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Biological Conservation
journal homepage: www.elsevier.com/locate/biocon
Land-use change is associated with a significant loss of freshwater fish
species and functional richness in Sabah, Malaysia
Clare L. Wilkinson
a,b,c,
⁎
, Darren C.J. Yeo
b
, Tan Heok Hui
c
, Arman Hadi Fikri
d
, Robert M. Ewers
a
a
Department of Life Sciences, Imperial College London, Silwood Park, Silwood Park, Buckhurst Road, Ascot, Berkshire, SL5 7PY, UK
b
Department of Biological Sciences, National University of Singapore, 14 Science Drive 4, Singapore 117543, Republic of Singapore
c
Lee Kong Chian Natural History Museum, National University of Singapore, 2 Conservatory Drive, Singapore 117377, Republic of Singapore
d
Institute of Tropical Biology & Conservation, Universiti Malaysia Sabah, Malaysia
ARTICLE INFO
Keywords:
Deforestation
Freshwater fish
Land-use change
Oil-palm
Southeast Asia
ABSTRACT
Global biodiversity is being lost due to extensive anthropogenic land cover change. In Southeast Asia, biodi-
versity-rich forests are being extensively logged and converted to oil-palm monocultures. The impacts of this
land-use change on freshwater ecosystems, and particularly on freshwater biodiversity, remain largely under-
studied and poorly understood. We assessed the differences between fish communities in headwater stream
catchments across an established land-use gradient in Sabah, Malaysia (protected forest areas, twice-logged
forest, salvage-logged forest, oil-palm plantations with riparian reserves, and oil-palm plantations without ri-
parian reserves). Stream fishes were sampled using an electrofisher, a cast net and a tray net in 100 m long
transects in 23 streams in 2017. Local species richness and functional richness were both significantly reduced
with any land-use change from protected forest areas, but further increases in land-use intensity had no sub-
sequent impacts on fish biomass, functional evenness, and functional divergence. Any form of logging or land-
use change had a clear and negative impact on fish communities, but the magnitude of that effect was not
influenced by logging severity or time since logging on any fish community metric, suggesting that just two
rounds of selective impact (i.e., logging) appeared sufficient to cause negative effects on freshwater ecosystems.
It is therefore essential to continue protecting primary forested areas to maintain freshwater diversity, as well as
to explore strategies to protect freshwater ecosystems during logging, deforestation, and conversion to plantation
monocultures that are expected to continue across Southeast Asia.
1. Introduction
Anthropogenic land cover change through agricultural expansion
and intensification is currently a major driver of global biodiversity loss
(MEA, 2005; Phalan et al., 2013). The destruction of tropical forests is
of particular significance owing to the disproportionately high levels of
biodiversity present in the tropics (Bradshaw et al., 2009; Laurance
et al., 2012), marked declines in biodiversity when tropical forest is
converted to other land-use types (Phalan et al., 2013), and the una-
bated levels of deforestation due to increasing human demands for
food, timber and other products (Sodhi et al., 2004; Wilcove et al.,
2013). Large areas of logged forest and agriculture will be key features
of future tropical landscapes. Primary forests are critically important for
conserving tropical biodiversity (Gibson et al., 2011) and once-logged
forests in Southeast Asia have high conservation value for terrestrial
taxa (Edwards et al., 2014), but focussing on these habitats alone is not
sufficient. The impacts of this large scale land-use change and other
anthropogenic activities on freshwater ecosystems and biodiversity in
tropical streams remains largely understudied and poorly understood
(Ramirez et al., 2008). It is important to understand how these chan-
ging landscapes impact upon aquatic as well as terrestrial biodiversity,
and to devise strategies that provide protection mechanisms.
The most widespread and destructive threat to aquatic ecosystems is
habitat modification that results from converting natural areas to
agricultural land (Allan and Flecker, 1993; Laurance et al., 2014). Ex-
tensive logging and deforestation across the tropics (Achard et al.,
2002; Hansen et al., 2010) has caused large scale modifications to
catchments, resulting in changes in water quantity, quality, de-regula-
tion in stream hydraulics and increased sedimentation levels (Inoue and
Nunokawa, 2005; Iwata et al., 2003). The effects of deforestation on the
species richness of fish are variable. Species richness can be increased
(Lorion and Kennedy, 2009), decreased (Brook et al., 2003; Toham and
Teugels, 1999), or unaffected (Bojsen and Barriga, 2002) by tropical
deforestation, with equally variable impacts on fish community
https://doi.org/10.1016/j.biocon.2018.04.004
Received 27 November 2017; Received in revised form 22 March 2018; Accepted 2 April 2018
⁎
Corresponding author at: Imperial College London, Silwood Park, Buckhurst Road, Ascot, Berkshire, SL5 7PY, UK.
E-mail address: clare.wilkinson12@imperial.ac.uk (C.L. Wilkinson).
Biological Conservation 222 (2018) 164–171
0006-3207/ © 2018 Elsevier Ltd. All rights reserved.
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