Nitrogen fate and transport in a conventional onsite wastewater treatment system installed in a clay soil; experimental results
Nitrogen fate and transport in a conventional onsite wastewater treatment system installed in a clay soil; experimental results
Vadose Zone Journal (August 2013) 12 (3)
- adsorption
- ammonium ion
- Appalachians
- biomass
- carbon
- chloride ion
- chlorine
- clastic sediments
- clay
- concentration
- denitrification
- effluents
- experimental studies
- Georgia
- grain size
- ground water
- halogens
- hydraulic conductivity
- hydrodynamics
- hydrologic cycle
- hydrology
- infiltration
- mobilization
- nitrate ion
- nitrification
- nitrogen
- North America
- oxidation
- Piedmont
- pits
- sediments
- septic systems
- size distribution
- soil profiles
- soils
- solute transport
- Spalding County Georgia
- statistical analysis
- time factor
- total maximum daily loads
- transport
- United States
- unsaturated zone
- variance analysis
- waste water
- water quality
- water treatment
- west-central Georgia
- pressure head
- drainage fields
Relationships between N transport and hydraulic function of onsite wastewater treatment systems (OWTSs) in clay-textured soils are largely unknown. The objectives of this study were to quantify N concentrations in a clay soil and estimate denitrification in the vadose zone beneath a conventional OWTS. An OWTS installed in the Piedmont region of Georgia was dosed with residential strength wastewater three times per day for 2 yr. Soil near trench bottoms cycled between saturated and unsaturated conditions under the dosing schedule we used. Mean NH (sub 4) -N concentrations decreased to <1 mg L (super -1) within 90 cm of trench bottoms due to adsorption, immobilization, and nitrification. Mean NO (sub 3) -N concentrations increased as the drainfield matured and ranged from 10 to 25 mg L (super -1) near the end of the two year study period. Mean pressure heads and Cl (super -) concentrations measured at 3.3 m and 6.6 m from trench inlets indicated that significantly more water infiltrated the drainfield at the 3.3 m position. Wet conditions at the 3.3 m position may have restricted nitrification, while dry conditions at the 6.6 m caused rapid nitrification. Nitrogen:chloride ratios suggested that 61% of N entering the drainfield was lost, potentially as volatile N-species. The 30-cm zone directly beneath the trenches had high biomass N and C contents (15 mg kg (super -1) N and 60 mg kg (super -1) C) and was presumably the most biologically active zone. The fate and transport of N was dynamic in this system due to variable moisture conditions near the trench-soil interface which may have intermittently stimulated denitrification.