• Plant Growth Trials
    Using Biochar
    At Celignis Biomass Lab

Background

Biochar is a carbon-rich solid material produced by the pyrolysis of biomass. This involves heating the feedstock in the absence of oxygen, which results in the formation of a high-carbon material that can potentially be used in a wide variety of applications, including: as a soil amendment, a component of biobased materials, and in pollution remediation.

Biochar can be made from a variety of feedstocks, including wood, agricultural residues, and municipal solid waste.


Biochar was used thousands of years ago as a soil amendment in the Amazon Basin, where it is known as "terra preta" or "black earth." However, it has only been the case in recent years that there has been a renewed interest in the use of biochar as a tool for sustainable agriculture and climate change mitigation.

The use of biochar in soil amendment has several benefits. Firstly, it improves soil fertility by increasing the soil's capacity to retain water and nutrients. Biochar has a high surface area, which provides a habitat for microorganisms and increases the soil's ability to hold onto nutrients. Secondly, biochar can help to mitigate climate change by sequestering carbon in the soil. This is because biochar is stable and does not break down easily, which means that the carbon in biochar remains in the soil for a long time.

Biochar can also help to reduce greenhouse gas emissions from agriculture by reducing the need for synthetic fertilizers, which are energy-intensive to produce and release large amounts of nitrous oxide, a potent greenhouse gas.


Biochar for Plant Growth Promotion

Biochar can also be used for plant growth promotion. Research has shown that biochar can improve plant growth and yield by improving soil structure, increasing nutrient availability, and enhancing the activity of beneficial microorganisms in the soil. Biochar can also help to reduce the uptake of heavy metals by plants, which can be a problem in contaminated soils.

The benefits of biochar for plant growth promotion are due to its effects on soil physical, chemical, and biological properties. Biochar improves soil physical properties by increasing soil porosity, which enhances water infiltration and aeration. This is particularly important in compacted soils, where water and air movement are restricted.

Biochar also improves soil structure by promoting the formation of stable aggregates, which helps to prevent soil erosion and increase the stability of soil organic matter.

Biochar also improves soil chemical properties by increasing soil pH and cation exchange capacity (CEC). This means that biochar can help to neutralize acidic soils and increase the availability of essential nutrients such as calcium, magnesium, and potassium. Biochar can also adsorb pollutants and prevent their uptake by plants.


Biochar improves soil biological properties by providing a habitat for beneficial microorganisms. It can act as a substrate for microbial growth and can enhance the activity of soil bacteria and fungi. This can improve nutrient cycling and promote plant growth.

The use of biochar in agriculture is still in its early stages, and there is much to learn about its effectiveness in different soils and under different management practices. However, there is growing interest in the use of biochar as a sustainable tool for improving soil fertility, mitigating climate change, and promoting plant growth. Researchers are exploring new ways to produce biochar and optimize its properties for specific soil types and crops.


Analyses at Celignis to Evaluate Biochar for Soil Amendment


There are a wide variety of variables that will influence the quality and suitability of biochar to be used in soil amendment. These include:
  • The type of feedstock used to produce the biochar.
  • The pyrolysis conditions employed for biochar production.
  • The resulting physical and chemical properties of the char.
  • Type of soil to which the biochar will be amended.
  • The plant(s) to be grown on this amended soil.
At Celignis we are happy to help you evaluate your biochar samples for this end-use. Below we describe a number of the different analytical parameters that we determine which are of relevance to using biochar in soil amendment.


Major and Minor Elements in Biochar

Many of the major elements can be beneficial for plant growth, for example potassium plays a vital role in photosynthesis whilst phosphorus is involved in energy transfer processes and the formation of nucleic acids. Furthermore, the presence of certain elements, such as calcium and magnesium, can affect the soil pH, influencing the availability of nutrients and the activity of soil microorganisms. As a result, elemental analysis can help to predict the impact of biochar on soil pH and inform decisions on its application in specific soil types.

It is also important to consider that some heavy metals can pose potential risks to plants, soil organisms, and human health. As a result, biochar with high heavy metal concentrations may not be suitable for soil amendment, as it can lead to the accumulation of toxic elements in the soil, plants, and the food chain.

The European Biochar Certificate organisation (EBC), sets an upper threshold concentration for certain heavy metals in biochar, with these limits vaying according to the planned market application. (e.g. lead can not exceed 45ppm when biochar is used in the Agro-Organic sector, rising to 120 ppm the biochar is to be used in consumer materials). At Celignis we check as to whether the values for each heavy metal are above or below the threshold values for each of the EBC application sectors and provide the results in a PASS/FAIL table for each feedstock according to the specific sector and test.


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Electrical Conductivity

The electrical conductivity of a material is a measure of its ability to conduct electric current. Biochar's electrical conductivity is due to the presence of carbon, which is an excellent conductor of electricity. The pyrolysis process, which produces biochar, also results in the formation of various carbonaceous structures, such as graphite-like layers, which further contribute to its electrical conductivity.

The electrical conductivity of biochar depends on several factors, including its feedstock, production temperature, and post-treatment processes. Feedstock type and composition can affect the final properties of biochar, with wood-derived biochars generally having higher electrical conductivities than those derived from agricultural residues. The pyrolysis temperature also influences the electrical conductivity, with higher temperatures (above 500 oC) leading to the formation of more conductive structures.

The electrical conductivity of biochar allows it to effectively retain and exchange nutrients in the soil, particularly cations like potassium, calcium, and magnesium. This property is crucial for soil fertility, as it helps plants absorb essential nutrients more efficiently. The electrical conductivity of biochar can enhance soil microbial activity by facilitating the transfer of electrons between microbes and their environment. This electron transfer is essential for various microbial processes, such as nutrient cycling, and can lead to an overall increase in soil fertility. The conductive properties of biochar can help mitigate the spread of soil-borne pathogens by generating reactive oxygen species (ROS) and inhibiting the growth of harmful microorganisms. This, in turn, can lead to healthier plant growth and reduced disease incidence.


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Water Holding Capacity

The water holding capacity of a material refers to its ability to absorb and retain water. Biochar's water holding capacity is attributed to its porous structure, which provides a large surface area for water absorption. Additionally, biochar's hydrophilic functional groups, such as carboxyl and hydroxyl groups, can form hydrogen bonds with water molecules, further contributing to its water holding capacity.

The water holding capacity of biochar is influenced by several factors, including its feedstock, and the conditions used for pyrolysis. Additionally, post-treatment processes, such as oxidation and activation, can modify the surface chemistry and porosity of biochar, potentially affecting its water holding capacity. For example, oxidizing biochar can introduce hydrophilic functional groups, increasing its affinity for water.

Biochar with good water holding capacity can offer several benefits when used in soil amdendment, including:
  • Improved Soil Water Retention: This can help plants better tolerate water stress and reduce the need for irrigation, conserving water resources.
  • Enhanced Plant Growth and Yield: Resulting from a more consistent water supply to plants, especially during periods of low rainfall.
  • Mitigation of Soil Salinization: By diluting salt concentrations in the soil and promoting the leaching of excess salts.
  • Support for Soil Microorganisms: By maintaining adequate moisture levels, which in turn can promote nutrient cycling and soil fertility.
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Cation Exchange Capacity

Cation exchange capacity (CEC) is a measure of a material's ability to attract and hold positively charged ions (cations) such as potassium, calcium, and magnesium. The cation exchange capacity of biochar is attributed to the presence of negatively charged functional groups, such as carboxyl and phenolic groups, which can form electrostatic bonds with cations in the soil. These functional groups can either be present in the biomass feedstock or formed during the pyrolysis process.

Biochars derived from plant materials with higher lignin content, such as wood, tend to have a higher CEC than those produced from agricultural residues. Lower pyrolysis temperatures (below 500 oC) typically result in biochars with a higher CEC, as higher temperatures can lead to the degradation of negatively charged functional groups responsible for cation exchange.

Biochar with a good CEC can offer several benefits when used in soil amdendment, including:
  • Enhanced Nutrient Use Efficiency: By retaining and exchanging cations in the soil, allowing plants to absorb essential nutrients more effectively.
  • Amelioration of Soil Acidity: Through the biochar buffering soil acidity and promoting the availability of essential nutrients, particularly in acidic soils.
  • Mitigation of Soil Salinization: By diluting salt concentrations in the soil and promoting the leaching of excess salts.
  • Mitigation of Heavy Metal Contamination: High CEC biochar can contribute to the immobilization of heavy metals in contaminated soils, reducing their bioavailability and potential toxicity to plants.
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Polycyclic Aromatic Hydrocarbons (PAH)

Polycyclic aromatic hydrocarbons (PAHs), are a class of organic compounds comprising multiple aromatic rings. They can be formed during the pyrolysis of biomass and accumulate in biochar with their concentrations and types dependent on several factors, including the type of feedstock, pyrolysis temperature, residence time, and post-treatment processes.

The presence of PAHs in biochar is an important concern when using it as a soil amendment, as these compounds can pose potential risks to the environment, including:
  • Toxicity to Plants and Soil Microorganisms.
  • Bioaccumulation and Transfer to the Food Chain: The consumption of crops grown in biochar-amended soils with high PAH concentrations can lead to the ingestion of these harmful compounds.
  • Environmental Persistence: PAHs are known to be persistent in the environment and can accumulate in soil over time, leading to long-term ecological risks.
As for heavy metals (see above) the European Biochar Certificate organisation (EBC), sets upper threshold concentrations for PAHs in biochar. At Celignis we check as to whether these thresholds are exceeded for each of the EBC application sectors and provide the results in a PASS/FAIL table for each feedstock according to the specific sector and test.

Click here to read our dedicated webpage covering our analyses of PAHs in biochar.

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Surface Area and Porosity

The surface area and porosity of biochar are critical properties that influence its effectiveness as a soil amendment for several reasons:
  • Water Holding Capacity: A biochar with a high surface area and porosity can more water, improving the soil's water holding capacity.
  • Nutrient Retention and Release: Biochars with high surface areas and porosity can provide more active sites for nutrient adsorption, improving soil fertility and plant nutrient uptake.
  • Cation Exchange Capacity: CEC increases with surface area.
  • Microbial Habitat: A biochar with high surface area and porosity can promote the establishment of diverse microbial communities, which can enhance nutrient cycling and improve soil health.
  • Pollutant Adsorption: Biochars with high surface areas and porosity can adsorb and immobilize pollutants, such as heavy metals and organic contaminants, reducing their bioavailability and potential toxicity to plants and soil organisms.
Click here for our dedicated page on surface area analysis of biochar.


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Scanning Electron Microscopy (SEM)

Scanning electron microscopy is a widely used technique for characterizing the morphology, structure, and composition of materials at the micro- and nanometer scales. In the case of biochar, SEM analysis can provide valuable insights into its surface properties, porosity, and elemental composition, which are crucial factors that influence its performance as a soil amendment.

SEM analysis is a very useful companion analysis to the surface area and porosity analysis of biochar as it helps to visualize the size, shape, and distribution of pores in biochar.

SEM analysis can provide valuable information on the effects of various production parameters, such as feedstock, pyrolysis temperature, and post-treatment processes, on the properties of biochar. This can help optimize the production process to create biochars with desired characteristics for specific soil amendment applications.

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Liming

Liming tests are used to determine the ability of biochar to neutralize soil acidity, a key property that can influence its performance as a soil amendment. There are a number of reasons why it is important to undertake liming tests of biochar:
  • Soil pH Modification: The ability of biochar to modify soil pH can influence nutrient availability, as certain nutrients are more readily available at specific pH levels.
  • Enhancement of Soil Microbial Activity: Soil pH can also affect the activity of soil microorganisms, which play a crucial role in nutrient cycling and decomposition of organic matter.
  • Alleviation of Aluminum Toxicity: In acidic soils, high levels of soluble aluminum can be toxic to plants and inhibit root growth. By neutralizing soil acidity, biochar can reduce aluminum solubility and alleviate its toxic effects on plants.
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Tests at Celignis to Assess the Effects of Biochar on Plant Growth

We can undertake experiments to see the effect of adding biochar to soil on the germination and growth of plants. Within these experiments we can consider various variables and their effect on growth including:
  • Type of biochar used (e.g. compare between biochars from different feedstocks or between biochars produced from the same feedstock but using different pyrolysis conditions or different upgrading approaches).
  • Biochar loading rate (i.e. ratio of soil to biochar).
  • Soil used.
  • Plant type (examples of plants we have used include potato, tomato, corn, and lettuce).
These plant growth trials can be run at various scales, ranging from small pots in the laboratory to large trays in a dedicated greenhouse. Each set of conditions is run in triplicate and compared against a control where no biochar is used.

We can collect various data associated with these trials, ranging from crop yields to detailed analyses of the physical and chemical properties of the plant and soil, as detailed below.


Germination and Plant Growth

In our standard Biochar Plant Growth Trials package (P388) we collect the following data:

Plant Health Analysis

Relevant analyses that we can undertake to see the effect of biochar supplementation on plant health include: pigments (highly dependent on the nutrient uptake efficiency of the plant), leaf lamella size, and nutrient uptake. We can also perform stomata count, if the leaf type allows such analysis (which can be correlated to water stress resistance)

These results can then be correlated with the physical and chemical characteristics of biochar and plant growth results.

Soil Biology Analysis

Soil biology analysis can include: soil respiration test, bacterial count, fungal count (fungi to bacteria ratio), and soil enzymes (C-degrading, N mineralisation and P solubilisation enzymes).

These results can then be correlated with the physical and chemical characteristics of biochar and plant growth results.

Germination Inhibition

This is a separate test that we can undertake to evaluate the potential phytotoxicity of biochar when applied as a soil amendment. We use seeds of a fast-growing and sensitive crop (e.g. lettuce or radish), and expose them to different concentrations of biochar or biochar-amended soil under controlled laboratory conditions. The seeds are typically placed in Petri dishes containing a moistened filter paper or a mixture of the tested biochar and a growth medium, such as sand or soil. The dishes are then incubated in a growth chamber or greenhouse with controlled temperature and light conditions.

After a predetermined period (usually 3-7 days), the germination rate and the growth of the seedlings (e.g., root and shoot length) are assessed. The results are compared to a control group of seeds exposed to the unamended growth medium or a non-toxic reference material.

If the germination inhibition test indicates that biochar has a negative impact on seed germination or seedling growth, we can potentially undertake further investigations to determine the cause of the phytotoxicity and identify possible mitigation strategies.

Additional Information on Evaluating Biochar for Soil Amendment Applications and Undertaking Plant Growth Trials

Feel free to get in touch with us if you have any questions about our analytical services for assessing the potential for using biochar in soil amendment or for plant growth promotion. We can also provide assistance if you need to screen biochar for potential phytotoxicity issues or to understand how variations in feedstock and/or pyrolysis conditions may affect the value of biochar for soil amendment. Relevant members of the Celignis biochar team will be happy to assist. Those team members with the most experience with undertaking these tests and interpreting the resulting data are listed below.

Sajna KV

Bioanalysis Developer

PhD

<p style="text-align: left;">Our Biomass Detective! Designs, tests, optimizes and validates robust analytical methods for properties of relevance to the various biochar market applications.</p>

Lalitha Gottumukkala

Chief Innovation Officer

PhD

<p style="text-align: left;">A serial innovator managing multiple projects. Has particular expertise related to the upgrading of biochar and on the assessment of its impact on plant productivity and soil health.</p>



Other Celignis Tests and Services for Biochar

Global Recognition as Biomass and Biochar Experts

Celignis provides valued services to over 1000 clients. We understand how the focus of biochar projects can differ between countries and have advised a global network of clients. We also have customs-exemptions for samples sent to us allowing us to quickly get to work no matter where our clients are based.

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Feedstock Evaluation

Our analysis packages can screen biochar feedstocks. We can estimate biochar yield and quality using feedstock chemical composition and can estimate biochar composition using the ultimate and major/minor elements analyses of the feedstock. With TGA analysis we can also monitor feedstock behaviour under pyrolysis conditions.

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Biochar Production

We can produce biochar samples from your feedstocks using a wide range of temperatures, heating rates, and residence times. We can formulate a Design of Experiments (DoE) to study the effects of varying process parameters on biochar yield and quality and can optimise these outputs according to your desired biochar market applications.

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Biochar Analysis

We have an extensive array of analysis packages to evaluate the suitability of biochar for a range of applications. These analyses cover properties relevant to combustion, soil amendment, feed, and biomaterials. Our reports compare the results against internationally-recognised limits for using the biochar in specific end-products.

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Biochar Combustion Properties

Biochar can be a superior fuel versus virgin biomass due to its greater carbon content and energy density. We offer a wide array of analysis packages to fully evaluate biochar as a fuel. For example, we can determine both organic and inorganic carbon and can monitor the behaviour of the biochar ash over wide temperature ranges.

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Analysis of PAHs in Biochar

Polycyclic aromatic hydrocarbons can be formed during the pyrolysis of biomass and accumulate in biochar, leading to potential risks to the environment. We can accurately quantify a range of different PAHs and determine if their concentrations exceed regulatory limits. We can also develop strategies to reduce the amount of PAHs in biochar.

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Surface Area and Porosity of Biochar

The suitable markets for a biochar are often greatly dependent on its surface area and pore size-distrubtion. We provide detailed reports on biochar surface area and porosity and can provide guidance on the implications of the results. We can also work on strategies to increase the surface area and modify the pore-size distribution of biochar.

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Thermogravimetric Analysis of Biochar

TGA is a powerful analytical technique for the study of biochars because it allows us to examine the thermal stability of the material as a function of temperature. The thermal stability of biochars is an important factor to consider when evaluating their potential use as a soil amendment or for carbon sequestration.

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Biochar Upgrading

There are several different methods (covering physical, chemical and biologial routes) by which we can upgrade your biochar in order to increase its value and make it more suitable for the desired market applications. We are able to fully characterise the changes in physicochemical properties associated with upgrading.

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Biochar for Carbon Sequestration

Biochar's efficacy as a means for sequestering carbon depends on a range of factors (e.g. feedstock and pyrolysis conditions). We can undertake a range of analytical tests to help you determine the stability of your biochar's carbon. We can also suggest alternative approaches to improve carbon sequestration potential.

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Technoeconomic Analyses of Biochar Projects

Our TEA experts work with you to evaluate the economic prospects of your biochar facility, considering various scale, technology, and feedstock options. We apply accurate costing models to determine CAPEX/OPEX of simulated and pilot scale processes which are then used to determine key economic indicators (e.g. IRR, NPV).

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Research Project Collaborations

Celignis is active in a number of important research projects focused on biomass valorisation. Biochar is a key component in some of these ongoing projects as well as in several prior projects. We are open to participating in future collaborative research projects where our extensive infrastructure and expertise in biochar can be leveraged.

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Publications on Biochar Digestion By The Celignis Team

Abdeldayem, O.M., Dupont, C., Ferrasa, D. and Kennedyab, M. (2025) An experimental and numerical investigation of secondary char formation in hydrothermal carbonization: revealing morphological changes via hydrodynamics, RSC Advances 15: 12723-12738

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Hydrothermal carbonization (HTC) research has mainly focused on primary char production, with limited attention to secondary char, which is formed through polymerization and condensation of dissolved organic compounds in the liquid phase. This research aims to address this gap via an experimental investigation of the impact of stirring on the mass and carbon balance of HTC reaction products, surface functional groups, and surface morphology of secondary char, using fructose as a model compound. A 3D hydrodynamic simulation model was developed for a two-liter HTC stirred reactor. The experimental results indicated that stirring did not significantly influence the pH, mass, carbon balance, and surface functional groups of secondary char produced under the range of experimental conditions (180 C, 10% biomass to water (B/W) ratio, and a residence time of 0-120 min) studied. Nonetheless, it was observed that a stirring rate of 200 rpm influenced the morphology and shape of the secondary char microspheres, leading to a significant increase in their size i.e., from 1-2 um in unstirred conditions compared with 70 um at a stirring rate of 200 rpm. This increase in size was attributed to the aggregation of microspheres into irregular aggregates at stirring rates > 65 rpm and residence times > 1 h. The hydrodynamic model revealed that high turbulence of Re > 104 and velocities > 0.17 m s-1 correlated with regions of secondary char formation, emphasizing their role in particle aggregation. Particle aggregation is significant above a stirring rate of 65 rpm, which corresponds to the onset of turbulent flow in the reactor. Finally, a mechanism is proposed, based on reactor hydrodynamics under stirred conditions, that explains secondary char deposition on the reactor walls and stirrer.

Kwapinska, M., Sommersacher, P., Kienzl, N., Retschitzegger, S., Lagler, J., Horvat, A. and Leahy, J.J. (2024) Release of N-containing compounds during pyrolysis of milk/dairy processing sludge - Experimental results and comparison of measurement techniques, Journal of Analytical and Applied Pyrolysis 178: 106391

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A dried dairy processing sludge (sludge from wastewater treatment of an effluent from a milk processing plant) was pyrolysed in a single-particle reactor at different temperatures from 400 C to 900 C. NH3 and HCN were measured online and offline by means of FTIR as well as by cumulative sampling in impinger bottles (in 0.05 M H2SO4 and 1 M NaOH, respectively) and analysed by photometric method. NO and NO2 were measured online using a nitric oxide analyser while N2O was measured by FTIR. Nitrogen (N) in the sludge and in the remaining char, char-N, was determined. Moreover, tar content in pyrolysis gas was measured and tar-N was determined. The results with respect to N mass balance closure are discussed. The different measurements techniques are compared. For pyrolysis at 520 and 700 nitrogen in the gas phase was mainly contained as N2 (36 % and 40 % respectively), followed by NH3 (15 % and 18 %), tar-N (10 % and 9 %), HCN (1 % and 3 %), NO (1 %) and NO2 (0.2 %). The dairy processing sludge has very specific properties with organic-N present predominantly as proteins and a high content of inherent Ca. These characteristics affected the distribution of N. The amount of char-N was higher while the amount of tar-N lower than for sewage sludge from literature, at comparable pyrolysis temperature.

Kwapinska, M., Pisano, I. and Leahy, J.J. (2023) Hydrothermal carbonization of milk/dairy processing sludge: Fate of plant nutrients, Journal of Environmental Management 345: 118931

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Dairy processing sludge (DPS) is a byproduct generated in wastewater treatment plants located in dairy (milk) processing companies (waste activated sludge). DPS presents challenges in terms of its management (as biosolids) due to its high moisture content, prolonged storage required, uncontrolled nutrient loss and accumulation of certain substances in soil in the proximity of dairy companies. This study investigates the potential of hydrothermal carbonization (HTC) for recovery of nutrients in the form of solid hydrochar (biochar) produced from DPS originating from four different dairy processing companies. The HTC tests were carried out at 160 C, 180 C, 200 C and 220 C, and a residence time of 1h. The elemental properties of hydrochars (biochars), the content of primary and secondary nutrients, as well as contaminants were examined. The transformation of phosphorus in DPS during HTC was investigated. The fraction of plant available phosphorus was determined. The properties of hydrochar (biochar) were compared against the European Union Fertilizing Products Regulation. The findings of this study demonstrate that the content of nutrient in hydrochars (biochars) meet the requirements for organo-mineral fertilizer with nitrogen and phosphorus as the declared nutrients (13.9-26.7%). Further research on plant growth and field tests are needed to fully assess the agronomic potential of HTC hydrochar (biochar).

Kwapinska, M., Pisano, I. and Leahy, J.J. (2023) Preliminary assessment of pyrolysis biochar derived from milk/dairy processing sludge as a potential component of fertilizers, ACS Sustainable Chemistry & Engineering 11(6): 2345-2353

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Disposal of waste-activated sludge [dairy processing sludge, (DPS)] from wastewater treatment plants located in milk processing companies is an increasing concern. DPS is usually applied to farmlands in the vicinity of the dairy companies. This practice is becoming unsustainable due to uncontrolled nutrient loss and potential soil contamination. We propose to recover nutrients in the form of biochar. This paper examines the properties of biochars obtained from slow pyrolysis of DPS. DPS samples were pyrolyzed at laboratory and pilot scale at 600 and 700 C. The elemental properties of biochars, the content of primary and secondary nutrients, as well as contaminants were examined and compared against the European Union Fertilizing Products Regulation. The biochars meet the specified limits for hydrogen-to-organic carbon ratio, chloride, and polycyclic aromatic hydrocarbons intended for gasification and pyrolysis component category materials. In six out of eight biochars, the content of phosphorus (P) as a single declared nutrient and the level of contaminants meet those required for an organo-mineral fertilizer. Only two biochars meet the required concentrations of nitrogen, phosphorus, and potassium. A minimum solid content of 30% in DPS is required to make the process of biochar production energetically sustainable.

Kwapinska, M., Horvat, A., Agar, D.A. and Leahy, J.J. (2021) Energy recovery through co-pyrolysis of wastewater sludge and forest residues-the transition from laboratory to pilot scale, Journal of Analytical and Applied Pyrolysis 158: 105283

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Anaerobically digested sewage sludge mixed with forest residues was pyrolysed at 800 C, at laboratory and pilot scale. The study quantified differences in char and gas yields for tests carried out in a simple fixed bed laboratory reactor and rotating retort pyrolyser at pilot scale, when the residence time of feedstock was 10 min in both cases. The yield of char from pilot scale was 4 % lower than from laboratory scale while the yield of gas was 15.7 % higher. During the pilot scale pyrolysis of anaerobically digested sewage sludge blended with forest residues the gas quality for energy recovery applications was assessed and the fate of impurities (tar, NH3 and H2S) was investigated. The raw pyrolysis gas contained 14.6 g/Nm3 of tar, 36.9 g/Nm3 of NH3 and 793 ppm of H2S. Sixteen N-containing tar species were identified of which pyridine, propenenitrile, 2-methyl-, benzonitrile, and indole are found to be the most abundant. The yield of N-containing tar compounds accounted for approx. 12 % of total tar content. Conditioned pyrolysis gas contained 7.1 g/Nm3 of tar, 0.036 g/Nm3 of NH3 and 119 ppm of H2S. Benzene was by far the most abundant tar compound followed by toluene and styrene. The specifications of the used internal combustion engine were exceeded due to the sum of tar compounds such as fluorantrene and pyrene with 4+ aromatic rings (at 0.0015 g/Nm3) and NH3 content The effectiveness and sustainability of energy recovery in wastewater treatment can be improved using forest industry by-products.

Kozyatnyk, I., Oesterle, P., Wurzer, C., Masek, O. and Jansson (2021) Removal of contaminants of emerging concern from multicomponent systems using carbon dioxide activated biochar from lignocellulosic feedstock, Bioresource Technology 340: 125561

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Adsorption of six contaminants of emerging concern (CECs) - caffeine, chloramphenicol, carbamazepine, bisphenol A, diclofenac, and triclosan - from a multicomponent solution was studied using activated biochars obtained from three lignocellulosic feedstocks: wheat straw, softwood, and peach stones. Structural parameters related to the porosity and ash content of activated biochar and the hydrophobic properties of the CECs were found to influence the adsorption efficiency. For straw and softwood biochar, activation resulted in a more developed mesoporosity, whereas activation of peach stone biochar increased only the microporosity. The most hydrophilic CECs studied, caffeine and chloramphenicol, displayed the highest adsorption (22.8 and 11.3 mg g-1) onto activated wheat straw biochar which had the highest ash content of the studied adsorbents (20 wt%). Adsorption of bisphenol A and triclosan, both relatively hydrophobic substances, was highest (31.6 and 30.2 mg g-1) onto activated biochar from softwood, which displayed a well-developed mesoporosity and low ash content.

Wurzer, C. and Masek, O. (2021) Feedstock doping using iron rich waste increases the pyrolysis gas yield and adsorption performance of magnetic biochar for emerging contaminants, Bioresource Technology 321: 124473

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Magnetic carbons can significantly lower the costs of wastewater treatment due to easy separation of the adsorbent. However, current production techniques often involve the use of chlorinated or sulfonated Fe precursors with an inherent potential for secondary pollution. In this study, ochre, an iron-rich waste stream was investigated as a sustainable Fe source to produce magnetic activated biochar from two agricultural feedstocks, softwood and wheat straw. Fe doping resulted in significant shifts in pyrolysis yield distribution with increased gas yields (+50%) and gas energy content (+40%) lowering the energy costs for production. Physical activation transformed ochre to magnetite/maghemite resulting in activated magnetic biochars and led to a 4-fold increase in the adsorption capacities for two common micropollutants - caffeine and fluconazole. The results show that Fe doping not only benefits the adsorbent properties but also the production process, leading the way to sustainable carbon adsorbents.

Kwapinska, M., Horvat, A., Liu, Y. and Leahy, J.J. (2020) Pilot scale pyrolysis of activated sludge waste from milk processing factory, Waste and Biomass Valorization 11(6): 2887-2903

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The majority of the sludge from the treatment of wastewater in milk processing plants is land spread. The drawbacks of land spreading include local oversupply due to high transport costs, which results in sludge being spread on lands in the vicinity of the dairy factories. Local oversupply can lead to accumulation of certain substances in soil through annual application over many years. Therefore, in the long term, there is a need for alternative methods to recover energy and nutrients from increasing volumes of sludge generated from dairy processing. Pyrolysis offers a potential alternative to land spreading, which can reduce health and environmental risks, while providing an avenue for the recovery of energy and nutrients. Pyrolysis allows energy recovery in the form of a high calorific value pyrolysis gas and a char which may be used as a soil amendment. In this study pyrolysis of dried dairy sludge was carried out at pilot scale. The results indicate that a dried biological sludge can be successfully pyrolysed and when mixed with wood the resulting char meets European Biochar Certificate criteria regarding carbon content. Most of the initial energy content of the feedstock was retained in the pyrolysis gas prior to cleaning, 53%, compared to 34.5% in the char and 1.5% in the tar. For the pyrolysis gas after cleaning (mainly cracking in presence of air) the initial energy content of the feedstock retained in the gas was only slightly higher than that retained in the char, 39.2% versus 34.5%, while the tar accounted for 0.8% of the initial energy content.

Rockwood, D.L., Ellis, M.F., Liu, R., Zhao, F., Ji, P., Zhu, Z., Fabbro, K.W., He, Z. and Cave, R.D. (2019) Short rotation eucalypts: opportunities for biochar, Forests 10(4): 314

Link

Eucalypts can be very productive when intensively grown as short rotation woody crops (SRWC) for bioproducts. In Florida, USA, a fertilized, herbicided, and irrigated cultivar planted at 2471 trees/ha could produce over 58 green mt/ha/year in 3.7 years, and at 2071 trees/ha, its net present value (NPV) exceeded $750/ha at a 6% discount rate and stumpage price of $11.02/green mt. The same cultivar grown less intensively at three planting densities had the highest stand basal area at the highest density through 41 months, although individual tree diameter at breast height (DBH) was the smallest. In combination with an organic fertilizer, biochar improved soil properties, tree leaf nutrients, and tree growth within 11 months of application. Biochar produced from Eucalyptus and other species is a useful soil amendment that, especially in combination with an organic fertilizer, could improve soil physical and chemical properties and increase nutrient availability to enhance Eucalyptus tree nutrition and growth on soils. Eucalypts produce numerous naturally occurring bioproducts and are suitable feedstocks for many other biochemically or thermochemically derived bioproducts that could enhance the value of SRWCs.



Publications on Biochar By The Celignis Team

Abdeldayem, O.M., Dupont, C., Ferrasa, D. and Kennedyab, M. (2025) An experimental and numerical investigation of secondary char formation in hydrothermal carbonization: revealing morphological changes via hydrodynamics, RSC Advances 15: 12723-12738

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Hydrothermal carbonization (HTC) research has mainly focused on primary char production, with limited attention to secondary char, which is formed through polymerization and condensation of dissolved organic compounds in the liquid phase. This research aims to address this gap via an experimental investigation of the impact of stirring on the mass and carbon balance of HTC reaction products, surface functional groups, and surface morphology of secondary char, using fructose as a model compound. A 3D hydrodynamic simulation model was developed for a two-liter HTC stirred reactor. The experimental results indicated that stirring did not significantly influence the pH, mass, carbon balance, and surface functional groups of secondary char produced under the range of experimental conditions (180 C, 10% biomass to water (B/W) ratio, and a residence time of 0-120 min) studied. Nonetheless, it was observed that a stirring rate of 200 rpm influenced the morphology and shape of the secondary char microspheres, leading to a significant increase in their size i.e., from 1-2 um in unstirred conditions compared with 70 um at a stirring rate of 200 rpm. This increase in size was attributed to the aggregation of microspheres into irregular aggregates at stirring rates > 65 rpm and residence times > 1 h. The hydrodynamic model revealed that high turbulence of Re > 104 and velocities > 0.17 m s-1 correlated with regions of secondary char formation, emphasizing their role in particle aggregation. Particle aggregation is significant above a stirring rate of 65 rpm, which corresponds to the onset of turbulent flow in the reactor. Finally, a mechanism is proposed, based on reactor hydrodynamics under stirred conditions, that explains secondary char deposition on the reactor walls and stirrer.

Kwapinska, M., Sommersacher, P., Kienzl, N., Retschitzegger, S., Lagler, J., Horvat, A. and Leahy, J.J. (2024) Release of N-containing compounds during pyrolysis of milk/dairy processing sludge - Experimental results and comparison of measurement techniques, Journal of Analytical and Applied Pyrolysis 178: 106391

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A dried dairy processing sludge (sludge from wastewater treatment of an effluent from a milk processing plant) was pyrolysed in a single-particle reactor at different temperatures from 400 C to 900 C. NH3 and HCN were measured online and offline by means of FTIR as well as by cumulative sampling in impinger bottles (in 0.05 M H2SO4 and 1 M NaOH, respectively) and analysed by photometric method. NO and NO2 were measured online using a nitric oxide analyser while N2O was measured by FTIR. Nitrogen (N) in the sludge and in the remaining char, char-N, was determined. Moreover, tar content in pyrolysis gas was measured and tar-N was determined. The results with respect to N mass balance closure are discussed. The different measurements techniques are compared. For pyrolysis at 520 and 700 nitrogen in the gas phase was mainly contained as N2 (36 % and 40 % respectively), followed by NH3 (15 % and 18 %), tar-N (10 % and 9 %), HCN (1 % and 3 %), NO (1 %) and NO2 (0.2 %). The dairy processing sludge has very specific properties with organic-N present predominantly as proteins and a high content of inherent Ca. These characteristics affected the distribution of N. The amount of char-N was higher while the amount of tar-N lower than for sewage sludge from literature, at comparable pyrolysis temperature.

Kwapinska, M., Pisano, I. and Leahy, J.J. (2023) Hydrothermal carbonization of milk/dairy processing sludge: Fate of plant nutrients, Journal of Environmental Management 345: 118931

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Dairy processing sludge (DPS) is a byproduct generated in wastewater treatment plants located in dairy (milk) processing companies (waste activated sludge). DPS presents challenges in terms of its management (as biosolids) due to its high moisture content, prolonged storage required, uncontrolled nutrient loss and accumulation of certain substances in soil in the proximity of dairy companies. This study investigates the potential of hydrothermal carbonization (HTC) for recovery of nutrients in the form of solid hydrochar (biochar) produced from DPS originating from four different dairy processing companies. The HTC tests were carried out at 160 C, 180 C, 200 C and 220 C, and a residence time of 1h. The elemental properties of hydrochars (biochars), the content of primary and secondary nutrients, as well as contaminants were examined. The transformation of phosphorus in DPS during HTC was investigated. The fraction of plant available phosphorus was determined. The properties of hydrochar (biochar) were compared against the European Union Fertilizing Products Regulation. The findings of this study demonstrate that the content of nutrient in hydrochars (biochars) meet the requirements for organo-mineral fertilizer with nitrogen and phosphorus as the declared nutrients (13.9-26.7%). Further research on plant growth and field tests are needed to fully assess the agronomic potential of HTC hydrochar (biochar).

Kwapinska, M., Pisano, I. and Leahy, J.J. (2023) Preliminary assessment of pyrolysis biochar derived from milk/dairy processing sludge as a potential component of fertilizers, ACS Sustainable Chemistry & Engineering 11(6): 2345-2353

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Disposal of waste-activated sludge [dairy processing sludge, (DPS)] from wastewater treatment plants located in milk processing companies is an increasing concern. DPS is usually applied to farmlands in the vicinity of the dairy companies. This practice is becoming unsustainable due to uncontrolled nutrient loss and potential soil contamination. We propose to recover nutrients in the form of biochar. This paper examines the properties of biochars obtained from slow pyrolysis of DPS. DPS samples were pyrolyzed at laboratory and pilot scale at 600 and 700 C. The elemental properties of biochars, the content of primary and secondary nutrients, as well as contaminants were examined and compared against the European Union Fertilizing Products Regulation. The biochars meet the specified limits for hydrogen-to-organic carbon ratio, chloride, and polycyclic aromatic hydrocarbons intended for gasification and pyrolysis component category materials. In six out of eight biochars, the content of phosphorus (P) as a single declared nutrient and the level of contaminants meet those required for an organo-mineral fertilizer. Only two biochars meet the required concentrations of nitrogen, phosphorus, and potassium. A minimum solid content of 30% in DPS is required to make the process of biochar production energetically sustainable.

Kwapinska, M., Horvat, A., Agar, D.A. and Leahy, J.J. (2021) Energy recovery through co-pyrolysis of wastewater sludge and forest residues-the transition from laboratory to pilot scale, Journal of Analytical and Applied Pyrolysis 158: 105283

Link

Anaerobically digested sewage sludge mixed with forest residues was pyrolysed at 800 C, at laboratory and pilot scale. The study quantified differences in char and gas yields for tests carried out in a simple fixed bed laboratory reactor and rotating retort pyrolyser at pilot scale, when the residence time of feedstock was 10 min in both cases. The yield of char from pilot scale was 4 % lower than from laboratory scale while the yield of gas was 15.7 % higher. During the pilot scale pyrolysis of anaerobically digested sewage sludge blended with forest residues the gas quality for energy recovery applications was assessed and the fate of impurities (tar, NH3 and H2S) was investigated. The raw pyrolysis gas contained 14.6 g/Nm3 of tar, 36.9 g/Nm3 of NH3 and 793 ppm of H2S. Sixteen N-containing tar species were identified of which pyridine, propenenitrile, 2-methyl-, benzonitrile, and indole are found to be the most abundant. The yield of N-containing tar compounds accounted for approx. 12 % of total tar content. Conditioned pyrolysis gas contained 7.1 g/Nm3 of tar, 0.036 g/Nm3 of NH3 and 119 ppm of H2S. Benzene was by far the most abundant tar compound followed by toluene and styrene. The specifications of the used internal combustion engine were exceeded due to the sum of tar compounds such as fluorantrene and pyrene with 4+ aromatic rings (at 0.0015 g/Nm3) and NH3 content The effectiveness and sustainability of energy recovery in wastewater treatment can be improved using forest industry by-products.

Kozyatnyk, I., Oesterle, P., Wurzer, C., Masek, O. and Jansson (2021) Removal of contaminants of emerging concern from multicomponent systems using carbon dioxide activated biochar from lignocellulosic feedstock, Bioresource Technology 340: 125561

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Adsorption of six contaminants of emerging concern (CECs) - caffeine, chloramphenicol, carbamazepine, bisphenol A, diclofenac, and triclosan - from a multicomponent solution was studied using activated biochars obtained from three lignocellulosic feedstocks: wheat straw, softwood, and peach stones. Structural parameters related to the porosity and ash content of activated biochar and the hydrophobic properties of the CECs were found to influence the adsorption efficiency. For straw and softwood biochar, activation resulted in a more developed mesoporosity, whereas activation of peach stone biochar increased only the microporosity. The most hydrophilic CECs studied, caffeine and chloramphenicol, displayed the highest adsorption (22.8 and 11.3 mg g-1) onto activated wheat straw biochar which had the highest ash content of the studied adsorbents (20 wt%). Adsorption of bisphenol A and triclosan, both relatively hydrophobic substances, was highest (31.6 and 30.2 mg g-1) onto activated biochar from softwood, which displayed a well-developed mesoporosity and low ash content.

Wurzer, C. and Masek, O. (2021) Feedstock doping using iron rich waste increases the pyrolysis gas yield and adsorption performance of magnetic biochar for emerging contaminants, Bioresource Technology 321: 124473

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Magnetic carbons can significantly lower the costs of wastewater treatment due to easy separation of the adsorbent. However, current production techniques often involve the use of chlorinated or sulfonated Fe precursors with an inherent potential for secondary pollution. In this study, ochre, an iron-rich waste stream was investigated as a sustainable Fe source to produce magnetic activated biochar from two agricultural feedstocks, softwood and wheat straw. Fe doping resulted in significant shifts in pyrolysis yield distribution with increased gas yields (+50%) and gas energy content (+40%) lowering the energy costs for production. Physical activation transformed ochre to magnetite/maghemite resulting in activated magnetic biochars and led to a 4-fold increase in the adsorption capacities for two common micropollutants - caffeine and fluconazole. The results show that Fe doping not only benefits the adsorbent properties but also the production process, leading the way to sustainable carbon adsorbents.

Kwapinska, M., Horvat, A., Liu, Y. and Leahy, J.J. (2020) Pilot scale pyrolysis of activated sludge waste from milk processing factory, Waste and Biomass Valorization 11(6): 2887-2903

Link

The majority of the sludge from the treatment of wastewater in milk processing plants is land spread. The drawbacks of land spreading include local oversupply due to high transport costs, which results in sludge being spread on lands in the vicinity of the dairy factories. Local oversupply can lead to accumulation of certain substances in soil through annual application over many years. Therefore, in the long term, there is a need for alternative methods to recover energy and nutrients from increasing volumes of sludge generated from dairy processing. Pyrolysis offers a potential alternative to land spreading, which can reduce health and environmental risks, while providing an avenue for the recovery of energy and nutrients. Pyrolysis allows energy recovery in the form of a high calorific value pyrolysis gas and a char which may be used as a soil amendment. In this study pyrolysis of dried dairy sludge was carried out at pilot scale. The results indicate that a dried biological sludge can be successfully pyrolysed and when mixed with wood the resulting char meets European Biochar Certificate criteria regarding carbon content. Most of the initial energy content of the feedstock was retained in the pyrolysis gas prior to cleaning, 53%, compared to 34.5% in the char and 1.5% in the tar. For the pyrolysis gas after cleaning (mainly cracking in presence of air) the initial energy content of the feedstock retained in the gas was only slightly higher than that retained in the char, 39.2% versus 34.5%, while the tar accounted for 0.8% of the initial energy content.

Rockwood, D.L., Ellis, M.F., Liu, R., Zhao, F., Ji, P., Zhu, Z., Fabbro, K.W., He, Z. and Cave, R.D. (2019) Short rotation eucalypts: opportunities for biochar, Forests 10(4): 314

Link

Eucalypts can be very productive when intensively grown as short rotation woody crops (SRWC) for bioproducts. In Florida, USA, a fertilized, herbicided, and irrigated cultivar planted at 2471 trees/ha could produce over 58 green mt/ha/year in 3.7 years, and at 2071 trees/ha, its net present value (NPV) exceeded $750/ha at a 6% discount rate and stumpage price of $11.02/green mt. The same cultivar grown less intensively at three planting densities had the highest stand basal area at the highest density through 41 months, although individual tree diameter at breast height (DBH) was the smallest. In combination with an organic fertilizer, biochar improved soil properties, tree leaf nutrients, and tree growth within 11 months of application. Biochar produced from Eucalyptus and other species is a useful soil amendment that, especially in combination with an organic fertilizer, could improve soil physical and chemical properties and increase nutrient availability to enhance Eucalyptus tree nutrition and growth on soils. Eucalypts produce numerous naturally occurring bioproducts and are suitable feedstocks for many other biochemically or thermochemically derived bioproducts that could enhance the value of SRWCs.



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