<strong>on</strong>g>and</str<strong>on</strong>g> expert operators.<br />

(Composting Council of Canada., 2010)<br />

2.1.5. Composting process cost<br />

Composting costs include costs that have to do with local criteria, facility<br />

operati<strong>on</strong>s <str<strong>on</strong>g>and</str<strong>on</strong>g> marketing of the finished product. The facility must be installed<br />

in a regi<strong>on</strong> according to each country’s laws in a way that public health is not<br />

damaged at any means. There may be some more requirements something that<br />

depends <strong>on</strong> the whole compost facility design such as h<str<strong>on</strong>g>and</str<strong>on</strong>g>ling equipment such<br />

as shredders, screens, c<strong>on</strong>veyers <str<strong>on</strong>g>and</str<strong>on</strong>g> turners. The cost of c<strong>on</strong>structing <str<strong>on</strong>g>and</str<strong>on</strong>g><br />

operating a windrow composting facility will vary from <strong>on</strong>e locati<strong>on</strong> to another.<br />

The operating costs depend <strong>on</strong> the volume of material processed. The use of<br />

additi<strong>on</strong>al feed materials, such as paper <str<strong>on</strong>g>and</str<strong>on</strong>g> mixed municipal solid <strong>waste</strong>,<br />

which will require additi<strong>on</strong>al capital investment <str<strong>on</strong>g>and</str<strong>on</strong>g> materials processing labor.<br />

(Aarhus University., 2004)<br />

The capital costs of windrow or aerated piles are c<strong>on</strong>sidered to be lower in than<br />

in-vessel composting systems. However, the potential cost of the facilities could<br />

increase remarkably when cover <str<strong>on</strong>g>and</str<strong>on</strong>g> other mechanisms are required to c<strong>on</strong>trol<br />

odors. In most of the cases though costs of windrow systems are the lowest<br />

compared to the other two techniques. Basically In-vessel system costs more<br />

than the other methods, mainly because it is more mechanized <str<strong>on</strong>g>and</str<strong>on</strong>g> more<br />

equipment maintenance is necessary, however the labor intensive trend’s to be<br />

less. (EPA., 1994).<br />

2.1.6.Envir<strong>on</strong>mental <str<strong>on</strong>g>and</str<strong>on</strong>g> health impacts<br />

Composting is mainly used as high quality soil in agriculture. This practice<br />

prevents other chemical substances which have been used in the past <str<strong>on</strong>g>and</str<strong>on</strong>g> are<br />

dangerous, to be used as a fertilizer for soil improvement. The negative impacts<br />

of composting are dangerous gases emissi<strong>on</strong>s (Figure.7) such as: greenhouse<br />

gases (GHGs), volatile <strong>organic</strong> compounds (VOCs) <str<strong>on</strong>g>and</str<strong>on</strong>g> odors. In order for the<br />

composting process to be effective these gases have to be c<strong>on</strong>trolled. In soils<br />

<str<strong>on</strong>g>and</str<strong>on</strong>g> water systems the major c<strong>on</strong>cerns are due to depositi<strong>on</strong> of salts <str<strong>on</strong>g>and</str<strong>on</strong>g> heavy<br />

metals.

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