Selection
Criteria
for
Hedgerow
Species
Litter
decomposition
and
nutrient
release
patterns
Nutrient
release
through
decomposition
of
hedgerow
biomass
can
be
synchronized
with
the
peak
period
of
crop
demand
by
regulating
the
quality,
quantity,
timing
and
method
of
application
of
tree
prunings
as
green
manure
or
mulch
(Nair
1993,
Palm
1995).
Studies
of
nutrient
release
patterns
have
mainly
focused
on
nitrogen
in
leguminous
species.
Prunings
from
various
leguminous
trees
used
in
alley
cropping
systems
differ
in
their
decomposition
dynamics
--
the
other
component
of
litter
quality
--
which
is
determined
in
a
large
part
by
their
chemical
composition.
Plant
materials
with
high
%N
(>
1.73)
and
low
C/N
ratio
(<
20)
decompose
rapidly
and
release
relatively
larger
quantities
of
mineralized
nitrogen
available
for
crop
uptake
(Palm
1995).
On
the
other
hand,
materials
of
high
C/N
ratio
tend
to
temporarily
immobilize
nitrogen
because
microbes
utilizing
the
additional
carbon
source
multiply
rapidly
and
draw
upon
the
nutrient
reserve
from
the
soil
(Nair
1993).
Nitrogen
incorporated
in
microbial
tissues
is
gradually
released
subsequently
when
the
microbial
population
declines.
Prunings
of
many
of
the
woody
nitrogen-fixing
legumes
used
in
alley
cropping
are
generally
high
in
nitrogen
(Nair
1993),
but
the
rates
of
decomposition
and
nutrient
release
vary
widely
and
are
not
necessarily
rapid.
In
a
field
study
by
Budelman
(1988)
in
Côte
d'Ivoire,
the
half-life
values
of
fresh
leaf
biomass
of
Leucaena
leucocephala
(C/N
=
12),
Gliricidia
sepium
(C/N=12)
and
Flemingia
macrophylla
(C/N=21)
were
found
to
be
31,
22
and
53
days
respectively.
In
a
review
of
laboratory
incubation
studies
by
Palm
(1995),
G.
sepium
consistently
released
a
higher
percentage
(30-70%)
of
its
nitrogen
compared
to
other
nitrogen
fixing
legumes
such
as
Calliandra
calothrysus
and
Inga
edulis,
which
released
less
than
20%
of
nitrogen
after
eight
weeks.
Palm
(1995)
suggested
that
the
polyphenol
to
nitrogen
(PP/N)
ratio
may
serve
as
an
index
for
short
term
immobilization
patterns
observed
for
legumes
with
relatively
high
polyphenol
content.
Laboratory
incubation
and
field
studies
found
that
legume
leaves
with
high
soluble
polyphenols
contents
(Inga
edulis
and
Cajanus
cajan)
decomposed
and
released
nitrogen
less
rapidly
than
those
with
low
polyphenol
contents
(Erythrina
sp.)
(Palm
and
Sanchez
1990,
1991).
The
lignin
plus
polyphenol
to
nitrogen
ratio
((LIG+PP)/N)
may
serve
as
an
index
for
longer
term
release
patterns
(Palm
1995).
Woody
stems
and
other
lignified
plant
materials
are
more
resistant
to
decomposition.
Despite
the
quantitative
importance
of
this
transfer
of
nutrients
from
the
hedgerow
biomass
to
soils
in
the
alleys,
uptake
by
the
crops
of
the
nutrients
released
from
the
mulch
is
often
quite
low.
Recovery
values
are
generally
less
than
20%
and
more
frequently
closer
to
10%
(Palm
1995).
By
labeling
the
nitrogen
in
the
mulch
(from
hedgerow
G.
sepium
and
Erythrina
poeppigiana)
with
the
isotope
15N,
Haggar
et
al.
(1993)
found
that
only
about
10%
of
the
total
nitrogen
taken
up
by
alley-cropped
maize
during
the
cropping
season
came
from
the
most
recently
applied
mulch.
The
majority
of
the
nitrogen
ends
up
in
some
readily
mineralized
fraction
of
SOM,
and
the
high
rates
of
mineralization
seen
in
the
alley
crop
represented
the
residual
effect
of
the
previous
years
of
mulch
application.
Haggar
et
al.
(1993)
suggested
that
the
benefit
of
leguminous
biomass
inputs
to
crop
production
is
through
the
long-term
buildup
of
soil
organic
nitrogen
rather
than
the
direct
release
of
nitrogen
from
the
decomposing
mulch.
Other
possible
reasons
for
the
low
nutrient
recovery
rates
in
the
crops
include
insufficient
synchrony
of
nutrient
release
with
crop
uptake,
leaching
and
volatilization
of
nitrogen,
and
re-absorption
of
the
nutrients
released
by
hedgerow
trees
(Fernandes
et
al.
1993a,
Kang
and
Mulongoy
1992).
Annual
crops
have
well-defined
critical
periods
of
high
nutrient
demand.
The
efficiency
of
nutrient
use
can
be
enhanced
if
nutrients
are
made
available
during
this
time,
which
can
also
reduce
nutrient
loss
to
leaching
and
to
hedgerow
trees.
Better
synchrony
and
nutrient
use
efficiency
can
be
accomplished
through
management
decisions
such
as
selecting
species
with
differing
rates
of
litter
decomposition;
adjusting
the
timing
of
pruning
and
addition
of
tree
biomass
to
soil;
and
modifying
the
method
of
tree
biomass
application
(surface
addition
as
mulch
or
soil
incorporation
as
plowed-in
green
manure)
(Nair
1993).
Introduction
|
Definition
|
Hedgerow
Species
I
Species
Selection
Criteria
|
Soil
Organic
Matter
&
Nutrients
|
System
Management
|
Crop
Yields
|
Soil
Conservation
|
Weed
Dynamics
|
Tree-Crop
Competition
|
References
BACK
Funded
by
a
grant
from
the
Cornell
Agroforestry
Working
Group
(CAWG)
and
the
Distance
Learning
Program
of
the
Cornell
International
Institute
for
Food,
Agriculture
and
Development
(CIIFAD).