SKAHA LAKE
A view on the lake

Photo: R.Nordin
A. LOCATION
  - British Columbia, Canada.
 
  - 49:25N, 119:35W; 338 m above sea level.
 
B. DESCRIPTION
  Skaha Lake is the fourth of the chain
  of five major lakes which occupy portion of the Okanagan Valley
  in the interior of British Columbia. The Okanagan Valley is a
  structural trench overlying a system of sub-parallel linked faults
  that separate the late Paleozoic or early Mesozoic Monoshee group
  of metamorphic rocks of differing lithology but of similar age.
  The trench is partially filled with several hundred meters of
  unconsolidated material (400 m in the Skaha Lake area). It is
  likely that the unconsolidated material was deposited in association
  with early glaciations of the Pleistocene Epoch. It seems probable
  that during the Pleistocene the valley was the site of deposition
  resulting from glacial outwash, direct glaciation and lacustrine
  fluvial sedimentation. During deglaciation a number of terraces
  were formed as lowering of post glacial lake levels was repeatedly
  arrested. 
  Prominent silt and clay cliffs border Skaha
  Lake as a result of this period of glacial down-washing and degradation.
  Deglaciation was well advanced by 9750 B. P. and the lakes of
  Okanagan valley were formed about 8900 B. P. 
  Skaha Lake is comprised of two distinct
  basins separated by a bedrock sill at a depth of 24 m. The surrounding
  watershed has "benches" (terrace) along the east and
  west shores which rise to mountainous slopes with the flat valley
  bottom at the north and south ends. Skaha Lake is separated from
  Okanagan Lake to the north by a narrow stretch of valley bottom
  on which the city of Penticton has developed. 
  The watershed of Skaha Lake was first settled
  by Europeans in the last half of the 19th century. The climate
  (dry warm summers) and soil and availability of irrigation water
  led to the development of a substantial tree fruit industry around
  the lake and throughout the valley. Logging occurs in the upper
  elevation forests of the valley. The lower elevation vegetation
  of the Skaha Lake watershed is described as a Ponderosa pine
  (Pinus ponderosa)/bunchgrass community and the higher elevation
  is dominated by Douglas fir (Pseudotsuga menziesii) forest. 
  Little limnological information was collected
  prior to 1969 when the Okanagan Basin Study was undertaken. Initiative
  for this comprehensive program came about primarily due to complaints
  to deteriorating water quality in Skaha Lake as a result of sewage
  discharge from the city of Penticton to the Okanagan River draining
  into Skaha Lake. Tertiary treatment was undertaken in 1971. Water
  quality subsequently improved. 
  The lake is highly utilized as summer recreation
  location and tourism is presently a major component of the local
  economy (Q, 2). 
C. PHYSICAL DIMENSIONS (Q, 2, 3)
  
    
      | 
      Surface area [km2] |  
      
      20 |  
    
    
      | 
      Volume [km3] |  
      
      0.558 |  
    
    
      | 
      Maximum depth [m] |  
      
      55 |  
    
    
      | 
      Mean depth [m] |  
      
      26 |  
    
    
      | 
      Water level |  
      
      Regulated |  
    
    
      | 
      Normal range of annual water level fluctuation [m] |  
      
      0.6 |  
    
    
      | 
      Length of shoreline [km] |  
      
      29.5 |  
    
    
      | 
      Residence time [yr] |  
      
      1.2 |  
    
    
      | 
      Catchment area [km2] |  
      
      6,090 |  
    
  
D. PHYSIOGRAPHIC FEATURES
D1 GEOGRAPHICAL
  - Sketch map: Fig. NAM-53-0l.
 
  - Bathymetric map: Fig. NAM-53-02.
 
  - Number of outflowing rivers and channels (name): 1 (Okanagan
  R.).
 
D2 CLIMATIC
  - Climatic data at Penticton Airport, 1940-1970 (4)
 
  
    
       | 
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
      
      Ann. |  
    
    
      | 
      Mean temp. [deg C] |  
      
      -2.9 |  
      
      0.3 |  
      
      4.7 |  
      
      8.7 |  
      
      13.4 |  
      
      17.1 |  
      
      20.1 |  
      
      19.2 |  
      
      14.7 |  
      
      8.7 |  
      
      3.1 |  
      
      -0.4 |  
      
      8.8 |  
    
    
      | 
      Precipitation [mm] |  
      
      9 |  
      
      10 |  
      
      12 |  
      
      23 |  
      
      28 |  
      
      36 |  
      
      25 |  
      
      22 |  
      
      18 |  
      
      20 |  
      
      19 |  
      
      10 |  
      
      232 |  
    
  
  
Fig. NAM-53-01
  Sketch map of Okanagan lakes (Q).
  
Fig. NAM-53-02
  Bathymetric map [50 ft=15.24 m](Q).
  - Number of hours of bright sunshine: 2,032 hr yr-1.
 
  - Solar radiation (Summerland)[MJ m-2 day-1](5)
 
  
    
      | 
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
      
      Ann. |  
    
    
      | 
      3.4 |  
      
      6.5 |  
      
      11.5 |  
      
      16.7 |  
      
      20.8 |  
      
      22.6 |  
      
      23.7 |  
      
      19.6 |  
      
      14.5 |  
      
      8.5 |  
      
      3.8 |  
      
      2.5 |  
      
      12.8 |  
    
  
  - Water temperature [deg C](6)
 
  
    
      | 
      Station 0500615, 1985 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      0.5 |  
      
      - |  
      
      - |  
      
      0.5 |  
      
      3.3 |  
      
      13.5 |  
      
      13.0 |  
      
      19.3 |  
      
      21.0 |  
      
      16.0 |  
      
      11.5 |  
      
      6.0 |  
      
      2.7 |  
    
    
      | 
      5 |  
      
      - |  
      
      - |  
      
      0.5 |  
      
      3.0 |  
      
      8.5 |  
      
      13.3 |  
      
      19.2 |  
      
      20.5 |  
      
      15.9 |  
      
      11.5 |  
      
      6.0 |  
      
      2.6 |  
    
    
      | 
      10 |  
      
      - |  
      
      - |  
      
      0.5 |  
      
      3.0 |  
      
      7.8 |  
      
      8.5 |  
      
      15.5 |  
      
      19.8 |  
      
      15.9 |  
      
      11.5 |  
      
      6.0 |  
      
      2.8 |  
    
    
      | 
      15 |  
      
      - |  
      
      - |  
      
      0.5 |  
      
      2.8 |  
      
      6.3 |  
      
      5.6 |  
      
      9.5 |  
      
      11.2 |  
      
      13.9 |  
      
      11.5 |  
      
      6.0 |  
      
      3.1 |  
    
    
      | 
      20 |  
      
      - |  
      
      - |  
      
      0.5 |  
      
      2.8 |  
      
      5.2 |  
      
      4.8 |  
      
      7.5 |  
      
      9.6 |  
      
      10.0 |  
      
      11.0 |  
      
      6.0 |  
      
      3.3 |  
    
    
      | 
      30 |  
      
      - |  
      
      - |  
      
      1.2 |  
      
      2.6 |  
      
      4.0 |  
      
      3.2 |  
      
      6.0 |  
      
      8.7 |  
      
      8.2 |  
      
      9.2 |  
      
      6.0 |  
      
      3.6 |  
    
    
      | 
      45 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      7.5 |  
      
      7.5 |  
      
      8.0 |  
      
      6.0 |  
      
      3.5 |  
    
    
      | 
      55 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      7.2 |  
      
      - |  
      
      6.0 |  
      
      - |  
    
  
  - Freezing period: January-February (not freeze every year).
 
  - Mixing type: Monomictic.
 
  - Notes on water mixing and thermocline formation
  Mixing dominated by the large inflow volume of the Okanagan River.
  Strong thermocline between 10-20 m from July to October. Free
  mixed November to April at 1-4deg C (if ice free). 
E. LAKE WATER QUALITY
E1 TRANSPARENCY [m]
  
    
      | 
      Station 0500615, 1985 | 
    
 
    
      | 
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      - |  
      
      - |  
      
      4.7 |  
      
      4.0 |  
      
      3.8 |  
      
      4.0 |  
      
      5.1 |  
      
      5.8 |  
      
      4.8 |  
      
      4.8 |  
      
      5.0 |  
      
      5.0 |  
    
  
E2 pH (6)
  
    
      | 
      Station 0500615, 1986 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      0 |  
      
      - |  
      
      - |  
      
      8.2 |  
      
      8.2 |  
      
      8.4 |  
      
      5.2 |  
      
      8.5 |  
      
      8.5 |  
      
      8.5 |  
      
      8.5 |  
      
      - |  
      
      - |  
    
    
      | 
      6 |  
      
      - |  
      
      - |  
      
      8.1 |  
      
      8.2 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      20 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      8.0 |  
      
      7.8 |  
      
      7.8 |  
      
      - |  
      
      - |  
    
    
      | 
      32 |  
      
      - |  
      
      - |  
      
      8.1 |  
      
      7.6 |  
      
      8.2 |  
      
      8.0 |  
      
      8.2 |  
      
      7.9 |  
      
      7.8 |  
      
      7.8 |  
      
      - |  
      
      - |  
    
  
E4 DO [mg l-1](6)
  
    
      | 
      Station 0500615, 1985 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      0.5 |  
      
      - |  
      
      - |  
      
      13.8 |  
      
      15.0 |  
      
      12.2 |  
      
      10.0 |  
      
      10.2 |  
      
      9.8 |  
      
      10.0 |  
      
      10.0 |  
      
      12.0 |  
      
      13.2 |  
    
    
      | 
      5.0 |  
      
      - |  
      
      - |  
      
      14.8 |  
      
      15.0 |  
      
      15.0 |  
      
      9.7 |  
      
      9.7 |  
      
      9.7 |  
      
      9.8 |  
      
      10.0 |  
      
      12.0 |  
      
      13.1 |  
    
    
      | 
      10 |  
      
      - |  
      
      - |  
      
      15.0 |  
      
      15.0 |  
      
      14.0 |  
      
      10.4 |  
      
      9.8 |  
      
      8.7 |  
      
      9.7 |  
      
      10.2 |  
      
      12.0 |  
      
      13.0 |  
    
    
      | 
      15 |  
      
      - |  
      
      - |  
      
      14.7 |  
      
      14.5 |  
      
      13.5 |  
      
      11.2 |  
      
      9.6 |  
      
      8.6 |  
      
      8.1 |  
      
      10.1 |  
      
      12.0 |  
      
      12.7 |  
    
    
      | 
      20 |  
      
      - |  
      
      - |  
      
      14.3 |  
      
      13.5 |  
      
      13.3 |  
      
      11.9 |  
      
      10.0 |  
      
      9.0 |  
      
      7.3 |  
      
      9.8 |  
      
      12.0 |  
      
      12.6 |  
    
    
      | 
      30 |  
      
      - |  
      
      - |  
      
      12.5 |  
      
      13.8 |  
      
      13.2 |  
      
      11.7 |  
      
      10.2 |  
      
      9.7 |  
      
      8.5 |  
      
      6.6 |  
      
      12.0 |  
      
      12.4 |  
    
    
      | 
      45 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      12.8 |  
      
      10.8 |  
      
      10.2 |  
      
      8.2 |  
      
      7.0 |  
      
      5.8 |  
      
      12.0 |  
      
      11.7 |  
    
    
      | 
      50 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      6.8 |  
      
      5.3 |  
      
      5.1 |  
      
      12.0 |  
      
      - |  
    
  
E6 CHLOROPHYLL CONCENTRATION [micro l-1](6)
  
    
      | 
      Station 0500615, 1986 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      0-10* |  
      
      - |  
      
      - |  
      
      9.3 |  
      
      5.9 |  
      
      3.7 |  
      
      1.7 |  
      
      1.4 |  
      
      1.7 |  
      
      1.8 |  
      
      - |  
      
      - |  
      
      - |  
    
  
* Mean.
E7 NITROGEN CONCENTRATION (6)
  - Total Kjeldahl N + NO3-N [mg l-1]
 
  
    
      | 
      Station 0500615, 1986 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      *1 |  
      
      - |  
      
      - |  
      
      .320 |  
      
      .230 |  
      
      .230 |  
      
      .230 |  
      
      .210 |  
      
      .230 |  
      
      .220 |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      *2 |  
      
      - |  
      
      - |  
      
      .300 |  
      
      .240 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      20 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      .230 |  
      
      .200 |  
      
      .240 |  
      
      .230 |  
      
      .320 |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      32 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      .270 |  
      
      .260 |  
      
      .250 |  
      
      .260 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      45 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      .240 |  
      
      .300 |  
      
      .370 |  
      
      .310 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
  
*1 0-10 composite. *2 0-45 composite.
E8 PHOSPHORUS CONCENTRATION (6)
  
    
      | 
      Station 0500615, 1986 | 
    
 
    
      | 
      Depth [m] |  
      
      Jan |  
      
      Feb*1 |  
      
      Mar |  
      
      Apr |  
      
      May |  
      
      Jun |  
      
      Jul |  
      
      Aug |  
      
      Sep |  
      
      Oct |  
      
      Nov |  
      
      Dec |  
    
    
      | 
      *2 |  
      
      - |  
      
      - |  
      
      16 |  
      
      16 |  
      
      15 |  
      
      20 |  
      
      8 |  
      
      11 |  
      
      8 |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      *3 |  
      
      - |  
      
      - |  
      
      15 |  
      
      16 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      20 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      17 |  
      
      12 |  
      
      6 |  
      
      10 |  
      
      16 |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      32 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      16 |  
      
      14 |  
      
      11 |  
      
      14 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
    
      | 
      45 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
      
      20 |  
      
      20 |  
      
      44 |  
      
      27 |  
      
      - |  
      
      - |  
      
      - |  
      
      - |  
    
  
*1 Overturn (February 1987: 24 micro l-1). Spring overturn
  variable.
  *2 0-10 composite. *3 20-45 composite.
F. BIOLOGICAL FEATURES
F1 FLORA
  - Emerged macrophytes
  Scirpus sp., S. lacustris, S. americanus, Equisetum fluviatile,
  Polygonum amphibium. 
  - Floating macrophytes: Lemna minor.
 
  - Submerged macrophytes (7)
 
  Myriophyllum spicatum (dominant), M. exalbescens, Elodea canadensis,
  Utricularia vulgaris, Ceratophyllum demersum, Najas flexilis,
  Chara sp., Potamogeton pectinatus, P. nodosus, P. praelongus,
  P. pusillus, P. natans, P. gramineus, P. zosteriformis, P. crispus,
  P. perfoliatus, P. foliosus, P. illinoensis, Hippuris vulgaris,
  Heteranthera dubia.
  - Phytoplankton (2, 31, 32, 33, 45, 46)
  Fragilaria crotonensis, Asterionella formosa, Anabaena circinalis. 
F2 FAUNA
  - Zooplankton (2, 31, 32, 33, 45, 46)
  Cyclops bicuspidatus thomaso, Diaptomus ashlandi, Mysis relicta. 
  - Benthos (2, 29, 50)
  Chironomus spp., Limnodrilus hoffmeisteri, Procladius sp. 
  - Fish (19, 38, 40)
  Peamouth chub, squawfish*, kokanee*. * Important for sport-fishing. 
  - Supplementary notes on the biota
  Hatchery in operation to supplement kokanee population. 
F6 PAST TRENDS (6)
  - Trend of annual mean epilimnetic (0-10 m) chlorophyll a concentration
  [micro l-
  1] 
  
    
      | 
      1975 |  
      
      1976 |  
      
      1977 |  
      
      1978 |  
      
      1979 |  
      
      1980 |  
      
      1981 |  
      
      1982 |  
      
      1983 |  
      
      1984 |  
      
      1985 |  
    
    
      | 
      4.4 |  
      
      4.5 |  
      
      3.0 |  
      
      6.7 |  
      
      6.7 |  
      
      6.6 |  
      
      3.3 |  
      
      5.3 |  
      
      7.4 |  
      
      - |  
      
      3.8 |  
    
  
F7 NOTES ON THE REMARKABLE CHANGES OF BIOTA IN THE LAKE
IN RECENT YEARS (6)
  Myriophyllum spicatum was introduced into Skaha Lake in the
  early 1970's. By the mid-1980's it had become the dominant plant
  in the lake's littoral zone.
G. SOCIO-ECONOMIC CONDITIONS
G1 LAND USE IN THE CATCHMENT AREA (8)
  
    
       | 
      
      [km2] |  
      
      [%] |  
    
    
      | 
      Natural landscape | 
    
 
    
      | 
      - Woody vegetation*1 |  
      
      ca. 3,650 |  
      
      60 |  
    
    
      | 
      Agricultural land | 
    
 
    
      | 
      - Crop field*2 |  
      
      ca. 1,220 |  
      
      20 |  
    
    
      | 
      Residential area*3 |  
      
      ca. 1,220 |  
      
      20 |  
    
    
      | 
      Total |  
      
      6,090 |  
      
      100 |  
    
  
*1 Forested.
  *2 Horticulture/orchard.
  *3 Urbanized.
  - Types of important forest vegetation
  Ponderosa pine (Pinus ponderosa)/bunchgrass community (low elevations),
  Douglas fir (Pseudotsuga menziesii) forest (higher elevations). 
  - Main kinds of crops and/or cropping systems: Orchards (tree
  fruits).
 
  - Levels of fertilizer application on crop fields: Moderate.
 
  - Supplementary notes
  Logging occurs in the upper elevation forests. Substantial tree
  fruit industry has developed over a larger part of the lower
  watershed with irrigation from Skaha Lake. 
G2 INDUSTRIES IN THE CATCHMENT AREA AND THE LAKE (9) (1981)
  
    
       | 
      
      Main products or major industries |  
    
    
      | 
      Primary industry Crop production |  
      
      Apples |  
    
  
G3 POPULATION IN THE CATCHMENT AREA (1981)
  Total population of much larger Similkameen Regional District:
  57,185. Largest urban settlement, Penticton: 23,181.
H. LAKE UTILIZATION
H1 LAKE UTILIZATION (10)
  Source of water, sightseeing and tourism (no. of visitors
  in 1980: total Okanagan 6.28 million; South Okanagan area 30%
  of the total), recreation (swimming, sport-fishing) and fisheries.
H2 THE LAKE AS WATER RESOURCES (10) (1985)
  
    
       | 
      
      Use rate [m3 day-1] |  
      
      [m3 yr-1] |  
    
    
      | 
      Domestic | 
    
 
    
      | 
      - Waterwork |  
      
      3,241 |  
       | 
    
    
      | 
      - Private intake |  
      
      875 |  
       | 
    
    
      | 
      Irrigation |  
       | 
      
      5,300,000 |  
    
    
      | 
      Industrial |  
      
      9 |  
       | 
    
  
I. DETERIORATION OF LAKE ENVIRONMENTS AND HAZARDS
I1 ENHANCED SILTATION
  - Extent of damage: Not serious.
 
I2 TOXIC CONTAMINATION
  - Present status: No information.
 
I3 EUTROPHICATION
  - Nuisance caused by eutrophication (Q)
  Unusual algal bloom (Lyngbya and Anabaena) and aesthetic damage
  to recreational use. 
  - Nitrogen and phosphorus loadings to the lake [t yr-1](11)
  (1980)
 
  
    
      | 
      Sources |  
      
      Industrial+Domestic* |  
      
      Agricultural |  
      
      Natural |  
      
      Total |  
    
    
      | 
      T-P |  
      
      2.4+1.8 |  
      
      0.4 |  
      
      7.5 |  
      
      12.7 |  
    
  
* Sewage plant+septic tanks.
  - Supplementary notes
  Increasing volume of discharge from Penticton sewage treatment
  plant in late 1960's was responsible for public concerns and
  complaints about deterioration of water quality (cyanobacteria
  blooms) in Skaha Lake. The sewage treatment plant was upgraded
  to incorporate tertiary treatment in 1971. The lake responded
  to the reduction in loading and then lake concentrations rose
  in the late 1970's and early 1980's. The significant effect of
  inter-annual variation in hydrology and increase in non-point
  loading appear to be major influences. Environmental standard
  for Total-P: 15 micro l-1 (spring overturn). (cf. 2, 10, 12,
  13, 28, 31, 33-36, 38, 39, 43, 47, 49). 
I4 ACIDIFICATION
J. WASTEWATER TREATMENTS
J1 GENERATION OF POLLUTANTS IN THE CATCHMENT AREA
  (d) Measurable pollution with limited wastewater treatment.
J3 SANITARY FACILITIES AND SEWERAGE
  - Municipal wastewater treatment systems
  No. of tertiary treatment systems: 1. 
M. LEGISLATIVE AND INSTITUTIONAL MEASURES FOR UPGRADING LAKE
ENVIRONMENTS
M1 NATIONAL AND LOCAL LAWS CONCERNED
  - Names of the laws (the year of legislation)
 
  
    - British Columbia Waste Management Act (1979)
 
    - British Columbia Waste Management Act (1982)
 
    - British Columbia Environment Management Act
 
    - Federal Fisheries Act
 
  
  - Responsible authorities
 
  
    - Government of British Columbia, Ministry of Environment
 
    - Government of British Columbia, Ministry of Environment
 
    - Government of British Columbia, Ministry of Environment
 
    - Government of British Columbia in cooperation with the Government
    of Canada
 
  
  - Main items of control
 
  
    - Discharge of water to land, air and water
 
    - Licensing of consumptive and non-consumptive water use
 
    - Prevention of detrimental environmental impacts
 
    - Management and protection of fisheries
 
  
M2 INSTITUTIONAL MEASURES
  - Okanagan Basin Study (Canada-British Columbia Okanagan Basin
  Agreement) 1969-1974 (2, 13, 14-27)
 
  - Okanagan Basin U. C. Implementation Study - Joint Agreement
  between Canada and British Columbia, 1976-1982 (11, 30-32, 44)
 
  - Okanagan Basin Water Quality Control Program, British Columbia
  Ministry of Environment, Penticton, B. C., 1986-1989 (49)
 
M3 RESEARCH INSTITUTES ENGAGED IN THE LAKE ENVIRONMENT STUDIES
  - National Water Research Institute (NWRI), Pacific & Yukon,
  West Vancouver
 
  - British Columbia Ministry of Environment, Okanagan Sub-regional
  Office, Penticton, B. C.
 
  - British Columbia Ministry of Environment, Fisheries Research
 
  - University of British Columbia, Vancouver
 
N. SOURCES OF DATA
  - Questionnaire filled by Dr. R. N. Nordon,
  Supervisor, Limnological Studies, B. C. Ministry of the Environment,
  Victoria, British Columbia.
 
  - National Topographic Series Maps, 1/50,000
  Map, Sheet 82E5.
 
  - Pinsent, M. E. & Stockner, J. G. (ed.) (1974) Limnology of
  the Major Lakes of Okanagan Basin. Tech. Suppl. V, Canada-British
  Columbia Okanagan Basin Agreement.
 
  - Historical Streamflow Summary. 606 pp. British Columbia Inland
  Waters Directorate, Water Survey of Canada, Ottawa, 1983. Station
  08NM050.
 
  - Climatic Normals 1941-1970, Climate of British Columbia.
  British Columbia Department of Agriculture.
 
  - Canadian Climate Normals 1951-1980, British Columbia. Environment
  Canada.
 
  - British Columbia Ministry of Environment. Computer Databases
  EQUIS (1970- 1985), SEAM (1985-present), Site 0500615.
 
  - Warrington, P. D. (1988) Aquatic Plants, Morphometry and
  Water and Sediment Chemistry for the Lakes in British Columbia.
  Unpublished Databases. British Columbia Ministry of Environment,
  Victoria.
 
  - Canada; Energy, Mines and Resources. N. T. S. Penticton Sheet
  82E/5, 1/50,000. Ed. EM, National Topographic Series Maps, 1:50,000
  Map, Sheet 82E/5, 1988.
 
  - Census of Canada (1981) Population Series, British Columbia,
  93-910, Table 4.
 
  - Water Management Branch, Waste Management Branch (1985) Phosphorus
  in the Okanagan Valley Lakes: Sources, Water Quality Objectives
  and Control Possibilities.
 
  - Alexander, D. G. (1982) Summary of Nitrogen and Phosphorus
  Loadings to the Okanagan Main Valley Lakes from Cultural and
  Natural Sources. Working Report, Okanagan Basin Implementation
  Agreement. 22 pp. Penticton, B. C.
 
  - Nordin, R. N. (1983) Changes in water quality of Skaha Lake,
  B. C., following reduction in phosphorus loading. "Lake
  Restoration, Protection and Management (EPA 440/5-83-001)",
  pp. 166-170. U.S. Environmental Protection Agency, Washington,
  D. C.
 
  - Stockner, J. G. & Nothcote T. G. (1974) Recent limnological
  studies of Okanagan Basin lakes and their contribution to comprehensive
  water resource planning. J. Fish. Res. Board Can., 31: 955-976.
  The following (14)-(27) are manuscript reports prepared as part
  of the Canada-British Columbia Okanagan Basin Agreement Study
  which were used extensively in the preparation of (2).
 
  - Blanton, J. 0. (1972) Relationships between heat content
  and thermal structure in the mainstem lakes of the Okanagan Valley,
  British Columbia. 17 pp.
 
  - Blanton, J. 0. & Ng. H. Y. F. (1971) Okanagan Basin studies;
  data report on the fall survey 1970. 125 pp.
 
  - --- & --- (1972) The physical limnology of the mainstem lakes
  in the Okanagan Basin. 2 volumes, 34 pp.+ 24 figures + 2 appendices.
 
  - --- & --- (1972) The circulation of the effluent from the
  Okanagan River as it enters Skaha Lake. 23 pp.
 
  - Lerman, A. (1972) Chemical limnology of the major lakes in
  the Okanagan Basin: nutrient budgets at present and in the future.
  41 pp.
 
  - Northcote, T. G., Halsey, T. G. & MacDonald, S. J. (1972)
  Fish as indicators of water quality in the Okanagan Basin lakes,
  British Columbia. 80 pp.
 
  - Patalas, K. & Salki, A. (1973) Crustacean plankton and the
  eutrophication of lakes in the Okanagan Valley, British Columbia.
  34 pp.
 
  - Saether, 0. A. & McLean, M. P. (1972) A survey of the bottom
  fauna in Wood, Kalamalka and Skaha Lakes in the Okanagan Valley,
  British Columbia. 20 pp.
 
  - St. John, B. E. (1972) The limnology of the Okanagan mainstem
  lakes. 46 pp.
 
  - Stockner, J. G. (1971) Preliminary evaluation; water quality.
  4 pp. (1972) Diatom succession in the recent sediments of Skaha
  Lakes, British Columbia. 17 pp. (1972) Nutrient loadings and
  lakes management alternatives. 13 pp.
 
  - ---, Pomeroy, M., Carney W. & Findlay, D. L. (1972) Studies
  of periphyton in lakes of the Okanagan Valley, British Columbia.
  19 pp.
 
  - ---, Carney, W. & McKenzie, G. (1972) Task 122: phytobenthos,
  littoral mapping supplement. 10 pp.+ 16 plates.
 
  - Williams, D. J. (1972) General limnology of the mainstem
  lakes in the Okanagan Valley, British Columbia. 12 pp.
 
  - Patalas, K. & Salki, A. (1973) Crustacean plankton and the
  eutrophication of lakes in the Okanagan Valley, British Columbia.
  J. Fish. Res. Board Can., 30: 519-542.
 
  - Saether, O. A. (1970) A survey of the bottom fauna in lakes
  of the Okanagan Valley, British Columbia. Fish Res. Board Can.
  Tech. Report, 196: 1-17.
 
  - Zeman, L. J. & Slaymater, H. 0. (1981) Determination of Nutrient
  Loads into and out of Skaha Lake. Inland Waters Directorate,
  Pacific and Yukon Region, Vancouver.
 
  - Truscot, S. J. & Kelso, B. W. (1979) Trophic Changes in Lakes
  Okanagan, Skaha and Osoyoos, B. C., Following Implementation
  of Tertiary Municipal Waste Treatment. Department of Environment,
  Environmental Protection Service, Pacific Region.
 
  - Jensen, E. V. (1981) Results of the Continuing Water Quality
  Monitoring Program on Okanagan Lakes for Years 1979 to 1980.
  73 pp. Waste Management Branch, British Columbia Ministry of
  Environment, Pentiction, B. C.
 
  - Stein, J. R. & Coulthard, T. L. (1971) A Report on the Okanagan
  Water Investigation. University of British Columbia. Prepared
  for Water Investigation Branch, British Columbia Water Resources
  Service.
 
  - Fleming, W. M. (1975) A model of the phosphorus cycle and
  phytoplankton growth in Skaha Lake, B. C. Verh. Int. Ver. Limnol.,
  19: 229-240.
 
  - --- & Stockner, J. G. (1975) Predicting the impacts of phosphorus
  management policies on the eutrophication of Skaha Lake, British
  Columbia. Verh. Int. Ver. Limnol., 19; 241-248.
 
  - Coulthard, T. L. & Stein, J. R. (1970) Water quality survey.
  Trans. ASAE, 13: 430-432.
 
  - Ferguson, R. G. (1949) The Interrelations among the Fish
  Populations of Skaha Lake, B. C., and Their Significance in the
  Production of Kamloops Trout (Salmo gardneri kamloops Jordan).
  84 pp. University of British Columbia, Vancouver.
 
  - British Columbia Research (1971) Sampling of the Okanagan
  Lakes - Spring 1970. Prepared for the Department of Lands, Forests
  and Water Resources, Victoria, B. C. Project No.1268 PHZ. 9 pp.+
  Tables and Figures.
 
  - Nordin, R. N. (1978) An Inexpensive in situ Algal Bioassay
  Procedure with Some Preliminary Results Bearing on Nutrient Limitations
  in Skaha Lake. 25 pp. Water Investigations Branch, British Columbia
  Ministry of Environment.
 
  - Parkinson, E. A. (1986) Skaha Hatchery Evaluation. Fisheries
  Management Report No. 87. 17 pp. Fisheries Branch, British Columbia
  Ministry of Environment.
 
  - Northcote, T. G. & Larkin, P. A. (1956) Indices of productivity
  in British Columbia lakes. J. Fish. Res. Board Can., 13: 515-540.
 
  - Larkin, P. A. & Northcote, T. G. (1958) Factors in lake typology
  in British Columbia. Verh. Int. Ver. Limnol., 13: 252-263.
 
  - Zeman, L. J. & Slaymaker, H. 0. (1985) Estimation of phosphorus
  flux in a regulated channel. Wat. Res., 19: 757-762.
 
  - Deimert, D. D. & Kelso, B. W. (1980) Algal Analysis of 0kanagan
  Area Lakes in 1979. Report prepared for the Canada-British Columbia
  Okanagan Basin Implementation Agreement. 14 pp. Environmental
  Protection Service, Environment Canada, Vancouver.
 
  - Findley, D. L., Findley, D. I. & Stein, J. R. (1973) Surface
  nitrogen and plankton in Skaha Lake, B. C., Canada. Freshw. Biol.,
  3: 111-122.
 
  - Coulthard, T. L. & Stein, J. R. (1969) A Report on the Okanagan
  Water Investigation, 1968-1969. Prepared for the Water Investigations
  Branch, British Columbia Water Resource Service.
 
  - Gray, C. B. J. (1986) Evaluation of Skaha Lake Database for
  Use in Predictive Models. Letter, 21 Feb. 1986, to P. F. Epp,
  British Columbia Ministry of Environment, Penticton, B. C.
 
  - Blanton, J. O. (1972) Relationships between the heat content
  and thermal structure in the mainstem lakes of the Okanagan Valley,
  British Columbia. "Symposium on Lakes of Western Canada",
  University of Alberta Water Resources Centre, Edmonton.
 
  - Bryan, J. E. (1988) Summary of Water Quality Trends in Lakes
  of the Okanagan Region to Spring 1988. Memo. Report to R. A.
  Nickel, 3 Oct. 1988, File 50.60000. 9 pp. British Columbia Ministry
  of Environment, Waste Management Branch, Penticton, B. C.
 
  - Saether, 0. A. & McLean, M. P. (1972) A Survey of the Bottom
  Fauna in Wood, Kalamalka and Skaha Lakes in the Okanagan Valley,
  British Columbia. Fish. Res. Board Can. Tech. Report, 342. 20
  pp.