TY - JOUR
T1 - Ecotoxicological characterization of biochars: Role of feedstock and pyrolysis temperature
AU - Domene, X.
AU - Enders, A.
AU - Hanley, K.
AU - Lehmann, J.
N1 - Funding Information:
This study was funded by the Spanish Ministry of Science and Innovation through the CARBONET project (MICINN, CGL2010-15766 ). The biochar material production and field plot construction and maintenance where the test soil was obtained was funded by the United States Department of Agriculture through a Hatch grant (USDA, NY-125487 ), the New York State Energy Research and Development Authority (NYSERDA contract 9891 ), and the National Science Foundation's Basic Research for Enabling Agricultural Development (NSF-BREAD, grant number IOS-0965336 ).
Publisher Copyright:
© 2014 Elsevier B.V.
PY - 2015/4/5
Y1 - 2015/4/5
N2 - Seven contrasting feedstocks were subjected to slow pyrolysis at low (300 or 350°C) and high temperature (550 or 600°C), and both biochars and the corresponding feedstocks tested for short-term ecotoxicity using basal soil respiration and collembolan reproduction tests. After a 28-d incubation, soil basal respiration was not inhibited but stimulated by additions of feedstocks and biochars. However, variation in soil respiration was dependent on both feedstock and pyrolysis temperature. In the last case, respiration decreased with pyrolysis temperature (r=-0.78; p<0.0001, n=21) and increased with a higher volatile matter content (r=0.51; p<0.017), these two variables being correlated (r=-0.86, p<0.0001). Collembolan reproduction was generally unaffected by any of the additions, but when inhibited, it was mostly influenced by feedstock, and generally without any influence of charring itself and pyrolysis temperature. Strong inhibition was only observed in uncharred food waste and resulting biochars. Inhibition effects were probably linked to high soluble Na and NH4 concentrations when both feedstocks and biochars were considered, but mostly to soluble Na when only biochars were taken into account. The general lack of toxicity of the set of slow pyrolysis biochars in this study at typical field application rates (≤20Mgha-1) suggests a low short-term toxicity risk. At higher application rates (20-540Mgha-1), some biochars affected collembolan reproduction to some extent, but only strongly in the food waste biochars. Such negative impacts were not anticipated by the criteria set in currently available biochar quality standards, pointing out the need to consider ecotoxicological criteria either explicitly or implicitly in biochar characterization schemes or in management recommendations.
AB - Seven contrasting feedstocks were subjected to slow pyrolysis at low (300 or 350°C) and high temperature (550 or 600°C), and both biochars and the corresponding feedstocks tested for short-term ecotoxicity using basal soil respiration and collembolan reproduction tests. After a 28-d incubation, soil basal respiration was not inhibited but stimulated by additions of feedstocks and biochars. However, variation in soil respiration was dependent on both feedstock and pyrolysis temperature. In the last case, respiration decreased with pyrolysis temperature (r=-0.78; p<0.0001, n=21) and increased with a higher volatile matter content (r=0.51; p<0.017), these two variables being correlated (r=-0.86, p<0.0001). Collembolan reproduction was generally unaffected by any of the additions, but when inhibited, it was mostly influenced by feedstock, and generally without any influence of charring itself and pyrolysis temperature. Strong inhibition was only observed in uncharred food waste and resulting biochars. Inhibition effects were probably linked to high soluble Na and NH4 concentrations when both feedstocks and biochars were considered, but mostly to soluble Na when only biochars were taken into account. The general lack of toxicity of the set of slow pyrolysis biochars in this study at typical field application rates (≤20Mgha-1) suggests a low short-term toxicity risk. At higher application rates (20-540Mgha-1), some biochars affected collembolan reproduction to some extent, but only strongly in the food waste biochars. Such negative impacts were not anticipated by the criteria set in currently available biochar quality standards, pointing out the need to consider ecotoxicological criteria either explicitly or implicitly in biochar characterization schemes or in management recommendations.
KW - Bioassays
KW - Biochar
KW - Collembolans
KW - Ecotoxicity
KW - Fauna
KW - Microorganisms
KW - Reproduction
KW - Soil basal respiration
UR - http://www.scopus.com/inward/record.url?scp=84921988932&partnerID=8YFLogxK
U2 - https://doi.org/10.1016/j.scitotenv.2014.12.035
DO - https://doi.org/10.1016/j.scitotenv.2014.12.035
M3 - Article
C2 - 25647370
SN - 0048-9697
VL - 512-513
SP - 552
EP - 561
JO - Science of the total environment
JF - Science of the total environment
ER -