“…This includes processes associated with operational issues, such as i) accelerated corrosion ( Andersson, 1990 ; Jenne et al., 1992 ); ii) the precipitation of carbonates ( Griffioen and Appelo, 1993 ) and Fe and Mn (hydr)oxides ( Andersson, 1990 ; Willemsen, 1990 ) that can cause scaling within heat exchangers, pipes and in and around wells; iii) the formation of a separate gas phase ( Lüders et al., 2016 ) that can block pipes or parts of the near-well pore space and iv) the dissolution of amorphous silica and silicates at increased temperatures ( Arning et al., 2006 ; M. Bonte et al., 2013b ; Holm et al., 1987 ) that can precipitate when the water is cooled in the surface installations during heat recovery ( Gunnarsson and Arnórsson, 2005 ). There are also processes associated with potential changes in groundwater quality, such as i) the release of dissolved organic carbon (DOC) and associated redox processes ( Bonte et al., 2013a ; Brons et al., 1991 ; Jesußek et al., 2013a ; 2013b ); ii) the release and fixation of trace elements and heavy metals ( M. Bonte et al., 2013b ; García-Gil et al., 2016 ; Lüders et al., 2020 ; Saito et al., 2016 ) and iii) increased or decreased solubility ( Koproch et al., 2019 ), volatilisation ( Schwardt et al., 2021 ) and degradation ( Men and Cheng, 2011 ; Němeček et al., 2018 ; Zuurbier et al., 2013 ) of organic contaminants.…”