Pedobiologia 56 (2013) 219–224
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Pedobiologia - International Journal of Soil Biology
jo ur nal ho mepage: www.elsevier.de/pedobi
Earthworms can modify effects of hydrochar on growth of Plantago
lanceolata and performance of arbuscular mycorrhizal fungi
Mohamed Salem
a
, Josef Kohler
a
, Susanne Wurst
a
, Matthias C. Rillig
a,b,∗
a
Freie Universität Berlin, Institut für Biologie, Plant Ecology, Altensteinstr. 6, D-14195 Berlin, Germany
b
Berlin-Brandenburg Institute of Advanced Biodiversity Research (BBIB), D-14195 Berlin, Germany
a r t i c l e i n f o
Article history:
Received 12 July 2013
Received in revised form 9 August 2013
Accepted 29 August 2013
Keywords:
Hydrochar
Hydrothermal carbonization
Earthworms
AMF
Plantago lanceolata
Biochar
a b s t r a c t
Hydrothermal carbonization (HTC) is a method to produce carbonized material at relatively low temper-
atures (180–250
◦
C) under pressure and aqueous conditions. The product is called hydrochar and can be
used as a soil amendment. However, applied in high dosages it may have detrimental effects on plants or
soil biota. The potential impact of hydrochar amendment on beneficial soil organisms such as arbuscular
mycorrhizal fungi (AMF) and earthworms and their interactions are not well understood. The goal of
the present study was to determine effects of hydrochar on plant growth and soil biota and to evaluate
interactions of earthworms and hydrochar on plant and AMF performance and to identify underlying
mechanisms. In a greenhouse experiment, we investigated the effect of hydrochar at different addition
rates (control, 1% and 10%, v/v) with or without the earthworm Aporrectodea caliginosa on the growth
of Plantago lanceolata L. and the performance of its AMF. We observed a positive interaction between
earthworms and 10% hydrochar on shoot and root biomass: added as a single treatment hydrochar had a
negative effect on plant growth at this dosage, but plant biomass increased significantly when hydrochar
was added together with earthworms. Root colonization by AMF increased significantly with increas-
ing concentration of hydrochar, but was not affected by earthworms. Contrastingly, extraradical hyphal
length of AMF was reduced by earthworms, but not affected by hydrochar. Thus, hydrochar and earth-
worms affected the performance of AMF, albeit of different AMF structures and in different directions.
Our results indicate that earthworms may play an important role in alleviating the negative impacts of
high dosages of hydrochar on plant growth; such interactions should move into focus of future research
on potential effects of HTC materials.
© 2013 Elsevier GmbH. All rights reserved.
Introduction
When searching for solutions to mitigate the greenhouse effect,
carbon storage in soil can be a potential way to curtail the increas-
ing concentration of CO
2
in the atmosphere. One possible solution
is soil amendment with carbonized material. Carbonized materials
are produced by thermal decomposition of organic material under
limited oxygen supply (Lehmann and Joseph, 2009) and are char-
acterized by a high C content with aromatic compounds which are
relatively stable in soil (Noguera et al., 2010). The product of this
pyrolysis is called biochar, which is obtained by heating organic
materials (up to 700
◦
C) in a closed system (Lehmann and Joseph,
2009). Hydrothermal carbonization (HTC) is a recently rediscov-
ered method to produce carbonized material at relatively low
∗
Corresponding author at: Freie Universität Berlin, Institut für Biologie, Plant
Ecology, Altensteinstr. 6, D-14195 Berlin, Germany. Tel.: +49 030 838 53165;
fax: +49 030 838 53886.
E-mail address: matthias.rillig@fu-berlin.de (M.C. Rillig).
temperatures (180–250
◦
C) in the presence of water and under
pressure (Titirici et al., 2007; Libra et al., 2011). The product is
called hydrochar (or HTC-biochar), and likely decomposes more
rapidly in soil than biochar (Steinbeiss et al., 2009; Libra et al.,
2011). Nevertheless, hydrochar is thought to have broadly similar
characteristics as the widely used biochar improving soil biological
activity, infiltration, water holding capacity, and cation exchange
capacity, which leads to a higher soil fertility and nutrient use effi-
ciency (Lehmann, 2007; Libra et al., 2011). In comparison with
pyrolysis-derived biochars, HTC materials are more hydrophilic
and more hygroscopic due to the higher abundance of polar func-
tional groups such as OH, C O and COOH. Furthermore hydrochar
material usually has a lower degree of graphitization (Titirici et al.,
2008; Baccile et al., 2009). Biochar including hydrochar is thought
to act primarily as a soil conditioner and driver of nutrient trans-
formation (DeLuca et al., 2009). However, in high dosages there
are some reports of negative effects of hydrochar on plant growth
(Gajic and Koch, 2012, George et al., 2012). But there is still little
information on how the application of carbonized materials affects
soil properties, plant productivity and soil biota (Lehmann et al.,
0031-4056/$ – see front matter © 2013 Elsevier GmbH. All rights reserved.
http://dx.doi.org/10.1016/j.pedobi.2013.08.003