LAKE PHEWA
Fish culture in the coastal area
Photo: B.D.Swar
A. LOCATION
- Gandaki Zone, Kaski District, Pokhara, Nepal.
- 28 10 N, 82 05 E; 742 m above sea level.
B. DESCRIPTION
Lake Phewa is one of the largest lakes
of Nepal. It is situated in Pokhara Valley in the western part of the country.
The main inflows into this lake are two perennial spring - fed streams,
Harpan Khola (Khola=stream) and Seti Khola. In addition, several temporary
streams drain into the lake belongs to a warm monomictic type with thermal
stratification. The lake water has very low electrical conductivity.
Lake Phewa is very young in geological terms as
tree trunks are still standing in water down to 6 m depth. There are two
versions about the formation of this lake. According to Hagen(1969), there
was a "Paleo-Pokhara Lake" filling whole Pokhara basin and the existing
lakes are the remails of the former huge lake. But Gurung (1970) and several
other workers agree with the view that this lake was formed by damming
of tributaries by sediments of Seti River.
Lake Phewa is one of the main sources of recreation,
natural beauty, drinking water, hydroelecricity, fisheries and irrigation
in Pokhara Valley(1,2,3).
C. PHYSICAL DIMENSIONS
Surface area [km2] | 5.0 |
Volume [km3] | 39 |
Maximum depth [m] | 21 |
Mean depth [m] | 8.6 |
Normal range of annual water level fluctuation
(regulated) [m] | 1 |
Length of shoreline [km] | 18 |
Catchment area [km2] | 110 |
D. PHYSIOGRAPHIC FEATURES
D1 GEOGRAPHICAL (6,7,8)
- Bathymetric map: Fig. ASI-04-01(4).
- Main islands (name and area) : Baraki Temple (5~10 4
m2).
- Outflowing rivers and channels (number and name): 1 (Patale Chhango).
Fig. ASI-04-01
Bathymetric map (4).
?
D2 CLIMATIC
- Climatic data at Pokhara, 1977-1978
| Jan | Feb | Mar | Apr | May | Jun |
Jul | Aug | Sep | Oct | Nov | Dec | Ann. |
Mean temp. [] | 12.6 | 15.7 | 20.5 |
20.8 | 21.6 | 23.9 | 26.1 |
25.3 | 24.7 | 20.6 | 18.4 |
13.8 | 20.3 |
Precipitation [mm] | 23 | 11 | 65 |
278 | 321 | 460 | 718 |
1,118 | 332 | 332 | 101 |
54 | 1,556 |
- Water temperature [] (2)
- Station1, 1977-1978
Depth[m] | Jan | Feb |
Mar | Apr | May |
Jun | Jul | Aug |
Sep | Oct | Nov |
Dec |
Surface(0) | 16 |
17 | 20 |
23 | - |
27 | 28 |
27 | 27 |
22 | 20 |
18 |
4 | 16 | 16 |
19 | 22 | - |
26 | 25 | 25 |
25 | 22 | 20 |
18 |
8 | 16 | 16 |
17 | 18 | - |
20 | 22 | 23 |
23 | 22 | 20 |
18 |
10 | 16 | - |
17 | 17 | - |
19 | 20 | 22 |
22 | 22 | 20 |
18 |
12 | 16 | 16 |
17 | 17 | - |
19 | 20 | 21 |
22 | 22 | 20 |
18 |
14 | 16 | 16 |
16 | 17 | - |
19 | 19 | 20 |
21 | 22 | 20 |
18 |
16 | 16 | 16 |
16 | 17 | - |
19 | 19 | 20 |
21 | 22 | 20 |
18 |
18 | 16 | 16 |
16 | 17 | - |
18 | 19 | 20 |
21 | 22 | 20 |
18 |
- Freezing period: None.
- Mixing type: Monomictic.
- Notes on water mixing and thermocline formation : A stable temperature
stratification exsits from the end of February until October. The pattern
is of a classical mononictic type with one turnover in winter.
E. LAKE WATER QUALITY (6,7,8,9,10,11)
E1 TRANSPARENCY [m] Station 1, 1977-1978
Jan | Feb | Mar |
Apr | May | Jun |
Jul | Aug |
Sep | Oct |
Nov | Dec |
4 | 3 |
1.7 | 2 |
1.6 | 1.7 |
1.9 | 1.3 | 2.6 |
2 | 2.4 | 1.8 |
E2 pH (2)
Station 1, Sep. 10, 1984
Depth[m] |
Jan | Feb | Mar | Apr |
May | Jun | Jul | Aug |
Sep | Oct | Nov | Dec |
0 | - | - |
- | - | - |
- | - | - |
8.3 | - | - |
- |
| - | - | - | - |
- | - | - | - | 8.3 |
- | - | - |
2.5 | - | - | - | - |
- | - | - | - | 8.0 |
- | - | - |
5 | - | - | - | - |
- | - | - | - | 6.9 |
- | - | - |
10 | - | - | - | - |
- | - | - | - | 6.4 |
- | - | - |
15 | - | - | - | - |
- | - | - | - | 6.9 |
- | - | - |
20 | - | - | - | - |
- | - | - | - | 6.9 |
- | - | - |
E4 DO [mg l-1] ,Station 1, 1977-1978
Depth[m] |
Jan | Feb | Mar | Apr |
May | Jun | Jul | Aug |
Sep | Oct | Nov | Dec |
0 | 9 | 10 |
10 | 9 | - |
9 | 8 | 8 |
8 | 8 | 8 |
8 |
4 | 9 | 9 | 9 | 9 |
- | 6 | 6 | 6 | 7 |
8 | 8 | 8 |
8 | 9 | 9 | 5 | 0 |
- | 0 | 1 | 2 | 0 |
5 | 2 | 8 |
10 | 9 | 9 | 3 | 0 |
- | 0 | 0 | 0 | 0 |
4 | 1 | 8 |
12 | 9 | 9 | 2 | 0 |
- | 0 | 0 | 0 | 0 |
4 | 1 | 8 |
14 |
9 | 9 | 2 | 0 | - |
0 | 0 | 0 | 0 | 1 |
0 | 8 |
16 | 9 | 9 | 2 | 0 |
- | 0 | 0 | 0 | 0 |
0 | 0 | 8 |
18 | 9 | 9 | 2 | 0 |
- | 0 | 0 | 0 | 0 |
0 | 0 | 8 |
E6 CHLOROPHYLL CONCENTRATION [Êg l-1] ,Sep. 10, 1984
Depth[m] |
Jan | Feb | Mar |
Apr | May | Jun |
Jul | Aug | Sep |
Oct | Nov | Dec |
0 | - |
- | - |
- | - |
- | - |
- | 4.8 |
- | - |
- |
1 | - | - |
- | - | - |
- | - | - |
5.6 | - | - |
- |
2.5 | - | - |
- | - | - |
- | - | - |
6.5 | - | - |
- |
5 | - | - |
- | - | - |
- | - | - |
15.3 | - | - |
- |
10 | - | - |
- | - | - |
- | - | - |
1.3 | - | - |
- |
15 | - | - |
- | - | - |
- | - | - |
1.1 | - | - |
- |
20 | - | - |
- | - | - |
- | - | - |
1.1 | - | - |
- |
E7 NITROGEN CONCENTRATION (2)
- Total-N* [mg l-1], Station 1, Sep.10, 1984
Depth[m] |
Jan | Feb | Mar | Apr |
May | Jun | Jul | Aug |
Sep | Oct | Nov | Dec |
0 | - | - | - |
- | - | - | - |
- | 0.117 | - | - |
- |
2.5 | - | - | - |
- | - | - | - |
- | 0.197 | - | - |
- |
5 | - | - | - |
- | - | - | - |
- | 0.163 | - | - |
- |
10 | - | - | - |
- | - | - | - |
- | 0.326 | - | - |
- |
15 | - | - | - |
- | - | - | - |
- | 1.010 | - | - |
- |
20 | - | - | - |
- | - | - | - |
- | 1.202 | - | - |
- |
-
* Total-N is estimated from PON and DTN concentrations.
E8 PHOSPHORUS CONCENTRATION
- Total-P [mg l-1], Station 1, Sep.10, 1984
Depth[m] |
Jan | Feb | Mar | Apr |
May | Jun | Jul | Aug |
Sep | Oct | Nov | Dec |
0 | - | - | - |
- | - | - | - |
- | 0.011 | - | - |
- |
2.5 | - | - | - |
- | - | - | - |
- | 0.012 | - | - |
- |
5 | - | - | - |
- | - | - | - |
- | 0.011 | - | - |
- |
10 | - | - | - |
- | - | - | - |
- | 0.011 | - | - |
- |
15 | - | - | - |
- | - | - | - |
- | 0.018 | - | - |
- |
20 | - | - | - |
- | - | - | - |
- | 0.026 | - | - |
- |
F. BIOLOGICAL FEATURES
F1 FLORA
- Phytoplankton: Merismopedia elegans, Microcystis spp., Synura
petersenii, Dinobryon divergens, Mallomonas spp., Navicula rhyncocepala,
Navicula spp., Cyclotella spp., Tabellaria fenestrata, Diatomella
spp., Stephanodiscus carconensis, Nitchia acicularis, Melosira granulata,
M. italica, M. spp., Synedra acus, Surirella robusta, Rhoicosphenia
curvata, Botryococcus braunii, Centritractus belonophorus, Ceratium hirundinella,
Gymnodinium spp., Peridinium spp., Crytomonas compressa,
C. spp., Gonyostumum semsu, G.spp., Staurastrum pseudopelagicum,
S. dimazum, S. dorsidentiferum, S. curvatum, S.spp., Srthrodesmus
triangularis, A. ralfsii, Arthrodesmus spp., Euastropsis richteri,
Cosmarium contractum, C. reniforme, Cosmarium spp., Spondirosium
spp., Closterium spp., Oocystis lacustris, O. spp., Nephrocytium
spp., Glaeotaenium loitelsbergerianum, Tetraedron hastatum, Crucigenia
tetrapedia, Galenkinia radiata, Carteria cordiformis, Chlamydomonas moewusii,
Dictyospherium ehrenbergianum, D. pulchellum, Gonotozygon pilosm(7,9).
F2 FAUNA
- Zooplankton: Rotifera (Collotheca sp., Conochilus unicornis,
Hexarthra mira, Keratella cochlearis, K. tropica, Brachionus patulus, Tricocera
cylindrica, T. similis) ; Cladocera (Diaphanosoma excisum, Daphnia
longispina, D. lumholtzi, Ceriodaphnia reticulata, C. cormuta, Simocephalus
vetulus elisabethae, Bosmina longirostris, Eubosmina coregoni, Moina micrura
) ; Copepoda (Neodiaptomus strigilipes, Phyllodiaptomus blanci, Mesocylops
leuckarti, Thermocyclops crassus, Tropocyclops confinis, Chaoborus
sp.) (12,13,14,15,16,17).
-
Fig. ASI-04-02. Seasonal abundance of Crustacean zooplankton in
Lake Phewa, Jan.-Dec., 1977. Numbers represent the animals/m2 and histograms
represent the percentage of different groups(15).
Months | Diaphanosoma excisum |
Daphinia longispina | Daphnia lumholtzi |
Ceriodaphnia cornuta | Bosmina longirostris |
Moina micrura | Calanoida |
Cyclopodia | Nauplii | Chaoborus spp. |
Jan | 116,900 | 1,200 | 5,600 |
5,800 | 200 | - | 77,800 |
6,600 | 6,000 | 1,200 |
Feb | 54,200 | 1,100 | 84,700 |
4,100 | 300 | - | 56,700 |
2,700 | 6,000 | 2,400 |
Mar | 15,400 | 2,700 | 157,200 |
33,900 | 6,200 | | 48,800 |
8,400 | 25,200 | - |
Apr |
4,500 | - | 2,200 | 2,100 |
- | - | 22,100 | 13,600 |
7,500 | 200 |
May | 41,100 | - | - |
1,200 | 500 | |
12,100 | 9,200 | 5,100 | 0 |
Jun | 4,900 | - | - |
3,500 | - | 12,200 | 8,400 |
1,500 | 3,900 | 1,200 |
Jul | 2,400 | - | 400 |
1,500 | - | 7,200 | 6,300 |
3,900 | 3,900 | 900 |
Aug | 5,100 | - | 800 |
- | 400 | 3,600 | 5,500 |
3,900 | 2,100 | 1,600 |
Sep | 51,300 | - | 2,300 |
35,400 | 85,500 | 10,600 | 23,100 |
608,600 | 130,300 | 1,700 |
Oct | 1,400 | 1,100 | 58,800 |
1,200 | 400 | - | 14,000 |
21,000 | 4,100 | 2,900 |
Nov | 3,800 | 300 | 800 |
15,000 | 700 | - | 3,000 |
9,000 | 6,600 | 2,100 |
Dec | 26,500 | 200 | 19,100 |
1,000 | - | - | 25,600 |
4,500 | 2,700 | 1,000 |
- Fish : Barilius barna, B. bendelensis, Cirrhinus rewa*,
Labeo gonius*, L. rohita*, Puntius sarana, P. sophora*,
Tor tor*, T. putitora*, Acrossochielus hexagonolepsis*,
Anguilla bengalensis, Xenentodon cancilla, Channa gachua, Mastacemgbelus
armatus, Aristichthys nobilis*, Hypophthalmichthys molitrix.*,
Ctemophargodon idellus*, Cyprinus carpio* (economically important)
(18,19).
F3 PRIMARY PRODUCTION RATE [mg O2 l-1 hr-1] ,1977-1978 (6)
| Annual total |
Net production | 0.35 |
Dark respiration | 1.85 |
Gross production | 2.2 |
* Estimated by a modified light/dark oxygen method.
F5 FISHERY PRODUCTS
- Annual fish catch in 1985 : 40 [metric tons].
G. SOCIO-ECONOMIC CONDITIONS (Q)
G1 LAND USE IN THE CATCHMENT AREA
| Area [km2] | [%] |
Natural landscape | | |
Woody vegetation | 30 |
27 |
Herbaceous vegetation | 10 |
9 |
Swamp | 2 | 2 |
Others | 8 | 8 |
Agricultural land | | |
Crop field | 20 |
18 |
Pasture land | 20 | 18 |
Residential area | 20 | 18 |
Total | 110 | 100 |
- Main types of woody vegetation : Subtropical deciduous broad leaf forest.
- Main types of crops : Rice, maize, wheat, fruit trees.
- Levels of fertilizer application on crap fields : Light.
G2 INDUSTRIES IN THE CATCHMENT AREA AND THE LAKE (1984)
| Gross product per year [US $] |
Fisheries | 75,000 |
G3 POPULATION IN THE CATCHMENT AREA
|
| Population |
Population density [km-2] | Main cities |
Urban | ca. | 10,000 |
- | Pokhara |
Rural | ca. | 5,000 |
- | |
Total | ca. | 15,000 |
136 | |
H. LAKE UTILIZATION (Q)
H1 LAKE UTILIZATION
Sightseeing and tourism (number of visitors in 1984 : 50,000), recreation
(swimming, sport fishing, yachting), fisheries and source of water.
H2 THE LAKE AS WATER RESOUCE (1984)
| Use rate [m3 sec-1] |
Domestic water | 1.2 x 10-4 |
Irrigation | 10 |
Power plant | 10 |
I. DETERIORATION OF LAKE ENVIRONMENTS AND HAZARDS (Q)
I1 ENHANCED SILTATION
- Extent of damage: Serious.
- Supplementary notes: The lake is receiving heavy silt loads every year
during the rainy season due to the derorestration on the northern belt
of the watershed area.
I3 EUTROPHICATION
- Nuisance caused by eutrophication: None.
I4 ACIDIFICATION
M. LEGISLATIVE AND INSTITUTIONAL MEASURES FOR UPGRANDING LAKE ENVIRONMENTS
(Q)
M3 RESEARCH INSTITUTE ENGAGED IN THE LAKE ENVIRONMENT STUDIES
- Fisheries Development Center, Baidam, Phewa Tal, Pokhara, Nepal
N. SOURCES OF DATA
-
(Q) Questionnaire filled by Mr.Deep B. Swar, Fisheries Development Center,
Pokhara, Nepal, based on the data from the following sources.
(1) Hagen, T. (1969) Report on the geological survey
of Nepal. Vol.1. Preliminary reconnaissance. Denkshr. d. Schweiz. Naturf.
Ges., 86: 1-185
(2) Gurung, H., (1970) Geomorphology of Pokhara Valley.
Himalayan Review, 2/3 : 37-49.
(3) Yamanaka, H., Yoshida, M. & Arita, K. (1982)
Terrace landform and quaternary deposit around Pokhara Valley, central
Nepal. Journal of Nepal Geological Society, 2 : 113-142.
(4) Ferro, W. & Swar, D. B. (1978) Bathymetric
maps from three lakes of the Pokhara Valley (Nepal). J.Inst Sc. Tribhuvan
University, Kathmandu, Nepal, 1: 177-188.
(5) Swar, D.B. (1980) Present status of limnological
studies and research in Nepal. "Proceedings of the First Workshop on the
Promotion of Limnology in the Developing Countries" (ed. Mori, S. &
Ikushima , I.), pp.43-47. XXI SIL Congress, Kyoto.
(6) Ferro,W. (1981/1982) Limnology of the Pokhara
Valley lakes (Himalayan Region, Nepal) and its implication for fishery
and fish culture. Journal of Nepal Research Center, Kathmandu, Nepal, 5/6
: 27-52.
(7) Hickel, B. (1973) Limnological investitations
in lakes of the Pokhara Valley, Nepal. Int. Revue ges. Hydrobiol., 58 :
659-672.
(8) Swar, D.B. & Fernando, C.H. (1980) Some studies
on the ecology of limnetic crustacean zooplankton in Lakes Begnas and Rupa,
Pokhara Valley, Nepal. Hydrobiologia, 70 : 235-245.
(9) Nakanishi, M. (1986) Limnological
study in Phewa, Begnas and Rupa Lakes. "Studies on Distribution, Adaptation
and Evolution of Microorganisma in Nepal Himalaya (Second Report)"(ed.
Ishida, Y.), pp.1-13. Kyoto Univ., Kyoto.
(10) Nakanishi, M., Terashima, A., Watanabe, M. &
Misra, P. (1984) Preliminary report on limnological survey in lakes of
Pokhara Valley (Nepal) in November-Dexember, 1982. "Studies on Distribution,
Adaptation and Evolution of Microorganisms in Nepal Himalaya (Preliminary
Report)" (ed. Kadota, H.), pp.31-41. Kyoto Univ., Kyoto.
(11) Kato, K. & Hayashi, H. (1982) Limnological
presurvey of Lake Phewa, Nepal J. Fac. Sc. Sinshu Univ., 15 : 27-29.
(12) Swar, D. B. & Fernando, C.H. (1979a) Seasonality
and fecundity of Daphnia lunholtzi Stars in Lake Phewa Nepal. Hydrobiologia,
64 : 261-268.
(13) - & - (1979b) Cladocera from Pokhara Valley,
Nepal with notes on Hydrobiologia, 66 : 113-128.
(14) Swar, D. B. (1979) Some studies on freshwater
crustacean zooplankton (natural fish food) from Nepal. M. Sc. thesis, University
of Waterloo, Ontario, Canada, 152 pp.
(15) - (1981) Seasonal abundance of limnetic crustacean
zooplankton in Lake Phewa, Pokhara Valley, Nepal. Verh. Int. Ver. Limnol.,
21 : 535-538.
(16) Dumont, H. J. & van de Velde, I. (1977)
Report on the collection of Cladocera and Copepoda from Nepal. Hydrobiologia,
53:1:55-65.
(17) Deans, G. & Dumont, H. J (1974)
Rotifers from Nepal, with description of a new species of Scaridium
and a discussion of Nepalese representative of the genus Hexarthra.
Biol. Jb. Dodonaea, 42:61-81.
(18) Ferro, W. (1980) Data on the
fishery in Pokhara Valley (Nepal) and their implications for the fishery
management. J. Inst. Sc. Tribhuvan University, Kathmandu, Nepal, 3:221-236.
(19) - & Badagami, P.R.(1980)
On the biology of the commercially important species of fish of the Pokhara
Valley (Nepal). J. Inst. Sc., 3:237-250.