Switchgrass is a perennial grass with a C4 photosynthetic pathway.
It is sown from seed and forms clumped growth above ground
and gradually spreading rhizomes below ground. It is distributed
across North, Central and South America and in parts of
Africa.
The stiff
erect stems grow to 0.5 – 2.5 m in height. There are
two main ecotypes, the lowland tall type with coarse leaves
and the
upland slower growing type with finer leaves but varieties
exist suited to a range of climatic conditions.
Agronomy
Seeds are sown using a small seed drill in spring into a well prepared
seed bed (ploughed and harrowed) at a depth of 1cm when soil
temperature has reached 10-15°C. Plant density can be up to 400
plants per m2, but in the UK a seed rate of 10kg / ha produced
a range of between 189-301 plants per m2 (Christian, 1994). Plants
will tolerate acid conditions but additions of lime to achieve
a neutral soil pH will produce best establishment and growth.
Fresh seed can have a high % of dormancy, thus to achieve a high
germination rate year old seed are often used. Switchgrass is highly frost tolerant, however, is not competitive
during the first year and therefore requires the elimination of
weed species (Vogel, 1995). Phosphorus and potassium may be added
to deficient soils to encourage seedling development, but nitrogen
additions to a new crop early in spring will encourage weed coverage
at a time when the crop is particularly susceptible to competition.
Treatment with pre-emergent herbicide is recommended, particularly
to combat broadleaved weeds. Switchgrass has a low nutrient demand,
as nutrients are transported to, and conserved within, the rhizome
before harvest. It displays efficient water-use so can tolerate
periods of dryness. Once established, switchgrass demonstrates
a good resilience to pest and disease.
Under good weed control, shoots emerge in late spring and senescence
starts with falling autumn temperatures. Crops can be harvested
during winter. Crops are harvested with a standard mower conditioner
and are baled to required sizes. Moisture content at baling is
variable at between 15-30% which is low enough to allow the crop
to be stored without a period of drying. The average yield for
the three best varieties in the UK at the end of a four year growing
period was 11t/ha dry matter per year but yields have reached up
to 18 odt/ha in south-east England (Bullard et al., 2004). Switchgrass
has a productive lifespan of 10-15 years. In the USA, Parrish et
al. (1993) demonstrated that 50 kg/ha Nitrogen additions produced
optimal results. Nutrient content at harvest is very low for switchgrass
which is beneficial to combustion efficiency and emission levels.
The crop is capable of producing an energy content of 18.4 MJ/kg.
Switchgrass is currently not considered a front-runner in the
search for viable and productive biomass crops in the UK. The main
reason for this is the required intensity of weed management needed
in the establishment phase of the crop. On a commercial scale this
level of unreliability makes switchgrass a high risk crop. However,
familiarity with the crop may develop to such a stage that low
establishment costs, high yields and standard management techniques
make it an attractive proposition. Alternative uses for switchgrass
include fodder, bedding, paper fibre, composite manufacture and
ethanol production (280 litres per tonne of dry matter).
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Bullard et al (2004) Identifying the yield potential of Miscanthus
x giganteus: an assessment of the spatial and temporal variability
of M. x giganteus biomass productivity across England and Wales.
Biomass and Bioenergy 26 (1): 3-13
Christian, D.G. (1994) Quantifying the yield of perennial grasses
grown as a biofuel for energy generation. Renewable Energy 5(2):
762-766.
Moser, L.E. & Vogel, K.P. (1995) Switchgrass, Big Bluestem
and Indiangrass. In: Barnes, R.F., Miller, D.A. and Nelson, C.J.
(eds) An introduction to grassland agriculture. Forages, 5th edn,
vol.1, Iowa State University Press, Ames, pp.409-420.
Parrish, D.J., Wolf, D.D. and Lee Daniels, W. (1993) Perennial
species for optimum production of herbaceous biomass in the Piedmont.
Management study, 1987-1991, ORNL/Sub/85-27413/7. National Technical
Information Service, US Departmrnt of Commerce, Springfield, USA.
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