Biomedical Engineering Reference
In-Depth Information
Table8.1 Acomparisonofselectednationalwastemanagementarrangements,
recyclingratesandMSWbiowastecomponent
Country
Landfill (%)
Incineration (%)
Recycled (%)
Biowaste (%)
Austria
65
11
24
27
Belgium
43
54
3
47
Canada
67
4
29
34
Denmark
20
55
25
37
Finland
66
4
30
33
France
59
33
8
30
Germany
46
36
18
30
Netherlands
30
42
28
35
Japan
21
74
5
26
Norway
68
18
14
35
Sweden
34
47
19
38
Switzerland
11
47
42
30
UK
85
9
6
30
USA
61
15
24
32
Sources: IEABioenergy,EuropeanCommissionandrelevantEmbassies.
Although a number of changes in the whole perception of waste have led to
a variety of relatively new options receiving attention, generally throughout the
world, the vast majority of refuse is dealt with either by means of landfill or
incineration. Different countries and administrations have favoured one or the
other at various times and, as with all things to do with waste, local custom and
circumstance have played a major part in shaping the current status quo. While
it is beyond the scope of the present discussion to examine this in any depth,
Table 8.1 may help to provide some indication of the wider situation.
Although there has been considerable development in incineration technology
over the years and today's facilities, with their energy recovery, power generation
and district heating potential, are a far cry from the simple smoking stacks of old,
for biological origin waste, mass burn incinerators cannot be viewed as the ideal
solution. Hence, while the incineration versus landfill argument still rages, and
has been re-visited with renewed vigour once again in some circles in the light
of the implications of recent European developments, the fact remains that, at
least from the standpoint of biowaste, both are nothing more than disposal routes.
Significant amounts of wet organic material, which is itself largely composed of
water to begin with, may be an inconvenience to the incinerator operator; the
situation in landfill is worse.
Landfill
Left to its own devices, all discarded biological waste gradually undergoes a natu-
ral process of biodegradation, typically beginning with autolysis and culminating
in putrefaction. The speed at which this progresses is governed by a number of
factors such as the nature and freshness of the material, the temperature, mois-
ture, and so on. When this happens in the open air, or in the upper levels of the
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