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
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