TY - JOUR
T1 - Priming effect of Miscanthus sinensis derived biochar on brown forest soil
AU - Iimura, Yasuo
AU - Natsuhara, Masaaki
AU - Ohtsuka, Toshiyuki
AU - Tomotsune, Mitsutoshi
AU - Yoshitake, Shinpei
AU - Koizumi, Hiroshi
N1 - Funding Information:
We thank the members of Laboratory of Soil Science, The University of Shiga Prefecture. The study was supported by JSPS (Japan Society for the Promotion of Science) KAKENHI Grant Number 15H01730 and 17K00524.
Funding Information:
This work was supported by the JSPS ?(Japan Society for the Promotion of Science) KAKENHI [15H01730 and 17K00524]. We thank the members of Laboratory of Soil Science, The University of Shiga Prefecture. The study was supported by JSPS (Japan Society for the Promotion of Science) KAKENHI Grant Number 15H01730 and 17K00524.
Publisher Copyright:
© 2019, © 2019 Japanese Society of Soil Science and Plant Nutrition.
PY - 2019/11/2
Y1 - 2019/11/2
N2 - The role of biochar in the mitigation of CO2 emissions has been extensively studied in agricultural soils but is not well understood in Japanese forest soils, especially in relation to CO2 emissions from applied biochar and native soil C (i.e., the priming effect; PE). We hypothesized that the type of biochar and/or the application method (mixed or sprinkled) affect the direction and magnitude of PE in forest soil, and in particular, negative PE can be achieved relatively easily if biochar produced under higher temperature conditions were sprinkled on the soil surface. To test our hypothesis, we measured CO2 emissions from biochar-amended brown forest soil in Japan and examined its PE by conducting a medium-term (~4 months) incubation study. As substrates, we used plain straw from the C4 grass Miscanthus sinensis (SU) and two qualities of biochar produced from it at either 300°C (BC300) or 800°C (BC800) and compared two application methods: mixed into or sprinkled onto the soil. BC800 had a greater C content and C:N ratio as well a lower volatile matter content and higher nonvolatile matter content than BC300. SU had the lowest C content and C:N ratio of all the substrates. We found that biochar quality (volatile and nonvolatile matter content) was clearly related to the decomposition rate when mixed into the soil, but we could not find this relationship when biochar was sprinkled onto the soil. The addition of biochar to the soil induced a positive PE in the early stages (except for BC800 sprinkled) but suppressed CO2 emissions from native soil organic matter (negative PE) in the later stages, whereas the PE with SU application was always positive regardless of application method. Our results suggest that when biochar is sprinkled onto soil it is more likely to suppress soil-derived CO2 emission than when mixed in soil; however, the trend based on biochar quality was unclear.
AB - The role of biochar in the mitigation of CO2 emissions has been extensively studied in agricultural soils but is not well understood in Japanese forest soils, especially in relation to CO2 emissions from applied biochar and native soil C (i.e., the priming effect; PE). We hypothesized that the type of biochar and/or the application method (mixed or sprinkled) affect the direction and magnitude of PE in forest soil, and in particular, negative PE can be achieved relatively easily if biochar produced under higher temperature conditions were sprinkled on the soil surface. To test our hypothesis, we measured CO2 emissions from biochar-amended brown forest soil in Japan and examined its PE by conducting a medium-term (~4 months) incubation study. As substrates, we used plain straw from the C4 grass Miscanthus sinensis (SU) and two qualities of biochar produced from it at either 300°C (BC300) or 800°C (BC800) and compared two application methods: mixed into or sprinkled onto the soil. BC800 had a greater C content and C:N ratio as well a lower volatile matter content and higher nonvolatile matter content than BC300. SU had the lowest C content and C:N ratio of all the substrates. We found that biochar quality (volatile and nonvolatile matter content) was clearly related to the decomposition rate when mixed into the soil, but we could not find this relationship when biochar was sprinkled onto the soil. The addition of biochar to the soil induced a positive PE in the early stages (except for BC800 sprinkled) but suppressed CO2 emissions from native soil organic matter (negative PE) in the later stages, whereas the PE with SU application was always positive regardless of application method. Our results suggest that when biochar is sprinkled onto soil it is more likely to suppress soil-derived CO2 emission than when mixed in soil; however, the trend based on biochar quality was unclear.
KW - Biochar
KW - C4 grass
KW - brawn forest soil
KW - priming effect
KW - δC
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U2 - 10.1080/00380768.2019.1672101
DO - 10.1080/00380768.2019.1672101
M3 - Article
AN - SCOPUS:85074046570
SN - 0038-0768
VL - 65
SP - 550
EP - 556
JO - Soil Science and Plant Nutrition
JF - Soil Science and Plant Nutrition
IS - 6
ER -