Lake Facts & History

Physical Lake Facts


Harbor Isle Bathymetric Map

A bathymetric map, also called a  depth contour map, displays the shape and depth of a lake.  The closer the contours, the steeper the slope of the underwater terrain. They provide valuable information about the area and volume of the lake at certain depths, which allows better lake management practices to be implemented.  

This map was provided to the City by the resident who contracted the survey. The City declined to comment and/or utilize this data.


Map Image Courtesy of: Resident who privately contracted the bathymertric survey

Harbor Isle Sediment Hardness Map

Sediment mapping uses software to evaluate the acoustic reflectivity returning from the bottom of the water body to the sounding device to create a relative bottom hardness output. From this information, a relative hardness of sediment throughout the water body can be illustrated. This type of map is useful in assessments for dredging and emphasizing potential areas of sediment accumulation.

Source: http://harrisenvironmental.com.au/services/bathymetry-and-sediment-mapping/

The results from the bottom sediment mapping revealed that Harbor Isle Lake is dominated by very soft silt/clay and organic layers. The bottom sediments in Harbor Isle Lake showed a similar result in the manual samples where hard bottom was never achieved. Typical values for "hard" bottom types (like packed sand or limestone) are to be found in the range of 85-100 on this relative unit less measure used. In Harbor Isle Lake's case, the values range from 0.91 - 7.41

The unknown fill material placed in the lake in 2001 to make it shallower contributed to this overall soft bottom. Further information on the Fill Project can be found in the timeline, farther down this page.


This map was provided to the City by the resident who contracted the survey. The City declined to comment and/or utilize this data.

Map Image Courtesy of: Resident who privately contracted the sediment mapping and samples

The following information is from historical public records, eye-witness testimony,  written documentation, observational journal entries and residents' E-mail correspondence sent to the City/ related agencies from Jan 2019 to present.

Lake History Timeline (1978-2002)

According to the Army Corps of Engineers 2001 Posted Public Notice: "Approximately 575,000 cubic yards of dredged shoal material" was to be filled into Harbor Isle Lake in order to create a new "depth of 6 feet"

This project was done without any previous study of the water body or thorough water quality analysis. No follow-up testing was done to assess the water quality after completion. 

The City personnel, Mr. Mike Connors, Director of Stormwater at that time, and previous Public Works Administrator until 2015, stated in a Jul 22, 2001 St. Pete Times Article, excerpted below: "The fill will be good-quality sand" in response to concern over the project's lack of analysis and proposed solution.

Left Image: This is one of multiple sediment samples taken, in May 2019, by privately contracted scientific researchers, from the Harbor Isle Lake.   This material was found to consist almost entirely of silt and fine particles with some organic decaying matter.  This type of material was acquired with a sediment coring device at a depth of 20" and could be more than 10 feet in thickness in the lake body. 

It does not resemble standard "sand" in texture or appearance.


Lake History Timeline (2002-Present)

Important Note: Filling the lake to half of its original depth decreased the total volume of water, reducing its diluting capability, and increased the negative effect of any and all input nutrients, like nitrogen and phosphorus, by 2x (doubled or a 100% increase). 

The City placed signs at the neighborhood entrance, after multiple written requests for public notification, – the signage installed fails to state critical information about bloom: the type of algae, the type of toxicity and the fact that it could be hazardous by direct contact or possibly by breathing the surrounding air.


Source: https://www.solitudelakemanagement.com/solitude-webinar-nanobubble-aeration

City does not explain their design choice and engineering rationale for their preference to this type of system. At this time, no water quality data from the City has been taken and/or released despite multiple written requests.

From a lay person’s observational standpoint, the current condition of the blooms was worse, year to date, with increased frequencies, concentrations of blue-green algae (BGA) scums and noxious odor from BGA and putrid odors from dead animals throughout the neighborhood at multiple simultaneous locations. 

The Northwest Lobe did have amounts of visible blue-green algae streaking, but it was not sampled/tested despite being sampled the month prior. This DEP follow-up sample did not have the same results as the March 2020 sample, where after 1 week of this algacide treatment, no Microcystin toxin was detected.

FL-DEP sampled at the southern entrance, northwest lobe areas, and also center of lake, by boat and/or shoreline -- the comments on the samples do not state which type for each sample nor mention the fact the City contractor Solitude was out on the lake spraying algaecide that morning prior to DEP sampling. Wind directions were not noted either. Microcystin values were lower and as follows: Northwest Lobe: 1.1 ppb,  Center: 1.4 ppb, Southern Entrance: 1.2 ppb. Another harmful algae bloom type: "Prorocentrum minimum" algae a.k.a. "mahogany tide" was also detected. This bloom type has reoccurred since March, see March-May 2021 photos.

Currently, after the 5th peroxide treatment, and countless copper algaecide treatments in Fall 2021, toxic blue-green algae (BGA) is still present in large visible quantities.  Therefore, algal toxins and their health risks to humans are still present and the long-term exposures of the Microcystin and BMAA in the air/water are compounding.  

The City continues to pay for and implement ineffective algaecide types. Why? Throughout 2021, again,  other methods for lake remediation to proactively prevent these toxic blooms (and improve overall water quality), like improving the current design of the aeration system (via additional bottom aerators in lake lobes) have not been attempted by the City and its contractor, despite multiple requests by citizens since 2020.