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Assessment of Mercury Releases from the Russian Federation
| Year |
Into the products
% |
Technological losses of mercury |
| Captured by absorbers |
Emitted to atmosphere |
Broken glass |
Wastewater |
To the sewerage system |
Unorganized emission/discharge |
| kg |
% |
kg |
% |
kg |
% |
kg |
% |
kg |
% |
kg |
% |
| 1998 |
99.35 |
1.6 |
0.01 |
0.32 |
0.002 |
20.56 |
0.134 |
0.669 |
0.004 |
72.833 |
0.47 |
3.833 |
0.03 |
| 1999 |
99.35 |
6.2 |
0.035 |
0.26 * |
0.001 |
0.075 |
0.0004 |
0.627 |
0.0035 |
102.862 |
0.58 |
5.414 |
0.03 |
| 2000 |
99.35 |
6.43 |
0.03 |
1.4 |
0.006 |
0.102 |
0.0004 |
0.718 |
0.003 |
134.38 |
0.58 |
7.073 |
0.031 |
| 2001 |
99.35 |
6.97 |
0.03 |
1.4 |
0.006 |
0.104 |
0.0004 |
0.605 |
0.003 |
140.756 |
0.58 |
7.408 |
0.03 |
| 2002 |
99.35 |
7.1 |
0.03 |
1.4 |
0.005 |
0.116 |
0.0004 |
0.772 |
0.003 |
150.059 |
0.58 |
7.898 |
0.03 |
* It is interesting to note that according to official data, in 1999, in Klin, no mercury vapours were detected in the air (Environmental Condition of the Moscow Oblast ..., 2000).
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Version 1.0 March 2005, © Danish Environmental Protection Agency
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