
| 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 |
| 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.
| 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. |
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| 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. |
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| 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.
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).