Health and Safety Executive, Buxton SK17 9JN, UK.
Sci Total Environ. 2017 Dec 31;609:1381-1389. doi: 10.1016/j.scitotenv.2017.08.014. Epub 2017 Aug 6.
Hydrogen sulphide gas (HS) produced by sulphate reducing bacteria (SRB) in stored animal slurry is highly toxic and, if emitted into poorly ventilated confined spaces, can build up to concentrations capable of causing asphyxiation. Therefore it is important to understand factors influencing HS emission from slurry. Powdered gypsum (hydrated calcium sulphate) may be used as animal bedding and, if it enters slurry systems, could be metabolised by SRB and further increase HS generation. Cattle slurry and cattle bedding collected from farms was used in laboratory-scale experiments sealed in 20litre vessels fitted with mechanical stirrers. HS was monitored in head space above the slurry using real-time gas detectors before and after stirring, and before and after adding 1% of two sources of gypsum powder. In one set of experiments, gypsum was already present in the slurry having been used in bedding on the farm. HS monitoring continued daily for up to 25days. Before stirring, HS levels in head spaces were minimal. After stirring, even without gypsum, maximum head space HS levels with slurry or bedding ranged from 330 to 1190ppm. By comparison, the UK short-term (15min) Workplace Exposure Limit is 10ppm. Statistically significant increases in HS levels were associated with gypsum addition, as high as 1772ppm with slurry and 3940ppm with bedding. Emissions peaked at around day 15 with slurry and bedding to which gypsum was freshly added, but within 5days when added to slurry already containing farm-added gypsum. Levels of HS produced from stirred slurry would constitute a hazard to anyone exposed to it, and adding gypsum further increased emission levels. Therefore, if gypsum residues enter slurry it could increase the risk of HS accumulation in confined spaces associated with slurry systems. It is important therefore to take this into account in managing risk.
硫化氢气体(HS)是由储存的动物粪便中的硫酸盐还原菌(SRB)产生的,具有高度毒性,如果排放到通风不良的密闭空间中,会积聚到足以致人窒息的浓度。因此,了解影响粪便中 HS 排放的因素非常重要。石膏粉(水化硫酸钙)可用作动物垫料,如果进入粪便系统,可能会被 SRB 代谢,并进一步增加 HS 的生成。从农场收集的牛粪便和牛垫料在实验室规模的实验中,装在装有机械搅拌器的 20 升容器中。在搅拌前后、添加 1%两种石膏粉源之前和之后,使用实时气体探测器监测粪便上方的 HS。在一组实验中,石膏已经存在于粪便中,之前曾用于农场的垫料。HS 监测持续了 25 天。在搅拌之前,顶部空间中的 HS 水平很低。搅拌后,即使没有石膏,粪便或垫料的最大顶部空间 HS 水平范围为 330 至 1190ppm。相比之下,英国的短期(15 分钟)工作场所暴露限值为 10ppm。HS 水平的统计显著增加与石膏的添加有关,添加新鲜石膏时,粪便的 HS 水平高达 1772ppm,垫料的 HS 水平高达 3940ppm。当新鲜添加到含有农场添加石膏的粪便或垫料中时,添加石膏后的 15 天内 HS 排放达到峰值,但在 5 天内达到峰值。搅拌后的粪便产生的 HS 水平会对接触到它的任何人构成危险,并且进一步增加了排放水平。因此,如果石膏残渣进入粪便,可能会增加与粪便系统相关的密闭空间中 HS 积聚的风险。因此,在管理风险时,必须考虑到这一点。