|
Tables
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Table 13. Quantities, composition and use of
Novo Nordisk's liquid waste worldwide
1993-1995.
|
|
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1993
|
1994
|
1995
|
|
Discharged liquid waste (m3)
|
2,173,000
|
2,137,000
|
1,935,000
|
|
Chemical oxygen demand, COD (t)
|
7,210
|
5,440
|
3,220
|
|
Nitrogen (N) (t)
|
725
|
522
|
212
|
|
Phosphorus (P) (t)
|
277
|
171
|
52
|
|
|
|
Recycled liquid waste (m3)*
|
1,555,000
|
1,825,000
|
1,898,000
|
|
Dry matter (t)
|
44,400
|
48,400
|
57,500
|
|
Nitrogen (N) (t)
|
1,710
|
1,530
|
2,040
|
|
Phosphorus (P) (t)
|
595
|
609
|
740
|
|
|
|
% liquid waste recycled
|
42
|
46
|
50
|
|
% nitrogen recycled
|
70
|
75
|
91
|
|
% phosphorus recycled
|
68
|
78
|
93
|
|
|
|
* including yeast slurry.
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|
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Table 14. Solid waste 1993-1995.
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Distribution
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1993
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1994
|
1995
|
|
|
t
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%
|
t
|
%
|
t
|
%
|
|
Recycling
|
4,050
|
16
|
5,100
|
27
|
4,100
|
25
|
|
Combustion
|
6,030
|
24
|
5,390
|
29
|
3,810
|
24
|
|
Land fills
|
*14,000
|
55
|
7,460
|
40
|
7,280
|
45
|
|
Controlled destruction
|
1,150
|
5
|
860
|
4
|
1,060
|
6
|
|
Total
|
25,23
|
100
|
18,81
|
100
|
16,25
|
100
|
|
|
|
|
|
|
|
|
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* including 9,755 metric tons of polluted soil.
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|
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Table 15. CO2 and SO2 emissions from own and external
energy supplies 1993-1995.
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|
|
1993
|
1994
|
1995
|
|
CO2 from own plant (t)
|
77,200
|
77,900
|
80,900
|
|
CO2 from external plant (t)
|
396,000
|
426,000
|
441,000
|
|
|
|
|
|
|
SO2 from own plant (t)
|
347
|
214
|
209
|
|
SO2 from external plant (t)
|
2,000
|
2,310
|
2,420
|
|
|
|
|
|
|
CO2 and SO2 emissions for external plant are calculated
on the basis of data for the individual countries from the
UMIP database, the Technical University of Denmark.
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|
|
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Table 16. Effect potentials for the greenhouse effect,
acidification and photochemical ozone formation as absolute
values and in relation to energy consumption.
|
|
|
Total emissions (t)
|
Relative emissions (g/GJ)
|
|
|
1993
|
1994
|
1995
|
1993
|
1994
|
1995
|
|
Greenhouse (CO2 equiv.)
|
481,000
|
525,000
|
544,000
|
138,000
|
140,000
|
140,000
|
|
Acidification (SO2 equiv.)
|
3,570
|
3,960
|
4,100
|
1,030
|
1,060
|
1,060
|
|
Photochemical ozone formation (C2H2 equiv.)
|
72
|
84
|
88
|
21
|
22
|
23
|
|
|
|
|
|
|
|
|
|
The effect potentials are calculated according to the
UMIP method. Reference: H. Wenzel et al., Environmental
Assessment of Products, DTU, Danish National Agency of
Environmental Protection and the Confederation of Danish
Industries, 1996.
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|
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Table 17. Storage of ozone-depleting substances in
1995.
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|
Substance
|
Use
|
Quantity, kg
|
|
CFC
|
Refrigeration and freezing plant
|
6,350
|
|
HCFC
|
Refrigeration and freezing plant
|
28,540
|
|
HFC
|
Refrigeration and freezing plant
|
298
|
|
Halons
|
Fire-fighting equipment
|
643
|
|
Methyl bromide
|
Chemical synthesis
|
45,000
|
|
|
|
|
|
The chlorinated refrigerants are for large refrigeration
and freezing plants which are subject to regular control.
The statistics are not complete, but are estimated to
comprise more than 90% of the total quantity. The figures
include FeF Chemicals, Denmark and Anagni, Italy.
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|
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Table 18. Purchase of ozone-depleting substances in
1994 and 1995 (kg).
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|
Substance
|
1994
|
1995
|
|
CFC
|
2,626
|
820
|
|
HCFC
|
9,412
|
1,913
|
|
HFC
|
53
|
44
|
|
Methyl bromide
|
205,000
|
239,610
|
|
|
|
|
|
The figures include FeF Chemicals and Anagni, Italy.
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Table 19. Registered quantities, number of kilometres
and fuel consumption for all domestic transportation.
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|
Transport
|
Metric tons
|
Kilometres
|
|
Biomass, tanker from Kalundborg
|
802,584
|
1,585,188
|
|
Biomass, pipeline from Kalundborg
|
420,746
|
-
|
|
Biomass, tanker from Copenhagen to Kalundborg
|
260,384
|
786,658
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|
Ordinary freight transport
|
229,041
|
1,460,224
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|
Of which hazardous cargoes
|
1,392
|
-
|
|
Total fuel consumption (environmentally sound
diesel/unleaded petrol): 766,072 litres
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