2020
DOI: 10.1016/j.scitotenv.2020.139786
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Enhanced transformation of phosphorus (P) in sewage sludge to hydroxyapatite via hydrothermal carbonization and calcium-based additive

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Cited by 72 publications
(23 citation statements)
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“…It was also found that more Ca 3 (PO 4 ) 2 and less AlPO 4 could be detected with increasing incineration temperature (from 675 to 950 • C) [49,76]. For sludge-derived hydrochar, quartz (SiO 2 ) has also been found as the main crystalline compound [22,98,100,[110][111][112][113]. However, crystalline P phases in hydrochar vary depending on the sludge properties and hydrothermal conditions.…”
Section: P Complexation and Mineralogymentioning
confidence: 98%
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“…It was also found that more Ca 3 (PO 4 ) 2 and less AlPO 4 could be detected with increasing incineration temperature (from 675 to 950 • C) [49,76]. For sludge-derived hydrochar, quartz (SiO 2 ) has also been found as the main crystalline compound [22,98,100,[110][111][112][113]. However, crystalline P phases in hydrochar vary depending on the sludge properties and hydrothermal conditions.…”
Section: P Complexation and Mineralogymentioning
confidence: 98%
“…Xu et al only detected Ca 7 Mg 2 (PO 4 ) 6 as the crystallized P in Ca-rich hydrochar (260 • C for 4 h) [98]. Zheng et al reported AlPO 4 as the main fraction in hydrochar (280 • C for 1 h), with the identification of other types (Ca-P and Fe-P) [100,112]. Another study also showed the dominance of AlPO 4 regardless of the hydrothermal Fig.…”
Section: P Complexation and Mineralogymentioning
confidence: 99%
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“…Several studies demonstrate the presence of calcium phosphates in biomass ashes/deposits [12], in particular, from olive pit [13][14][15], manure [16], agricultural and forest residues [17], and from bone material [18]. Recently, hydroxlyapatite (Ca 10 (PO 4 ) 6 (OH) 2 , HAp) was found to be the most frequent mineral phase in sewage sludge ashes [19][20][21].…”
Section: Introductionmentioning
confidence: 99%
“…Moreover, the inclusion of P resources onto the CRMs list should have stimulated development of methods and technologies for P recovery from internal waste resources [9]. The most promising secondary sources of P are wastes produced in the municipal wastewater treatment plants (WWTPs) [18], wherein the P recovery potential appears at various stages of waste processing [19], as effluent from the treatment station, leachate (sedimentary liquid) [20,21], sewage sludge (SS) [22][23][24][25][26][27][28] and sewage sludge ash (SSA) [29,30]. In each of the subsequent waste treatment processes, the volume of substrate used for the P recovery is getting smaller, but the concentration of this element per unit volume is increasing [31].…”
Section: Introductionmentioning
confidence: 99%