Health impact of odor from on-situ sewage sludge aerobic composting throughout different seasons and during anaerobic digestion with hydrolysis pretreatment

• Published in: Chemosphere (Oxford) 2020-06, Vol.249, p.126077, Article 126077
• Main Authors: Han, Zhangliang, Qi, Fei, Li, Ruoyu, Wang, Hui, Sun, Dezhi
• Format: Article
• Language: English
• Subjects: Anaerobic digestion; Composting; Health impact; Odor active value; Odor intensity; Sludge
• ISSN: 0045-6535; 1879-1298
• DOI: 10.1016/j.chemosphere.2020.126077

Aerobic composting and anaerobic digestion with hydrolysis pretreatment are two mainstream methods used to recycle and reclaim sewage sludge. However, during these sludge treatment processes, many odors are emitted that may cause severe emotional disturbance and health risks to those exposed. This study identified odor pollution (i.e. sensory influence, odor contribution, and human risks) from samples collected during sludge aerobic composting throughout different seasons as well as during anaerobic digestion with hydrolysis pretreatment. Odor intensity, odor active values, and permissible concentration-time weighted averages for ammonia and five volatile sulfur compounds were assessed. The results revealed serious odor pollution from all sampling sites during aerobic composting, especially in winter. Excessively strong odors were identified in the composting workshop, with total odor active values between 997 and 8980 which accounted for 78.45%–96.18% of the total sludge aerobic composting plant. Levels of ammonia and dimethyl disulfide in the ambient air were high enough to harm employees’ health. During anaerobic digestion, excessively strong odors were identified in dehydration workshop 2, and the total odor active values of six odors reached 32,268, with ammonia and hydrogen sulfide levels significant enough to harm human health. [Display omitted] •In the MSSACP, the most serious odor occurred during winter, followed by summer.•Odor intensity, odor active values, and PC-TWA assessment methods were implemented.•Key odor sites were compost workshop (CW) and dehydration workshop 2 (DW2).•Key odors were NH3, DMS, and DMDS in CW, and NH3, H2S, and MT in DW2.