Radioactivity in surface water, 1980-2000
| Target value1) | 1980 | 1990 | 1995 | 1998 | 1999 | 2000 | |
| Bq/l | |||||||
| Rhine (Lobith) | |||||||
| Residual beta activity | <0.2 | 0.08 | 0.07 | 0.06 | 0.05 | 0.06 | 0.04 |
| Tritium | <10 | 12.8 | 7.1 | 5.6 | 5.0 | 4.6 | 4.0 |
| Alpha activity | <0.1 | 0.06 | 0.07 | - | - | - | - |
| Meuse (Eijsden) | |||||||
| Residual beta activity | <0.2 | 0.1 | 0.05 | 0.02 | 0.04 | 0.04 | 0.02 |
| Tritium | <10 | 22.1 | 32 | 4.8 | 10.5 | 18.1 | 14.7 |
| Alpha activity | <0.1 | 0.06 | 0.03 | - | - | - | - |
| Westerschelde (on Belgian border) | |||||||
| Residual beta activity | <0.2 | 0.2 | 0.15 | 0.07 | 0.08 | 0.08 | 0.07 |
| Tritium | <10 | 8.9 | 14.5 | 8.5 | 9.9 | 12.3 | 6.3 |
| Alpha activity | <0.1 | 0.27 | 0.21 | - | - | - | - |
| Source: RIZA | RIVM/EDC/Oct02 | ||||||
| 1) Target value for surface water (V&W, 1999). | |||||||
Developments in radioactivity in surface water
Discharges by nuclear power plants and the processing industry are the main human sources of radioactivity in surface water. Since 1980, most activity values in surface water have fallen. Most values now fluctuate below or around the target value.
Relevance
The monitoring of radioactivity in the surface water fits in with the Dutch government policy. This is geared specifically to limiting as much as possible additional radiation and the associated health risks, such as cancer.



