Caution
Rating icon - Chlorophyll a Rating icon - Total Nitrogen Rating icon - Total Phosphorous Rating icon - Dissolved Oxygen Saturation

3 out of 4 primary indicators were rated as PASS.

"Primary" are nutrient related (Chl, N, P) and bacteria (B) parameters.

All four indicators must pass for the creek to be rated as PASS.

Greyed out values indicate no data for the report year.

  • Size: 6,399 acres
  • Location: Central Sarasota County
  • Discharges into: Roberts Bay (Venice)

For more information, please see: Curry Creek Basin Master Plan Update, Venice County Model (2001)

View county-wide water quality trends »

Curry Creek

Water Chemistry Ratings

Monitoring data is analyzed to determine stream health based on State water quality standards. Official determination of impairment or attainment of the water quality standards is performed by FDEP and is based on at least three years and up to seven and a half years of data. Information on approximately 17 different parameters are collected at stream sites, but only total nitrogen, total phosphorus, chlorophyll a, dissolved oxygen (percent saturation), and bacteria are assessed according to established water quality criteria mandated by the Clean Water Act. Additionally, the floral and faunal communities (SCI) are assessed at some sites to determine whether waters support a healthy aquatic community.

The "pass/fail" conditions presented here do not indicate impairment as determined by the official Florida Department of Environmental Protection Impaired Waters Rule assessment but, rather, give an indication of stream condition in a particular year in relation to the set regulatory numeric limits. Streams receive an annual "PASS" rating for each parameter if the mean value is below the regulatory value and a "FAIL" rating if the mean value exceeds the regulatory value. Not all water quality parameters have an established numeric criterion, so only some of the graphs below show the regulatory limit, represented by a horizontal red line.

Chart Legend
  • Monthly Average
  • Threshold
  • Annual Mean

The graphs here illustrate results over the past five years. Data from sites monitored within a single waterbody identification basin (WBID) are combined to determine water quality status for each WBID, and the annual geometric mean of sample results is indicated on the graph for the most recent year. The table to the left of the graph gives the annual and historic range of values for the indicator.

Click the graph to view a larger image and to download the full dataset.

Freshwater Portion of the Creek

Data for the following WBIDs is averaged when compiling the data below:
  • 2009
  • 2009B
  • 2009C
  • 2016

Chlorophyll a

Units: µg/l Year
2022
Historical
period of record
High 27.50 132.00
Mean 5.7778 6.9579 10.83779
Low 2.42 0.25
No. of Samples 24 621
  • Monthly Average
  • NNC 20.00 µg/l
  • Annual Mean

Nitrogen, Total

Units: mg/L Year
2022
Historical
period of record
High 3.155 3.155
Mean 1.0195 1.0895 0.39945402
Low 0.133 0.117
No. of Samples 24 492
  • Monthly Average
  • NNC 1.65 mg/L
  • Annual Mean

Phosphorus, Total

Units: mg/L Year
2022
Historical
period of record
High 0.465 0.885
Mean 0.1661 0.2426 0.16049686
Low 0.071 0.043
No. of Samples 24 563
  • Monthly Average
  • NNC 0.49 mg/L
  • Annual Mean

Dissolved Oxygen Saturation

Note: Dissolved oxygen saturation percentages above the regulatory threshold meet established water quality targets.
Units: percent (%) Year
2022
Historical
period of record
High 84.7987 166.80
Mean 34.1 51.95 21.64794
Low 1.3632 1.3632
No. of Samples 24 633
  • Monthly Average
  • NNC 38.00 percent (%)
  • Annual Mean

BOD, Biochemical oxygen demand

Units: mg/l Year
2022
Historical
period of record
High 2.21 6.58
Mean 1.12 1.33 0.72723
Low 1.00 0.50
No. of Samples 22 479
  • Monthly Average
  • Annual Mean

Color

Units: PCU Year
2022
Historical
period of record
High 450.00 450.00
Mean 89.89 109.28 90.2233
Low 25.00 5.00
No. of Samples 24 674
  • Monthly Average
  • Annual Mean

Escherichia coli

Units: MPN/100ml Year
2022
Historical
period of record
High 871.00 4106.00
Mean 157.79 160.46 434.0196
Low 52.00 10.00
No. of Samples 11 126
  • Monthly Average
  • Annual Mean

Nitrogen, Ammonia + Ammonium as N

Units: mg/L Year
2022
Historical
period of record
High 0.856 25.57
Mean 0.04 0.02 1.03547553
Low 0.008 0.00
No. of Samples 24 636
  • Monthly Average
  • Annual Mean

Nitrogen, Kjeldahl

Units: mg/L Year
2022
Historical
period of record
High 2.84 26.19
Mean 0.95 1.04 1.14222163
Low 0.10 0.05
No. of Samples 24 603
  • Monthly Average
  • Annual Mean

Nitrogen, Nitrite + Nitrate as N

Units: mg/L Year
2022
Historical
period of record
High 0.315 0.79
Mean 0.05 0.06 0.07131449
Low 0.006 0.00
No. of Samples 24 568
  • Monthly Average
  • Annual Mean

pH

Units: None Year
2022
Historical
period of record
High 8.88 8.90
Mean 7.49 7.56 0.3168
Low 7.04 5.52
No. of Samples 24 4,351
  • Monthly Average
  • Annual Mean

Salinity

Units: PSS Year
2022
Historical
period of record
High 35.471 78.50
Mean 2.22 10.65 15.79622
Low 0.1667 0.00
No. of Samples 24 4,294
  • Monthly Average
  • Annual Mean

Specific conductance

Units: µmho Year
2022
Historical
period of record
High 52838.20 61277.60
Mean 3965.85 15614.55 16379.89734
Low 345.958 0.286
No. of Samples 24 4,322
  • Monthly Average
  • Annual Mean

Temperature, water

Units: °F Year
2022
Historical
period of record
High 188.2259 191.9267
Mean 169.67 75.25 14.47576
Low 142.9586 47.858
No. of Samples 24 4,238
  • Monthly Average
  • Annual Mean

Turbidity

Units: NTU Year
2022
Historical
period of record
High 40.00
Mean 2.55 2.17166
Low 0.70
No. of Samples 0 482
  • Monthly Average
  • Annual Mean
Other Measures of Creek Health:

Tidal Portion of the Creek

Data for the following WBIDs is averaged when compiling the data below:
  • 1991G
  • 2009A
Other Measures of Creek Health:

Oysters

Because they are immobile and will tolerate a fairly wide salinity range, eastern oysters (Crassostrea virginica) are valuable as an indicator of the relative health of aquatic ecosystems in the tidally-influenced portions of coastal creeks. Sarasota County has established an oyster monitoring program to track the location, types, and status of oyster reefs. Data from this monitoring program is shown below. Learn more about Oysters »

Loading oyster site map...
Most Recent Sarasota County Oyster Monitoring Program Data
Icon Site ID Year Dead Live Total % Live
1 CC1 2020 23 135 158 85
2 CC2 2020 13 92 105 87

Impervious Features

Curry Creek is located within the Dona and Roberts Bay Watershed. View details about the Dona and Roberts 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 2013. A map showing impervious surfaces can be viewed using the Water Atlas Map Viewer tool.

13% of the land area within the Curry Creek Basin is covered by impervious surfaces

Impervious Surface Coverage by Type

Land Use / Land Cover

Curry Creek is located within the Dona and Roberts Bay Watershed. View details about the Dona and Roberts Bay Watershed »

Land use within a creek'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 (e.g. upland or wetland), 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 »

Acreage and Percentage within each Land Use / Land Cover Category for Curry Creek Basin
Land Use Classification 1990 1995 1999 2005 2011 2014 2017 2020 2023 Trend
Urban & Built-up 2,08932.7% 2,33136.4% 2,91545.6% 3,50454.8% 3,62156.6% 3,51955% 3,82559.8% 4,02562.9% 4,27666.8% Land Use Trend Sparkline
Agriculture 1,53223.9% 1,37421.5% 1,20118.8% 73611.5% 3856% 3695.8% 2704.2% 2253.5% 1562.4% Land Use Trend Sparkline
Rangeland 1742.7% 2123.3% 1882.9% 751.2% 3175% 3225% 2143.3% 1532.4% 1121.7% Land Use Trend Sparkline
Upland Forests 1,45222.7% 1,22919.2% 82612.9% 76712% 70711.1% 81312.7% 70111% 5358.4% 4046.3% Land Use Trend Sparkline
Water 3505.5% 4386.8% 4827.5% 4937.7% 4927.7% 4927.7% 5087.9% 5498.6% 5598.7% Land Use Trend Sparkline
Wetlands 5268.2% 4637.2% 4617.2% 4837.6% 5228.2% 5228.2% 5198.1% 5108% 4887.6% Land Use Trend Sparkline
Barren Land 80.1% 210.3% 00% 00% 00% 00% 00% 00% 00% Land Use Trend Sparkline
Transportation and Utilities 2664.2% 3305.2% 3265.1% 3415.3% 3545.5% 3625.7% 3605.6% 4026.3% 4046.3% Land Use Trend Sparkline
Land Use Chart