Journal list menu

Volume 40, Issue 5 p. 1395-1404
Special Submission: Agricultural Air Quality

Ammonia Emission Factors from Broiler Litter in Barns, in Storage, and after Land Application

Philip A. Moore Jr.

Corresponding Author

Philip A. Moore Jr.

USDA–ARS, Poultry Production and Product Safety Research Unit, Plant Science 115, Univ. of Arkansas, Fayetteville, AR, 72701

Corresponding author ([email protected]).Search for more papers by this author
Dana Miles

Dana Miles

USDA–ARS, 810 Hwy. 12 East, Mississippi State, MS, 39762-5367

Search for more papers by this author
Robert Burns

Robert Burns

Iowa State Univ., 3224 NSRIC, Ames, IA, 50011

Search for more papers by this author
Dan Pote

Dan Pote

USDA–ARS, Hwy. 23, Booneville, AR, 72927

Search for more papers by this author
Kess Berg

Kess Berg

Cyngenta Seed, Lebanon, IN, 46052

Mention of a trade name, proprietary product, or specific equipment does not constitute a guarantee or warranty by the USDA and does not imply its approval to the exclusion of other products that may be suitable. Assigned to Associate Editor Wendy PowersSearch for more papers by this author
In Hag Choi

In Hag Choi

Dep. of Companion Animal & Animal Resources Science, Joongbu Univ., 101 Daehak-ro, Chubu myeon, Kumsan-gun, Chungnam, 312-702 South Korea

Search for more papers by this author
First published: 01 September 2011
Citations: 56

All rights reserved. No part of this periodical may be reproduced or transmitted in any form or by any means, electronic or mechanical, including photocopying, recording, or any information storage and retrieval system, without permission in writing from the publisher.

Abstract

We measured NH3 emissions from litter in broiler houses, during storage, and after land application and conducted a mass balance of N in poultry houses. Four state-of-the-art tunnel-ventilated broiler houses in northwest Arkansas were equipped with NH3 sensors, anemometers, and data loggers to continuously record NH3 concentrations and ventilation for 1 yr. Gaseous fluxes of NH3, N2O, CH4, and CO2 from litter were measured. Nitrogen (N) inputs and outputs were quantified. Ammonia emissions during storage and after land application were measured. Ammonia emissions during the flock averaged approximately 15.2 kg per day-house (equivalent to 28.3 g NH3 per bird marketed). Emissions between flocks equaled 9.09 g NH3 per bird. Hence, in-house NH3 emissions were 37.5 g NH3 per bird, or 14.5 g kg−1 bird marketed (50-d-old birds). The mass balance study showed N inputs for the year to the four houses totaled 71,340 kg N, with inputs from bedding, chicks, and feed equal to 303, 602, and 70,435 kg, respectively (equivalent to 0.60, 1.19, and 139.56 g N per bird). Nitrogen outputs totaled 70,396 kg N. Annual N output from birds marketed, NH3 emissions, litter or cake, mortality, and N2O emissions was 39,485, 15,571, 14,464, 635, and 241 kg N, respectively (equivalent to 78.2, 30.8, 28.7, 1.3, and 0.5 g N per bird). The percent N recovery for the N mass balance study was 98.8%. Ammonia emissions from stacked litter during a 16-d storage period were 172 g Mg−1 litter, which is equivalent to 0.18 g NH3 per bird. Ammonia losses from poultry litter broadcast to pastures were 34 kg N ha−1 (equivalent to 15% of total N applied or 7.91 g NH3 per bird). When the litter was incorporated into the pasture using a new knifing technique, NH3 losses were virtually zero. The total NH3 emission factor for broilers measured in this study, which includes losses in-house, during storage, and after land application, was 45.6 g NH3 per bird marketed.