Weir J, Li H, Warren L K, Macon E, Wickens C
J Anim Sci. 2017 Aug;95(8):3598-3608. doi: 10.2527/jas.2017.1648.
Evaluating impact of animal agriculture on air quality has been the focus of recent research. Ammonia (NH) volatilization occurs when undigested protein in feces and urea in urine is broken down by bacteria and enzymes. Information regarding NH emission from equine facilities is limited, and effects of CP intake on NH emissions have not been investigated. Nine mature geldings were used in a 3 × 3 replicated Latin square design study to determine effects of dietary CP on potential NH losses from feces and urine. We hypothesized feeding horses above the CP requirement would result in an increase in NH emissions from urine and feces and different bedding materials would affect NH emissions from urine. Diets were formulated using different ratios of bahiagrass () and Tifton-85 bermudagrass () hays, and a commercial vitamin mineral supplement to provide 3 different CP concentrations and labeled in relation to each other: LOW-CP, MED-CP, and HIGH-CP (10.6%, 11.5%, and 12%, respectively). Each study period consisted of an 11-d diet adaptation phase, followed by a 3-d total collection of urine and feces. To determine total nitrogen (TN) and urea-N concentrations, samples were pooled by period ( = 9). For in vitro determination of NH concentrations, urine and fecal samples were pooled within period by diet ( = 3) and mixed with either wheat straw or wood shavings. Ammonia emission of these samples was measured using a vessel system with an airflow rate (2.5 L/min) at 20°C over a 7-d period. Concentration of NH in each vessel was measured using a photoacoustic multigas analyzer. Temperature, airflow rate, and NH concentration in each vessel were used to calculate NH emission rate (ER). Data were analyzed using a mixed model ANOVA with repeated measures. Urinary TN and urea-N excretion increased as CP intake increased ( < 0.0001). Vessel urinary NH concentrations were not different across diets ( = 0.1225), ranging from 55.48 ppm (LOW-CP) to 101.14 ppm (HIGH-CP); however, they differed between bedding types ( < 0.0001), with straw higher than shavings (97 vs. 73.5 ppm, respectively). Cumulative urinary NH ER tended to be different across diets ( = 0.0550) ranging from 5.87 g/m to 9.97 g/m and bedding types ( = 0.0129), with straw being higher than shavings (11.1 vs. 6.9 g/m, respectively). Overfeeding CP to horses can lead to increased urinary TN and urea-N excretion, which could lead to greater of NH in the atmosphere.
评估畜牧业对空气质量的影响一直是近期研究的重点。当粪便中未消化的蛋白质和尿液中的尿素被细菌和酶分解时,就会发生氨(NH₃)挥发。关于马厩设施中NH₃排放的信息有限,且尚未研究粗蛋白摄入量对NH₃排放的影响。本研究采用3×3重复拉丁方设计,选用9匹成年公马,以确定日粮粗蛋白对粪便和尿液中潜在NH₃损失的影响。我们假设,给马匹饲喂超过其粗蛋白需求量的饲料会导致尿液和粪便中NH₃排放量增加,且不同的垫料会影响尿液中NH₃的排放。日粮由不同比例的巴哈雀稗(Paspalum notatum)和蒂夫顿85百慕大草(Cynodon dactylon)干草以及一种商业维生素矿物质预混料配制而成,以提供3种不同的粗蛋白浓度,并相互标记为:低粗蛋白、中粗蛋白和高粗蛋白(分别为10.6%、11.5%和12%)。每个研究期包括11天的日粮适应期,随后是3天的尿液和粪便总收集期。为了测定总氮(TN)和尿素氮浓度,按时间段(n = 9)对样品进行合并。为了体外测定NH₃浓度,按日粮在时间段内(n = 3)对尿液和粪便样品进行合并,并与小麦秸秆或刨花混合。使用气流速率为2.5 L/min的容器系统,在20°C下,对这些样品的NH₃排放进行为期7天的测量。使用光声多气体分析仪测量每个容器中NH₃的浓度。利用每个容器中的温度、气流速率和NH₃浓度来计算NH₃排放速率(ER)。数据采用重复测量的混合模型方差分析进行分析。随着粗蛋白摄入量的增加,尿TN和尿素氮排泄量增加(P < 0.0001)。不同日粮间容器内尿液NH₃浓度无差异(P = 0.1225),范围为55.48 ppm(低粗蛋白)至101.14 ppm(高粗蛋白);然而,不同垫料类型间存在差异(P < 0.0001),秸秆垫料组高于刨花垫料组(分别为97 ppm和73.5 ppm)。不同日粮间累积尿液NH₃ ER存在差异趋势(P = 0.0550),范围为5.87 g/m²至9.97 g/m²,不同垫料类型间也存在差异(P = 0.0129),秸秆垫料组高于刨花垫料组(分别为11.1 g/m²和6.9 g/m²)。给马匹过量饲喂粗蛋白会导致尿TN和尿素氮排泄增加,这可能会导致大气中NH₃含量增加。