Soil degradation is a long-term
reduction in the soil’s ability to provide ecosystem services (in particular food
production and carbon sequestration). It is primarily caused by
agriculture – both directly via poor land management and indirectly via
deforestation. 1/3 of the world’s soils are now
considered degraded. This means (a) less food and (b) less carbon storage.
To avoid widespread famine and catastrophic climate change we
must restore currently degraded soils, prevent future degradation and
sustainably enhance both agricultural production and carbon sequestration via good soil management techniques. (Growing
plants without soil is possible but unlikely to provide a global solution.)
Will soil be the cause of our downfall or the key to our salvation? The choice is
in our hands…
We know burning fossil fuels is bad because it emits CO2 (a
greenhouse gas)… but did you know that soils emit CO2 too?!
Some of these ‘emissions’ are natural, but poor soil management has significantly increased
them, accelerating climate change. HOWEVER, soils can also absorb
CO2, which could help mitigate climate change. The balance between emission
and absorption determines whether soils are a carbon source (bad) or sink
(good). Let’s investigate …
How much carbon is stored in the soil? Around 2700Pg (Pg = petagram = 1015g
= 1 billion tonnes) of carbon is stored in the soil globally. This consists of~40% inorganic carbon (SIC), mainly
carbonates and ~60% organic carbon (SOC). SOC is more dynamic (more
easily lost and restored), so this post will focus on SOC. All SOC values are
estimates that have varied widely over recent decades, as shown in the graphbelow. Total SOC is currently estimated at ~1500Pg.
Fig. 1. Estimates of global soil organic carbon stocks from the
literature through time. Median across all estimates 1460.5 Pg C, range
504–3000 Pg C, n = 27 studies, based on spatially explicit (red; median 1437 Pg
C, range 504–2469.5 Pg C, n = 7) and nonspatially explicit methods (blue;
median 1388.5 Pg C, range 710–3000 Pg C, n = 20). Lines connect minimum and
maximum estimates of soil organic carbon reported by the same study. (Source:
Scharlemann et al., 2014)
Is 2700Pg a lot or a little? To give some sense of scale I’ve
placed these values in the context of the 5 main global carbon pools in the diagram
below. (The circles aren’t drawn to scale because the oceanic pool
is comparatively so large).
Fig. 2 The five major global carbon pools along with the % of total carbon that they contain (diagram drawn by me but based on data from Lal, 2008 and Scharlemann et al., 2014)
WOW – the oceans vastly overshadow the other four pools! However soils
are clearly still significant. They store over 3 times as much as the
atmosphere and around 4 times as much as all living organisms. In fact, soils
are responsible for most of the biotic storage because ~80-90% of this is land plants.
The SOC budget: The mass of SOC depends on the balance
between inputs and outputs (Fig.3), just as the water level in a bathtub is determined
by the flow rate in through the tap and out through the drain. The diagram below
shows the main inputs and outputs to the ‘SOC bath’.
Fig. 3 The balance between carbon inputs and
outputs determines the quantity and flux of the soil organic carbon pool
Fig. 4 Soil organic carbon budget represented as water in a bath along
with the main carbon inputs and outputs (diagram made by me).
Distribution of SOC: SOC levels vary globally. The first map
below shows large-scale SOC trends that result from differences in climate. The
most carbon rich soils are found in cold, often waterlogged, northern regions where oxidation of organic matter is slow. The second map shows carbon
stored in the terrestrial biome. Dr Ed Tanner, co-author of these maps,
explained that, “if we’re interested in conserving carbon, which we ought to
be, we ought to conserve soils in temperate regions, and plants in tropical
regions”.
Fig. 5 (A) global distribution of soil organic carbon (SOC) storage
(tons of C ha-1) to 1m depth based on Harmonized World Soil Database
version 1.1; (B) global distribution of biotic carbon storage (tons of C ha-1)
(Source: Scharlemann et al., 2014)
Are we losing SOC? Yes! Cultivated (although not all) soils have lost
between 50-75% of their original SOC pool. But remember that only
chemical SOC loss increases atmospheric CO2. Depletion of SOC has so
far contributed about 78±12 Pg C to the atmosphere.
Land-use change has contributed a further 136±55 Pg C. This compares to an
estimated 270±30 PgC contributed by fossil
fuel combustion.
Fig. 6 The historic CO2 emissions from the pedologic,
biotic and geologic carbon pools into the atmosphere (based on data from Zomer et al., 2017)
Why are we losing SOC?
(1) Land use change from forests to agriculture has reduced organic
inputs because the crops that replaced the trees are harvested, not left
as litter when they die. (2) Conventional ploughing increases the exposure of soil to air,
which increases the rate of oxidation.(I
had no idea that ploughing was such an issue!).
(3) You may imagine the carbon rich soils of the Northern hemisphere are safe
because these areas are too cold for agriculture... but unfortunately not.
Increased temperatures due to climate change are predicted to increase rates of decomposition and
therefore increase the amount of CO2 they
release, triggering a positive feedback loop.
Increased CO2 = more photosynthesis = more
terrestrial carbon storage… this makes sense but:
(1) there still needs to be land available for this extra plant
growth (2) a recent paper found
that increased atmospheric CO2 levels may also increase
soil microbial activity and thus the rate of SOC decomposition. The authors
estimate that this would largely neutralise the positive effect of increased
photosynthesis, suggesting that ‘nature may not be as efficient at slowing global warming as we
previously thought’.
Fig. 8 Increased atmospheric CO2 may
increase photosynthesis (which absorbs CO2) but it may also increase
the rate of microbial decomposition of soil organic matter (which releases CO2).
These two processes are predicted to balance each other out.
How can we increase soil carbon? (1) Reforestation/afforestation (2) Soil management techniques such as retention of crop residues, cover cropping and no till planting (see video below). A recent paper estimates that altering land
management practices on cropland could sequester up to 1.85Pg of carbon per
year. This is around 25% of fossil fuel CO2 emissions (~7.5-8Pg yr-1),
equal to the transportation sector’s current carbon emissions!!!
(3) There is a limit to sequestering carbon using the above techniques and this is approximately equal to the
historic C loss (~80Pg). Adding biochar (i.e. charcoal used for soil amendment) to
soils has been proposed as a method of surpassing this limit. Biochar is stable, resistant to
microbial degradation and can remain in the soil for millennia. Using data from the World Bank, I calculated that adding ~70 t/ha
of biochar to all cultivated soils would sequester enough carbon to return
atmospheric CO2 to pre-industrial levels.
Fig. 9 A fine textured biochar that could be added
to the soil to help sequester carbon (Source: NOVA – PBS, 2015)
(4) Let’s not entirely forget
SIC. When silicate rocks are exposed to air and water they react with CO2
to form innocuous bicarbonates. These are then stored in the soil or washed into the
oceans. For the magnesium-silicate
olivine, the reaction is as follows:
Current agricultural practices are causing
soils to emit more CO2 than normal, accelerating climate change. Rising
temperatures may further increase these emissions (particularly on unfarmed
northern soils), creating a positive feedback loop. Changing agricultural
practices could restore much of the SOC that has been lost. Addition of biochar
and accelerated silicate weathering could then increase soil carbon storage
beyond natural levels. Converting soil from a carbon source to a carbon sink
could be a key strategy to mitigating climate change.