Increased agricultural production through both intensification and extensification is a major driver of the current biodiversity crisis. As a response, two contrasting approaches have been advocated: ‘land sparing’, which minimizes demand for farmland by increasing yield, and ‘land sharing’, which boosts densities of wild populations on farmland but decreases agricultural yields. While these approaches have been useful in drawing attention to the impact of meeting the growing global demand for agricultural products on biodiversity, they have been driven mainly by conservation ecologists, and have often overlooked important issues related to farming. As agronomists with practical experience in developing, testing and scaling alternative forms of agriculture in some of the most biodiversity-rich areas of Latin America, Eastern and Southern Africa and South Asia, we are pointing in this paper at what we see as being two major limitations of the land sparing/sharing framework: (1) the reliance on yield-density relationships that focus on trade-offs and overlook synergies between agriculture and biodiversity, and (2) the overemphasis on crop yield, neglecting other metrics of agricultural performance which may be more important to local farmers, and more strongly associated with positive biodiversity outcomes. It is our hope that this paper will stimulate other agricultural scientists to contribute to the land sparing/sharing framework, in order to develop together with conservation ecologists viable solutions for both improved agricultural production and biodiversity conservation.
1st lunch meeting - 18 August 2021 - Frédéric Baudron
1. Sparing or sharing land?
Views from agricultural scientists
Frédéric Baudron, Systems Agronomist, CIMMYT Zimbabwe
SIP/SEP Zimbabwe lunch meeting, 18th August 2021
2.
3. (WWF 2020)
(Rockström et al. 2009)
Maintaining the Earth system into the
only state, supporting life as we know it
4. Tropical forests: climate regulation and regulation of
rainfall patterns (Zheng and Eltahir 1998, Fu 2003,
Bonan 2008)
Great whales: nutrient cycling, ocean primary
productivity & carbon sequestration (Roman and
McCarthy 2010, Lavery et al. 2014, Roman et al., 2014)
Gray wolves: reducing over-browsing of riparian
vegetation by elks and impacting the morphology of
rivers (Beschta and Ripple 2012)
Salmon: moving nutrients from marine to terrestrial
ecosystems (Gende et al. 2002, Doughty et al. 2015)
Maintaining the Earth system into the only state
we know can support human development
5. Many emerging infectious diseases (incl. COVID-19
pandemic) have root causes in biodiversity loss
6. For the majority of species, most populations
are found in land it shares with people…
• Human population tends to be
concentrated in areas rich in
biodiversity
– 80% of the land area that is of
priority for the conservation of
mammals is occupied by
agriculture (Ceballos et al. 2005)
• PAs only cover 5.1% of all
terrestrial land (Hoekstra et al., 2005)
– Numerous ‘gap species’ not
represented in the global network
of protected areas
• Most ice-free land is occupied or
used by humans (Ellis and
Ramankutty, 2008)
(Ceballos et al. 2005)
(Baldi et al. 2017)
7. (Maxwell et al. 2016)
Change in agricultural practices is the 2nd biggest
‘killer’ for 62% of (nearly) threatened species
8. Both agricultural expansion &
agricultural intensification are implicated
Biotic additions
Biotic removal
Altered biogeochemical
cycles
Altered hydrological
cycles
Altered species
habitats
Increased use of
pesticides
9. In response: land sparing vs
land sharing
• Land sparing (a.k.a. ‘Borlaug hypothesis’)
(Green et al., 2005; Balmford et al., 2019; Borlaug,
2007; Phalan et al., 2011)
– Concentrating production on areas as small as
possible by maximizing yield
– Segregation of production & conservation into
distinct land units
• Land sharing (a.k.a. ‘wildlife friendly farming’)
(Green et al., 2005; Clough et al., 2011; Perfecto
and Vandermeer, 2010; Wright et al., 2012)
– Minimizing the use of external inputs & retaining
patches of natural habitat within farmlands
– Integration of production & conservation within
the same land units
Land sparing
Land sharing
10. Sparing or sharing land?
• Heated debate since the seminal
paper of Green et al. (2005)…
• … but largely confined to the circle
of conservation ecologists
– minimizing the negative impact of
farming to biodiversity, not solving
trade-offs
• Views from agricultural scientists:
– Reliance on yield-density
relationships: not enough attention
paid to synergies between
agriculture and biodiversity
– Too much emphasis on crop yield,
neglecting other metrics of
agricultural performance
Yield-density relationships
classically used by
conservation ecologists
11. 1.1. Agriculture supporting biodiversity
• Many species find complementary
resources in different land covers
• Several species are totally dependent on
farmland (e.g., including open-habitat bird
species)
– In many landscapes, agriculture is often the
only force creating open patches in an
otherwise homogeneous forest cover
• Clear cases of coexistence
– Cacao & coffee tropical agroforests
structurally similar to native tropical forest
– Livestock coexisting with wildlife in savannas
(+ facilitation)
– Biomass production systems
– Human-wildlife coexistence in many
landscapes dominated by agriculture
(Colding et al. 2007)
12. 1.2. Biodiversity supporting agriculture
• Land sparing would threaten low-input
smallholder production systems by
disconnecting them from ES
• ES are important for all other
production systems as well
– 25% of croplands & 33% of grassland
globally are degraded (Le et al., 2016)
– Declining global consumption of
insecticides (Zhang, 2018), but
increasing crop losses due to pests
(e.g., CC; Deutsch et al., 2018)
– The global decline in pollinators also
led to a decline in the yield of several
crops (Garibaldi et al., 2009)
• Agroecology, ecological intensification,
regenerative agriculture, nature-based
solutions for agriculture, etc
13. 1.3. Yield- vs. input-density relationships
• A simple direct & positive
relationship is often assumed in
land sparing:
+ inputs + yield - biodiversity
• Reducing input further in many
parts of the Global South would be
a threat to agricultural production &
the environment
• Alternatives to increased input use
(to achieve land sparing) & reduced
input use (to achieve land sharing)
– Increasing input use efficiency:
precision ag, mechanization etc
– Reducing spillover of inputs:
conservation agriculture,
agroforestry, etc
14. 2.1. Crop yield is a too narrow evaluation of ag performance
• Systematic review in Scopus in
November 2020
• Keywords ‘land sparing’ and ‘land
sharing’
• 195 articles
• 161 articles related to LSS
• 65 reviews or essays
• 96 empirical or modeling
papers
15. 2.1. Crop yield is a too narrow evaluation of ag performance
(Baudron et al. 2017, 2019; Duriaux Chavarria et al. 2018; Wood et al. 2018)
Simple Intermediate Diverse
16. 2.2. High yields may not be the primary objective of farmers
• Most farms, even in the most remote
areas, are connected to markets to
some degree (Frelat et al., 2016)
– The link between yield and profitability
is not direct (Baudron et al. 2019)
• Labour productivity may be more
important than land productivity (e.g., in
sparsely populated areas; Baudron et al.,
2012)
– Many technologies increasing yield also
tend to increase labour input (Dahlin and
Rusinamhodzi, 2019)
• Extensification for land appropriation
& speculation (Demont et al., 2007;
Roebeling and Hendrix, 2010)
• Farming style (Van der Ploeg, 1994;
Leeuwis, 1993)
17. 2.3. Looking beyond the plot
• LSS focuses on yield – a plot-
level process – & thus ignores
processes at higher scales
– Landscape composition &
configuration could be more
important than farming intensity
(Benton et al., 2003; Kleijn et al.,
2004)
– ‘Ecological land-use
complementation’ (Colding, 2007)
• Losses & wastes, the majority
of which occurring on farm
(agricultural & postharvest
stages) in low-income countries
– Hermetic metal silos & bags
– Mechanization: harvesting,
shelling/threshing, transport
18. Conclusions
• Increased agricultural production is a major cause of the
current global biodiversity crisis
– The majority of vertebrates are projected to lose habitat to agriculture by
2050 (Williams et al., 2021)
– The Global Biodiversity Framework to be adopted by the CBD (vision
2050) ignores biodiversity outside of PAs! (Gassner et al., 2020)
• The land sparing/sharing framework has brought considerable
attention to the issue, but limited impact:
– Reliance on yield-density relationships (that focus on trade-offs and
overlook synergies)
– Evaluation of agricultural performance through the narrow lens of crop
yield only (neglecting other metrics of ag performance which may be
more important to local farmers).
• Complexity of the interactions between agriculture & biodiversity
• Call for further involvement of agricultural scientists in biodiversity
conservation in ‘working landscapes’
The Living Planet Index (measures the population abundance of 4392 vertebrate species around the world) declined by 68% between 1970 and 2016.
Off course we should conserve biodiversity for its intrinsic value, independent of any contribution it makes to human wellbeing, and we have an ethical responsibly towards other species, including a moral obligation not to eliminate them. But if this is not enough, we should acknowledge the irreplaceable role biodiversity plays in maintaining the Earth system in the only state we know can support life as we know it, including human development (and food production).
Adapting to more frequent extreme climatic events, mitigating climate change, regulating biogeochemical cycles, regulating hydrological cycles, remediating pollutants, etc
The connections between biodiversity and the Earth system run deep and are actually quite fascinating.
Tropical forests: 25% of the carbon in the terrestrial biosphere; cooling effect thanks to their high rate of evapotranspiration and their low albedo; deforestation has affected the Asian monsoon area (Fu, 2003) and rainfall patterns in West Africa.
Whales recycle nutrients from the depth of the ocean to its surface (‘whale pump’) and from high-latitude feeding areas and low-latitude areas (‘great whale conveyor belt’). Carbon sequestration in oceans through sinking carcasses of dead animals and by excreting limiting nutrients (N, Fe) that stimulate phytoplankton productivity.
Species moving nutrients against the entropic forces of erosion, from lowland to upland and from marine to terrestrial systems in the case of salmons.
Large predators having an influence on hydrological systems through trophic cascades (cascading effect to species lower in the trophic web, affecting the entire ecosystem).
With biodiversity found mainly in production landscapes, it is no surprise that changes in agricultural practices in these landscapes tend to have negative consequences on biodiversity
Change in crop production threatens 54% of these species and change in livestock production 26%
Either at a particular time (supplementation), or at different times in their life cycles (complementation)
In many landscapes, large wild herbivores that create and maintain patches of open vegetation have declined or have been extirpated
Message of negative correlation between agriculture and biodiversity conveyed by yield-density relationships
Positive correlations between biodiversity & yield are the basis of a broad basket of technologies
Exacerbating nutrient mining and land degradation, which could fuel in some cases agricultural expansion by farmers in search of new fertile land
The majority of farms in the Global South are mixed crop-livestock operations; a quarter of the global terrestrial surface is used for grazing
Fuelwood is another important product in many landscapes lacking alternative energy sources
Several studies have found more diverse and nutritious diets consumed by people living in more forested areas, which also tend to be more biodiverse
‘ecological land-use complementation’ = the clustering of land uses to
purposefully enhance supplementation and complementation (Colding,
2007).
We have the technologies and the analytics to make a contribution there.
I calculated 9 years of that the annual budget of the 4 largest conservation organizations (TNC, WCS, WWF, CI) is larger than the annual budget of CGIAR (>1.2 billion US$)