2011
DOI: 10.1299/jee.6.119
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Mechanisms of Malodor Reduction in Dewatered Sewage Sludge by Means of The Hydrothermal Torrefaction

Abstract: To evaluate malodor reduction by means of the hydrothermal torrefaction, concentrations of the main malodorous compounds in odor samples from solid products before and after treatment were measured using gas chromatography. The concentrations of the sulfur-containing compounds were decreased by this treatment. To elucidate the mechanisms of this malodor reduction, odor distributions were analyzed with an odor-measuring device. The odor intensities in the odor sample from the solid product were lower than those… Show more

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Cited by 9 publications
(7 citation statements)
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“…The sensory assessment of the smell and colour of the carbonized end products recovered after the M-HTC process showed them to be similar and consistent with thermochemical conversion/transformation processes of organic biomass reported in literature involving other conventional heating methods (35,42,43,44). In essence, these similarities in the organoleptic properties of smell and colour of the end products from the M-HTC of HBW with existing methods, and the characteristic colour and smell change of end products typical of HTC processes, provide preliminary evidence that suggests M-HTC converted HBW to carbonaceous materials.…”
Section: Mechanisms Behind Smell and Colouration Changessupporting
confidence: 85%
See 1 more Smart Citation
“…The sensory assessment of the smell and colour of the carbonized end products recovered after the M-HTC process showed them to be similar and consistent with thermochemical conversion/transformation processes of organic biomass reported in literature involving other conventional heating methods (35,42,43,44). In essence, these similarities in the organoleptic properties of smell and colour of the end products from the M-HTC of HBW with existing methods, and the characteristic colour and smell change of end products typical of HTC processes, provide preliminary evidence that suggests M-HTC converted HBW to carbonaceous materials.…”
Section: Mechanisms Behind Smell and Colouration Changessupporting
confidence: 85%
“…The eradication of the foul odour in carbonized biowastes is primarily due to the thermal hydrolysis of these organic macromolecular components during the M-HTC process. The hydrolytic process facilitates the solubilization of compounds causing foul odour in HBW, such as the nitrogenous benzopyrrole compounds -notably indole and skatole, hydrogen sulphide, the methyl sulphides and other sulphur-containing compounds (32,33,34); and renders them nonvolatile, dissolved and trapping them in the liquid phase (35). Other reactions associated with HTC, including aromatization, may also suppress odour (36).…”
Section: Mechanisms Behind Smell and Colouration Changesmentioning
confidence: 99%
“…This is due to the solubility of organic and inorganic components in the pressurized subcritical water, which also decreases the amount of salts and minerals contained in the biomass [20]. Namioka et al [90] observed that in the WT of sewage sludge, thermal-odour caused from high sulfur content reduces after the treatment of WT, whereas the amount of aldehydes, light aromatics, and organic acid components increased marginally. During hydrothermal torrefaction with hot compressed water from the 200 to 265°C disintegration of hemicellulose with water occurs rapidly, whereas lignin is relatively inactive, resulting in good binding properties during pelletization [91].…”
Section: Comparison Of Torrefaction Processmentioning
confidence: 99%
“…Tokyo Institute of Technology has been investigating sewage sludge hydrothermal treatment system, resulted in improved natural drying performance and reduced odor [22][23][24], and recent research confirmed that NO reduction occurred on the hydrothermally treated sludge compared to untreated sludge [25]. The proposed refuse-derived fuel (RDF) production system is shown in Fig.…”
Section: Hydrothermal Treatment Of Sludgementioning
confidence: 99%
“…This experiment was conducted in northern Japan sewage sludge with characteristics shown in Table 15.6 using 3 m 3 horizontal steel vessel shown in Fig. 15.5 at 19.6 MPa and 200°C for 30 min [24]. After being treated, 150 g of each solid product sample was placed into a 5 L gas sampling bag, and 3 L of fresh air was injected into the bag.…”
Section: Changes In Product Odormentioning
confidence: 99%