Study 2 - From September 1993 to November 1994, a suction lysimeter pulled samples of sand filter effluent from 12" below a drip system's tubing. (The drip system was buried 3" below grade). 44 data points were generated. The average nitrate of the sand filter effluent was 86 mg/L. After passing through the 12" of soil in the drip bed drainfield, the average nitrate of the effluent was 50 mg/L... a 42% reduction in average nitrate. (Additional facts: sewage source was an office building; total kjeldahl nitrogen leaving the septic tank ranged from 90 to 190 mg/L; the drip bed was 3' x 50'; soil was clay loam covered by native lawn grass; the average daily flow was 370 gallons; the average soil loading rate was 2.5 gpd/ft2.)
Study 3 - From November 1993 to September 1994, a suction lysimeter pulled samples of polished trickling filter effluent from 12" below a shallow gravelless drainfield trench. 40 data points were generated. The average nitrate of the polished trickling filter effluent was 13.7 mg/L. After passing through the 12" of soil below the shallow gravelless drainfield, the average nitrate of the effluent was 5.9 mg/L... a 57% reduction in average nitrate. (Additional facts: sewage source was a two-bedroom home; total kjeldahl nitrogen leaving the septic tank was 66 mg/L; the shallow gravelless drainfield was 12" (w) x 20' (long) x 12" deep; the soil was a silty clay loam with no vegetative covering; the average daily flow was 115 gpd; the average soil loading rate was 5.75 gpd/ft2.)
These studies show that the widely used practice of placing pretreated effluent in deeper drainfield soil results in a "missed opportunity" for additional wastewater treatment and nutrient removal. See also Wert, S. and R.C. Paeth, 1985. "Performance of disposal trenches charged with recirculating sand filter effluent." In: 5th Northwest On-Site Waste Water Treatment Short Course "On-Site Waste Water Treatment: Environmental Significance." State of Washington Department of Social and Health Services, Olympia, Washington.