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publications > circular > circular 1207 > major findings > DOC and DOM


U.S. Department of the Interior
U.S. Geological Survey
Circular 1207

Water Quality in Southern Florida
Summary
Intro to S Florida NAWQA Study Unit
Major Findings
- Nutrients
- DOC and DOM
- Pesticides, VOCs, Trace Elements and Herbicides
- Bottom Sediments and Fish
- Biological Communities
Study Unit Design
Glossary
References
Appendix
PDF version
Dissolved organic carbon concentrations are commonly high.

Dissolved organic carbon (DOC) originates from natural sources, such as living and decaying plants, and from human sources. DOC represents about half the dissolved organic matter (DOM) in natural waters (Hem, 1985). In southern Florida, DOC concentrations commonly are high compared with other natural waters in the Nation and may constitute, as DOM, a significant fraction of the dissolved solids (table 2).

Concentrations of DOC ranged from 4.8 to 52.0 mg/L at the SOFL surface-water sites, and from 0.6 to 80 mg/L at the ground-water sites (table 2). The highest DOC concentrations (median of 34.0 mg/L) occurred at Hillsboro Canal at S-6 in the northern Everglades downgradient from the Everglades Agricultural Area, which has highly organic muck soils that are thought to be a source of DOC. In contrast, the Big Cypress Swamp reference site at Tamiami Trail Bridge 105 had the lowest concentrations (median of 9.5 mg/L) of the routinely sampled sites. This site is characterized by natural swamp vegetation and thin carbonate soils and rock. Concentrations of DOC at sites along the Tamiami Trail (1996-97) ranged from 4.8 to 26.9 mg/L (table 2), and tended to be low in the central and eastern Big Cypress Swamp and higher in the western Big Cypress and to the east in the Everglades (Miller and others, 1999).

The amount of DOC in water is significant. It can (1) contribute to water color, which absorbs sunlight and reduces the amount of light available for use by submerged aquatic plants and phytoplankton; (2) serve as a source of carbon for bacterial growth; (3) form complexes with trace elements, such as mercury, and make them more soluble and mobile in water (Reddy and others, 1999); (4) reduce bioavailability of nonionic organic compounds through sorption, entrapment, or sequestering the compounds (Nowell and others, 1999, p. 296); (5) increase the solubilities of relatively insoluble compounds, such as p,p'-DDT, PCBs, and lindane (Chiou and others, 1986); and (6) react with chemicals used to disinfect public water supplies and produce undesirable by-products, such as chloroform and other trihalomethanes, that may have harmful effects on human health.


Table 2. Concentrations of dissolved organic carbon, in milligrams per liter, at surface- and ground-water sites in southern Florida, 1996-98

[Dissolved organic carbon (DOC) in natural water typically is 45 to 55 percent of the dissolved organic matter (DOM; Robert Wershaw and Jerry Leenheer, oral commun., 1997) and averages about 50 percent of the DOM that also includes other elements such as oxygen, hydrogen, nitrogen, phosphorus; --, no data]

Sampling site Range Median Number of DOC samples DOM as a percentage of
dissolved solids
Surface Water
Kissimmee River at S-65E 13.0-22.0 16.0 29 20-39
Peace River Arcadia 8.6-26.0 15.0 30 6-36
Caloosahatchee River at Alva 13.0-22.0 16.0 27 5-15
Hillsboro Canal at S-6 15.0-52.0 34.0 48 7-13
U.S. Sugar 17.0-30.0 20.0 37 11-16
Tamiami Canal at Bridge 105 7.1-14.0 9.5 35 5-18
Canal C-111 at S-177 5.0-18.0 6.6 51 4-9
All 7 Basic Fixed Sites 5.0-52.0 16.0 257 4-39
Tamiami Trail, SOFL data (1996-97) 4.8-26.9 12.5 43 --
Ground Water
Urban/residential land-use wells 1.9-36 11.5 32 --
Citrus wells 2.7-80 24 29 --
Public-supply wells 0.6-22 9.4 30 --


Naturally occurring dissolved organic matter (DOM) causes the tea-colored water in many of Florida's rivers and swamps. Water color can have significant ecological effects by decreasing available light in the water column and reducing algal and aquatic plant productivity and growth. In the Peace River and upper Charlotte Harbor, for example, color can contribute up to about half of the total light attenuation in the water column, and this high attenuation limits algal phytoplankton and seagrass growth (McPherson and Miller, 1987). The range in color for southern Florida water, including the NAWQA sites, is shown in table 3.

Table 3. Water color for southern Florida surface-water sites, 1913-1999 (Color is reported in platinum-cobalt units. Data from U.S. Geological Survey data bases)
Sampling site Range Median Number of samples Period of record
Kissimmee River, S-65E 25-240 85 51 1959-75
Peace River, Arcadia 0-320 82.5 414 1930-99
Caloosahatchee River at S-79 5-500 62.5 144 1953-88
Hillsboro Canal at S-6 30-560 120 89 1945-84
Tamiami Canal at Bridge 105 10-100 30 56 1967-99
Canal, C-111 at S-18-C 0-40 5 40 1970-83
Everglades P-33 10-120 45 82 1959-85
878 southern Florida sites in Miami USGS data base 0-640 55 11,457 1913-99


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