Ecological Indicators 23 (2012) 482–490
Contents lists available at SciVerse ScienceDirect
Ecological Indicators
jo ur n al homep ag e: www.elsevier.com/locate/ecolind
The FungiResp method: An application of the MicroResp
TM
method to assess
fungi in microbial communities as soil biological indicators
Meriem Ben Sassi
a,b
, Jeanne Dollinger
a,b
, Pierre Renault
a,b
, Ahmed Tlili
c
, Annette Bérard
a,b,∗
a
INRA, UMR1114 EMMAH, F-84914 Avignon, France
b
UAPV, UMR1114 EMMAH, F-84914 Avignon, France
c
Institute of Freshwater Ecology and Inland Fisheries, Alte Fischerhütte 2, Neuglobsow, Germany
a r t i c l e i n f o
Article history:
Received 23 January 2012
Received in revised form 3 May 2012
Accepted 7 May 2012
Keywords:
Substrate-induced respiration
Selective inhibition
MicroResp
TM
Soil microbial catabolic structure
Soil fungal catabolic structure
a b s t r a c t
Soil ecosystem services need to monitor soil quality in terms of soil functions. This need in turn requires
functional indicators. Microbial functional diversity offers a way to characterize soil quality and any
changes to it. Among soil microbial communities, fungi play a critical role in organic matter decomposition
and nutrient cycling in soil by decomposing complex substrates, but only a few studies have focused
on the function of soil fungal communities. We have developed a protocol based on substrate-induced
respiration using the MicroResp
TM
technique combined with a selective inhibition (SI) procedure to
characterize the fungal biomass and catabolic profiles for soil microbial and fungal communities: the
FungiResp method. After comparisons with oxytetracycline, we chose bronopol as a bactericide to extend
the FungiResp protocol. An optimal bronopol concentration of 78 g g
-1
soil was selected for the four
soils tested to minimize the risk of inhibiting non-target communities (fungi). We used this convenient,
miniaturized method to compare different soils and different perturbations (drought and heat). The
FungiResp method gave further data on the fungal part of the microbial substrate-induced respiration
in these different contexts. Also, the catabolic structure of microbial and fungal communities measured
as pattern of substrate utilization (CLPPs) enabled us to contrast the functional contributions of the
decomposer groups in the different soils studied and highlight the functional impacts of the different
perturbations applied to them.
© 2012 Elsevier Ltd. All rights reserved.
1. Introduction
Soil faces a broad range of threats from human activities
and global change. These pressures may degrade it through an
increase in erosion, contamination, sealing, compaction, salin-
ization, and loss of organic matter, structure and biodiversity
(Commission of the European Communities, 2002). Soil ecosys-
tem services (Millennium Ecosystem Assessment, 2005), need to
monitor soil quality in terms of soil functions, which demands func-
tional indicators (Romaniuk et al., 2011; Ritz et al., 2009). Doran
and Zeiss (2000) suggested complementary criteria of soil bioindi-
cators: they should be sensitive to variations in management
and climate change, well correlated with beneficial soil func-
tions, useful for elucidating ecosystem processes, comprehensible
and useful to land managers and finally easy and inexpensive to
measure.
Soil microbial communities are extremely diverse in their
composition and play an essential role in nutrient cycling
∗
Corresponding author at: INRA, UMR1114 EMMAH, F-84914 Avignon, France.
E-mail address: annette.berard@paca.inra.fr (A. Bérard).
functions such as organic matter decomposition and mineraliza-
tion, nutrient mobilization and carbon sequestration (Reynolds
et al., 2003; Strickland and Rousk, 2010). Recent studies have
sought to assess the importance of microbial diversity, micro-
bial community composition and interactions between microbial
species for soil functioning (Bell et al., 2005). Also, the loss of
microbial functions is an indicator of decrease in soil quality
(Chapman et al., 2007). Hence it is useful to assess microbial
functional diversity to characterize soil quality and any decrease
it may undergo. Community-level physiological profiles (CLPPs),
usually assessed by carbon substrate utilization, are good tools
to evaluate the microbial functional diversity of a soil, and have
been widely implemented with the Biolog method (Calbrix et al.,
2005). Alternative microplate methods derived from Biolog were
devised for fungi (Buyer et al., 2001; Dobranic and Zak, 1999).
However, these techniques are limited to the assessment of
the extractable and cultivable fraction of soil microbial com-
munities, and need long incubation times to induce microbial
selection and growth. A respirometric technique based on the
analysis of the substrate-induced respiration (SIR) response of
whole-soil samples was investigated with a multiple carbon-
source substrate for CLPP by Degens and Harris (1997). However,
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http://dx.doi.org/10.1016/j.ecolind.2012.05.002