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Published in J Environ Qual 18:463-467 (1989)
© 1989 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Infiltration of Wastewater in a Newly Started Pilot Sand-Filter System: III. Transformation of Nitrogen

Mikael Pell*

Dep. of Microbiol., Swedish Univ. of Agric. Sci., S-750 07 Uppsala, Sweden;

Fred Nyberg

Dep. of Water Resour. Eng., Royal Inst. of Technol., S-100 44 Stockholm, Sweden.

* Corresponding author.

ABSTRACT

The objective of the study was to monitor the chemical dynamics associated with N transformations from start-up until a steady state was reached in a pilot sand-filter system consisting of a three-chambered septic tank, a sand filter with a one person capacity, and eight columns. The system was loaded with 67 L m–2 d–1 of an artificial wastewater. The untreated wastewater contained 114 mg Kjeldahl N L–1 and 0.12 mg NH+4-N L–1. Mineralization reached a steady state in the septic tank after 2 wk of operation; thereafter, 65 ± 6% of the effluent N was NH+4-N. In the column effluent the concentrations of NH+4-N increased during the first 6 wk of operation, whereafter a stabilization at 60 to 80 mg NH+4-N L–1 occurred. The mean proportion of effluent N in mineralized form for the whole period was 88 ± 6%. Three weeks after start-up, all effluent N from the sand filter was in mineralized form and remained high for the rest of the study period. The effluent concentrations of NH+4-N increased rapidly during the first 2 wk after which it decreased to less than 3 mg L–1. The concentration of NO3-N was initially low. It then increased until about Day 30 when it stabilized at 64 to 71 mg NO3-N L–1. Elevated concentrations of NO2-N were observed between Days 8 and 45. Nitrifying activity reached a steady state after 6 wk of operation. During this state a considerable amount of nitrification took place in the upper 1.5 cm and all wastewater N had been nitrified after 15 cm of percolation. By the end of the operating period the total amount of influent N in the septic tank had been reduced by 17%. Corresponding reductions for the columns and sand filter were 18 and 33%, respectively.


NOTES

Contribution by the Dep. of Microbiology, Swedish Univ. of Agric. Sci., S-750 07 Uppsala, Sweden.

Work funded by the research council at the National Swedish Environment Protection Board (SNV).

Received for publication July 11, 1988.


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Vadose Zone Journal
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Copyright © 1989 by the American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America.