Process water from hydrothermal carbonization: from waste to liquid fertilizer and soil health amendment in circular bioeconomy
Qingnan Chu , Xiangyu Liu , Yanfang Feng , Detian Li , Shuai Yin , Chengrong Chen , Zhimin Sha
Biochar ›› 2026, Vol. 8 ›› Issue (1) : 96
Hydrothermal carbonization (HTC) transforms wet or dry biomass into hydrochar, generating a nutrient-rich process water, hereafter termed HTC-PW, which is often overlooked as waste. This review synthesizes current knowledge on HTC-PW composition, including varied pH (3.5–9.2), high organic content (TOC 4,000–31,700 mg L−1), and nutrients such as NH₄⁺–N (up to 4,400 mg L−1) and potassium (5,870–6,330 mg L−1), derived from feedstocks such as sewage sludge and food waste. Process controls such as temperature and residence time tune HTC-PW properties for agronomic use, enabling enhanced partitioning of elements between solid and liquid phases. Pathways include direct fertigation, co-application with biogas slurry, and conditioned recovery, such as struvite precipitation yielding 92–99% P and 43–88% N. Performance metrics demonstrate yield increases of 6.7–29.2% and improved nutrient use efficiency of 15–30% in crops such as rice, alongside microbiome shifts favoring bacterial communities for better nutrients cycling. Beyond fertilization, valorization routes encompass anaerobic digestion for biogas (250–350 mL CH4 g−1 COD, with 70–85% COD removal) and catalytic reforming for H₂. Risks such as salinity (EC 5–24 mS cm−1) and context-dependent N2O responses (suppression under inhibitory organics versus pulses under high NH4⁺ loading) necessitate bioassays and regulatory compliance, while techno-economic analysis and life-cycle assessment indicate scenario-dependent benefits, including economic savings where avoided wastewater-treatment credits apply and 20–50% reductions in global warming potential when mineral fertilizer substitution is credited. Gaps in long-term trials and scalability are identified, with future directions emphasizing machine learning for predictive optimization of HTC-PW properties and applications. Overall, current evidence supports HTC-PW primarily as a nutrient-rich liquid amendment (fertilizer-like input) that alters soil DOM and microbial processes, while direct evidence for consistent improvements in soil physical structure remains limited and warrants targeted measurement in future field trials.
Energy / Greenhouse gas / Hydrochar / Life cycle assessment / Sustainable agriculture / Waste management
| [1] |
|
| [2] |
|
| [3] |
|
| [4] |
|
| [5] |
|
| [6] |
|
| [7] |
|
| [8] |
|
| [9] |
|
| [10] |
|
| [11] |
|
| [12] |
|
| [13] |
|
| [14] |
|
| [15] |
|
| [16] |
|
| [17] |
|
| [18] |
|
| [19] |
|
| [20] |
|
| [21] |
|
| [22] |
|
| [23] |
|
| [24] |
|
| [25] |
|
| [26] |
Farm Bureau (2025) Fertilizer Outlook: Global Risks, Higher Costs, Tighter Margins. American Farm Bureau Federation, Washington, DC. https://www.fb.org/market-intel/fertilizer-outlook-global-risks-higher-costs-tighter-margins. Accessed 24 Nov 2025 |
| [27] |
|
| [28] |
|
| [29] |
|
| [30] |
|
| [31] |
|
| [32] |
|
| [33] |
|
| [34] |
|
| [35] |
|
| [36] |
|
| [37] |
|
| [38] |
|
| [39] |
|
| [40] |
|
| [41] |
|
| [42] |
|
| [43] |
|
| [44] |
|
| [45] |
|
| [46] |
|
| [47] |
|
| [48] |
|
| [49] |
|
| [50] |
|
| [51] |
|
| [52] |
|
| [53] |
|
| [54] |
|
| [55] |
|
| [56] |
|
| [57] |
|
| [58] |
|
| [59] |
|
| [60] |
|
| [61] |
|
| [62] |
|
| [63] |
|
| [64] |
|
| [65] |
|
| [66] |
|
| [67] |
|
| [68] |
|
| [69] |
|
| [70] |
|
| [71] |
|
| [72] |
|
| [73] |
|
| [74] |
|
| [75] |
|
| [76] |
|
| [77] |
|
| [78] |
|
| [79] |
|
| [80] |
|
| [81] |
|
| [82] |
|
| [83] |
|
| [84] |
|
| [85] |
|
| [86] |
|
| [87] |
|
| [88] |
|
| [89] |
|
| [90] |
|
| [91] |
|
| [92] |
|
| [93] |
|
| [94] |
|
| [95] |
|
| [96] |
|
| [97] |
|
| [98] |
|
| [99] |
|
| [100] |
|
| [101] |
|
| [102] |
|
| [103] |
|
| [104] |
|
| [105] |
|
| [106] |
|
The Author(s)
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