GENEVA LAKE ENVIRONMENTAL AGENCY


Geneva Lake Data


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Hydrography and Morphometry of Geneva Lake


geneva Lake outline
Size
Area of Lake 5,425 acres
Area of Watershed 12,806 acres
Lake Volume (1) 299,182 acre ft (1)
Residence Time (2) 13.9 years
Acres of watershed per acre of Lake 3:1
(1) If the volume of water in the lake was spread out at a depth of only one foot the size of the lake would be 299,182 acres.
(2) The “residence time” is estimated as the time required for the full volume of the lake to be replaced once by the inflowing surface and ground waters associated with periods of normal precipitation.
Shape
Length of Lake 7.6 miles
Length of Shoreline 20.2 miles
Maximum Width of Lake 2.1 miles
Minimum Width of Lake 0.5 miles
Acres of watershed per acre of Lake 3:1
Depth
Percent of Lake less than 10 ft 11
Percent of Lake 10 to 70 ft 45
Percent of Lake more than 70 ft 44
Mean Depth 57 ft
Maximum Depth 144 ft


Annual Count of Boats Docked or Moored on Geneva Lake


Boat Count on Lake conducted July 30, 2009, Dry storage counts August 7, 2009
Location 2009 2008 2007 2006 2005 Shoreline (Ft)
Big Foot Beach State Park -- Riviera 318 305 281 356 352 11300
Geneva lake Outlet Lagoon (lips) 69 64 62 58 61 479
Riviera -- Geneva Bay 264 202 254 195 251 6600
Geneva Bay -- Wrigley Estate 78 23 34 33 57 5000
Wrigley Estate -- Chapin Road 97 98 112 94 122 7200
Chapin Road -- Knollwood 186 255 173 240 243 8000
Knollwood -- Cedar Point (pier 205) 299 148 179 161 140 5900
Cedar Point (peir 205) -- Williams Bay Beach 282 244 343 244 232 5000
Mun. Pier Williams Bay -- Conference Point 379 331 397 355 300 5400
Gage Marine Dry Dock 144 184 167 220 174 0
Conference Point -- George Williams College 178 178 108 133 199 4600
GW College -- Fontana Beach 348 400 465 470 395 7900
Abbey Harbor 382 396 421 408 322 3425
Gordy's Dry Dock Storage 129 54 61 46 69 0
Abbey Springs 148 144 257 257 142 0
Abbey Harbor Channel -- Rainbow Point 252 312 247 267 290 3875
Rainbow Point -- Brookwood Subdividion 287 273 275 163 276 5500
Yacht Club Dry Storage 144 251 205 121 209 0
Yacht Club -- Linn Pier 560 557 592 572 582 17200
Linn Pier -- Trinke Lagoon (include. Lagoon) 167 143 151 160 123 6800
Trinke Lagoon -- BFB State Park 343 281 271 262 314 8500
TOTALS 5054 4843 5055 4815 4853 112679
*As of 2007 all boats included. Prior to 2007count does not contain 2 new locations (leatherlips and Yacht Club) Counted only in 2004.

Year Motorboats Sailboats P.W.C's Other Totals
2005 3049 532 577 695 4853
2006 3441 449 553 372 4815
2007 3441 466 527 621 5055
2008 3358 497 546 519 4920
2009 3392 430 791 441 5054
*P.W.C. were included in others.

Town Totals: 2009 2008 2007 2006 2005
Lake Geneva 651 648 597 609 664
Linn - N. Shore 361 376 319 367 422
Williams Bay 1138 901 1027 893 871
Fontana 1269 1608 1665 900 961
Linn - S. Shore 1070 981 1014 994 1019
Totals (Dry storage not included) 4489 4514 4622 3763 3937

Totals vs Shoreline Town Shoreline 2009
  Shoreline % of Total Boat Count % of Total
Lake Geneva 18379 16% 651 15%
Linn - N. Shore 20200 18% 361 8%
Williams Bay 20900 19% 1138 25%
Fontana 20700 18% 1269 28%
Linn - S. Shore 32500 29% 1070 24%
Total: 112679 100% 4489 100%
Totals do not include dry storage boats (Gordies, Gage and Yacht Club excluded.)

Shoreline per BOAT 2009
  ShoreLine 2009 Boat Count* Ft. of Shoreline per Boat*
Lake Geneva 18379 651 28.2
Linn - N. Shore 20200 361 56.0
Williams Bay 20900 994 21.0
Fontana 20700 991 20.9
Linn - S. Shore 32500 1070 30.4
Total: 112200 4067 27.6
* does not include dry storage. ** includes dry storage.
Source: Geneva Lake Environmental Agency and the Geneva Lake Water Safety Patrol.


During August 2001, the Geneva Lake Environmental Agency conducted an aquatic plant survey to assess the condition of the submerged aquatic plant community. This plant survey was conducted as a part of the Geneva Lake Aquatic Plant Management Plan that the Agency is preparing as a part of the larger overall Geneva Lake Management Plan.

Some preliminary findings of the plant survey were interesting. Twenty-seven transects were used with each transect divided into five depth classes and a random depth within each class sampled. Twenty-three species representing 11 genera were identified. Two new species were found in this survey. Perhaps the most interesting finding of the survey was the significant increase in the aquatic plant called widgeon grass or nut grass, Ruppia currhhosa. This is a long stringy type plant with leaves that look very similar to its stem. Cut parts of this plant have been found floating in large mats in the middle of the lake and washed up on the shores.

It was by far the most abundant plant encountered in this survey. Although it was identified as being in the lake during the last aquatic plant survey in 1994, it was not found at the present densities.

Watch the Agency's web page for a more complete discussion on the aquatic plant survey and aquatic plant management plan. A complete report and a less technical summary are available at the Agency's office.

Another product of the aquatic plant survey was the preparation of an aquatic plant management plan (see map of recommended management below). In general the lake was divided into three separate aquatic plant management areas. The “No Restriction Zone” where it is recommended that there be no restriction on the aquatic plant management strategies if they are compatible with State requirements. The “Native Zone” are areas that have a diverse and healthy plant community and thus no management is needed or recommended unless conditions change. The “Watch Zone” is the largest area in size and includes areas were the plant community may need some minor management but for the most part is relatively stable. An overlay “Riparian Zone” can be located in any one of the other three zones but is restricted to only a 30 ft. wide strip running perpendicular to the shore and extends out into deeper water. This zone is to allow for riparian management of aquatic plants in their swim, mooring or pier areas.

aquatic plant management
2006 ZEBRA MUSSEL COUNTS AT FOUR LOCATIONS ON GENEVA LAKE, WALWORTH COUNTY WISCONSIN
All data expressed in mussels per meter squared
Date Lake Geneva Hillside Rd. Fontana Williams Bay
7/06 50 32 36 157
8/06 41 48 3,502 508
10/06 6,733 2,012 25,906 28,522
Sampling Results using artifical substrates in Geneva Lake, Wisconsin, Summer of 2006.
All samplers were cleaned after each count.

2007 ZEBRA MUSSEL COUNTS AT FOUR LOCATIONS ON GENEVA LAKE, WALWORTH COUNTY WISCONSIN
All data expressed in mussels per meter squared
Date Lake Geneva Hillside Rd. Fontana Williams Bay
7/07 83 72 527* 27
8/07 ** 68,779 130,437 80,797
10/07 32,861 9,937 131,807 25,264
Sampling Results using artifical substrates in Geneva Lake, Wisconsin, Summer of 2007.
All substrates cleaned after counting.
* = Sampler found laying on bottom of lake.
** = Sampler missing.

2009 E-COLI COUNTS AT THE MUNICIPAL BEACHES, GENEVA LAKE WI

E.coli Counts at Geneva Lake Public Beaches - Period 1 2009
5/20/09 5/27/09 6/1/09 6/8/09 6/15/09 GeoMean Average
Williams Bay
WB1 West End 2 40 3 12 3 6.13 12.0
WB2 Swim Pier 1 46 2 276 6 10.88 66.2
WB3 Creek/Lake Mix 1 54 3 1414 1 11.80 294.6
WB4 East of Creek 1 142 11 23 1 8.15 35.6
Fontana
F1 North End 29 120 1 7 4 9.95 32.2
F2 Guard Stand 38 13 2 7 2 6.73 12.4
F3 Swim Pier 1 19 1 3 2 2.58 5.2
F4 Abbey/Channel Mix 1 62 28 23 3 10.37 23.4
F4A 1 36 4 11 1 13.0 10.6
Linn Pier
LP1 Beach 1 43 13 2 1 14.8 12.0
Robinson Hillside
HR1 Hillside Creek 54 237 1203 2419 1046 978.3 991.8
HR2 Lake/Creek Mix 6 687 78 261 56 258.0 217.6
HR3 Hillside Beach 1 921 133 91 23 286.5 233.8
Geneva Beach
LG 1 West End 2 11 9 1 1 5.8 4.8
LG 2 Swim Pier 1 3 24 5 1 8.3 6.8
LG 3 East End 5 12 38 6 3 15.3 12.8
Rain within 24 hrs 0 0.5 0.45 0.5 0
Source: GLEA & SLH Exceed Advisory Criteria Exceed Closing Criteria

E.coli Counts at Geneva Lake Public Beaches - Period 2 2009
6/24/09 6/29/09 7/6/09 7/13/09 7/22/09 GeoMean Average
Williams Bay
WB1 West End 6 26 38 4 30 14.81 19.80
WB2 Swim Pier 12 19 31 5 7 11.99 14.33
WB3 Creek/Lake Mix 3 33 28 23 20 16.64 20.61
WB4 East of Creek 7 21 14 3 14 9.71 11.45
Fontana
F1 North End 13 1 1 7 11 3.98 6.16
F2 Guard Stand 13 6 1 4 17 5.56 7.76
F3 Swim Pier 3 5 7 6 99 9.10 21.52
F4 Abbey/Channel Mix 9 6 16 33 2419 36.96 419.99
F4A 4 3 1 35 411 11.15 77.53
Linn Pier
LP1 Beach 2 2 6 1 2 2.17 2.53
Robinson Hillside
HR1 Hillside Creek 205 75 461 240 411 233.84 270.94
HR2 Lake/Creek Mix 3 7 4 1 12 3.99 5.16
HR3 Hillside Beach 4 1 9 9 12 5.22 6.70
Geneva Beach
LG 1 West End 6 5 5 4 28 7.00 9.17
LG 2 Swim Pier 126 7 28 23 36 28.98 41.50
LG 3 East End 24 9 4 15 37 13.68 17.11
Rain within 24 hrs 0 0.05 0 0 0.2
Source: GLEA & SLH Exceed Advisory Criteria Exceed Closing Criteria

E.coli Counts at Geneva Lake Public Beaches - Period 3 2009
7/27/09 8/3/09 8/10/09 8/17/09 8/24/09 8/31/09 9/9/09 GeoMean Average
Williams Bay
WB1 West End 13 1 18 6 1 5.3 10 5.00 7.76
WB2 Swim Pier 4 1 350 27 12 1.0 96 12.30 70.14
WB3 Creek/Lake Mix 12 29 1600 461 26 488.4 26 97.70 377.49
WB4 East of Creek 15 91 1100 461 46 1.0 5 39.80 245.57
Fontana
F1 North End 1 5 1 29 5 7.4 31 5.60 11.34
F2 Guard Stand 6 5 4 23 6 2.0 435 10.50 68.71
F3 Swim Pier 19 4 6 10 9 8.5 517 15.10 81.93
F4 Abbey/Channel Mix 96 2 8 9 29 67.7 1 11.50 30.39
F4A 96 15 69 3 411 1.0 1 14.30 85.14
Linn Pier
LP1 Beach 3 7 9 2 1 1.0 1 2.30 3.43
Robinson Hillside
HR1 Hillside Creek 196 180 820 69 548 178.9 548 271.00 362.84
HR2 Lake/Creek Mix 10 1 5 7 1 7.4 173 6.40 29.20
HR3 Hillside Beach 12 4 68 10 7 1.0 10 8.1 16.00
Geneva Beach
LG 1 West End 4 9 23 2419 3 2.0 14 15.0 353.43
LG 2 Swim Pier 18 21 29 89 5 5.2 345 27.8 74.60
LG 3 East End 13 4 20 378 7 214.3 89 34.0 103.61
Rain within 24 hrs .43 0 0.45 0.53 0 0 0
Source: GLEA & SLH Exceed Advisory Criteria Exceed Closing Criteria  

Yellow colored results indicate an individual exceedence of the advisory criteria of 235 colonies per 100 ml of sample. Red colored results indicate an individual exceedence of the closing criteria of 1000 colonies per 100 ml of sample. An orange color of the geomean results indicate an exceedence of the criteria for the geomean of not less than 5 samples collected in 30 day should not exceed 126 colonies per 100 ml.

Every attempt will be made to keep this site updated and posted with the most recent data when received from the State Lab of Hygiene.


TEMPERATURE AND DISSOLVED OXYGEN PROFILES


oxygen dissolve

Lakes in temperate regions of the world follow a seasonal cycle: winter ice cover and inverse stratification where the warmest water is near the bottom and the coolest is at the top, a period after the ice melts called spring turnover when the lake is mixing from top to bottom, summer stratification when the lake establishes a warm top layer and a cold deep layer, and fall turnover when the lake mixes and is uniform from top to bottom.

The September 15, 2009 temperature and dissolve oxygen readings show the lake is strongly stratified. Surface water temperature was recorded as 23.3 C. (73.9 F) . By definition the thermocline has established from 12m (39 ft) to 17 meters (55.3 ft). In the hypolimnium water temperature changes from 10.9 C (51.6 F) at the top of the hypolimnium to 6.9 C (44.4 F) at the lake bottom.

Surface dissolved oxygen was measured at 8.7 mg/L. Good mixing of the top 10 m (32.5 m) results in rather uniform dissolved oxygen levels in the upper epolimnium. Towards the bottom of the epolimnium dissolve oxygen levels start to decrease. The top of the hypolimnium shows lower levels of oxygen until 15 meters (48.8 ft) where the dissolved oxygen levels begin to increase. Oxygen levels continue to either increase or remain rather high (7.00 mg/l +) till 34 m (110.5 ft) Oxygen levels then shaprly decrease to a value of 0.5 mg/l at the bottom. The decrease is due to the oxygen in these waters being used in both biological and chemical processes with no replacement. There is not enough light for plant to produce oxygen. Strong stratification and the limited mixing between the epolimnium and the hypolimnium caused by the thermocline, no oxygen can be added.

Fish experience higher levels of stress when dissolved oxygen levels drops below 5 mg/L. Most fish species can not survive for any period of time where dissolved oxygen is less than 2 mg/L. At this time of the year there is plenty of oxygen available for fish above 39 m (126.8 ft).