Biomedical Engineering Reference
In-Depth Information
Table 3.1
Classification of the
Miscanthus
species in Japan
Section
Species (scientific name)
Japanese name
Eumiscanthus
Honda
M. sinensis
Andersson
Susuki
M. sinensis
Andersson form.
gracillimus
(Hitch-
cock) Ohwi
Ito-susuki
M. sinensis
Andersson form.
zebrinus
(Nicholson)
Nakai
Takanoha-susuki
M. sinensis
Andersson form.
variegatus
Nakai
Shima-susuki
M. sinensis
Andersson var.
condensatus
Hachijyo-susuki
M. floridulus
(Labill.) Warburg
Tokiwa-susuki
Triarrhena
(Maxim.) Honda
M. sacchariflorus
(Maxim.) Bentham
Ogi
M. sacchariflorus
(Maxim.) Bentham var.
brevibarbis
(Honda) Adati
Ogi-susuki
M. sacchariflorus
(Maxim.) Bentham var.
glaber
Adati
Kariyasua
Ohwi
M. tinctorius
(Steudel) Hackel
Kariyasu
M. oligostachyus
Staff
Kariyasumodoki
M. intermedius
(Honda) Honda
Oohigenagakari-
yasumodoki
Fig. 3.2
A traditional style
of Japanese architecture
with a thatched roof
the land area of Japan in the early 1900s [
48
] but in recent years only have
constituted 4 % of the country [
49
], are comprised of several graminoid and forb
species, including
M. sinensis
and
M. sacchariflorus.
Between the two,
M. sinensis
dominates most of these highly diverse grasslands.
M. sinensis
grasslands in many
locations have been managed for hundreds of years in Japan by annual harvesting
and/or burning [
50
,
51
]. In the Aso mountain region of southern Japan, seminatural
grasslands have been maintained by annual harvests and/or burning for more than
1,000 years. Grassland ecosystems can contribute to carbon (C) mitigation through
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