La production de biochars et hydrochars permet de former des amendements enrichis en carbone aromatique, potentiellement plus récalcitrant contre les dégradations dans le sol, tout en produisant massivement des énergies renouvelables. Ces amendements ont pour objectif d’augmenter la quantité de matières organiques des sols (MOS), ainsi que leur fertilité. Néanmoins, due à la diversité des biomasses pouvant être utilisé et des procédés de production, des incompréhensions existent sur le potentiel de ces matériaux à stocker du C dans le sol, à court et à long terme. De plus, des méthodes permettant d’évaluer rapidement la stabilité à long terme de ces matériaux restent à mettre au point, afin de permettre aux utilisateurs de statuer de la qualité de ces nouveaux amendements. Ces travaux ont consisté à évaluer la stabilité de biochars et hydrochars, biologiquement par des incubations de sols, et chimiquement par des oxydations à l’acide dichromate. Les biochars ont montré un haut niveau de stabilité biologique et chimique, permettant de stocker une quantité importante de carbone à l’échelle du siècle. De façon contrastée, les hydrochars se sont caractérisés par une stabilité beaucoup plus faible que les biochars, ne permettant probablement pas de séquestrer massivement du carbone au-delà de la décennie. L’hydrochar a induit un priming effect positif (stimulation), alors que le biochar a induit un priming effect négatif (protection). L’altération physique des deux matériaux a conduit à une augmentation de la stabilité et à une diminution du priming effect, mettant en lumière l’importance des paramètres environnementaux dans les stratégies de séquestration de carbone du sol. Les sols d’anciennes charbonnières ont été utilisés comme modèle d’étude à long terme de l’effet d’un apport de biochar après plusieurs siècles. Leur analyse a mis en évidence que l’apport de biochar améliore durablement les propriétés physicochimiques du sol, telle que la teneur en argile, la capacité d’échange cationique (CEC), la quantité de carbone soluble, et les teneurs en azote et phosphore. Toutefois, après plusieurs siècles d’un amendement de biochar, les communautés microbiennes ne présentaient pas d’adaptation spécifique à la dégradation d’un nouvel apport de biochar. Dans ce modèle, l’apport de résidus de plante a entrainé un priming effect négatif. Ainsi, l’apport de biochar, en générant des conditions particulières, permet le maintient de communautés de microorganismes avec la capacité de réorienter leur métabolisme, afin de dégrader spécifiquement de nouveaux substrats plus facilement minéralisables. D’autres travaux seront nécessaires afin d’évaluer la stabilité des biochars dans le système sol-plante. / Biochars and hydrochars production can form amendments enriched in aromatic carbon, potentially recalcitrant against microbial degradation, while massively producing renewable energy. These amendments are aimed to increase soil organic matter (SOM) quantity, and soil fertility. However, due to the diversity of their feedstock and production processes, misunderstandings exist on the potential of these materials to store C in soil at short and long term. In addition, methods to rapidly evaluate the long-term stability of these materials remain to be developed, in order to allow users to determine the quality of these new amendments. This work was consisted for assessing the stability of biochar and hydrochars, biologically by soil incubations, and chemically by oxidation with acid dichromate. The biochar showed a high level of biological and chemical stability, allowing to storage a large amount of carbon throughout the century. In opposite, the hydrochars might not allow sequestering massively carbon beyond the decade, due to its lower biological and chemical stability. The hydrochars induced a positive priming effect (stimulation) while biochar induced a negative priming effect (protection). Physical weathering of both materials led to an increase of stability and a decrease of the priming effect, highlighting the importance of environmental factors in evaluation of strategies for sequestering carbon. Charcoal kiln soils were used as a model for long-term study of the input of biochar in soil after several centuries. Their analysis showed that the contribution of biochar sustainably improves the physicochemical properties of the soil, such as clay content, cation exchange capacity (CEC), amount of nitrogen, phosphorus, and soluble carbon. However, after several centuries of biochar amendment, microbial communities showed no specific adaptation to the degradation of a new biochar input. In this soil model, the input of plant residues resulted in a negative priming effect. Thus, the contribution of biochar in generating specific conditions, allows the maintenance of microbial communities with the ability to switch of substrates, for a new source of substrates more easily degradable. Further works are needed to assess the stability of biochar in soil-plant system.

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Margretelunds reningsverk i Åkersberga står såsom andra svenska avloppsreningsverk inför nya utmaningar i samband med anpassningen till ett mer hållbart och cirkulärt samhälle. För att bidra till en bra lokal miljö med få transporter och minimerad lukt, uppnå en hög grad av fosforåtervinning, samt reducera organiska och icke-organiska föreningar i slammet ska Roslagsvattenb i samarbete med IVL Svenska Miljöinstitutet utvärdera C-Greens OxyPower HTC-teknik. HTC-tekniken är hydrotermisk karbonisering (HTC) kombinerat med våtoxidation av HTC- vatten. Det våta slammet tas om hand på reningsverket och omvandlas till en fast kolanrikad produkt så kallad HTC-biokol eller hydrokol. HTC-processen innebär uppvärmning av det våta slammet (180–260°C) under högt tryck och syrefria förhållande med vatten närvarande. Hydrokolet som bildas kan uppgraderas till bränsle, jordförbättringsmedel eller aktiverat kol.  I detta arbete studerades potentialen att använda hydrokol som jordförbättringsmedel genom att undersöka biokolets fysikaliska- och kemiska egenskaper. Hydrokol jämfördes med biokol från pyrolys som också är en förkolningsprocess av biomassa vid höga temperaturer (300–650 °C) under syrefria förhållande dock utan närvaro av vatten.  Baserat på resultatet från publicerade studier, har hydrokol potentialen att ersätta eller komplettera mineralgödsel. Hydrokol förbättrar markens bördighet och produktivitet genom att t.ex. öka den totala växttillväxten, förbättrar mineraliseringen av näringsämnen och tillgängligheten av fosfor, samt ger en långsam frisättning av näringsämnen. / Margretelund's treatment plant in Åkersberga, like other Swedish sewage treatment plants, faces new challenges in connection with the adaptation to a more sustainable and circular society. In order to contribute to a good local environment with few transports and minimized odors, achieve a high degree of phosphorus recovery, and reduce organic and inorganic pollutants in the sludge, Roslagsvatten, in collaboration with the IVL Swedish Environmental Institute, will evaluate C-Green's OxyPower HTC-technology.  The HTC-technology is hydrothermal carbonization (HTC) combined with wet oxidation of HTC-water. The wet sludge is taken care of at the treatment plant and converted into a fast carbon-enriched product called HTC-biochar or hydrochar. The HTC-process involves heating the wet sludge (180–260°C) under high pressure and oxygen-free conditions with water present. The hydrochar that is formed can be upgraded to fuel, soil improver or activated carbon.  In this work, the potential of using hydrochar as a soil improver is studied by examining the biochar's physical and chemical properties. Hydrochar was compared with biochar from pyrolysis, which is also a charring process of biomass at high temperatures (300–650 °C) under oxygen-free conditions but without the presence of water.  Based on the results of published studies, hydrochar has the potential to replace or supplement mineral fertilizers. Hydrochar improves soil fertility and productivity by e.g. increase overall plant growth, improve nutrient mineralization and phosphorus availability, and provide a slow release of nutrients.

Increasing population across the globe paved the way for rapid growth in industrialization. Pharmaceuticals, automotive, textiles, agriculture, electronics, electrical and many other industries discharge different types of heavy metals, dyes and organic contaminants into ground water. These discharges are released into lakes and rivers without prior treatment causing huge environmental impact to the environment. Among different remediation techniques, adsorption was considered the most promising method because of its low-cost and high efficiency. Biomass is considered as the most practical and renewable source for production of bio products and biofuels. Biomass is also used for carbon sequestration and as an essential element to produce hydrochar and biochar which are considered as the 21st century black gold. Hydrochar and biochar can be used as an excellent low-cost adsorbent for the removal of heavy metals, dyes and organic contaminants from water. This dissertation work focuses on, firstly, development of novel oxone treated hydrochar as an adsorbent for the efficient removal of Pb(II) and Methylene Blue (MB) from aqueous solutions. Secondly, preparing novel ozone oxidized hydrochar treated with polyethyleneimine for removal of Remzol Brilliant Blue (RBB) and Remzol Reactive Black (RRB) dyes from aqueous solutions. Thirdly, producing high-performance CO2 activated biochar as an adsorbent for efficient removal of Aniline from aqueous solution. All prepared hydrochar and biochar adsorbents were characterized by SEM, TGA, FTIR, Elemental analysis, conductometric titration, and N2 adsorption-desorption isothermal analyses (BET and BJH). The adsorption capacities were determined by Atomic absorption spectrometry (AAS) and Ultraviolet–visible spectroscopy (UV-VIS) respectively. The adsorption capacity of each prepared biochar or hydrochar was determined and both kinetic and isothermal studies were performed. The optimal preparation conditions and adsorption parameters were determined for each adsorbent.

La carbonisation hydrothermale (HTC) est un procédé de conversion en énergie de la biomasse dans l’eau sous critique (180-250°C) à faibles pressions (10-40 bars). Ce procédé conduit à la production d’un matériau solide carboné appelé "hydro-char". L’objectif de ce travail est d’optimiser le procédé HTC par l’étude des performances de l’hydro-char comme source d’énergie. La biomasse étudiée est un résidu d’extraction d’huile d’olive dénommé grignons d’olive constitués de peau, de pulpe et de noyau (taux d’humidité de 70%). Ces grignons d’origine marocaine ont été préalablement séchés (GOS). Au cours de l’HTC, la biomasse est décomposée via des réactions de déshydratation et de décarboxylation. Les hydro-chars sont moins humides et plus riches en carbone que les GOS. Aussi, ils s’appauvrissent en cendres en les transférant dans la phase liquide. Les hydro-chars ont un PCS plus élevé que celui de la tourbe et de lignite. Les résultats montrent que le rendement et les propriétés de l’hydro-char dépendent surtout de la température du procédé. Pour mieux analyser l’effet des conditions opératoires, l’approche des plans d’expériences a été appliquée pour optimiser et modéliser le procédé HTC. Grâce au plan de Doehlert, on peut relier les propriétés de l’hydro-char avec son rendement massique et son comportement thermique de combustion. La représentation des surfaces de réponses a permis de définir les zones de production d’hydro-char avec ses propriétés permettant d’orienter l’élaboration de l’hydro-char pour répondre aux critères d’une application prédéfinie. Le liquide issu de l’HTC des GOS montre une sensibilité à la variation des conditions opératoires. Le carbone soluble dans ce liquide lui donne un pouvoir polluant. Pour le diminuer, deux procédés de traitement ont été testés: l’évaporation et l’oxydation en voie humide. Les résultats ont montré que la quantité d’eau utilisée pour le traitement est le facteur le plus influent sur le bilan énergétique du procédé HTC. / Hydrothermal carbonization (HTC) allows pre-treating humid biomass in subcritical water (180-250°C) and at low pressures (10-40 bars) in the absence of air. This process produces a carbonaceous solid material called "hydro-char". The main aim of this work is to optimize the HTC process by studying the potential of hydro-char to produce energy. The studied biomass is a by-product of the olive oil industry called olive pomace containing water, residual oil, olive skin, olive pulp, and olive stones (with 70% moisture content). The moroccan olive pomace was first air-dried (DOP) and characterized. During the HTC process, the biomass is decomposed via dehydration and decarboxylation reactions. The obtained hydro-char has much less moisture and higher carbon contents than that of untreated DOP. Also, the hydro-char becomes poor in ashes by transferring them into the liquid phase. Hydro-chars have a higher HHV than that of peat and lignite. The results show that hydro-char mass yield and its properties depend on the process temperature especially. For a better analysis of the effect of operating conditions, a Design of Experiments Response Surface Methodology (DoE/RSM) approach was applied to optimize the HTC process. The DoE/RSM allows identifying a relationship between hydro-char properties and its mass yield and thermal combustion behavior. Response-surface plots show defined areas of production of hydro-char which allows tailoring hydro-char elaboration to a specific application. The process liquid from the HTC treatment of DOP shows a sensibility to operating conditions. The soluble carbon in the HTC liquid increases its polluting power and to decrease it two treatment process have been tested: evaporation and wet oxidation. Finally, the results show that the amount of water used for the hydrothermal treatment is the most influential factor on the energy balance of the HTC process.

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The production of municipal solid waste has continued to grow in recent years. In Italy, municipal solid waste production reaches about 29 million tons per year. The organic fraction of municipal solid waste (OFMSW), which accounts for 30-40% of the total waste, usually undergoes biological treatments such as anaerobic digestion or composting, or is incinerated or landfilled. Biological treatments are considered not economically viable due to the long processing time (20-30 days), while incineration and landfilling are considered as low cost but polluting processes. In contrast, Hydrothermal Carbonization (HTC) is a cost-effective process to treat organic waste especially for the shorter processing time (0.5-8 h) and the possibility to treat directly wet heterogeneous materials. This thesis aims to investigate the potential use of HTC to upgrade OFMSW and other biomasses to biofuels or valuable byproducts. Chapter 1 gives an overview on the state of the art of HTC technology applied to organic wastes, focusing both on mechanisms and on the characteristics of reaction products. Chapter 2 investigates the potential use of HTC to upgrade the organic fraction of municipal solid waste (OFMSW) into biofuel and byproducts. The impact of process conditions (process time, temperature and solid load) on the formation, chemical and energy properties of hydrochar was deeply investigated. To analyze the behavior of hydrochar as a solid biofuel, the combustion (oxidation) of hydrochar and the co-firing (co-oxidation) of hydrochars and coals was also investigated. The results show that, especially at HTC harsher conditions, hydrochar is a “coal-like” material, that can be used as a valuable solid biofuel. The results evidenced that hydrochar is composed of primary char and secondary char. Primary char (non-extractable with organic solvents) has characteristics similar to coal and could be recovered for combustion, while secondary char is an amorphous and more volatile solid, easily extracted with organic solvents, which found possible application as a source of biochemicals and liquid bio-fuel. Chapter 3 investigates the use of HTC as a promising pre-treatment to enhance the biomethane potential during anaerobic digestion of OFMSW. Anaerobic digestion experiments were carried out using the HTC process liquid and the entire HTC reaction mixtures. Results proved that, when compared to the raw OFMSW, the use of HTC liquid and HTC mixture into AD lead to an increase of biomethane production of up to 37% and 363% by volume, respectively. Chapter 4 reports an HTC kinetics study and a kinetic model, which accounted for reactions leading to the production of primary and secondary char, as well as the liquid and gas phases. The model was optimized using experimental data performed on a lignocellulosic feedstock (olive trimmings) and validated on two other types of biomasses (grape marc and Opuntia Ficus Indica) and was used as a reliable tool to predict the carbon distribution among HTC products. In this chapter an in-depth analysis was also carried out to understand the evolution of feedstock characteristics during the heat-up transient phase before reaching the HTC set-point temperature. The results show that during heat up, the feedstock carbonized to a considerable extent at 220-250 °C. Tests clearly show evidence of the transition between thermal hydrolysis and HTC. Chapter 5 presents a study conducted to evaluate the economic feasibility and the detailed energy and cost analyses of a hypothetical HTC plant transforming wet biomass into pelletized dry hydrochar. To achieve these goals, a model was developed on the basis of experimental results obtained previously on two other organic materials (grape marc and off-specification compost). The results show that, when operating the HTC plant with grape marc at the optimal HTC conditions (T=220 °C, t=1 h, dry biomass to water ratio=0.19), the production cost of hydrochar were determined to be 157 €/ton, competitive with the price of wood pellets (150-200 €/ton). This makes HTC a promising process for a large development at the industrial scale.

Phytomining is a promising method for metal recovery, but rare studies have been devoted to metal recovery from hyperaccumulator biomass. The objective of this study was to propose efficient and sustainable methods for treating REE hyperaccumulators, aimed at enhancing REE recovery and obtaining value-added byproducts. Firstly, grass seeds fed with a solution containing Y, La, Ce, and Dy, were found to have the capacity to accumulate around 510 mg/kg (dry basis) of total rare earth elements (TREEs) in grass leaves. With the use of conventional hydrometallurgy, around 95% of Y, La, Ce, and Dy were extracted from the GL using 0.5 mol/L H2SO4 at a solid concentration of 5 wt.%. Subsequently, microwave-assisted hydrothermal carbonization (MHTC) was used to convert the leaching residue into hydrochar to achieve a comprehensive utilization of GL biomass. Scanning electron microscopy (SEM) analysis revealed that the original structure of GL was destructed at 180 °C during MHTC, producing numerous microspheres and pores. As the reaction temperature increased, there was a concurrent increase in carbon content, HHV, and energy densification, coupled with a decrease in hydrogen and oxygen contents of hydrochar. The results showed that the waste biomass of the GL after REE extraction can be effectively converted into energy-rich solid fuel and low-cost adsorbent via MHTC. In addition to utilizing conventional hydrometallurgy for REE recovery and employing MHTC to convert leaching residue into hydrochar, MHTC was also applied to directly recover REEs and produce hydrochar from the GL as a more efficient approach. The effects of acid type and acid concentration on REE extraction from GL using MHTC were investigated. The utilization of 0.2 mol/L H2SO4 led to the extraction of nearly 100% of REEs from the GL into the resulting biocrudes. Concurrently, the acid-mediated MHTC system also caused the degradation of amorphous hemicellulose and crystalline cellulose present in the GL, thereby enhancing the thermal stability of the resulting hydrochar. The physiochemical properties of the hydrochar were also influenced by acid type and acid concentration. Using 0.2 mol/L H2SO4 as the reaction medium, MHTC resulted in a yield of 28% hydrochar with enhanced high heating value and energy densification. These results suggest that MHTC in the presence of an appropriate concentration of H2SO4 is an effective way to extract REEs and produce hydrochar from the GL. A process that combines solvent extraction and struvite precipitation was developed for the treatment of biocrudes containing REEs and other elements. In the extraction step, 95.6% of REEs were extracted using 0.05 mol/L di(2-ethylhexyl)phosphoric acid (D2EHPA) with an aqueous to organic (A/O) ratio of 1:1 at pH 3.0. However, other impurity metals were co-extracted into the organic phase with the REEs. To solve this issue, a subsequent scrubbing step using deionized water was applied, with the removal of over 98% of these impurities, while incurring negligible loss of REEs. After the scrubbing step, over 97% of REEs were ultimately stripped out from the organic phase as REE oxalates using 0.01 mol/L oxalic acid. Furthermore, phosphorous (P) was found to be retained in the raffinate after the solvent extraction process. 94.4% of the P was recovered by forming struvite precipitate at pH 9.0 and a Mg/P molar ratio of 1.5. In general, high purity and value-added REE products and struvite precipitate were eventually achieved from biocrudes in environmentally friendly and economically viable ways. In summary, this study contributes a sustainable and efficient framework for REE hyperaccumulator treatment that integrates acid leaching, MHTC, solvent extraction, and struvite precipitation. This work supports a circular economy, minimizing waste and promoting resource reuse. / Doctor of Philosophy / Rare Earth Elements (REEs) are essential for technologies like smartphones and electric vehicles, but traditional mining is environmentally harmful and resource-intensive. Innovations are needed to reduce waste and enhance resource reuse. In this study, grass, a natural accumulator, was found to be able to extract REEs from contaminated soils. Nearly all REEs can be recovered efficiently using a mild sulfuric acid solution, and the residual biomass was also transformed into valuable byproducts such as energy-rich solid fuel and low-cost adsorbents. Furthermore, a more sustainable and efficient method, microwave-assisted hydrothermal carbonization, was also investigated to treat grass aiming at recovering REEs and achieving value-added products. High purity REE product and phosphorous-rich fertilizer were finally produced. This method reduces the environmental impact of REE mining, utilizes renewable resources, and cuts costs, thereby supporting economic sustainability. By turning environmental challenges into opportunities, this research highlights how innovative, greener methods can drive a more sustainable future in resource management.