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Comparison of Low‐Cost Methods for Measuring Ammonia Volatilization
Author(s) -
Shigaki Francirose,
Dell Curtis J.
Publication year - 2015
Publication title -
agronomy journal
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.752
H-Index - 131
eISSN - 1435-0645
pISSN - 0002-1962
DOI - 10.2134/agronj14.0431
Subject(s) - environmental science , ammonia , volatilisation , nitrogen , fertilizer , ammonia volatilization from urea , chemistry , zoology , urea , environmental engineering , biology , organic chemistry
Nitrogen fertilizer use to improve crop production is increasing worldwide, and subsequent N losses via NH 3 emissions generate undesirable economic and environmental consequences. Thus, low cost and practical methods to quantify NH 3 emissions are essential for the development of management practices that minimize environmental impacts. The objective of this study was to compare different methods to quantify NH 3 loss following urea application to a grass field and indoor soil boxes. The methods tested were: semi‐open chamber (SOC), open‐collector (OC), closed chamber (CC), and a recirculating chamber (RC). The SOC and OC were shown to be equally efficient. Cumulative recoveries through 216 h for the outdoor study were 9.5 and 8.5 kg NH 3 –N ha −1 for OC and SOC (respectively), corresponding to 8 and 7% of the applied N. The closed‐chamber recovered only 3.6% of applied N. For the indoor study, higher recovery rates were observed with all methods. Cumulative losses measured through 216 h did not differ between SOC and OC (24.4 and 24.9 kg NH 3 –N, respectively) and represented about 20% of N applied. However RC and CC recovered 10 to 12% of the applied N (14.8 and 12 kg NH 3 –N ha −1 , respectively), which was significantly less than amounts recovered with OC and SOC. Results from this study showed that SOCs and OCs are simple, practical, and low cost tools for quantifying NH 3 emissions either for indoor and outdoor studies compared with closed and recirculating chambers which presented disadvantages such as low NH 3 recovery and higher costs.