Pass

3 out of 3 indicators were rated as PASS.

All three indicators must pass for the bay to be rated as PASS.

Learn more about how this report is created

Summary:

Overall water quality in Blackburn Bay continued to be good in 2022. The mean values of both Chlorophyl and Total Nitrogen increased slightly, with nitrogen edging above the target level of 0.36 mg/l. Considering the impact of Hurricane Ian on coastal water quality, these slight increases are not unexpected. Total Phosphorus concentrations continued to be very low and not of concern.

Note: Beginning in 2020, Sarasota County switched from measuring apparent color to true color. The latter will be added to Bay Conditions reports in the near future.

Blackburn Bay

Blackburn Bay

Water Chemistry Ratings

Total nitrogen, total phosphorus, and chlorophyll a levels are monitored carefully by water resource managers and used by regulatory authorities to determine whether a bay meets the water quality standards mandated by the Clean Water Act. The trend graphs for these indicators are shown below, along with their target and threshold values. A target value is a desirable goal to be attained, while a threshold is an undesirable level which is to be avoided. An individual indicator receives an "Excellent" rating if its mean value is below the target, a "Good" rating if its mean value is above the target but does not exceed the threshold, and a "Caution" rating if the mean value exceeds the threshold. Learn More about these ratings and how they are calculated »

The charts below illustrate the general trend of water quality parameters. They show a six-month running average, which moderates high and low values in the data.

Chart Legend
  • Six-month Moving Average
  • Annual Mean
  • Target
  • Threshold
Good

Chlorophyll a

Units: ug/l Year
2022
Historical
period of record
High 39.55 59.70
Mean 6.69 5.47 6.02916 6.0000000000
Low 0.92 0.20
No. of Samples 48 2172
  • Six-month
    Moving Average
  • Annual
    Mean
Good

Nitrogen, Total

Units: mg/L Year
2022
Historical
period of record
High 1.065 2.205
Mean 0.369 0.336 0.18391913 0.3600000000
Low 0.175 0.055
No. of Samples 48 1331
  • Six-month
    Moving Average
  • Annual
    Mean
Excellent

Phosphorus, Total

Score: Excellent How was this determined?
Units: mg/L Year
2022
Historical
period of record
High 0.170 0.530
Mean 0.063 0.092 0.0632406 0.1700000000
Low 0.050 0.050
No. of Samples 48 1342
  • Six-month
    Moving Average
  • Annual
    Mean

Dissolved Oxygen

Units: mg/l Year
2022
Historical
period of record
High 8.63 11.90
Mean 6.12 6.42 1.1292
Low 3.93 1.27
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Apparent Color

Note: The latest available sample for this parameter is from December 2019
Units: PCU Year
2022
Historical
period of record
High 250.00
Mean 19.86 26.58372
Low 2.00
No. of Samples 0 1194
  • Six-month
    Moving Average
  • Annual
    Mean

BOD, Biochemical oxygen demand

Units: mg/l Year
2022
Historical
period of record
High 4.20 7.10
Mean 1.11 1.06 0.67962
Low 0.50 0.50
No. of Samples 48 1227
  • Six-month
    Moving Average
  • Annual
    Mean

Dissolved oxygen saturation

Units: percent (%) Year
2022
Historical
period of record
High 115.00 198.00
Mean 90.33 93.81 15.46853
Low 63.00 20.00
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Karenia brevis ("red tide")

Units: #/l Year
2022
Historical
period of record
High 1246000.00 2280000.00
Mean 59229.17 59134.60 225786.73904
Low 0.00 0.00
No. of Samples 48 893
  • Six-month
    Moving Average
  • Annual
    Mean

Light Attenuation

Units: K(1/m) Year
2022
Historical
period of record
High 2.38 5.03
Mean 0.87 0.89 0.49236
Low 0.26 0.02
No. of Samples 48 1213
  • Six-month
    Moving Average
  • Annual
    Mean

Nitrogen, Ammonia + Ammonium as N

Units: ug/l Year
2022
Historical
period of record
High 37.00 132.00
Mean 16.17 15.50 13.9245
Low 5.00 5.00
No. of Samples 48 1340
  • Six-month
    Moving Average
  • Annual
    Mean

Nitrogen, Kjeldahl

Units: mg/L Year
2022
Historical
period of record
High 1.060 2.200
Mean 0.393 0.369 0.18253483
Low 0.170 0.050
No. of Samples 48 1343
  • Six-month
    Moving Average
  • Annual
    Mean

Nitrogen, Nitrite + Nitrate as N

Units: mg/L Year
2022
Historical
period of record
High 0.006 0.065
Mean 0.005 0.006 0.00426667
Low 0.005 0.005
No. of Samples 48 1664
  • Six-month
    Moving Average
  • Annual
    Mean

pH

Units: None Year
2022
Historical
period of record
High 8.08 8.40
Mean 7.92 7.93 0.16782
Low 7.66 6.10
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Salinity

Units: PSS Year
2022
Historical
period of record
High 36.30 39.30
Mean 32.68 32.79 4.12469
Low 20.40 5.70
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Specific conductance

Units: umho Year
2022
Historical
period of record
High 54700.00 58760.00
Mean 49797.92 49934.46 5727.779
Low 32700.00 10130.00
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Temperature, water

Units: deg F Year
2022
Historical
period of record
High 89.24 92.84
Mean 78.59 76.80 8.8402
Low 59.00 47.84
No. of Samples 48 1356
  • Six-month
    Moving Average
  • Annual
    Mean

Turbidity

Units: NTU Year
2022
Historical
period of record
High 8.00 39.00
Mean 3.26 3.88 3.20278
Low 1.30 0.20
No. of Samples 48 1338
  • Six-month
    Moving Average
  • Annual
    Mean

Annual Averages

Indicator Units 2018 2019 2020 2021 2022 Trend
Dissolved Oxygen mg/l 6.00 6.26 6.34 6.78 6.12
Dissolved oxygen saturation percent (%) 87.46 90.96 91.10 96.67 90.33
Light Attenuation K(1/m) 0.99 0.95 0.83 0.84 0.87
Salinity PSS 32.58 31.38 31.39 31.97 32.68
Turbidity NTU 2.81 5.11 3.61 2.59 3.26

Other Measures of Bay Health

In addition to nutrient levels and chlorophyll concentration, dissolved oxygen levels, and water clarity are also objective indicators of bay health. These have complex interactive cycles which are affected by rainfall, temperature, and tidal action, as well as other factors. High nutrient levels (nitrogen and phosphorus) can stimulate excessive growth of marine algae (indicated by chlorophyll a level), resulting in reduced water clarity (and increased light attenuation) and depleted oxygen levels. Both plants and animals in a bay need oxygen to survive, and the seagrasses which provide food and cover for bay creatures need light for photosynthesis.

Bay Contour Maps (2022)

Contour mapping is one of the best ways to visualize spatial differences in coastal water quality. The interactive map shown below presents monthly data for one selected water quality indicator atop an aerial view of the bay. Choose a different water quality parameter from the list at the top to change the map. Learn More about Water Quality Contour Mapping »

Showing 2022 Monthly Contour Maps for: January
Loading interactive contour map viewer...
Contour Visibility:

Visit the Water Quality Contour Mapping Tool to view and compare monthly water quality contour maps for ten different water quality indicators. In addition, you can generate your own custom maps.

Contour Legend:

  • Less than 1 ug/l
  • 1.0 - 5.9 ug/l
  • 6.0 - 10.9 ug/l
  • 11.0 - 17.9 ug/l
  • Greater than 18 ug/l

Seagrasses

Among the most important habitats in Florida's estuarine environments, seagrass beds are indispensable for the role they play in cycling nutrients, supplying food for wildlife, stabilizing sediments, and providing habitat for juvenile and adult finfish and shellfish. Use the interactive map below to observe the size, density and location of seagrass beds from year to year. The graph shows how the total amount of seagrass in the bay has changed over time. Seagrass calculations are aggregates of patchy and continuous seagrass measurements only. Recordings of attached algae are not included in these summaries.
Learn More about Seagrasses »

Showing Seagrass Coverage for :
Loading interactive seagrass coverage viewer...
Loading interactive chart...
  • Target 447 acres

Visit our Seagrass page to discover the beauty and importance of seagrass habitats, and sign up to help monitor their health.

Impervious Features

Blackburn Bay is located within the Little Sarasota Bay Watershed. View details about the Little Sarasota Bay Watershed »

Rain that falls on land that is in a natural state is absorbed and filtered by soils and vegetation as it makes it way into underground aquifers. However, in developed areas, "impervious surfaces" impede this process and contribute to polluted urban runoff entering surface waters. These surfaces include human infrastructure like roads, sidewalks, driveways and parking lots that are covered by impenetrable materials such as asphalt, concrete, brick and stone, as well as buildings and other permanent structures. Soils that have been disturbed and compacted by urban development are often impervious as well. Learn more about Impervious Features »

The Sarasota County Stormwater Environmental Utility (SEU) mapped impervious surfaces in the County in 2014. A map showing impervious surfaces can be viewed using the interactive Sarasota NPDES Viewer.

14% of the land area within the Little Sarasota Bay Watershed is covered by impervious surfaces

Impervious Surface Coverage by Type

Land Use / Land Cover

Land use within a bay's watershed has a major effect on its water quality. In general, less development means better water quality. Land Cover/Land Use classifications categorize land in terms of its observed physical surface characteristics (upland or wetland, e.g.), and also reflect the types of activity that are taking place on it (agriculture, urban/built-up, utilities, etc.). Florida uses as its standard a set of statewide classifications which were developed by the Florida Department of Transportation. Learn More about Land Use and Land Cover »

Blackburn Bay is located within the Little Sarasota Bay Watershed. The chart below shows the land use / land cover characteristics for Little Sarasota Bay Watershed within the boundary of this Water Atlas. View details about the Little Sarasota Bay Watershed »

Acreage and Percentage within each Land Use / Land Cover Category for Little Sarasota Bay Watershed
Land Use Classification 1990 2005 2011 2014 2017 2020 Trend
Urban & Built-up 8,94331.9% 11,83442.2% 12,10243.1% 12,16243.3% 12,77745.5% 13,34347.5%
Agriculture 3,55012.6% 3,22811.5% 3,25811.6% 4,22315% 3,12411.1% 2,83710.1%
Rangeland 8252.9% 1,8226.5% 1,4745.3% 5792.1% 1,2334.4% 8773.1%
Upland Forests 7,09825.3% 3,06610.9% 2,98110.6% 2,7259.7% 2,6879.6% 2,6039.3%
Water 3,42912.2% 4,12314.7% 4,14714.8% 4,17514.9% 4,22715.1% 4,33715.5%
Wetlands 3,49012.4% 3,13311.2% 3,19111.4% 3,22711.5% 3,12111.1% 3,12011.1%
Barren Land 620.2% 180.1% 190.1% 200.1% 60% 60%
Transportation and Utilities 6752.4% 8413% 8923.2% 9523.4% 8983.2% 9483.4%
Land Use Chart

Data Sources

The data sources listed below provided water quality data used to create the report on this page. Not all data sources provided data for every bay, and not every Bay Conditions Report used data from all listed data sources. While some data sources have no data for the scored year, they provided period-of-record (historical high, mean, low) data. Click on a data source name to review its metadata.