On Site Wastewater Treatment Systems

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B. Residential

6. On-Site Wastewater Treatment Systems

On-site wastewater treatment systems serve an estimated over 93 percent of the land and approximately 40 percent of the watershed people and homes (See Figure 27).  

Figure 27:  On-Site Wastewater Treatment

Total Acres

Total People

Total Homes

  On-Site Areas

 331,500

 28,141

 10,339

  Entire Watershed

 355,600

 71,456

 25,813

  Percentage On-Site

 93.2%

 39.4%

 40.1%

A variety of systems exist in the watershed but the most common system is a septic system which treats domestic wastewater through soil-based leaching.  In order for a septic system to function properly two feet of “useable” soil is needed to properly treat and remove all bacteria and viruses for wastewater.  Very few “useable” soils exist in the watershed because the soils are limited by poor or excessive drainage, seasonably high water table, low soil permeability rates, and a variety of other limitations.  Figure 28 below provides an overview by county of soil suitability for the placement of septic systems. 

Figure 28:  Percent of Soils Suitable for Placement of listed Onsite Wastewater Treatment Systems

County

Acres

Traditional or Mound

Mound only

Onsite w/ Irrigation

Non Suited (hydric)

Champaign    

277,120

1.9%

45.2%

29.1%

23.8%

Franklin

344,064

3.8%

18.1%

62.1%

16.0%

Logan

294,464

1.7%

35.0%

39.6%

23.7%

Madison

296,320

0.4%

16.1%

45.3%

38.2%

Pickaway

322,560

7.0%

45.5%

26.2%

21.3%

Union

277,760

1.4%

14.2%

54.2%

30.2%

Statewide

 

6.4%

25.4%

49.1%

19.1%

Watershed Avg.

 

2.7%

29.0%

42.8%

25.5%

Source: Mancl and Slater, 2002. Suitability of Ohio Soils for Treating Wastewater.  The Ohio State University Extension.  Appendix 1

County Health Departments attempted to overcome severe soil limitations through the installation of alternative systems such as aeration systems and sand filters.  Aeration systems were designed to create an aerobic treatment system in which air would be incorporated into the holding tank to promote the growth of oxygen-using bacteria.  Newer aeration systems then discharge into a small absorption field for additional treatment whereas older systems may discharge to tiles, ditches, or streams.  In order to create the aerobic treatment process a mechanical device is necessary to pump or agitate the wastewater.  Such systems require additional maintenance to ensure that proper treatment.  There are approximately 1,076 known aeration systems in the watershed (See Figure 29). 

Figure 29:  Aerators by County

County

Known Aerators

Champaign

10

Franklin

674

Logan

20

Madison

96

Pickaway

34

Union

242

Total

1076

Health Department officials from each county estimated there were an additional 10 to 25 percent more aeration systems existing in the watershed that were not yet documented.  

As mentioned above sand filters have been installed in areas across the watershed that suffer from soil limitations due to high seasonal water table or low permeability rates.  The installation of sand filters was a common practice in Union County in the past.  Currently, the installation of sand filters is discouraged but still occurs under certain circumstances.  As previously stated, two feet of “useable” soil is necessary to treat wastewater effectively.  In situations where less than two feet of useable soil is available, sand is used in place of the soil to assist in the treatment process.  However, sand does not effectively treat bacteria and viruses.  Elevated bacteria levels were found throughout the watershed (See IV. Water Quality for additional information on Ohio EPA sampling results for bacteria).  The exact number of sand filters in the watershed is not known at this time. 

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For problems or questions regarding this website please contact the Darby Watershed Coordinator.
Last updated: June 09, 2008.