Impacts of Sixteen Different Biochars on Soil Greenhouse Gas Production

One potential abatement strategy to increasing atmospheric levels of carbon dioxide (CO 2 ) is to sequester atmospheric CO 2 captured through photosynthesis in biomass and pyrolysed into a more stable form of carbon called biochar. We evaluated the impacts of 16 different biochars from different pyrolysis/gasification processes and feed stock materials (corn stover, peanut hulls, macadamia nut shells, wood chips, and turkey manure plus wood chips) as well as a steam activated coconut shell charcoal on net CO 2 , methane (CH 4 ) and nitrous oxide (N 2 O) production/consumption potentials through a 100 day laboratory incubation with a Minnesota agricultural soil (Waukegan silt loam, total organic carbon = 2.6%); Wisconsin forest nursery soil (Vilas loamy sand, total organic carbon = 1.1%); and a California landfill cover soil (Marina loamy sand plus green waste-sewage sludge, total organic carbon = 3.9%) at field capacity (soil moisture potential = -33 kPa). After correcting for the CO 2 , CH 4 and N 2 O production of the char alone, the addition of biochars (10% w/w) resulted in different responses among the soils. For the agricultural soil, five chars increased, three chars reduced and eight had no significant impact on the observed CO 2 respiration. In the forest nursery soil, three chars stimulated CO 2 respiration, while the remainder of the chars suppressed CO 2 respiration. In the landfill cover soil, only two chars increased observed CO 2 respiration, with the remainder exhibiting lower CO 2 respiration rates. All chars and soil combinations resulted in decreased or unaltered rates of CH 4 oxidation, with no increases observed in CH 4 oxidation or production activity. Biochar additions generally suppressed observed N 2 O production, with the exception being high nitrogen compost-amended biochar, which increased N 2 O production. The general conclusions are: (1) the impact on trace gas production is both dependent on the biochar and soil properties and (2) biochar amendments initially reduce microbial activity in laboratory incubations. These preliminary results show a wide diversity in biochar properties that point to the need for more research. Permanent URL: http://hdl.handle.net/2047/d10019583

[1]  Masanori Okazaki,et al.  Effects of charcoal addition on N2O emissions from soil resulting from rewetting air-dried soil in short-term laboratory experiments , 2007 .

[2]  M. Schmidt,et al.  Black carbon in soils and sediments: Analysis, distribution, implications, and current challenges , 2000 .

[3]  Anthony V. Bridgwater,et al.  A Review of Biomass Pyrolysis and Pyrolysis Technologies , 1991 .

[4]  M. Engelhard,et al.  Stability of biomass-derived black carbon in soils , 2008 .

[5]  Robert H. Hurt,et al.  Structural and compositional transformations of biomass chars during combustion , 1995 .

[6]  C. Morterra,et al.  IR studies of carbons—III: The oxidation of cellulose chars , 1984 .

[7]  Yuesi Wang,et al.  Nitrous oxide emissions as influenced by amendment of plant residues with different C:N ratios , 2004 .

[8]  Y. Imamura,et al.  Reactivity of wood charcoal with ozone , 2005, Journal of Wood Science.

[9]  A. Mosier,et al.  Soil processes and global change , 1998, Biology and Fertility of Soils.

[10]  Rodney T. Venterea,et al.  Effects of Soil Physical Nonuniformity on Chamber‐Based Gas Flux Estimates , 2008 .

[11]  A. Mosier,et al.  Laboratory investigations into the effects of the pesticides mancozeb, chlorothalonil, and prosulfuron on nitrous oxide and nitric oxide production in fertilized soil , 2005 .

[12]  J M Tiedje,et al.  Nitrous Oxide from Soil Denitrification: Factors Controlling Its Biological Production , 1980, Science.

[13]  Johannes Lehmann,et al.  Biochar—One way forward for soil carbon in offset mechanisms in Africa? , 2009 .

[14]  A. Pütün,et al.  Fixed-bed pyrolysis of cotton stalk for liquid and solid products , 2005 .

[15]  G L Fisher,et al.  Fly Ash Collected from Electrostatic Precipitators: Microcrystalline Structures and the Mystery of the Spheres , 1976, Science.

[16]  D. Reicosky,et al.  Impacts of woodchip biochar additions on greenhouse gas production and sorption/degradation of two herbicides in a Minnesota soil. , 2009, Chemosphere.

[17]  D. W. Nelson,et al.  Total Carbon, Organic Carbon, and Organic Matter , 1983, SSSA Book Series.

[18]  R. Aravena,et al.  Radiocarbon Dating of Total Soil Organic Matter and Humin Fraction and Its Comparison with 14C Ages of Fossil Charcoal , 2001, Radiocarbon.

[19]  R. Evans,et al.  BIOMASS DERIVED, CARBON SEQUESTERING, DESIGNED FERTILIZERS , 2009 .

[20]  Y. Imamura,et al.  Analysis of chemical structure of wood charcoal by X-ray photoelectron spectroscopy , 1998, Journal of Wood Science.

[21]  G. Gee,et al.  Particle-size Analysis , 2018, SSSA Book Series.

[22]  Georg Guggenberger,et al.  The 'Terra Preta' phenomenon: a model for sustainable agriculture in the humid tropics , 2001, Naturwissenschaften.

[23]  P. Voroney,et al.  Turnover of carbon in the free light fraction with and without charcoal as determined using the 13C natural abundance method , 2007 .

[24]  K. Toyota,et al.  Suppression of nitrous oxide production by the herbicides glyphosate and propanil in soils supplied with organic matter , 2007 .

[25]  David A. Laird,et al.  The Charcoal Vision : A Win – Win – Win Scenario for Simultaneously Producing Bioenergy , Permanently Sequestering Carbon , while Improving Soil and Water Quality , 2008 .

[26]  J. Lehmann,et al.  Microbial Response to Charcoal Amendments of Highly Weathered Soils and Amazonian Dark Earths in Central Amazonia — Preliminary Results , 2004 .

[27]  R. J. Holmes,et al.  An examination of how exposure to humid air can result in changes in the adsorption properties of activated carbons , 1988 .

[28]  B. Girgis,et al.  Adsorption characteristics of activated carbons obtained from corncobs , 2001 .

[29]  R. Aravena,et al.  OF TOTAL SOIL ORGANIC MATTER AND HUMIN FRACTION AND ITS COMPARISON WITH 14 C AGES OF FOSSIL CHARCOAL , 2002 .

[30]  A. Chughtai,et al.  The Structure of Hexane Soot. Part III: Ozonation Studies , 1987 .

[31]  Jeff Baldock,et al.  Chemical composition and bioavailability of thermally altered Pinus resinosa (Red pine) wood , 2002 .

[32]  M. G. Evans,et al.  The growth of surface oxygen complexes on the surface of activated carbon exposed to moist air and their effect on methyl iodide-131 retention , 1984 .

[33]  F. Carrasco-Marín,et al.  Changes in surface chemistry of activated carbons by wet oxidation , 2000 .

[34]  Serpil Yenisoy-Karakaş,et al.  Production of granular activated carbon from fruit stones and nutshells and evaluation of their physical, chemical and adsorption properties , 2003 .

[35]  W. E. Marshall,et al.  Surface functional groups on acid-activated nutshell carbons , 1999 .

[36]  Mark H. Engelhard,et al.  Oxidation of Black Carbon by Biotic and Abiotic Processes , 2006 .

[37]  E. Veenendaal,et al.  Stability of elemental carbon in a savanna soil , 1999 .

[38]  S. Şensöz Slow pyrolysis of wood barks from Pinus brutia Ten. and product compositions. , 2003, Bioresource technology.

[39]  F. Rodríguez-Reinoso,et al.  Chemistry and Physics of Carbon , 2022 .

[40]  María U. Alzueta,et al.  Pyrolysis of eucalyptus at different heating rates: studies of char characterization and oxidative reactivity , 2005 .

[41]  Thallada Bhaskar,et al.  Comparative studies of oil compositions produced from sawdust, rice husk, lignin and cellulose by hydrothermal treatment , 2005 .