Source: SOUTH DAKOTA STATE UNIVERSITY submitted to NRP
EFFECT OF SOIL ORGANIC MATTER SELF-ASSEMBLY ON CARBON SEQUESTRATION
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0219691
Grant No.
2009-65107-05775
Cumulative Award Amt.
$349,934.00
Proposal No.
2009-02660
Multistate No.
(N/A)
Project Start Date
Sep 1, 2009
Project End Date
Aug 31, 2013
Grant Year
2009
Program Code
[94440]- Soil Processes
Recipient Organization
SOUTH DAKOTA STATE UNIVERSITY
PO BOX 2275A
BROOKINGS,SD 57007
Performing Department
Chemistry & Biochemistry
Non Technical Summary
Interest in enhancing the residence time of soil organic matter (SOM) through natural or engineered mechanisms as a possible means of sequestering carbon dioxide to mitigate the impacts of carbon-dioxide induced global warming effects has steadily increased over the last decade. In addition to the natural resistance of some components of SOM to mineralization, SOM can be stabilized through the interaction with other components of the soil matrix (for example, minerals) and/or the absence of a microbial consortium adapted to utilize it as a nutrient and energy source. While the finite capacity of the SOM carbon pool limits its ability to mitigate atmospheric carbon dioxide levels, it remains a viable strategy for moderating increases over the short-term. This project is based on recent research that demonstrates that SOM can self-organize or self-assemble into a composite material with different characteristics than those of the starting materials. We believe that a detailed understanding of how the assembled nature of SOM affects its residence time in soil, will contribute to the search for solutions to reduce greenhouse gases. The experiments in this proposal will explore how microbial degradation of SOM varies with self-assembly, how SOM utilization by microbes varies as a function of its chemical composition, what mechanism(s) initiates SOM self-assembly, and determine if it is possible to control SOM self-assembly. Microbial incubations, small-angle neutron scattering, and solid-state NMR experiments will be used to determine the nature of the self-assembly process. Experiments using carbon-13 labeled molecules will be used to provide the data necessary to achieve the project?s objectives. Results from the experiments proposed here have the potential to contribute to the development of long-term soil management strategies by identifying the contributions of self-organization as a factor in the stability of SOM, and how this understanding may be used to increase the residence time of organic carbon in the soil.
Animal Health Component
5%
Research Effort Categories
Basic
95%
Applied
5%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
10201102000100%
Knowledge Area
102 - Soil, Plant, Water, Nutrient Relationships;

Subject Of Investigation
0110 - Soil;

Field Of Science
2000 - Chemistry;
Goals / Objectives
The overall project hypothesis is that the ability of soil organic matter (SOM) to resist mineralization is directly related to its structural organization. The specific objectives and their expected outcomes are given below. 1. Determine the amount and type of soil organic carbon utilized by microbes when SOM is transformed from a self-assembled system to a disassembled mixture. The observed differences in the mineralization rate between assembled and disassembled SOM samples that have the same bulk chemical composition will indicate the effect of SOM component organization on its resistance to biodegradation. The comparison of the chemical fingerprint of the assembled and disassembled SOM components remaining in the cultures after incubation period is complete will indicate if the changes induced by microbial activity depend on the SOM's structural organization. Assessing the carbon mineralization and transformation of SOM in the microbial cultures is important for understanding C-sequestration and sustainable soil productionvity. 2. Determine how these changes compare with the ones resulting from variation of SOM chemical composition. The data will demonstrate the extent that variations in structural organization and chemical composition have on microbial degradation of SOM. It will resolve the importance of explicitly accounting for SOM's structural organization in the modeling of SOM's biodegradation. The study will also establish the relationship between SOM's chemical composition and structural organization. 3. Determine the mechanism(s) that initiates the self-assembly process and controls the resulting organization. This objective will establish the specific organizational changes that occur going from the assembled to disassembled NOM state. The data will identify the presence or absence of different chemical domains in the assembled and disassembled samples based on differences in motion and proximity of different chemical species to one another. It will provide information about the role of lipids in assembling SOM and the resulting organized structure and a conceptual understanding of the self-assembled architecture of the hierarchical composites comprised of SOM components. 4. Determine if it possible to "tune" the environmental behavior of SOM by controlling its organization. This Objective will provide a scientific basis for strategies intended to control the architecture of SOM and consequently its functionality. The data will determine the extent of the variations in the amount and nature of amphiphilic and lipid components needed to change the architecture of SOM.
Project Methods
Objective 1. SOM fractions will be isolated from materials that represent a range of organic carbon contents and carbon type distributions: leonardite (IHSS BS104L), peat (IHSS BS103P), Cryohemist and fine-silty, mixed Udic Haploborolls soils. Humic acid (HA) and humin (HMN) will be extracted from each using a traditional alkali extraction method. A combination of aqueous alkaline and organic solvent extractions will "disassemble" HA and HMN. Mixtures will be prepared to resemble disassembled HA or HMN samples. These samples will be the sole carbon source in microbial degradation experiments. Samples before and after incubation with a water extract of a fresh soil as an inoculum will be characterized by C13 DPMAS NMR. Objective 2. Statistical analysis of the mineralization data obtained in Objective 1 will be used to correlate the effects of the structural organization and chemical composition on microbial degradability of SOM. The contribution of organization will be obtained as the relative difference between mineralization of samples having variable organization but constant chemical characteristics. The contribution of chemical composition will be obtained as the relative difference between mineralization of samples having variable chemical composition but constant structural organization. Parametric (e.g., t-test and ANOVA) and/or nonparametric (Mann-Whitney U test and Kolmogorov-Smirnov two-sample test) statistical methods will be used to assess significance. Objective 3. Solid-state NMR and small angle neutron scattering (SANS) are complimentary techniques used to study materials that display an absence of long-range order. Both techniques will be applied to the assembled and disassembled samples from Objective 1. SANS will determine the open (accessible) and closed pore structure of the assembled and disassembled SOM samples through contrast variation using benzene and deuterated benzene (C6D6) as contrast probes. NMR experiments to be performed include: H-C13 heteronuclear correlation spectroscopy to quantitatively characterize mobile domains; 2D WISE (WIde-line SEparation) spectroscopy to characterize domain mobility when H resonances overlap; and spin diffusion to measure molecular associations between alkyl and aromatic components in the assembled and disassembled SOM materials. These measurements will enable us to determine if the assembled and disassembled samples differ in their morphology and domain structure. Objective 4. Assembled and disassembled HA and HMN containing various amounts of lipids will be obtained by Soxhlet extraction for various times. The organizational differences between these samples will be quantified using heat capacities obtained by differential scanning calorimetry. Based on these experiments, carbon-13 labeled compounds such rhamnolipids, fatty acids, and alkyl benzene carboxylic acids will be used as model compounds. Solutions of the model compounds will be added to the solid SOM materials in their original form and the corresponding disassembled mixtures and incubated. The samples will then be analyzed by DSC and solid-state NMR to determine whether it is possible to manipulate SOM organization.

Progress 09/01/09 to 08/31/13

Outputs
Target Audience: The primary target audiences reached during this year (a no-cost extension year) were other scientists working in the field. These inviduals were reached via oral dissemnination of the research results via presnetations at technical meetings and submission of manuscripts for publication. Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided? This project has supported 2 undergraduate chemistry majors who have done research as a part of their undergraduate degree requirements, 2 postdoctoral research associates and a senior reserch staff member. The senior reserch staff meember has accepted a tenure-track university positoin in environmental chemistry. How have the results been disseminated to communities of interest? The results of this research project have been disseminated via oral presentations at regional, national and international scientific meetings. One manuscripts is in prepss and 2 others are under review. What do you plan to do during the next reporting period to accomplish the goals? This is the final project report.

Impacts
What was accomplished under these goals? The primary findings of this project during this project year are stated below. · Similarities and differences in the self-assembly of humic acid and humin were identified. Both NOM samples have shown similarities at the second hierarchical level that mirror the similarities in the distribution of the corresponding components, HA1 and L0. We have also shown that differences at the first hierarchical level that mirror the differences in the distribution and nature of the corresponding fractions, HA2 and L1. The first hierarchical level is composed primarily of amphiphilic components and has a positive cpE in case of humic acid while for humin is composed of mainly lipids and the cpE has negative values. · The amphiphilicity of HA2, crystallinity of L1 and the mass ratio of the HA2/L1 fractions were identified as factors that affect the self-assembly process however no exact dependence of the self-assembly process on these factors has been possible to date. · The existence of these operationally defined NOM fractions (HA1, HA2 and L1) that have been isolated from both humic acid and humin using two different extractants and from two geomaterials with different chemical characteristics and geochemical histories, suggests that the hierarchical associative mechanism is one that is characteristic of NOM. · The mineralization of self-assembled samples is higher by as much as 70% compared to their corresponding physical mixtures and does not show preferential mineralization. · The mineralization enhancement follows the same trend as the extent of the self-assembly as determined by the variation in heat capacity values. The larger the change in heat capacity the more self-assembled the sample is and the more mineralized it is when compared to its corresponding physical mixture. · The extent of mineralization of the self-assembled samples was not correlated to chemical composition based on the carbon-type distribution or hydrophobicity index, both of which were derived from the samples quantitative 13C solid-state NMR spectra. In contrast, the extent of mineralization of the physical mixtures and the individual fractions did vary with chemical composition and was accompanied by preferential mineralization of alkyl carbon. · The mineralization of humic acid and its most abundant fraction (HA1) samples in the solid state at 85% relative humidity showed significantly lower values than the ones from the solution mineralization experiments. · Domains within HA0 fractions with different amounts of motion were identified using 2D WISE (WIde-line SEparation) and T2 NMR measurements. A mobile domain in a peat humic acid fraction was not apparent from T2 measurements.

Publications

  • Type: Journal Articles Status: Awaiting Publication Year Published: 2014 Citation: Khalaf, M.; Chilom, G.; Rice, J. A., 2014, Mineralization of natural organic matter: Role of chemical composition and structural organization, Soil Biology & Biochemistry, 73:96-105, http://dx.doi.org/10.1016/j.soilbio.2014.02.013
  • Type: Conference Papers and Presentations Status: Published Year Published: 2010 Citation: Chilom, G.*; Nagy, Z.; Delp, S.; Huff, G.; Rice, J. A., Self-assembly of humic acid: influence of pH and chemical composition, Biogeosciences Section 04, AGU Fall Meeting, San Francisco, Dec. 2010, paper B41E-0350.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2011 Citation: Khalaf, M.*; Chilom, G.; Rice, J. A.; Microbial utilization and transformation of humic acid and its fractions, 241rst ACS National Meeting, Anaheim, CA, March 2011, GEOC 33.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2011 Citation: Chilom, G.; Khalaf, M.; Rice, J. A.*, Effect of self-assembly on the microbial degradation of humic acid, European Geophysical Union Congress, April 2011, Vienna, Austria, EGU2011-5049.
  • Type: Conference Papers and Presentations Status: Published Year Published: 2011 Citation: Chilom, G.*; Rice, J. A., Unifying characteristic of soil organic matter, 242nd ACS National Meeting, Denver, CO, Aug. 2011, ENVR 375.
  • Type: Journal Articles Status: Published Year Published: 2013 Citation: Chilom, G.; Baglieri, A.; Johnson-Edler, C. A.; Rice, J. A., 2013, Hierarchical self-assembling properties of natural organic matters components, Organic Geochemistry, 57, 119-126, http://dx.doi.org/10.1016/j.orggeochem.2013.02.008.


Progress 09/01/10 to 08/31/11

Outputs
OUTPUTS: Three fractions referred to as the non-amphiphilic humic, the amphiphilic fraction and the lipid fraction were isolated from NOM samples using a combination of organic solvent and aqueous alkaline extractions. Microbial degradation studies were performed for fractions of humic acid and their corresponding physical mixtures isolated from Leonardite and Guanella peat (Objective 1 & 2). The two materials are both reach in organic carbon but have different carbon-type distribution, with leonardite being primarily aromatic and Guanella being primarily aliphatic. Humic acid fractions and mixtures were analyzed before and after short term degradation experiments by solid state 13C NMR. Long term experiments of microbial degradation of these materials and two more isolated from Pahokee peat and Poinsett soil are in progress. Self-assembly of materials isolated from Leonardite, Pahokee and Guanella peat was described by the value of the excess heat capacity of these materials (Objective 4). The heat capacity of the composite formed at first level of organization and of its components, amphiphilic and lipid fractions were determined by differential scanning calorimetry. Correlations between the magnitude of the excess heat capacity and properties of these materials, such as carbon-type distribution, composition, surfactant character and crystallinity, were made. Work for the fourth system, Poinsett soil, is in progress. The 2D WISE (WIde-line SEparation) solid-state NMR spectra of the fractions and its corresponding mixtures in both hydrated and dehydrated samples were measured. Using spin-diffusion 2D WISE spectroscopy, spin diffusion between different types of proton sites was detected based on changes in the linewidths of the 1H resonances. The 1H T1 and T2 of the samples were also measured. A NMR spin-echo acquisition sequence was used to determine the relaxation time T2. The spin-echo is generated by two pulses separated by a time, τ. Using an echo with a long τ (200 μs), the protons with long T2 (fast motion) were selectively measured. (Objective 3). The results of these experiments were presented in papers at the Spring and Fall ACS National Meeting (2011), and the European Geophysics Union 2011 Annual Meeting. PARTICIPANTS: Gabriela Chilom (co-PI), Research Associate, South Dakota State University; James Rice (co-PI), Professor, South Dakota State University; Jay S. Shore (co-PI), Associate Professor, South Dakota State University; Moustafa Khalaf, Postdoctoral Research Associate, South Dakota State University; Zoltan Nagy, Postdoctoral Research Associate, South Dakota State University. TARGET AUDIENCES: Environmental scientists, environmental chemists and global change scientists. PROJECT MODIFICATIONS: None anticipated at this time

Impacts
Regardless of their origin, nature or pretreatment, natural organic matter has in common the ability to self-assembly into supramolecular structures that are controlled by a rather small portion of its components. These components are identified as amphiphilic humic-like and lipid components. Similar excess heat capacity values were found for Leonardite and Pahokee peat and smaller values were found for Guanella. Distribution of the three fractions was similar for Leonardite and Guanella but their characteristics, in terms of amphiphilic character and crystallinity were similar for leonardite and Pahokee. The self-assembly of these materials depends more on the relative properties of the fractions than on the ratio of amphiphilic and lipid components. In addition, not all the fractions of humic acid showed the same degradability. The amphiphilic fraction of humic acid was the one most mineralized, suggesting that properties like organization might have a major impact on mineralization of humic samples. A comparison of the intensities and the linewidths of the 1H slices of the 1H-13C WIdeline Separation (WISE) NMR spectra indicate that there is spin diffusion between different components of the samples suggesting that they are multiple domains in most of the samples, excluding the lipid fraction. Further work is necessary to try to determine an estimate of domain size and to determine what types of domains these may be. The observation of both broad and narrow 1H resonances in the spin echo experiment is significant because it is related to the morphology of the sample and it may be possible to obtain more detailed understanding of the domains in the samples by using 2D NMR techniques to measure the proximity of the protons to each and protons to carbon types using the narrow and broad resonances. The narrow resonances were not apparent in the 2D WISE spectra, because the parameters used to measure these spectra were optimized to ensure that the measured carbon signals came from carbon in very close proximity to the hydrogen.

Publications

  • No publications reported this period


Progress 09/01/09 to 08/31/10

Outputs
OUTPUTS: Using a combination of organic solvent and aqueous alkaline extractions various NOM samples and were separated into three fractions referred to as the non-amphiphilic humic (HA1), the amphiphilic (HA2) fraction and the lipid fraction (L1). The carbon-type distribution of each fraction was determined for each material by 13C DPMAS solid-state NMR. Fractions of humic acid isolated from four materials, Leonardite, Guanella peat, Pahokee Peat and Poinsett soil were prepared and based on their calculated distribution the physical mixtures were prepared. All these samples will be used for the microbial biodegradation studies (Objective 1 and 2) that are in progress. The microbial inoculum was isolated from a soil and its growing kinetic was determined using glucose as the mineralizable substrate. Leonardite humic acid samples at various degrees of deprotonation were prepared by drying from solutions of pH values between 2 and 11, and fractionated using the same combination of organic solvent and aqueous alkaline extractions described earlier (Objective 4). The variation of the fractions' distribution and carbon-type composition with pH was determined. The amphiphilic fraction was also characterized by tensiometry and the lipid fraction by differential scanning calorimetry. The variation of surfactant character of HA2 and crystallinity of L1 with pH were determined. Interactions specific to first level of organization between the amphiphilic and lipid fractions of Leonardite, were assessed by using 2D WISE (WIde-line SEparation) solid-state NMR spectroscopy. 2D WISE is a 1H-13C heteronuclear correlation technique where broad dipolar-coupled 1H resonances are measured. From these broad dipolar-coupled 1H resonances, correlation times of the molecular motion of different domains of the individual fractions were estimated and compared to the ones of the composite material (Objective 3). The results of these experiments were presented in papers at the AGU Fall Meeting (2009), 45th Midwest Regional Meeting of the American Chemical Society (ACS) (2010), the 239th ACS National Meeting (2010), and the Soil Science Society of America 2010 Annual Meeting. PARTICIPANTS: James Rice (PI), Professor, South Dakota State University, Gabriela Chilom (co-PI), Research Associate, South Dakota State University, Jay S. Shore (co-PI), Associate Professor, South Dakota State University, Moustafa Khalaf, Postdoctoral Research Associate, South Dakota State University, Zoltan Nagy, Postdoctoral Research Associate, South Dakota State University, Gary Huff, Undergraduate Research Assistant, South Dakota State University, Sara Delp, Undergraduate Research Assistant, University of Wisconsin- Platteville, Andrea Baglieri, Assistant Professor, University of Catania, Italy. TARGET AUDIENCES: Other biogeochemists and soil scientists PROJECT MODIFICATIONS: Nothing significant to report during this reporting period.

Impacts
NOM has a positive role in the environment regardless of its origin or chemical composition that is due to its organization and the interactions between its individual components. NOM is present in a self-assembled supramolecular-state that is controlled by a small portion of its components that define its core. This "core" consists of lipids and amphiphilic components, chemically similar to their parent material, that self-assemble in nanoparticles and then further engage the non-amphphilic humic to form supramolecular structures. While the non-amphphilic humic components are difficult to control, the amphiphilic and lipid components are manageable so it opens the opportunity of controlling the NOM's behavior depending on the application desired. NOM organization varies with the pH. Based on the data obtained from Leonardite and Guanella peat, the higher the pH the L0 nanocomposite amount decreased, the contribution of lipids to it increases and the surfactant character of amphiphilic components increased too. Changes in the self-assembled state were observed with pH varied over environmental values. In addition the data showed that the core of NOM is defined by the strength of surfactant character and degree of lipid crystallinity as major factors that control its self assembly. This finding was also supported by the 2D WISE NMR study which showed that the mobility of aliphatic carbon from lipids increased upon interaction with the surfactant components. While we do not expect that the crystalline matrix to change considerably upon interaction we suggest that pockets of amorphous carbon are formed inside the matrix that interacts with the amorphous carbon of the surfactant. To test this hypothesis experiments are currently underway using various samples of NOM.

Publications

  • Chilom, G., Baglieri,A., Rice, J.A. (2009) Effect of Soil Organic Matter Self-Assembly on Carbon Biodegradability, AGU Fall Meeting, San Francisco, December 2009.
  • Delp, S., Chilom, G., Nagy, Z., Rice, J.A. (2010). Influence of pH on the self-assembly of humic acid, ACS regional Meeting, Wichita, KS, October 2010.
  • Huff, G., Nagy, Z., Chilom, G., Rice, J.A. (2010) Self-assembly of Humic Acid: Influence of Composition, ACS regional Meeting, Wichita, KS, October 2010.
  • Chilom, G., Baglieri,A., Rice, J.A. (2010) Comparative study of composite materials isolated from the humic acid and humin of a mineral soil, ACS National meeting San Francisco 2010.
  • Chilom, G., Nagy, Z., Rice, J.A. (2010) Size Separation and Characterization of Fractions Involved in Humic Acid Self-Assembly, SSSA Annual Meeting, Long Beach, CA, Nov 2010.