In situ polymerization of soil organic matter by oxidative biomimetic catalysis
© The Author(s) 2017
Received: 25 November 2016
Accepted: 6 February 2017
Published: 5 June 2017
Agricultural practices that enhance organic matter content in soil can play a central role in sequestering soil organic carbon (SOC) and reducing greenhouse gases emissions.
We used a water-soluble iron-porphyrin to catalyze directly in situ oxidative polymerization of soil organic matter in the presence of H2O2 oxidant, with the aim to enhance OC stabilization, and, consequently, reduce CO2 emissions from soil. The occurred SOC stabilization was assessed by monitoring soil aggregate stability, OC distribution in water-soluble aggregates, soil respiration, and extraction yields of humic and fulvic acids.
Soil treatment with H2O2 and iron-porphyrin increased the physical stability of water-stable soil aggregates and the total OC content in small aggregates, thereby suggesting that the catalyzed oxidative polymerization increased OC in soil and induced a soil physical improvement. The significant reduction of CO2 respired by the catalyst- and H2O2-treated soil indicated an enhanced resistance of polymerized SOC to microbial mineralization. The catalyzed oxidative polymerization of SOC also significantly decreased the extraction yields of humic and fulvic acids from soil.
The recognition of the agricultural activities in the production of greenhouse gases (GHG) is intensively debated at international level. The Kyoto Protocol states that subscribing countries should promote a sustainable policy in order to reduce the impact of agriculture on climate change, and, thus, invite to draft national or regional programs to reduce GHG emissions also from agriculture . One strategy may rely on the improvement of practices or new methods for carbon sequestration in soil.
Soil organic matter (SOM) is a basic soil component and plays a major role in maintaining soil functions and quality [2, 3]. The organic matter management practices currently adopted to sequester organic carbon in croplands are mainly focused on the physical protection of SOM by combining minimum or zero tillage with crop rotation and the beneficial use of crop, and exploiting plant residues such as in green manuring and mulching. The stable incorporation of soil organic carbon (SOC) is closely related to both the physical protection in soil aggregates and the biochemical recalcitrance of clay-humic complexes. Even though SOC content may be enhanced by reduced tillage, a persistent carbon sequestration is not warranted since incorporation in soil of plant-derived biolabile components is nullified when soil management is reversed to conventional tillage and organic carbon is rapidly mineralized again . Moreover, while the mineral properties of a soil are constant, SOC stabilization is a function of the variable and still poorly understood molecular characteristics of the humified organic matter.
The humified organic matter is the most important SOM pool and represents the largest reservoir of OC in the biosphere . Humic matter is a complex mixture of heterogeneous aliphatic and aromatic molecules of plant and microbial origin [6, 7], whose hydrophobic components progressively separate from the soil solution for thermodynamic reasons [8, 9], and accumulate on soil particles, thus giving rise to chemical and physical protection of SOC . Recent experimental evidence changed the paradigm on the chemical nature of humus as being composed by relatively small (≤1000 Da) heterogeneous molecules , rather than the previously assumed macropolymers de novo synthesized in soil [12, 13]. Soil humic molecules were shown to be self-assembled in supramolecular structures, which are prevalently stabilized by weak non-covalent bonds and may be easily disrupted by interactions with organic acids [14, 15]. A relevant implication towards carbon sequestration in soil is that the self-assembled small humic molecules may be coupled together into larger molecular weight materials by catalytic technologies that form stable intermolecular covalent bonds. Based on the proved activity of the heme prosthetic group of oxidative enzymes in the oxidative couplings of humic phenols [16, 17], the use of much more resilient biomimetic catalysts, such as biocompatible metal-porphyrins, can be employed to promote an effective oligo-/polymerization of the phenolic components of humus [18, 19]. The oxidative coupling among humic molecules can be catalyzed by either water-soluble or immobilized metal-porphyrins and induced either by an oxidizing agent such as hydrogen peroxide (H2O2) [18, 20] or photo-chemically [21, 22].
Metal-porphyrins were also employed to catalyze in situ photopolymerization of soil humic matter. In fact, both a water-soluble iron-porphyrin and a manganese-porphyrin immobilized on spacer-functionalized montmorillonite were found to couple humic phenolic molecules in the soil complex matrix by photo-oxidation under solar radiation [23–26]. However, up to our knowledge, no investigation has been reported so far on the in situ oxidative polymerization of soil humic molecules under biomimetic catalysis in the presence of a chemical oxidant. Therefore, the objective of this work was to investigate the enhancement in chemical stability of SOM when a soil was subjected to oxidative catalysis, by applying in situ a water-soluble iron-porphyrin and H2O2 as oxidants.
Soil sample and characterization
The soil sample was a Fluventic Xerochrept (FAO Soil Classification) which was collected from the surface layer (0–20 cm) of an agricultural area near Naples, Italy. After air drying and sieving through a 2-mm sieve, the soil texture was measured using pipet method, and total organic carbon (TOC) was determined by an EA 1108 Elemental Analyzer (Fisons Instruments). Soil properties are reported elsewhere .
The synthesis of meso-tetra(2,6-dichloro-3-sulfonatophenyl)porphyrinate of Fe(III) (Fe-Pha) has been previously described . A meso-tetra(2,6-dichlorophenyl)porphyrin (H2TDCPP) was first synthesized and then dissolved in steaming H2SO4 (25 mg mL−1) and stirred for 12 h at 160 °C under argon atmosphere. The product was recovered with cool water in a flask immersed in ice. The pH of the solution was increased up to 7 with a saturated NaOH solution and then evaporated at 60–70 °C under vacuum. The residue was recovered with methanol, again evaporated under vacuum, re-dissolved in methanol, and recrystallized in ethyl ether. The product was obtained by filtration and then purified through a cationic exchange resin Dowex 50W X8–100 (50–100 mesh), previously conditioned with a 10% HCl solution. The product was eluted with water and the recovered fraction-dried under vacuum. The final material, meso-tetra(2,6-dichloro-3-sulfonatophenyl)porphyrin (H2TDCPPS), was recrystallized in a methanol–acetone solution with a final reaction yield of 75%. The H2TDCPPS (200 mg) and 100 mg of Fe(II)SO4 were dissolved in 100 mL of water. The solution was degassed and left for 12 h under argon atmosphere. Then the solution was vacuum-evaporated and the residue re-dissolved in water. This solution was filtered and purified through a cationic exchange resin Dowex 50W X8–100 (50–100 mesh), previously conditioned with a 10% HCl solution. The column was eluted with water and the recovered material dried upon vacuum. The final Fe-Pha product was recrystallized in methanol-acetone in order to purify the sample from residual salts. The yield of the reaction was 80%.
In situ oxidative polymerization experiments
Two control series were obtained by placing either 40 or 200 g of air-dried soil samples on a Petri dish (12 cm diameter) and kept at 40% of water-holding capacity (WHC) by adding 20 and 100 mL of water, respectively, and either 0 or 3 mL of H2O2 8.6 M. Soil samples subjected to oxidative polymerization were similarly prepared and added with 0.1 mg mL−1 of synthetic water-soluble Fe-Pha and H2O2 8.6 M. All series were prepared in 6 replicates, covered with a Petri dish and incubated in the dark at room temperature for 5 days.
Soil aggregate stability
The amount of OC (%) in each aggregate fraction was normalized to the weight of each fraction: OC content in fraction (g kg−1) × mass of recovered fraction (g kg−1)/total OC recovered (g kg−1).
Soil respiration was evaluated by a static absorption method . In brief, 9 g of a 2-mm sieved, air-dried, and rewetted soil sample, a beaker containing 20 mL of distilled water (blank), and another one added with 20 mL of 0.05 M NaOH were placed in a tightly closed 1-L jar. The beaker with distilled water served to maintain a constant humidity in the closed system. The amount of CO2 emitted from the respiration of soil sample and adsorbed by NaOH solution was determined every 3–4 days (longer incubation periods could result in anaerobic conditions) by back titration with 0.05 M HCl after addition of 7 mL of 0.5 M BaCl2 in both water blank and NaOH solutions. The estimation of evolved CO2 in the closed system was referred to 23 days of soil incubation.
Soil respiration measurements were then repeated after soil fumigation treatment . Briefly, for the fumigation, the soil sample was placed in a glass beaker and put in a large desiccator lined with moist paper. The desiccator contained a beaker with alcohol-free CHCl3 and a few anti-bumping granules. The desiccator was evacuated until the CHCl3 boiled vigorously. Finally, the tap was closed and the desiccator was left in the dark at 25 °C for 18–24 h. The beaker with the CHCl3 and the paper were then removed and CHCl3 vapor was removed from the soil by repeated evacuation in the desiccator. Six 3-min evacuations, three with a water pump and three with a high-vacuum oil pump, were usually sufficient to remove the smell of CHCl3 from the soil; two additional evacuations were then carried out with the high-vacuum pump.
Humic and fulvic acids extraction
At the start and end of the experiment, humic (HA) and fulvic (FA) acids were extracted and isolated from soil sample as described elsewhere . Two different amounts of soil (40 and 200 g) were extracted with 0.1 M NaOH and 0.01 M Na4P2O7*10H2O 1:8 extraction (soil:solution), under N2 atmosphere. The solutions were then centrifuged at 7000 rpm for 20 min and the supernatants were filtered with glass fibers and acidified to pH 1 with 12 M HCl to promote precipitation of HA. The acidified solutions were allowed to stand on a bench overnight, and then centrifuged at 7000 rpm for 20 min to recover the HA fraction. The supernatants containing FA were separated as such, while the precipitated HAs were treated with a solution of 0.06 M HF and 0.03 M HCl to remove the co-extracted silicates. Thereafter, the solution was centrifuged at 7000 rpm for 20 min and the HA re-dissolved in water. Both solutions of HA and FA were dialyzed against water until it is Cl-free and freeze-dried.
The Tukey’s test was used to compare values obtained for control and treatments, and the difference was considered to be significant at the level of P ≤ 0.05. All values were based on triplicate samples from which the mean and the standard error of the mean were calculated.
Results and discussion
Soil respiration measurements were repeated after the chloroform fumigation treatment of soil. Chloroform is toxic towards soil microbial communities, and, due to the death and lysis of soil microbes, the presence of additional metabolic carbon derived by dead cells resulted in a significant increase of respired CO2 from soil . In fact, the re-emergent microbial activity had more accessible carbon to respire. Despite the enhanced respiration due to fumigation, the oxidative treatment with water-soluble Fe-Pha catalyst still enabled a reduction of about 50% of CO2 emission respect to control. Again, this finding confirms that the catalyzed oxidative polymerization of SOM phenolic components reduced CO2 emission from soil because of the increased difficulty of soil microbial communities to mineralize SOM, due to either an enhanced chemical stabilization or physical protection in less accessible micro-aggregates.
Our findings indicate that the in situ oxidative coupling of humic molecules under biomimetic catalysis effectively increased their molecular mass and content of chemical energy. This resulted in less microbial mineralization of SOM, because the new intermolecular covalent bonds either required more energy from soil microorganisms for their breakage or favored a tighter stabilization of clay-humic complexes and a reduced accessibility to the microflora. This is in line with the improved soil physical quality observed after the catalyzed soil treatment that favored interparticle aggregation and stabilization of humus carbon into meso- and micro-aggregates. A soil management practice based on the use of biomimetic oxidative catalysts may represent an innovative strategy for the control of SOM aimed to limit GHG emissions from soils and, hence, mitigate global climate changes.
All authors have contributed equally to the work. All authors read and approved the final manuscript.
The authors thank the Italian Ministry of University and Research (MIUR) for providing funding.
The authors declare that they have no competing interests.
Consent for publication
All authors give their personal consent for publication.
This work was partially supported by the project PON03PE_00107_1 “BIOPOLIS” funded by the Italian Ministry of University and Research (MIUR).
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