2019
DOI: 10.1016/j.jenvman.2018.12.009
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Chemical and odor characterization of gas emissions released during composting of solid wastes and digestates

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Cited by 89 publications
(40 citation statements)
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“…Figure 4 shows the daily odour emission rates (OER) obtained during the SS composting process, together with the average temperature of the reactor and the specific airflow. Similarly to other works where odour emission from SS composting were studied [24,42], the profiles of odour emission reached its maximum during the thermophilic phase, when biological activity is higher and then tended to decrease as temperature and biological activity decreased. In fact, the distribution of the odour emissions during the whole SS composting process shows that more than 64% of these emissions happened during the thermophilic phase of the process, whereas the rest was divided between the pre-thermophilic and the mesophilic stages.…”
Section: Nh 3 H 2 S Tvocs and Odour Emissionmentioning
confidence: 53%
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“…Figure 4 shows the daily odour emission rates (OER) obtained during the SS composting process, together with the average temperature of the reactor and the specific airflow. Similarly to other works where odour emission from SS composting were studied [24,42], the profiles of odour emission reached its maximum during the thermophilic phase, when biological activity is higher and then tended to decrease as temperature and biological activity decreased. In fact, the distribution of the odour emissions during the whole SS composting process shows that more than 64% of these emissions happened during the thermophilic phase of the process, whereas the rest was divided between the pre-thermophilic and the mesophilic stages.…”
Section: Nh 3 H 2 S Tvocs and Odour Emissionmentioning
confidence: 53%
“…On the other hand, few works dealing with the OEFs of SS biological treatment have been found. However, [42] evaluated the OEFs of different substrates in a 300 L aerated pilot-scale reactor, reporting an OEF of 9.35 × 10 8 ou•Mg −1 DM-SS for SS composting and [24] obtained an OEF of 9.45 × 10 7 ou•Mg −1 DM-SS in a full-scale sewage sludge composting plant. For SS composting, different ranges of target pollutants and odour concentrations can be found in literature depending on the characteristics of the feedstocks or the composting process itself [43][44][45].…”
Section: Nh 3 H 2 S Tvocs and Odour Emissionmentioning
confidence: 99%
“…Finally, often, VOCs, which are responsible for the odor properties of gaseous mixtures, are present at concentrations in the range of ppb or even ppt, which is lower than the instrumental detection Atmosphere 2020, 11, 92 6 of 27 limit. Therefore, pre-concentration techniques are commonly adopted before GC-MS. Common pre-concentration techniques include adsorption of the static headspace on active carbons followed by thermal desorption (TD), purge and trapping, and solid phase microextraction (SPME) [34,35].…”
Section: Applicability and Limitationsmentioning
confidence: 99%
“…However, these papers did not take into account odor properties of the sludge before and after the fermentation process. The importance of the issue of further processing of the post-fermentation sludge is highlighted in the works of Ricón et al In [26], it was demonstrated that the composting of post-fermentation sludge generates emissions in the range of app. 30 ou E per gram of the initial content of the composted matter.…”
Section: Introductionmentioning
confidence: 99%
“…These are the adjustment of the process parameters in such a way as to minimize the odor nuisance of the post-fermentation sludge, and the use of the lowest possible number of instruments for measurements in order to reduce the cost of process control. The former issue can be solved by using combinatory techniques for odor analysis, such as sensory and instrumental methods [26,27].…”
Section: Introductionmentioning
confidence: 99%