On the lakeshore at Stockholm
Photo: A. Kurata
>Lake Malaren is situated in a region
with Archaean rocks. The deposits around the lake, especially
its northeastern and southern parts, are dominated by lime-rich
clays which make these areas well suited for cultivation. Central
Sweden is a highly cultivated area where the use of inorganic
fertilizers contributes to the nutrient loading on the lakes.
Lake Malaren is a very complicated system
of waters composed of bays of different character. On the basis
of its topography the lake can be divided into five basins each
with its own chemical and biological status.
An early description of the lake mentions
its importance as a route of communication between Stockholm,
the capital, and many inland towns, the traveller being able
to enjoy the many beautiful bays en route (Fischerstrom, 1785).
Another comment from this early period, more interesting from
a water quality point of view, says that the water usually has
a good taste and is sound enough to drink. Water-blooming algae,
Aphanizomenon flos-aquae ,were however observed in shallow creeks.
The quotient between drainage area and
lake surface is about 20 which indicates a large surrounding
area contributing to the loading on the lake. The expansion of
population and industry around the lake has been and is still
very high. Lake Malaren has become more eutrophic during the
last 30 to 40 years. Its importance as a freshwater reservoir
is steadily increasing.
Stockholm, the capital of Sweden, is situated
at the outlet of Lake Malaren into the Baltic. Seventy-five percent
of the inflow to Lake Malaren enters the western part of the
lake but the inflow into the northeastern area is also important.
This means that the water flows mainly in two directions, one
from west to east and another from northeast to south before
entering the connection with the Baltic.
Surface area [km2] | 1,140 |
Volume [km3] | 13.6 |
Maximum depth [m] | 61 |
Mean depth [m] | 11.9 |
Water level | Regulated |
- Normal range of annual water | |
level fluctuation [m] | 0.5 |
Length of shoreline [km] | 1,410 |
Residence time [yr] | 2.2* |
Catchment area [km2] | 21,460 |
* 1981-1985. |
D1 GEOGRAPHICAL (Q)
D2 CLIMATIC (Q, 2)
Mean temp. [deg C] | ||||||||||||
Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | Ann. |
---|---|---|---|---|---|---|---|---|---|---|---|---|
-2.9 | -3.1 | -0.7 | 4.4 | 10.1 | 14.9 | 17.8 | 16.6 | 12.2 | 7.1 | 2.8 | 0.1 | 6.6 |
Precipitation [mm] | ||||||||||||
43 | 30 | 26 | 31 | 34 | 45 | 61 | 76 | 60 | 48 | 53 | 48 | 555 |
Fig. EUR-13-01
Bathymetric map [m].
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 0.5 | - | 5.6 | 12.5 | 18.5 | 17.5 | 13.9 | 11.0 | - | - |
5 | - | - | 0.7 | - | 4.8 | 11.8 | 17.8 | 17.2 | 13.9 | 10.9 | - | - |
10 | - | - | 0.9 | - | 4.6 | 10.9 | 14.7 | 16.3 | 13.9 | 10.9 | - | - |
15 | - | - | 1.0 | - | 4.5 | 9.9 | 11.0 | 14.2 | 13.9 | 10.9 | - | - |
20 | - | - | 1.1 | - | 4.2 | 8.3 | 9.4 | 11.2 | 13.6 | 10.9 | - | - |
30 | - | - | 1.3 | - | 4.1 | 7.3 | 8.0 | 9.4 | 10.9 | 10.7 | - | - |
40 | - | - | 1.5 | - | 4.0 | 6.4 | 7.5 | 8.7 | 9.8 | 10.3 | - | - |
E1 TRANSPARENCY [m](Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
- | - | 1.8 | - | 1.9 | 2.1 | 3.0 | 3.2 | 3.4 | 2.9 | - | - |
E2 pH (Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | SeP | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 7.4 | - | 7.7 | 8.1 | 8.0 | 7.7 | 7.6 | 7.6 | - | - |
5 | - | - | 7.4 | - | 7.7 | 7.9 | 8.0 | 7.7 | 7.7 | 7.6 | - | - |
10 | - | - | 7.5 | - | 7.6 | 7.8 | 7.6 | 7.4 | 7.7 | 7.6 | - | - |
15 | - | - | 7.5 | - | 7.5 | 7.7 | 7.3 | 7.3 | 7.7 | 7.6 | - | - |
20 | - | - | 7.5 | - | 7.5 | 7.6 | 7.2 | 7.2 | 7.6 | 7.6 | - | - |
30 | - | - | 7.5 | - | 7.5 | 7.5 | 7.2 | 7.2 | 7.2 | 7.6 | - | - |
40 | - | - | 7.4 | - | 7.5 | 7.4 | 7.2 | 7.1 | 7.1 | 7.5 | - | - |
E3 SS [mg l-1](Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 3.2 | - | 2.7 | 3.0 | 2.2 | 2.2 | 1.8 | 1.9 | - | - |
5 | - | - | 4.2 | - | 2.6 | 3.4 | 1.4 | 2.9 | 1.9 | 1.7 | - | - |
10 | - | - | 4.0 | - | 2.2 | 2.8 | 1.6 | 2.6 | 1.8 | 1.7 | - | - |
15 | - | - | 2.3 | - | 2.6 | 2.8 | 1.9 | 3.3 | 1.5 | 1.9 | - | - |
20 | - | - | 2.2 | - | 2.6 | 2.8 | 2.4 | 4.0 | 1.2 | 1.7 | - | - |
30 | - | - | 2.0 | - | 3.0 | 2.8 | 3.3 | 4.0 | 3.0 | 2.1 | - | - |
40 | - | - | 1.9 | - | 2.9 | 4.1 | 5.6 | 5.3 | 3.6 | 2.3 | - | - |
E4 DO [mg l-1](Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 12.5 | - | 12.3 | 10.8 | 9.0 | 8.3 | 9.1 | 9.2 | - | - |
5 | - | - | 12.2 | - | 12.4 | 10.5 | 8.8 | 8.2 | 9.1 | 9.2 | - | - |
10 | - | - | 12.2 | - | 12.2 | 10.1 | 8.4 | 7.9 | 8.9 | 9.4 | - | - |
15 | - | - | 12.2 | - | 11.5 | 10.8 | 8.7 | 7.6 | 8.9 | 9.3 | - | - |
20 | - | - | 12.2 | - | 12.2 | 10.7 | 8.7 | 7.5 | 8.6 | 9.2 | - | - |
30 | - | - | 12.0 | - | 12.1 | 10.7 | 9.1 | 7.4 | 7.4 | 9.2 | - | - |
40 | - | - | 11.5 | - | 11.9 | 10.8 | 9.0 | 7.5 | 6.6 | 8.3 | - | - |
E5 COD [mg l-1] Determined by KMnO4 method.
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 25.5 | - | 25.1 | 26.8 | 26.5 | 25.4 | 23.6 | 22.1 | - | - |
5 | - | - | 24.5 | - | 24.5 | 26.1 | 25.9 | 25.3 | 23.9 | 22.9 | - | - |
10 | - | - | 22.4 | - | 25.8 | 24.7 | 24.3 | 24.8 | 23.1 | 23.3 | - | - |
15 | - | - | 21.9 | - | 25.8 | 24.1 | 24.5 | 24.5 | 23.2 | 23.1 | - | - |
20 | - | - | 21.0 | - | 25.5 | 23.9 | 23.8 | 24.4 | 23.0 | 22.8 | - | - |
30 | - | - | 21.9 | - | 25.3 | 24.0 | 24.0 | 24.2 | 23.2 | 22.4 | - | - |
40 | - | - | 22.1 | - | 26.1 | 24.1 | 23.9 | 24.9 | 23.3 | 22.8 | - | - |
E6 CHLOROPHYLL CONCENTRATION [micro g l-1](Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 0.8 | - | 3.8 | 9.8 | 6.6 | 5.3 | 4.7 | 3.2 | - | - |
5 | - | - | 0.3 | - | 4.5 | 8.2 | 6.6 | 5.1 | 4.2 | 2.7 | - | - |
10 | - | - | 0.3 | - | 3.7 | 7.2 | 3.1 | 3.4 | 4.1 | 2.7 | - | - |
15 | - | - | 0.3 | 3.6 | 6.0 | 1.6 | 3.2 | 4.0 | 2.7 | - | - | |
20 | - | - | 0.3 | - | 3.6 | 5.1 | 0.9 | 1.1 | 3.3 | 2.7 | - | - |
30 | - | - | 0.3 | - | 3.1 | 5.2 | 0.9 | 0.7 | 1.6 | 2.7 | - | - |
40 | - | - | 0.4 | - | 2.9 | 5.6 | 1.9 | 0.8 | 1.1 | 2.5 | - | - |
E7 NITROGEN CONCENTRATION (Q)
Prastfjarden, 1981-1985 | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 0.962 | - | 0.843 | 0.830 | 0.720 | 0.709 | 0.718 | 0.735 | - | - |
5 | - | - | 0.872 | - | 0.825 | 0.798 | 0.707 | 0.710 | 0.717 | 0.695 | - | - |
10 | - | - | 0.775 | - | 0.843 | 0.775 | 0.714 | 0.717 | 0.716 | 0.698 | - | - |
15 | - | - | 0.747 | - | 0.874 | 0.786 | 0.772 | 0.764 | 0.700 | 0.704 | - | - |
20 | - | - | 0.733 | - | 0.856 | 0.793 | 0.847 | 0.842 | 0.709 | 0.727 | - | - |
30 | - | - | 0.753 | - | 0.875 | 0.799 | 0.872 | 0.891 | 0.827 | 0.707 | - | - |
40 | - | - | 0.770 | - | 0.857 | 0.852 | 0.879 | 0.906 | 0.860 | 0.737 | - | - |
E8 PHOSPHORUS CONCENTRATION (Q)
Prastfjarden | ||||||||||||
Depth [m] | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec |
---|---|---|---|---|---|---|---|---|---|---|---|---|
0 | - | - | 0.043 | - | 0.042 | 0.032 | 0.026 | 0.022 | 0.024 | 0.024 | - | - |
5 | - | - | 0.043 | - | 0.040 | 0.031 | 0.024 | 0.020 | 0.024 | 0.025 | - | - |
10 | - | - | 0.037 | - | 0.041 | 0.031 | 0.021 | 0.019 | 0.021 | 0.022 | - | - |
15 | - | - | 0.033 | - | 0.042 | 0.033 | 0.023 | 0.022 | 0.021 | 0.024 | - | - |
20 | - | - | 0.031 | - | 0.039 | 0.033 | 0.025 | 0.028 | 0.023 | 0.023 | - | - |
30 | - | - | 0.034 | - | 0.041 | 0.036 | 0.031 | 0.031 | 0.033 | 0.023 | - | - |
40 | - | - | 0.036 | - | 0.042 | 0.042 | 0.040 | 0.037 | 0.041 | 0.030 | - | - |
E10 PAST TRENDS (3): Fig. EUR-13-02, 03, 04 and 05.
Fig. EUR-13-02
Past trend of transparency with map of its sampling station [m].
Fig. EUR-13-03
Past trend of chlorophyll a [micro g l-1].
Fig. EUR-13-04
Past trend of NO3-N [micro g l-1].
Fig. EUR-13-05
Past trend of Total-P [micro g l-1]
F1 FLORA
F2 FAUNA
F3 PRIMARY PRODUCTION RATE (Q)
Ekoln Bay | ||
1967 | 1968 | 1974 |
---|---|---|
125 | 120 | - |
Lilla Ullfjarden | ||
1967 | 1968 | 1974 |
- | 100 | 135 |
F5 FISHERY PRODUCTS (Q)
F6 PAST TRENDS: Fig. EUR-13-06 and 07.
Fig. EUR-13-06
Past trend of phytoplankton biomass [mm3 l-1](3)
Fig. EUR-13-07
Past trend of annual fish catch [metric tons](6).
G1 LAND USE IN THE CATCHMENT AREA (8, 7)
1981 | ||
Area [km2] | [%] | |
---|---|---|
- Natural landscape | ||
Woody vegetation | 11,819 | 64.5 |
- Agricultural land | 4,647 | 25.4 |
- Others | 1,853 | 10.1 |
- Total | 18,319 | 100.0 |
G2 INDUSTRIES IN THE CATCHMENT AREA AND THE LAKE (7)
1981 | ||
No. of persons engaged | No. of establishments | |
---|---|---|
- Secondry industry | ||
Mines and manufacturing industry | 103,225 | 990 |
Food stuffs | 7,687 | 77 |
Textile | 1,954 | 36 |
Wood | 2,830 | 81 |
Pulp and paper | 6,923 | 105 |
Chemical | 6,575 | 63 |
Soil and stone | 2,815 | 63 |
Metal products | 11,825 | 31 |
Work shop | 60,323 | 504 |
- Others | 482 | 11 |
All exclusive Stockholm. |
G3 POPULATION IN THE CATCHMENT AREA (7)
1980 | |||
Population | Population density [km-2] | Major cities (population) | |
---|---|---|---|
Total | 1,086,400 | 50.6 | Stockholm (700,000), Uppsala, Vasteras, Eskilstuna |
H1 LAKE UTILIZATION
Source of water, navigation and transportation, sightseeing and tourism, recreation (swimming, sport-fishing, yachting) and fisheries.
I1 ENHANCED SILTATION (Q)
I2 TOXIC CONTAMINATION
Concentration [ppm] | |||
---|---|---|---|
Bottom mud (dry wt.) (before 1977) | Fish*1 (wet wt.) (1977) | Fish*2 (wet wt.) (1986) | |
Hg | 0.5 | - | - |
Cu | 188 | - | - |
Ni | 189 | - | - |
Pb | 132 | - | - |
Zn | 446 | - | - |
Cr | 701 | - | - |
Total Hg | - | - | 0.3 |
DDE+DDT+DDD | - | 3.1 | - |
PCBs | - | 23 | - |
*1 Liver of burbot at Lambarfjarden. | |||
*2 Muscle of pike at Kalmarviken. |
I3 EUTROPHICATION (Q)
1981-1985 | |
Sources |
Total |
---|---|
T-N | 13,400 |
T-P | 590 |
I4 ACIDIFICATION (Q)
J1 GENERATION OF POLLUTANTS IN THE CATCHMENT AREA
f) Extensive development of the catchment area with provision for municipal wastewater treatment.
J2 APPROXIMATE PERCENTAGE DISTRIBUTION OF POLLUTANT LOADS
1981-1985 | ||
N[%] | P[%] | |
---|---|---|
Natural background from ground | 21 | 17 |
Atmospheric deposition | 5 | 1 |
Municipal and industrial sources | 30 | 24 |
Cultured fields minus background | 38 | 48 |
Other fields minus background | 6 | 10 |
Total | 100 | 100 |
J3 SANITARY FACILITIES AND SEWERAGE
K1 RESTORATION
Weed cutting in small areas.
M1 NATIONAL AND LOCAL LAWS CONCERNED
M2 INSTITUTIONAL MEASURES