Ammonia emissions from non-agricultural sources in the UK

被引:302
作者
Sutton, MA [1 ]
Dragosits, U [1 ]
Tang, YS [1 ]
Fowler, D [1 ]
机构
[1] Inst Terr Ecol, Edinburgh Res Stn, Penicuik EH26 0QB, Midlothian, Scotland
关键词
ammonia; emission inventory; atmospheric budget; sewage; wild animals; transport; industry;
D O I
10.1016/S1352-2310(99)00362-3
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
A detailed literature review has been undertaken of the magnitude of non-agricultural sources of ammonia (NH3) in the United Kingdom. Key elements of the work included estimation of nitrogen (N) excreted by different sources (birds, animals, babies, human sweat), review of miscellaneous combustion sources, as well as identification of industrial sources and use of NH3 as a solvent. Overall the total non-agricultural emission of NH3 from the UK in 1996 is estimated here as 54 (27-106) kt NH3-N yr(-1), although this includes 11 (6-23) kt yr(-1) from agriculture related sources (sewage sludge spreading, biomass burning and agro-industry). Compared with previous estimates for 1990, component source magnitudes have changed both because of revised average emissions;pei source unit (emission factors) and changes in the source activity between 1990 and 1996. Sources with larger average emission factors than before include horses, wild animals and sea bird colonies, industry, sugar beet processing, household products and non-agricultural fertilizer use, with the last three sources being included for the first time. Sources with smaller emission factors than before include: land spreading of sewage sludge, direct human emissions (sweat, breath, smoking, infants), pets (cats and dogs) and fertilizer manufacture. Between 1990 and 1996 source activities increased for sewage spreading (due to reduced dumping at sea) and transport (due to increased use of catalytic converters), but decreased for coal combustion. Combined with the current UK estimates of agricultural NH3 emissions of 229 kt N yr (-1) (1996), total UK NH3 emissions are estimated at 283 kt N yr (-1). Allowing for an import of reduced nitrogen (NHx)of 30 kt N yr (-1) and deposition of 230 kt N yr(-1), these figures imply an export of 83 kt NH3-N yr (-1). Although export is larger than previously estimated, due to the larger contribution of non-agricultural NH3 , emissions, it is sill insufficient to balance the UK budget, for which around 150 kt NH3-N are estimated to be exported, The shortfall in the budget is, nevertheless, well within the range of uncertainty of the total emissions. (C) 2000 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:855 / 869
页数:15
相关论文
共 72 条
[11]  
BUIJSMAN E, 1987, AMMONIA ACIDIFICATIO, P13
[12]   Critical loads and the relevance of ammonia to an effects-based nitrogen Protocol [J].
Bull, KR ;
Sutton, MA .
ATMOSPHERIC ENVIRONMENT, 1998, 32 (03) :565-572
[13]   Ammonia and nitrogen fluxes in landfill sites: applicability to sustainable landfilling [J].
Burton, SAQ ;
Watson-Craik, IA .
WASTE MANAGEMENT & RESEARCH, 1998, 16 (01) :41-53
[14]  
Cairns D.K., 1991, Canadian Special Publication of Fisheries and Aquatic Sciences, V113, P277
[15]  
CARLESSO B, 1995, ZUCKERINDUSTRIE, V120, P598
[16]  
Cass G.R., 1982, 826 CALTECH ENV QUAL
[17]  
*CGF, 1993, CHILD GROWTH STAT
[18]  
CLANCY J, 1995, PHYSL ANATOMY HOMEOS
[19]   Determination of gas-phase sidestream cigarette smoke components using Fourier transform infrared spectrometry [J].
Cole, SK ;
Martin, P .
ANALYST, 1996, 121 (04) :495-500
[20]  
COLUMBANI P, 1997, Z ERNAHRUNGSWISS, V36, P237