Julie 2017
20
soil fertility management
Part 1: Theoretical principles and practices
I
n South Africa, crop production sys-
tems based on intensive and continuous
soil tillage have led to excessively high
soil degradation rates with a reduction
in natural soil fertility in areas under grain
production. It also results in the consis-
tent recommendation of the use of huge
quantities of chemical fertilisers that are
biologically unnecessary, economically ex-
travagant and ecologically damaging.
Tillage results in the oxidation and destruc-
tion of carbon in the soil by increasing the
soil oxygen levels, thereby promoting bac-
teria populations to expand and consume
active carbon in the soil. Soil organic car-
bon, or soil organic matter, is the key ele-
ment that drives soil health, which in turn
is the primary factor having an impact on
sustainable crop production.
If sound farming practices are sustained
over time, soil health improvement could
significantly escalate, influenced by posi-
tive changes in a wide spectrum of soil pa-
rameters, including soil fertility, which then
result in improved productivity and profit-
ability of farming systems.
There is general agreement among key
stakeholders in South Africa, that soil health
and sustainable crop-livestock production
will only be achieved through the adoption
and implementation of conservation agri-
culture (CA) principles and practices.
CA is seen as an ideal system for sustain-
able and climate-smart agricultural inten-
sification and regeneration, through which
producers can attain higher levels of pro-
ductivity and profitability, while improving
soil health and the environment.
One of the good agricultural practices as-
sociated with CA is integrated soil fertility
management, which essentially depends on
locally adapted CA principles and practices
to build-up soil health, allowing producers
to reduce the use of fertilisers, while sus-
taining good and stable yields and increas-
ing profitability.
This understanding is important if we wish
to sustain productivity at the lowest pos-
sible costs, both economic and ecological.
Without being able to go into details, this
article aims to provide a few principles, ad-
vantages and examples of integrated soil
fertility management.
Integrated soil fertility
management
This concept of integrated soil fertility
management emphasises the maximisa-
tion of nutrient use efficiency, the enhanced
access of soil nutrients to plant roots, the
response of soil as a living ecosystem and
the role of sound locally adapted soil man-
agement practices enhancing ecosystem
functions and services leading to improved
soil fertility.
The concept acknowledges that neither
practices based solely on mineral fertilisers
nor solely on soil ecosystems services are
sufficient for sustainable crop production,
especially during the transition years after
starting with CA on degraded soils.
It also requires well-adapted, disease- and
pest-resistant germplasm, as well as other
good agricultural practices. The critical soil
ecosystem processes involved are trans-
formations of carbon, cycling of nutrients,
maintenance of the structure and fabric
of the soil and biological regulation of soil
populations.
Ways to increase nutrient
use efficiency
Nutrient use efficiency, which may be de-
fined as the yield obtained per unit of avail-
able nutrients in the soil (supplied by the
soil and fertilisers), could be improved as
follows:
Adjustment of fertiliser application rates
based on (natural) soil fertility levels tak-
ing account of soil organic carbon level,
organically bonded nutrients, nutrient
cycling and/or previous cropping prac-
tices, especially legumes and their resi-
due biomass.
Apply fertiliser at the right time and
place, using the right source.
Plant crops at the right planting density
having enough plants to ensure optimal
and efficient nutrient access and yield.
In CA higher planting densities (around
30% higher than the norm) or at least
above 22 000 plants per hectare ensure
effective use of soil nutrients and wa-
ter in the whole soil profile and surface
area, while reducing temperature at soil
surface level.
CA principles and prac-
tices enhancing integrated
soil fertility management
Many producers world-wide have achieved
large improvements in soil health in a rela-
tively short time. What are these producers
doing differently?
Minimum soil disturbance
Physical soil disturbance, such as tillage
with a plough, disk, or chisel plough, that
results in bare or compacted soil is destruc-
tive and disruptive to soil microbes and
creates a hostile, instead of hospitable,
place for them to live and work (
Photo 1
).
The soil may also be disturbed chemically
or biologically through the misuse of inputs,
such as fertilisers and pesticides. This dis-
rupts the symbiotic relationship between
micro-organisms and crop roots. By stra-
tegically reducing chemical inputs, we can
take advantage of these soil ecosystem ser-
vices to allow plants to freely access essen-
tial nutrients.
Diversify with crops
and animals
Sugars made by plants, through the miracle
of photosynthesis, are released from their
roots into the soil as liquid carbon and trad-
ed to soil microbes for nutrients to support
plant growth. This soil ecosystem service is
a vital element of healthy soils and can be
enhanced through the inclusion of as many
different plants and animals as practical.
Livestock utilising cover crop mixtures, for
example, contribute to this diversity.
With ultra-high-density grazing utilising
30% to 50% of available material, livestock
can stimulate root development and re-
cycle 80% of nutrients in the form of dung
(
Photo 2
). Biodiversity directly leads to-
wards a diverse array of soil microbes from
a range of functional groups, which again
improves the soil’s ability to support nutri-
ent dense, high vitality crops, pastures, fruit
and vegetables.
FOCUS
Fertiliser
Special
DR HENDRIK SMITH,
conservation agriculture facilitator, Grain SA and
GERRIE TRYTSMAN,
ARC-DPI