• No results found

Waste incineration in Sweden - past and future

N/A
N/A
Protected

Academic year: 2021

Share "Waste incineration in Sweden - past and future"

Copied!
3
0
0

Loading.... (view fulltext now)

Full text

(1)

WASTE MANAGEMENT AND THE ENVIRONMENT KALMAR, SWEDEN, November 5-7, 1997

19

WASTE INCINERATION IN

SWEDEN - PAST AND FUTURE

Kjerstin Ekwall SYSA V Utveckling AB Sweden

SUMMARY

Today there are 21 energy-from-waste plants with a total of 39 incinerators in operation in Sweden. Statistics for 1995 show that a total of more than 1.8 mil­ lion tonnes of waste were combusted, and the energy produced amounted to 5.0 TWh (see diagram below).

D

Waste (Mt)

Energy (TWh)

5

1980 1983 1986 1991 1994 1995

Diagram 1. Quantities of waste incinerated and energy produced at Swedish waste incineration plants in the period 1980-1995.

The quantity of combusted waste has more than doubled since 1980, and energy production during the same period has almost quadrupled. This is because the

Kjerstln Ekwall, Sweden 165

(2)

45

35

WASTE MANAGEMENT AND THE ENVIRONMENT KALMAR, SWEDEN, November 5-7, 1997

waste has become more energy-rich, but above all it is because energy recovery is more efficient and the proportion of energy lost by cooling has been reduced. Initially the plants were equipped only with a cyclone or electrofilter for cleaning of dust-bound pollutants in the flue gases. Because of stricter environmental requirements, all the plants have been supplemented with advanced cleaning sys­ tems which also remove gaseous pollutants from the flue gases. For plant-specific flue-gas cleaning equipment see table 3.2, chapter 3.

A total of 12 plants have also taken measures to reduce NO, emissions. Three plants have installed flue-gas recycling, five plants have installed SNCR, and four plants have combined SNCR and flue-gas recycling.

The investments in advanced flue-gas purification systems and equipment for re� duction of NO, have resulted in heavily reduced emissions from the waste incine­ ration plants (see table 1).

Table 1. Annual emissions from waste incineration in Sweden 1985, 1991, 1995.

Substance Unit 1985 1991 1995 Change 1985-95

Dust t/year 420 27 -94%

Hydrogen chloride t/year 8400 4 10 360 -96%

Sulphur oxides t/year 3400 700 1160 -66%

Nitrogen oxides t/year 3400 3200 1550 -54%

Mercury kg/year 3300 170 90 -97%

Cadmium kg/year 400 8 -98%

Lead kg/year 25000 720 133 -99%

Dioxins g/year 90 8 2.2 -98%

In 1986, 1.53 million tonnes of waste were incinerated, and energy production amounted to 3.4 TWh. In 1995, 1.81 million tonnes of waste were incinerated and energy production was 5.0 TWh. The last ten-year period of Swedish waste incineration can thus be summed up as follows: Increased quantity of incinerated waste per year (+18%), significantly higher energy production (+47%), and gre­ atly reduced emissions (-54 to -99%).

In environmental terms, energy production from waste is fully comparable to (and in some cases better than) conventional energy production with e.g. oil, co­ al, and gas. The waste can mostly be classified as bio-fuel, and the energy from the waste can be used efficiently in the Swedish district heating networks. The view of energy production from waste differs from country to country, however. The EU Commission is working today to draw up new guidelines for the incineration of waste. The working material that has been presented shows that the emission criteria will be much stricter and that they are not at all in

pro-Kjerstln Ekwall, Sweden 166

(3)

WASTE MANAGEMENT AND THE ENVIRONMENT KALMAR, SWEDEN, November 5-7, 1997

portion to the much higher emission levels permitted for other types of energy

plants. This is due to a difference in the basic view of waste incineration. In nort­

hern Europe we have a well-developed district heating network and hence greater

opportunities and interest as regards the use of waste energy. In the rest of Euro­

pe, above all in the southern countries, there is very slight interest in waste ener­

gy, so waste incineration plants are mostly viewed as destruction plants; this me­

ans that they are not seen as a substitute for other types of energy stations but

just as a source of emissions.

If tougher EU criteria are introduced, as per appendix 1, the investment cost for

the Swedish waste incineration plants will amount to a total of about SEK 840

million for rebuilding and additions to flue-gas cleaning.

Figure

Diagram 1.  Quantities  of waste  incinerated and energy produced at Swedish  waste incineration plants in  the period  1980-1995
Table  1.  Annual  emissions from waste incineration in Sweden 1985,  1991,  1995.

References

Related documents

Comparison of composting technologies in table 4.1 showed as predicted that mechanical technologies, such as the aerated static pile and in-vessel systems, are

After considering the situation of textile industry, textile waste and textile consumption in Sweden, this report gives a new prevention scheme from the scope of

The results from sample analysis revealed that PFAAs were present in all solid samples at concentrations in the low to sub ng/g range and in all but one condensate and

Mainly clean pre-consumer waste from construction industry (e.g. pipes) is separately collected and sent for recycling abroad.. 94 PVC waste treatment in the Nordic

The analysis in this paper is general and can without difficulty be extended to any coupled system of partial differential equations posed as an initial boundary value problem

Packarna jobbar här efter målet att inte blanda delar som kan vara skadliga för varandra i samma låda, till exempel undviker de att packa el och gjutna delar i samma låda, eftersom

Concentrations of both zinc and total phosphorus in the effluent water at Volvo corresponded well to the BREF-plants using the same treatment method..

Ty även om man radikalt redu­ cerar diktens inslag av referens till »verkligheten», dess egenskap av kanal för åsikter och syften, kvarstår ju ändå