The effect of external wind speed and direction on sampling point concentrations, air change rate and emissions from a naturally ventilated dairy building

被引:45
作者
Saha, Chayan K. [1 ,3 ]
Ammon, Christian [1 ]
Berg, Werner [1 ]
Loebsin, Christiane [2 ]
Fiedler, Merike [1 ]
Brunsch, Reiner [1 ]
von Bobrutzki, Kristina [1 ]
机构
[1] Leibniz Inst Agr Engn Potsdam Bornim ATB, Dept Engn Livestock Management, D-14469 Potsdam, Germany
[2] State Inst Agr & Fishery MV, Inst Anim Prod, D-18196 Dummerstorf, Germany
[3] Bangladesh Agr Univ, Dept Farm Power & Machinery, Mymensingh 2202, Bangladesh
关键词
MASS-TRANSFER COEFFICIENT; AMMONIA EMISSIONS; GASEOUS EMISSIONS; AQUEOUS-SOLUTIONS; CATTLE BUILDINGS; TRACER GAS; METHANE; FLOW; GREENHOUSE; QUANTIFICATION;
D O I
10.1016/j.biosystemseng.2012.12.002
中图分类号
S2 [农业工程];
学科分类号
0828 ;
摘要
Natural ventilation (NV) of buildings refers to the exchange of indoor air with outdoor air due to pressure differences caused by wind and/or buoyancy. Increased knowledge of the factors that affect NV and emissions from naturally ventilated dairy (NVD) buildings may lead to a better understanding of indoor air quality, an improvement of emission abatement technologies and a refinement of emission models. The influence of external wind speed and direction on point concentration, air change rate, ammonia (NH3) and methane (CH4) emissions was evaluated in an NVD building located in northern Germany. The measured data were classified according to four wind direction groups: 0 degrees-10 degrees (N), 85 degrees-95 degrees (E), 175 degrees-185 degrees (S), and 265 degrees-275 degrees (W), with consideration for similar wind frequencies and representation of each major side for further analyses and comparisons. The results showed that wind speed and wind direction had significant influence on air change per hour (ACH) (P < 0.05) both individually and when interacting. In contrast, only wind speed and interactions of external wind speed and direction significantly affected NH3 and CH4 emissions (P < 0.05). The surrounding obstacles, other climate parameters (temperature and relative humidity) and other emission sources should be taken into account when interpreting the effects of wind direction on ACH and emissions. Empirical models for ACH, NH3 and CH4 emissions were developed. Intensive experiments in the lab (e.g. scale model in boundary layer wind tunnel) and long-term measurement including all seasons at full scale are required to establish a good empirical model. (C) 2012 IAgrE. Published by Elsevier Ltd. All rights reserved.
引用
收藏
页码:267 / 278
页数:12
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