Amendments for reducing ammonia emissions from open-lot beef cattle feedlot
s were evaluated in the laboratory. A mixture of 1550 g of soil, 133 g of f
eces, and 267 g of urine was placed into plastic containers that were 20 cm
X 20 cm X 12 cm deep. Using a vacuum system, clean air (3.2 L/min) was pas
sed over the soil-manure surface and ammonia was trapped by bubbling the ai
r through dilute sulfric acid. Treatments were a blank (soil with no manure
), control (soil-manure mixture with no amendment), 4500 kg/ha Al-2(SO4)(3)
(alum), 9000 kg/ha alum, 375 kg/ha commercial product (CP)for reducing amm
onia emissions, 750 kg/ha CP, 4500 kg/ha calcium chloride (CaCl2), 9000 kg/
ha CaCl2, 9000 kg/ha. brown humate, 9000 kg/ha black humate, 1 kg/ha of the
urease inhibitor N-(n-butyl) thiophosphoric triamide (NBPT), and 2 kg/ha N
BPT There were four replications of each treatment. Ammonia emissions were
measured for 21 days following application of the amendments. Cumulative am
monia emissions after 21 days, expressed as a percentage of the control, we
re 0.4% for the blank, 8.5% for 4500 kg/ha alum, 1.7% for 9000 kg/ha alum 7
3.6% for 375 kg/ha. CP, 68.2 % for 750 kg/ha. CP, 28.8% for 4500 kg/ha CaCl
2, 22.5% for 9000 kg/ha CaCl2, 32.4% for 9000 kg/ha brown humate, 39.8% for
9000 kg/ha black hum-ate, 35.9% for 1 kg/ha. NBPT, and 34.4% for 2 kg/ha N
BPT Calculated costs of the amendments ranged from $0.12 to $5.53 per appli
cation per head. Only one treatment had a benefit/cost ratio greater than 1
.0. Results suggest that amendments can reduce ammonia emissions from open
feedlots, but the costs may be prohibitive. Site-specific environmental imp
acts should be evaluated before using these amendments in a commercial sett
ing.