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OPINION
Exploiting plant drought stress biology to increase resourceuse efficiency and yield of crops under water scarcity
William J. Davies
Received: 5 September 2013 / Accepted: 6 September 2013
� The Author(s) 2014
Increasing the availability of food to meet a growing
global demand is one of the greatest challenges facing
humankind in the twenty-first century. Accelerating
trends in urbanization, environmental degradation,
and climate change as well as a host of social issues all
hinder our ability to feed the world’s growing human
population, projected to exceed 9 billion by 2050
(Godfray et al. 2010).
We fully recognize that increased food security is
not just about producing more but it seems perverse to
argue, as has often been the case, that we already
produce enough food (and have the science to
underpin its delivery!) and focus solely on the many
other issues underpinning the food system. Rather, we
argue here that there are many opportunities available
to exploit existing science via both crop improvement
and crop management, to increase potential yield,
reduce the yield gap and increase the efficiency of
resource use in agriculture (e.g. Foulkes et al. 2010). In
addition, addressing some of the grand challenges of
plant science (Reaping the Benefits, The Royal
Society of London 2009) provides substantial oppor-
tunities to move towards these targets.
Many countries in the world have responded to the
challenge of increasing global food insecurity by
focusing efforts on increasing food production. For
example, in China between 1949 and 2011, total grain
output increased by fivefold from 113 to 571 MT (Fan
et al. 2012), while per capita grain production grew
from 209 to 424 kg/year (National Bureau of Statistics
of China 2012). This marked achievement, which is an
inspiration to researchers and producers in many parts
of the world, is attributed to the introduction of new
genetic material and new intensive cropping systems
but largely to massive increases in the use of irrigation,
fertilizer, and other agricultural chemicals (Zhu and
Chen 2002). However, resulting environmental issues
such as reduced ground water levels, water contam-
ination from diffuse pollution (Kang et al. 2008) and
soil acidification are now causing concern in many
parts of the world. Hence, whether or not grain
production can grow in a sustainable way to meet
increasing global demand remains an open question.
For many parts of the world, water availability for
agriculture is recognized as a significant and growing
limitation. For example, on the North China Plain
(NCP) a crucial food producing region for China, a
winter wheat crop will consume around 450 mm of
water while annual precipitation averages only
500 mm. Furthermore, only 20–30 % of the precipi-
tation occurs during the winter wheat growing season
and therefore the crop relies heavily on irrigation. In
this region, around 70 % of water used in agriculture is
derived from groundwater. Excessive mining of
groundwater aquifers in many parts of the world has
caused water tables to recede from a few meters below
the soil surface in 1970s to 30 m or more (e.g. Kang
W. J. Davies (&)
Lancaster Environment Centre, Lancaster University,
Lancaster LA1 4YQ, UK
e-mail: [email protected]
123
Theor. Exp. Plant Physiol.
DOI 10.1007/s40626-014-0004-4
et al. 2008), an enormous problem for farmers and for
the natural environment. The total groundwater
reserves in the NCP are around 75 billion tons.
Assuming realistic water use efficiencies for wheat
and maize, Li et al. (2013) calculate that to attain the
wheat and maize output required for an appropriate
contribution to national yield targets for 2030, would
require nearly 100 billion tons of water. Climate
change predictions suggest that in future, an even
bigger mismatch between supply and demand is likely.
Calculation like these suggest that in most regions
of the world either there already is, or there will be, a
shortfall in the availability of water for agriculture and
that to sustain yields and minimize environmental
impact, we must seek to exploit plant drought stress
biology to increase resource use efficiency and yield of
crops. This can be done through modified management
practices (e.g. deficit irrigation) (Davies et al. 2011).
Optimisation of these methods (and also the produc-
tion of drought resistant genotypes) requires some
understanding of how droughted plants regulate yield.
In this paper we focus upon the need to understand the
role of phytohormones in both vegetative and repro-
ductive development of crops. We argue that it is
important to discriminate effects of altered chemical
status and water status, as many studies indicate that
cereal crops can maintain turgor in vegetative and
reproductive structures in the field in response to a
range of environmental challenges. Environmental
effects on yield development in cereals can be
extremely subtle. For example, Boyer (1982) has
shown that even well irrigated, well fed crops in the
USA may yield only 20 % of potential yield values.
We believe that hormonal and other chemical signals
have an important role to play in regulating yield, even
in plants that are to all appearances ‘unstressed’.
Deficit irrigation (DI) techniques have generated
substantial increases in water use efficiency and mild
water deficits can, if scheduled appropriately, actually
increase yields as result of modified partitioning to
grains (Yang and Zhang 2010). DI may also enhance
food safety (Price et al. 2013). We suggest that
appropriate operation of these techniques and progress
towards the development of new genotypes with
improved yielding and water productivity under
drought might be made via exploitation of new
understanding of the involvement of ethylene, ABA
and CK in yield regulation. Modified trait screening for
drought productivity might include physiological
variables such as maximal stress ethylene production
(‘‘eth-max’’), ABA-ACC/ethylene concentration
ratios (Yang et al. 2007) and sensitivity of plant
development and physiology to ethylene and
ABA:Eth. Maximal ethylene production can be wheat
genotype-dependent in response to stress (Balota et al.
2004). Exploitation of this kind of information might
be achieved by combining relevant physiological traits
(PTs) deterministically whereby progeny might show,
for example, expression of low Eth-max and/or
appropriate ABA:Eth with additional stress adaptive
traits in elite agronomic backgrounds. This approach
might allow the development of a crop that is resilient
under a combination of stresses. To accelerate genetic
gains in yield in the future, it is now accepted that
complex physiological traits can be incorporated as
additional criteria in more conventional trait selection
programmes (e.g. Lopes and Reynolds 2010) but it will
be necessary to carefully define targets and environ-
ments. Impacts might be assessed across a broad range
of scenarios via modeling of G 9 E 9 M (genet-
ics 9 environment 9 management) (Tardieu (2012).
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