CAYUGA LAKE
A view over looking the western shore
Photo: C. Rossano
A. LOCATION
New York, USA. 42:2 N, 76:1 W; 116.4 m above sea level.
B. DESCRIPTION
Cayuga Lake is one of a group of long and narrow lakes
located in western New York State known as the Finger Lakes. The basins
of these north-south oriented lakes were formed by the advance of ice masses
during the Ice Ages, and further sculpted by glacial meltwater during the
interglacial and postglacial periods. The lake has a maximum depth of 132
m, with the deepest point extending below sea level. Cayuga is the longest
of the Finger Lakes, with a length of 61.4 km, yet the average width is
a mere 2.8 km. The lake is the lowest in elevation among the Finger Lakes,
and this has resulted in the formation of extensive marshes around its
northern end.
Although the Finger Lakes region is now well-known
for its many vineyards and orchards, it had been densely forested up until
the early 1800's when large areas were cleared for agriculture by white
settlers. The forests are now in the process of expanding as marginal farmland
is abandoned and gradually invaded by trees. In the drainage basin, approximately
half the land area is in active agriculture, one-third is forested, and
2% is residential.
The water level of the lake is regulated by Mud
Lock at the north end. The lake has been connected to Lake Ontario by the
Erie Barge Canal system since 1828. The lake is also connected by the Seneca
River to Seneca Lake. Cayuga Lake is drawn down in mid-December to minimize
ice damage and for maximizing storage during the period of heavy spring
runoff. The lake is a major recreational resource for the region, and its
waters are also used for both drinking and waste disposal. Industrial development
is low and does not constitute a substantial pollution hazard. The fish
population is managed to maximize salmonid production. Significant sport-fishing
also exist for smelt, smallmouth bass, and other species (2).
C. PHYSICAL DIMENSIONS (2, 3)
Surface area [km2] |
172 |
Volume [km3] |
9.4 |
Maximum depth [m] |
132.6 |
Mean depth [m] |
54.5 |
Water level |
Regulated |
Length of shoreline [km] |
153.4 |
Residence time [yr] |
18.2* |
Catchment area [km2] |
2,033 |
* From Singley (1973). |
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D. PHYSIOGRAPHIC FEATURES
D1 GEOGRAPHICAL (2) Bathymetric map: Fig. NAM-17-01. Names of main
islands: None. Number of outflowing rivers and channels (name): 1.
D2 CLIMATIC Climatic data at Ithaca, 1942-1962 (2)
Mean temp [deg C]
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Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Ann. |
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-4.4 |
-3.9 |
0.6 |
7.2 |
12.8 |
18.3 |
20.5 |
20.0 |
16.1 |
10.6 |
3.9 |
-2.8 |
8.3 |
Precipitation [mm]
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Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
Ann. |
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52 |
56 |
68 |
77 |
94 |
89 |
95 |
98 |
79 |
84 |
74 |
58 |
924 |
Number of hours of bright sunshine (Binghamton): 612 hr yr-1 (4). Snowfall
(Binghamton): 132 mm (4). Solar radiation: 13.7 MJ m-2 day-1 (2).
Fig. NAM-17-01
Bathymetric map (2).
Water temperature: Fig. NAM-17-02.
Fig. NAM-17-02
Euphotic zone temperature, 1968-1970 (5).
Freezing period: Maximum coverage in February (2). Mixing type: Monomictic
(2).
E. LAKE WATER QUALITY
E1 TRANSPARENCY (2) Light extinction coefficient K [m-1] 1968-1970
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Depth |
Jan |
Feb |
Mar |
Apr |
May |
Jun |
Jul |
Aug |
Sep |
Oct |
Nov |
Dec |
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.250 |
.292 |
.250 |
.463 |
.301 |
.370 |
.854 |
.598 |
.403 |
.321 |
.286 |
- |
E2 pH (2) Taughannock, Summer 1968
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Min |
Max |
Ann. |
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Epilimnion |
8.0 |
8.8 |
8.4 |
Hypolimnion |
7.5 |
8.2 |
8.1 |
Glenwood, Summer 1968
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Min |
Max |
Ann. |
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Epilimnion |
7.5 |
8.7 |
8.2 |
Hypolimnion |
7.7 |
8.2 |
8.0 |
E4 DO [mg l-1](2) 1968
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Late May-early Jun |
Sep |
Nov |
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Hypolimnion |
12 |
6.2*1 - |
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Near the bottom |
- |
- |
6.8-9.6*2 |
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- |
- |
7.9*1 |
*1 Sheldrake. *2 Milliken.
E6 CHLOROPHYLL CONCENTRATION [micro g l-1](2) Mean of 1-16 stations,
1968-1969
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Depth[m] |
Jun |
Aug |
Sep |
Oct |
Nov |
Jan |
Feb |
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00-09 |
3.7 |
3.8 |
1.9 |
1.6 |
2.5 |
1.3 |
1.4 |
10-19 |
2.1 |
0.9 |
1.3 |
2.5 |
2.0 |
- |
- |
20-29 |
1.2 |
0.5 |
0.7 |
1.1 |
1.4 |
- |
- |
30-39 |
0.7 |
0.4 |
0.2 |
0.5 |
0.6 |
1.1 |
1.5 |
40-49 |
0.2 |
0.3 |
0.2 |
0.8 |
0.2 |
0.6 |
1.6 |
50-59 |
- |
- |
- |
0.2 |
1.4 |
- |
1.4 |
60-69 |
- |
0.4 |
0.3 |
0.3 |
0.9 |
1.4 |
1.6 |
70-79 |
- |
0.2 |
0.2 |
- |
1.0 |
0.4 |
1.3 |
80-89 |
- |
- |
0.2 |
0.2 |
0.2 |
- |
- |
90-99 |
- |
- |
0.2 |
- |
0.2 |
0.9 |
1.6 |
100- |
- |
- |
- |
- |
0.2 |
0.8 |
1.4 |
E7 NITROGEN CONCENTRATION (2) NH4-N [micro g l-1] Lakewide averages,
1972
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Depth[m] |
May |
Jul |
Nov |
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S*1 |
0 |
43 |
- |
*2 |
0 |
36 |
0 |
*1 Surface. *2 All depth.
NO3-N [micro g l-1]: Fig. NAM-17-03.
Fig. NAM-17-03
NO3-N distribution during 1968-69.
E8 PHOSPHORUS CONCENTRATION (2) PO4-P [micro g l-1] 1968-1969
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Depth[m] |
Jul |
Aug |
Sep |
Oct |
Nov |
Jan |
Feb |
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00 -09 |
3.7 |
1.3 |
1.0 |
1.0 |
1.8 |
12.2 |
11.4 |
10 -19 |
3.3 |
3.2 |
2.6 |
1.2 |
2.6 |
- |
- |
20 -29 |
4.5 |
4.0 |
1.4 |
1.3 |
5.7 |
- |
- |
30 -39 |
5.4 |
6.0 |
5.7 |
3.1 |
7.3 |
16.0 |
12.7 |
40 -49 |
6.2 |
6.2 |
6.0 |
6.6 |
4.4 |
12.5 |
10.3 |
50 -59 |
- |
- |
- |
9.6 |
8.1 |
- |
12.1 |
60 -69 |
- |
11.4 |
10.8 |
13.3 |
10.0 |
13.1 |
13.0 |
70 -79 |
- |
12.9 |
10.5 |
- |
17.7 |
12.2 |
12.6 |
80 -89 |
- |
- |
10.2 |
14.0 |
20.1 |
- |
- |
90 -99 |
- |
- |
9.7 |
- |
21.9 |
12.7 |
11.6 |
100- |
- |
- |
- |
- |
- |
12.9 |
12.7 |
Total-P [g m-2]* Averages of 5-9 stations, 1969-1970
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1969 |
1970 |
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Winter |
Jul |
Nov |
Apr |
May |
Jun |
Jul |
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1.74 |
1.64 |
1.86 |
2.21 |
1.67 |
1.50 |
1.46 |
* In a 100 m water column.
E10 PAST TRENDS (2) pH*1
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1927*2 |
1950*3 |
1951*3 |
1952*3 |
Epilimnion |
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Minimum |
7.9 |
8.1 |
8.1 |
8.1 |
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Maximum |
9.0 |
8.3 |
8.5 |
8.4 |
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Annual |
8.5 |
8.2 |
8.3 |
8.2 |
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Hypolimnion |
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Minimum |
7.8 |
7.5 |
7.6 |
7.8 |
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Maximum |
8.8 |
8.1 |
8.1 |
8.1 |
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Anual |
8.2 |
7.9 |
7.9 |
7.9 |
*1 During the summer months. *2 Glenwood. *3 Taughannock.
F. BIOLOGICAL FEATURES
F1 FLORA (2) Submerged macrophytes Myriophyllum exalbescens, Heteranthera
dubia, Potamogeton crispus, P. pectinatus, Ceratophyllum demersum, Vallisneria
americana. Phytoplankton Coelastrum microporum, Dictyosphaerium pulchellum,
Scenedesmus bijuga, S. quadricauda, Asterionella formosa, Fragilaria crotonensis,
Stephanodiscus astraea, Synedra spp., Peridinium cinctum, Aphanizomenon
flos-aquae.
F2 FAUNA (2) Zooplankton Diaptomus minutas, Cyclops bicuspidatus,
Bosmina longirostris, Ceriodaphnia laticaudata, Codonella cratera, Ascomorpha
sultans, Chonochilus unicornis, Keratella cochlearis, Polyarthra major.
Benthos Mysidea (Mysis relicta), Amphipoda (Gammarus linnaeus), Diptera
(Ablabesmyia spp., Paralauterborniella nigrohalterale, Paratendipes albimanus,
Cryptochironomus nais, Stitochironomus devinctus, Tribelos jucundus, Microspectra
deflecta). Fish Salvelinus namaycush, Micropterus dolomieui, Osmerus mordax,
Alosa pseudoharengus, Salmo gairdneri, S. salar, Perca flavescens, Petromyzon
marinus, Coregonus artedii. Supplementary notes on the biota The composition
of the phytoplankton is especially illustrative of the intermediate trophic
status of Cayuga.
F3 PRIMARY PRODUCTION RATE (2) Primary production rate [mg C
m-2 day-1] 1969-1970: 366-418.
F4 BIOMASS (2) Total number of phytoplankton cells [cells l-1]
1972
June: ca. 200,000. |
July: 7800,000. |
Fig. NAM-17-04
Biomass of the major crustacean zooplankton and the total of all in
the epilimnion, 1972.
F5 FISHERY PRODUCTS Annual fish catch [kg]: 5.675*. * Lake trout.
F7 NOTES ON THE REMARKABLE CHANGES OF BIOTA IN THE LAKE IN RECENT
YEARS (2) Since the early 1940's marked decreases have occurred in
the abundance and/or the areal distribution of submerged macrophytes. Anacharis
canadensis, Potamogeton richarsonii, Najas flexilis, Nitella sp., Vallisneria
americana, Potamogeton pectinatus, Zannichellia palustris, and the alga
Chara sp. Increases occurred in Myriophyllum exalcescens, Heteranthera
dubia, Potamogeton crispus, and Ceratophyllum demersum and were particularly
large for the first two.
G. SOCIO-ECONOMIC CONDITIONS (2)
G1 LAND USE IN THE CATCHMENT AREA
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Area [km2] |
[%] |
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Natural landscape |
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Forest |
582.44 |
37.1 |
Agricultural land |
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Active agriculture |
903.96 |
58 |
Residential area |
36.85 |
2.3 |
Others |
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Commercial |
3.55 |
0.2 |
Industrial |
1.56 |
0.1 |
Outdoor recreation |
13.14 |
0.8 |
Extractive |
3.85 |
0.2 |
Public |
15.52 |
1.0 |
Transportation |
4.91 |
0.3 |
Total |
1,565.78 |
100 |
Types of important forest Elm-ash-red maple forest (willow, sycamore, beech,
cottonwood), Oak-hickory forest (yellow poplar, elm, red maple, hard maple,
hemlock, beech), Beech-hard maple forest (hemlock, basswood, white pine,
white ash, black cherry, red maple, birch). Types of the other important
vegetation: Marsh (Typha, Scirpus). Main kinds of crops Field and forage
crops, grain, rotated tillable pasture.
G3 POPULATION IN THE CATCHMENT AREA 1970
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Population |
Major cities |
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Population |
density [km-2] |
(population) |
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Total |
90,221 |
43.9 |
Ithaca (26,226) |
H. LAKE UTILIZATION
H1 LAKE UTILIZATION Source of water, fisheries, tourism and recreation
(swimming, sport-fishing, boating).
I. DETERIORATION OF LAKE ENVIRONMENTS AND HAZARDS
I3 EUTROPHICATION (2) Nitrogen and phosphorus loadings to the lake
Fig. NAM-17-05
Inputs of phosphorus (molybdate reactive and total) and nitrogen (nitrate
and ammonium) during the 1970-1971 hydrologic year from tributaries and
atmospheric fallout [metric tons yr-1].
J. WASTEWATER TREATMENTS (2)
J2 APPROXIMATE PERCENTAGE DISTRIBUTION OF POLLUTANT LOADS Nitrogen
and phosphorus inputs and loadings (excluding the Seneca River) for 1970-71
with waste discharges calculated and land runoff determined by difference
[t yr-1]
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Soluble-N |
Total- P |
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Waste discharge |
200.3 |
88.6 |
Land runoff |
1,694.1 |
47.4 |
Precipitation |
565.6 |
3.4 |
Groundwater |
- |
- |
Other |
- |
- |
Volumetric loading [micro g 1-1 yr-1] |
262 |
14.9 |
Areal loading [g m-2 yr-1] |
14.2 |
0.54 |
Computation data for non-point source total-P runoff in the basin
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Land use |
Runoff factor |
Runoff of total-P |
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[g km-2 yr-1] |
[1,000 kg yr-1] |
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Active agriculture |
46 |
41.6 |
Forest |
11.7 |
6.8 |
Inactive agriculture and other |
23.3 |
9.0 |
J3 SANITARY FACILITIES AND SEWERAGE
Percentage of rural population with adequate sanitary facilities (on-site
treatment systems): ca. 52%.
N. SOURCES OF DATA
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Greeson, P. E. & Williams, G. E. (1970) U.S., Geol. Surv. N. Y. State
Dep. Environ. Conserv. Bull. 68B, 1-122.
-
Oglesby, R. T. (1978) The limnology of Cayuga Lake, "Lakes of New York
State 1, Ecology of the Finger Lakes" (ed. Bloomfield, J. A.), pp. 1-120.
Academic Press, New York, San Francisco, London.
-
Singley, G. W. (1973) Report prepared for New York State Electric and Gas
Corporation by NUS Corp., Rockville, Maryland.
-
Court, A (1974) The climate of the conterminous United States. "World Surveys
of Climatology, Volume 11, Climates of North America" (ed. Bryson, R. A.
& Hare, F. K.), p. 312. Elsevier Scientific Publishing Company, Amsterdam-London-New
York.
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Peterson, B. J. (1971) Ph. D. Thesis, Cornell University, Ithaca, New York.