Source: UNIVERSITY OF CALIFORNIA, DAVIS submitted to NRP
DEVELOPMENT OF NOVEL APPLICATIONS OF ANIMAL WASTES AND BIOCHAR FOR NUTRIENT CAPTURE AND SUBSEQUENT FERTILIZER VALUE
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1012284
Grant No.
2017-67019-26334
Cumulative Award Amt.
$499,800.00
Proposal No.
2016-08693
Multistate No.
(N/A)
Project Start Date
Mar 15, 2017
Project End Date
Mar 14, 2021
Grant Year
2017
Program Code
[A1401]- Foundational Program: Soil Health
Recipient Organization
UNIVERSITY OF CALIFORNIA, DAVIS
410 MRAK HALL
DAVIS,CA 95616-8671
Performing Department
College of Ag & Env Sci
Non Technical Summary
Animal wastes are a potential source of valuable nutrients, but pose environmental problems when disposed or used improperly. Nutrient pollution has serious environmental consequences, ranging from water quality degradation, to ecosystem disruption, to loss of recreational value of water bodies. Recycling strategies for P and N in organic wastes are clearly under-researched. The pressing need for sustainable nutrient management in agriculture continues to be driven by increasing population growth and energy consumption associated with fertilizer production and use. It is therefore imperative to develop enhanced management strategies to optimize waste recycling and nutrient use efficiency. We propose to investigate the use of biochar to address the aforementioned issues related to sustainable recycling of nutrients within animal wastes. We will conduct research to help mitigate N and P leakage from agricultural soils. More specifically we will compost manures with biochars selectively tailored for enhanced nutrient use efficiency. The biochars will store N and P (and phosphatases) in manure in forms that will be bioavailable later to crop plants.
Animal Health Component
15%
Research Effort Categories
Basic
85%
Applied
15%
Developmental
0%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1020110200060%
1025210200040%
Knowledge Area
102 - Soil, Plant, Water, Nutrient Relationships;

Subject Of Investigation
0110 - Soil; 5210 - Fertilizers;

Field Of Science
2000 - Chemistry;
Goals / Objectives
Co-composting of animal wastes with biochar is proposed as a new and transformative way to utilize the nutrients within animal manures to reduce nutrient leakage and provide agronomic benefits through improved nitrogen and phosphorus use efficiency in crop production. Although biochar has shown potential to improve soil fertility, its benefits are often inconsistent and unimpressive. Through the unique on-farm management approach of composting tailored biochars with animal wastes, we hypothesize that specific alterations in biochar physical and chemical properties can provide novel materials for use in co-composting with animal manures to retain bioavailable nutrients. Therefore, the objectives are to 1) tailor biochars for enhanced capacity and affinity for orthophosphate, ammonium, nitrate, and phytate by various novel means encompassing cation exchange, anion exchange, hydrogen bonding, and metal coordination; 2) develop biochar-supported phosphatase catalysts (phytase) to convert org-P to PO4-P; 3) test tailored biochar mixtures for efficacy in nutrient retention and stabilization through co-composting with dairy and chicken manures; and 4) evaluate nutrient use efficiency of co-composted biochar amendments on plant growth and nutrition.
Project Methods
Preparation of raw biochars. Pyrolysis of feedstocks will be carried out in a programmable vacuum chamber furnace of 7600 cm3 capacity (VBF-1200X-H8; MTI Corp.). The furnace employs a ramping rate of 25 oC/min and can be set to any heat treatment temperature (HTT) up to 1100 oC, verifiable with a thermocouple insert. Select gases can be passed through ports to maintain constant headspace composition. Post pyrolysis air oxidation (PPAO) is performed simply by reheating the biochar in air at 400 oC in an oven. A small loss of solid is expected due to volatilization of carbon as CO2.Characterization of biochars. Biochars will be routinely analyzed with respect to elemental composition (C, H, N, and O), ash, volatile C (ASTM method D5142), cation exchange capacity (CEC, ammonium acetate method at pH 7, and pH. Surface area, pore size distribution, pore volume distribution and total pore volume will be determined on outgassed samples (200 oC) by combined methods of N2 and CO2 high-resolution gas poroisimetry at 77 K and 273 K, respectively, on a Quantachrome Autosorb-1 gas analyzer using built-in software with Brunaur-Emmett-Teller, non-local density functional theory, and Grand Canonical Monte Carlo Density Functional Theory models.Incorporating magnesium. Mg will be introduced pre-pyrolysis by soaking the biomass feedstock with Mg2+ acetate salt. Specifically, the feedstock material will be suspended in, or uniformly sprayed with, an aqueous solution of Mg(OAc)2, allowed to equilibrate for 24 h, and then air dried. Enriching feedstock plants such as tomatoes with Mg2+ during growth is another possible approach, but we consider it highly impractical.Grafting. Citrate is covalently grafted using the carbodiimide dehydration agent 1-ethyl-3-[3-dimethylaminopropyl]carbodiimide in neutral aqueous solution. The carbodiimide is added to a suspension of the biochar and mixed for 2 h. Then citrate is introduced and the reaction is allowed to proceed overnight. The product is collected and rinsed thoroughly with water. PolyDADMAC is non-covalently grafted simply by suspending the biochar in polyDADMAC chloride salt dissolved in water, equilibrating for 24 h, recovering the solid by filtration, and finally washing the solid with clean water.Supported phytase catalysts. Phytase (6-phytase; EC 3.1.3.26) will be purchased (Sigma Aldrich) and baseline characterizations will be performed in the free state (i.e., in solution) to provide a comparison of the effects of biochar and compost interactions, using the same buffer as will be used for the latter experiments. These characterizations include Km, Vmax, pH optima, and isoelectric point (pI) and are requisite for investigations of enzymes. To graft phytase, the biochar is suspended in 0.1 M sodium acetate buffer, pH 4.5, and the carbodiimide is added to the slurry and mixed for 20 min at room temperature. The slurry is washed repeatedly with cold 0.1 M sodium phosphate buffer, pH 7.0. Then an enzyme solution is added to the activated biochar and mixed gently for 24-48 h at 4 oC. The immobilized enzyme is then washed thoroughly with 0.1 M sodium phosphate buffer at pH 7.0 to remove any unattached enzyme and urea byproduct of the carbodiimide reagent.Co-compositing of biochar and animal manuresComposting of biochars with animal manures (dairy, chicken) will follow two approaches. Initially, composting in small batches will be conducted at 50 °C following standard methods.Nutrient and phytase retention by tailored biocharsThe sorption of soil nutrients and phytase to the tailored biochars will be examined via a series of batch sorption studies. These experiments will determine the affinity of NO3-, NH4+, PO4-P, phytate, and phytase for biochar before and after tailoring via surface chemistry modifications. Batch experiments will be performed in 10 mM NaCl at pH 7 (20° C) for 48h with end-over-end shaking (8 rpm). Phytase activity in biochar and compostTo determine binding effects on phytase activity, potential activity assays of free and immobilized phytase will be measured colorimetrically by the p-nitrophenol (pNP) method [78] to calculate enzyme activity constants (Km) and maximum activities (Vmax) (Michaelis-Menten). As a second measure of enzyme activity, mineralization assays, will also be performed using pure compounds (phytate, inositol phosphate, phosphatidyl choline) and mixtures (soil NaOH-extractable Porg). Enzymatic mineralization to produce orthophosphate P (PO43-) will be quantified by molybdate colorimetry modified to increase sensitivity to enzymatic Porg hydrolysis.Greenhouse BioassaysWith the greenhouse bioassay we aim to meticulously investigate the effect of using tailored biochar soil amendments (including co-composted) on plant growth, soil nutrient retention and leaching, and soil-biochar complexes under controlled conditions. The experimental design consists of pots arranged in a complete randomized block design. Treatments use three soil types and two sets of unreacted and modified co-composted biochars selected based on nutrient retention results of the tailored biochars. Composted biochar will be added at 3% w/w to pots and soils wetted to field capacity using deionized water will then be packed into pots w. A crop rotation of lettuce and tomato will be grown in the pots that will be watered to maintain water content at field capacity. Leachate samples will be collected weekly via a tap system installed at pot bottoms and be analyzed for C, NO3, NH4, P, K, Mg, Ca, pH, and EC. For all pots, once the crops reach a harvestable stage, wet and dry yield measurements will be obtained.Analytical Methods for N, P, C, and other ElementsInorganic N species will be extracted from soil, biochar, and compost samples with 2 mol L-1 KCl (solution to solid ratio 5:1) and analyzed colorimetrically on a spectrophotometer (Thermo Genesys 10s UV-Vis). Nitrate is analyzed using a single reagent that reduces nitrate to nitrite which is complexed by sulfanilamide. Further reaction with N-(1-naphthyl)-ethylenediamine produces a red dye that is quantified colorimetrically at 540 nm. The NH4+ concentration will be determined by the salicylate method. This method is based on the Berthelot reaction in which ammonium reacts with phenol and hypochlorite to form a green indophenol compound whose concentration is determined colorimetrically at 650 nm. Phosphorus from solid samples will follow the sequential extraction scheme. Following these standard extraction procedures aliquots are neutralized and analyzed for inorganic P (Pi) and total P (Pt). Pi is determined by molybdate colorimetry at 880 nm, Pt is determined by the same procedure following acid -persulfate digestion (80 °C, 16 hr), and Organic P (Po) is estimated as the difference between total and inorganic P (Po = Pt - Pi). Total P will also be estimated independently of the Hedley fractionation by ashing (550 °C, 1 hr) followed by acid extraction (1 mol L-1 H2SO4, 1:50 soil:extractant, 16 hr) and molybdate colorimetry to determine total P as Pi. Total C and N of solid (e.g., soil, compost) samples will be determined by the dry combustion method. Subsamples are finely ground in a ball mill and weighed into tin cups. Total C and N will be analyzed using a Costech analyzer (Costec Inc., Lake Zurich, IL). DOC analysis will be carried on a Total Organic Carbon Analyzer (TOC-V CSH. Analysis of other relevant ions and metals will be determined via ion chromatography (IC; Dionex ICS-200) and atomic absorption spectroscopy (AA; Perkin Elmer AAnlyst 800).

Progress 03/15/17 to 03/14/21

Outputs
Target Audience:During this project period, our research was presented numerous times at scientific conferences where the audience composed of primarily of scientists. The efforts of this research have also been shared with numerous stakeholder groups, such as the California Almond Board and the California Governors Office of Planning and Research. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?This project has been critical for the training of seven postdoctoral scholars who have conducted the majority of this research. Their responsibilities have included assisting in experimental design, execution of experiments, and data analysis. The postdoctoral scholars have been working with the project PIs to ensure these research activities are appropriately carried out. How have the results been disseminated to communities of interest?The activities and results of this reporting period have been shared at least five times at conferences,seminars, or directly to stakeholder groups. One research paper was published in Water Research and another has been submitted to Science of the Total Environment. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? The primary objectives of this project have been completed. The Parikh lab completed its studies examining the potential of biochars to immobilize phystase. The results show that enzyme loading to biochars creates strong bonds which drastically reduce the activity of the enzyme. While this does not rule out the use of this method for adding enzymes for P mineralization, it does suggest that it may only be useful as a long-term and slow-release strategy. Overall it was determined that: 1) different biochars had different enzyme loading capacities and generally a higher pyrolysis temperature led to a larger loading capacity; 2) physical adsorption was the main immobilization mechanism, instead of covalent bonding, and specific forces include the electrostatic forces and hydrophobic effects; 3) reversibility tests showed that less than 4% of the immobilized phytase leached from biochar surface after a 7-d sequential extraction; 4) the activity of immobilized phytase markedly decreased compare to the free state phytase as the former only showed <1% activity compared to the latter. Modified biochars were co-composted with poultry litter and dairy manure to create a stable biochar-compost product with high retention of phosphate and nitrates. The composting process was successful and high-quality compost was made. Experiments were then conducted growing lettuce, fertilized with these composts. The data demonstrate that co-composting the modified biochars with animal manures lead to increased lettuce growth and nutrient levels. The Pignatello group successfully developed methods to increased the anion exchange capacity (AEC) or biochars, aiming to extract anionic nutrients, such as phosphate and nitrate, from animal waste leachate. Biochar materials derived from two wood species, pine and maple, were generated via programmed heating processes. To enhance the AEC of biochars, two strategies, including coating the raw biochar with poly (dimethyldiallyl ammonium chloride) (polyDADMAC) and integrating magnesium ions (Mg2+) to biomass feedstock (i.e., the wood) to obtain Mg-doped biochars. Isotherms of multiple biochar samples adsorbing orthophosphate (PO43-) demonstrate that both polyDADMAC-coated and Mg-doped biochars show enhanced PO43- adsorption capability compared to non-treated biochars. At environmentally relevant concentrations, PO4-P sorption at final pHs 7.6-7.8 by the pDADMAC-treated PCMs was more than 100 times greater than that of the corresponding unmodified PCMs. PO4-P sorption by the pDADMAC-treated biochars was further enhanced by post-pyrolysis hot air oxidation of the raw biochars, which enlarges pores and introduces acidic groups that can act as additional anchoring sites for pDADMAC strands. Sorption to the pDADMAC-treated softwood and maple biochars is comparable with sorption to the corresponding Mg-doped biochars . The pDADMAC-coated carbons bind PO4-P principally by ion exchange, while the Mg-doped biochars bind PO4-P principally by complexation with Mg. Susceptibility to competition from other relevant anions (Cl-, NO3-, HCO3-/CO32-, SO42-) and extracts of poultry or dairy manure was of a similar magnitude for the two types of modified softwood biochars. Sorption to the pDADMAC-treated biochars appears to be more reversible than to the Mg-doped biochars using stepwise extraction with 18.2 MΩ?cm water. pDADMAC-treated biochars show some advantages for use in trapping and recycling phosphate from animal wastes.

Publications

  • Type: Journal Articles Status: Published Year Published: 2020 Citation: Zhang, M., G. Song, D.L. Gelardi, L. Huang, E. Khan, O. Maaek, S.J. Parikh, Y.S. Ok. 2020.Evaluating biochar and its modifications for the removal of ammonium, nitrate, and phosphate in water. Water Research. 186:116303.
  • Type: Journal Articles Status: Submitted Year Published: 2020 Citation: Li, C Z. Wang, S. Bakshi, N. Pignatello, S.J. Parikh. Evaluation of select biochars and clays as supports for phytase to increase the fertilizer potential of animal wastes. Science of the Total Environment.


Progress 03/15/19 to 03/14/20

Outputs
Target Audience:During the current reporting period our research was presented numerous times at scientific conferences where the audience composed of primarily of scientists. The efforts of this research have also been shared with numerous stakeholder groups, such as the California Almond Board and the California Governors Office of Planning and Research. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?This project has been critical for the training of six postdoctoral scholars who have conducted the majority of this research. Their responsibilities have included assisting in experimental design, execution of experiments, and data analysis. The postdoctoral scholars have been working with the project PIs to ensure these research activities are appropriately carried out. How have the results been disseminated to communities of interest?The activities and results of this reporting period have been shared at least five times at conferences,seminars, or directly to stakeholder groups. What do you plan to do during the next reporting period to accomplish the goals?In the coming year we will complete the analysis of the plant growth experiments and do a complete analysis of all the data. A draft of the enzyme work is near complete and will be submitted for publication soon. From the continued analysis we aim to write and submit an addition two papers in the next year.

Impacts
What was accomplished under these goals? The Parikh lab completed its studies examining the potential of biochars to immobilize phystase. The results show that enzyme loading to biochars creates strong bonds which drastically reduce the activity of the enzyme. While this does not rule out the use of this method for adding enzymes for P mineralization, it does suggest that it may only be useful as a long-term and slow-release strategy. Overall it was determined that: 1) different biochars had different enzyme loading capacities and generally a higher pyrolysis temperature led to a larger loading capacity; 2) physical adsorption was the main immobilization mechanism, instead of covalent bonding, and specific forces include the electrostatic forces and hydrophobic effects; 3) reversibility tests showed that less than 4% of the immobilized phytase leached from biochar surface after a 7-d sequential extraction; 4) the activity of immobilized phytase markedly decreased compare to the free state phytase as the former only showed <1% activity compared to the latter. Modified biochars (provided by the Pignatello) group were co-composted with poultry litter and dairy manure to create a stable biochar-compost product with high retention of phosphate and nitrates. The composting process was successful and high quality compost was made. Experiments were then conducted growing lettuce, fertilized with these composts. Preliminary data reveal that the modified biochars provided more favorable conditions for plant growh. The Pignatello group has completed most of its work to improve the anion exchange capacity (AEC), aiming to extract anionic nutrients, such as phosphate and nitrate, from animal waste leachate. Biochar materials derived from two wood species, pine and maple, were generated via programmed heating processes. To enhance the AEC of biochars, two strategies, including coating the raw biochar with poly (dimethyldiallyl ammonium chloride) (polyDADMAC) and integrating magnesium ions (Mg2+) to biomass feedstock (i.e., the wood) to obtain Mg-doped biochars. Isotherms of multiple biochar samples adsorbing orthophosphate (PO43-) demonstrate that both polyDADMAC-coated and Mg-doped biochars show enhanced PO43- adsorption capability compared to non-treated biochars. At environmentally relevant concentrations, PO4-P sorption at final pHs 7.6-7.8 by the pDADMAC-treated PCMs was more than 100 times greater than that of the corresponding unmodified PCMs. PO4-P sorption by the pDADMAC-treated biochars was further enhanced by post-pyrolysis hot air oxidation of the raw biochars, which enlarges pores and introduces acidic groups that can act as additional anchoring sites for pDADMAC strands. Sorption to the pDADMAC-treated softwood and maple biochars is comparable with sorption to the corresponding Mg-doped biochars . The pDADMAC-coated carbons bind PO4-P principally by ion exchange, while the Mg-doped biochars bind PO4-P principally by complexation with Mg. Susceptibility to competition from other relevant anions (Cl-, NO3-, HCO3-/CO32-, SO42-) and extracts of poultry or dairy manure was of a similar magnitude for the two types of modified softwood biochars. Sorption to the pDADMAC-treated biochars appears to be more reversible than to the Mg-doped biochars using stepwise extraction with 18.2 MΩ?cm water. pDADMAC-treated biochars show some advantages for use in trapping and recycling phosphate from animal wastes.

Publications

  • Type: Conference Papers and Presentations Status: Published Year Published: 2019 Citation: Keynote lecture, J.J. Pignatello Interactions of organic compounds with pyrogenic carbonaceous materials of importance in agriculture and environmental management, at the International Workshop on Organic Pollutants in Agro-Environments (IWOPAE), at Nanjing Agricultural University, China, October 12-15, 2019.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2019 Citation: J.J. Pignatello, Yi Yang, Santanu Bakshi, Zhengyang Wang, Jingjing Yang, Hsin-se Hsieh, Feng Xiao, Some ways to modify chars for enhanced binding of certain organic and inorganic contaminants at the Soil Science Society Meeting in San Antonio, TX, November 10-13, 2019.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2019 Citation: Keynote lecture, J.J. Pignatello  Some properties of wood-derived chars important for their interactions with organic compounds, at the 11th International Symposium on Environmental Geochemistry at Peking University, Beijing, China, August 7-10, 2019.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2019 Citation: Parikh, S.J. Evaluating biochar for agriculture and environmental applications. China Agricultural University. September 9, 2019 (Invited).
  • Type: Conference Papers and Presentations Status: Other Year Published: 2019 Citation: Parikh, S.J. Adventures in biochar! Departmental Seminar, UC Merced. April 4, 2019 (Invited).
  • Type: Journal Articles Status: Submitted Year Published: 2020 Citation: Wang, Z., S. Bakshi, C. Li, S.J. Parikh, H.Hsieh, and J.J. Pignatello. 2019. Modification of pyrogenic carbonaceous materials for phosphate sorption through binding of a cationic polymer.


Progress 03/15/18 to 03/14/19

Outputs
Target Audience:During the current reporting period our research was presented numerous times at scientific conferences where the audience composed of primarily of scientists. The efforts of this research have also been shared with numerous stakeholder groups, such as the California Almond Board and the California Governors Office of Planning and Research. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?This project has been critical for the training of three postdoctoral scholars who have conducted the majority of this research. Their responsibilities have included assisting in experimental design, execution of experiments, and data analysis. The postdoctoral scholars have been working with the project PIs to ensure these research activities are appropriately carried out. How have the results been disseminated to communities of interest?The activities and results of this reporting period have been shared at least eight times at conferences,seminars, or directly to stakeholder groups - such as the Almond Board of California and the California Governors Office of Planning and Research. What do you plan to do during the next reporting period to accomplish the goals?In the coming year we will: 1) refine our approach for increasing nitrate and phosphate retention on biochar surfaces; 2) determine the long-term activity of phosphatase enzymes bound to biochrs; 3) complete the writing of two manuscripts and submit them for publication in peer-reviewed journals; 4) test tailored biochar mixtures for efficacy in nutrient retention and utilization after co-composting with dairy and chicken manures; and 5) evaluate nutrient use efficiency of the co-composted biochar manure mixtures on plant growth.

Impacts
What was accomplished under these goals? The Parikh lab focused on immobilizing phytase, which mineralizes a main class of organic phosphorus, onto nine different biochars as an enzyme preservation mechanism. Both covalent grafting and physical sorption were used as the immobilization methods and conditions were optimized to maximize the enzyme loading capacity and enzyme activity while minimize the leaching of enzymes. It is found that: 1) different biochars had different enzyme loading capacities and generally a higher pyrolysis temperature led to a larger loading capacity; 2) physical adsorption was the main immobilization mechanism, instead of covalent bonding, and specific forces include the electrostatic forces and hydrophobic effects; 3) reversibility tests showed that less than 4% of the immobilized phytase leached from biochar surface after a 7-d sequential extraction; 4) the activity of immobilized phytase markedly decreased compare to the free state phytase as the former only showed <1% activity compared to the latter. The drastic enzyme activity decrease, however, was less likely caused by enzyme denaturation through sorption; instead, it might be caused by the lower accessibility of the substrates towards the enzyme. The Pignatello group so far has been focusing on developing biochars with high anionic exchange capacity (AEC), aiming to extract anionic nutrients, such as phosphate and nitrate, from animal waste leachate. Biochar materials derived from two wood species, pine and maple, were generated via programmed heating processes. To enhance the AEC of biochars, two strategies, including coating the raw biochar with poly (dimethyldiallyl ammonium chloride) (polyDADMAC) and integrating magnesium ions (Mg2+) to biomass feedstock (i.e., the wood) to obtain Mg-doped biochars. Isotherms of multiple biochar samples adsorbing orthophosphate (PO43-) demonstrate that both polyDADMAC-coated and Mg-doped biochars show enhanced PO43- adsorption capability compared to non-treated biochars.

Publications

  • Type: Conference Papers and Presentations Status: Other Year Published: 2018 Citation: Parikh, S.J. Explorations into the Biochar Frontier. Environmental Studies Departmental Seminar. University of Santa Cruz, Santa Cruz, CA. April 2, 2018.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2017 Citation: Pignatello, J.J. Roles of Biochars and Other Carbons in Agricultural and Environmental Management. Connecticut Agricultural Experiment Station Seminar Series, January 17, 2018.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2018 Citation: Pignatello, J.J. Roles of Pyrogenic Carbon Materials in the Fate, Bioavailability, and Management of Pollutants. Biology Department, University of Saint Joseph, West Hartford, CT; March 28, 2018.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2018 Citation: Pignatello, J.J., S. Bakshi, C. Li, S.J. Parikh, and H. Hsieh. Biochars Tailored to Remove Nutrients from Animal Wastes. Soil Science Society of America International Soils Meeting in San Diego, CA, January 8, 2019.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2019 Citation: Bakshi, S. and J.J. Pignatello. Oxyanion sorption onto treated biochar surfaces. Division of Environmental Chemistry, American Chemical Society National Meeting, New Orleans, LA; March 19, 2018.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2018 Citation: Parikh, S.J., C. Li, S. Bakshi, and J.J. Pignatello. Development of novel applications of animal wastes and biochar for nutrient capture and subsequent fertilizer value. USDA-NIFA Project Director's Meeting, Newark, DE. Oct. 1-3, 2018.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2018 Citation: Parikh, S.J. and D. Gelardi. 2018. Deciphering Biochars for Agronomic and Environmental Applications. Agronomy Society of America Annual Meeting. Baltimore, MD. November 4-7, 2018.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2019 Citation: Li. C S. Bakshi, J.J. Pignatello. The feasibility of immobilizing phytase onto biochars as an enzyme preservation strategy to increase the fertilizer value of animal wastes. Soil Science Society of America International Soils Meeting in San Diego, CA, January 8, 2019.


Progress 03/15/17 to 03/14/18

Outputs
Target Audience:During this reporting period our efforts have been directed on producing biochars and conducting experiments to modify biochars for enhanced sorption of phosphate and phospatase enzymes. During the current reporting period our research was presented at one conference in 2018 where the audience composed of primarily of scientists. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?This project has been critical for the training of two postdoctoral scholars who have conducted the majority of this research. Their responsibilities have included assisting in experimental design, execution of experiments, and data analysis. The postdoctoral scholars have been working with the project PIs to ensure these research activities are appropriately carried out. How have the results been disseminated to communities of interest?The results from all aspects of the project were presented to relevant audiences at the USDA NIFA Project Directors' Meeting in January 2018. What do you plan to do during the next reporting period to accomplish the goals? Methods for altering biochars for nutrient retention and phystase immobilization will be refined. We will test tailored biochar mixtures for efficacy in nutrient retention and utilization after co-composting with dairy and chicken manures. We will evaluate nutrient use efficiency of the co-composted biochar manure mixtures on plant growth.

Impacts
What was accomplished under these goals? Preparation and characterization of biochars made from different biomass feedstocks. Development of methods for increased cation exchange capacity via grafted functional groups and cation incorporation Development of methods for production of biochars with immobilized phytase.

Publications

  • Type: Conference Papers and Presentations Status: Published Year Published: 2018 Citation: Pignatello, J.J., C. Li, S. Bakshi, and S.J. Parikh. 2018. Development of novel applications of animal wastes and biochar for nutrient capture and subsequent fertilizer value. Project Directors Annual Meeting for AFRI Water for Agriculture, AFRI Foundational-Biology Natural Resources and Environment (BNRE), National Integrated Water Quality (NIWQP), and NSF/NIFA Water Sustainability and Climate (WSC) Programs. January 29-31. Washington, DC.