Plant Physiol. (1999) 119: 1423-1436
Fluxes of Reserve-Derived and Currently Assimilated Carbon and
Nitrogen in Perennial Ryegrass Recovering from Defoliation. The
Regrowing Tiller and Its Component Functionally Distinct
Zones1
Hans Schnyder* and
Ries de Visser
Chair of Grassland Science, Technische Universität
München, D-85350 Freising-Weihenstephan, Germany (H.S.); Research Institute of Agrobiology and Soil Fertility (AB-DLO),
P.O. Box 14 NL-6700 AA Wageningen, The Netherlands (R.d.V.); and Institut für Pflanzenbau, Universität Bonn, Katzenburgweg
5, D-53115 Bonn, Germany (H.S.)
 |
ABSTRACT |
The quantitative significance of
reserves and current assimilates in regrowing tillers of severely
defoliated plants of perennial ryegrass (Lolium perenne
L.) was assessed by a new approach, comprising C/12C and 15N/14N
steady-state labeling and separation of sink and source zones. The
functionally distinct zones showed large differences in the kinetics of
currently assimilated C and N. These are interpreted in terms of
"substrate" and "tissue" flux among zones and C and N turnover
within zones. Tillers refoliated rapidly, although C and N supply was
initially decreased. Rapid refoliation was associated with (a)
transient depletion of water-soluble carbohydrates and dilution of
structural biomass in the immature zone of expanding leaves, (b) rapid
transition to current assimilation-derived growth, and (c) rapid
reestablishment of a balanced C:N ratio in growth substrate. This
balance (C:N, approximately 8.9 [w/w] in new biomass) indicated
coregulation of growth by C and N supply and resulted from
complementary fluxes of reserve- and current assimilation-derived C and
N. Reserves were the dominant N source until approximately 3 d
after defoliation. Amino-C constituted approximately 60% of the net
influx of reserve C during the first 2 d. Carbohydrate reserves
were an insignificant source of C for tiller growth after d 1. We
discuss the physiological mechanisms contributing to defoliation tolerance.
 |
INTRODUCTION |
Photosynthesis decreases drastically when a plant is defoliated as
a consequence of grazing or mowing (Davidson and Milthorpe, 1966b
;
Richards, 1993
). Also, root growth (Davidson and Milthorpe, 1966b
) and,
with some delay, N uptake (Jarvis and Macduff, 1989
) and assimilation
(Macduff et al., 1989
) are transiently depressed, most likely as a
result of decreased assimilate availability to roots. Clearly,
refoliation and, thus, the restoration of active photosynthesis are the
crucial elements of a plant's response to severe defoliation.
Refoliation may be controlled by the availability of substrate to the
(re)growing shoot (source control) or by meristematic constraints (sink
control). Sink control may be important where defoliation involves the
removal of all or most of the currently expanding leaf tissue and
active shoot meristems, thus requiring the activation of dormant
meristems for refoliation (such as in dicots with orthotropic stems,
e.g. alfalfa or caespitose grasses after apex elevation, compare with
Richards, 1993
). Conversely, where defoliation is severe but all active
meristems and expanding leaf tissue are left behind intact (such as in
grasses during vegetative growth), source control of regrowth is
likely.
A critical role of carbohydrate and N reserves as the substrates for
refoliation has been advocated previously (Sullivan and Sprague, 1943
).
Extensive mobilization of nonstructural carbohydrates and nitrogenous
compounds (Alberda, 1957
; Prud'homme et al., 1992
; Ourry et al., 1994
;
Volenec et al., 1996
) regularly occurs in the residual parts of
defoliated plants. However, the supply of mobilized carbohydrates and N
to the regrowing shoots has seldom been studied with quantitative
methods. Quantification of reserve-derived C or N accumulation in
regrowing shoots requires steady-state labeling of all pre- or
postdefoliation fixed C or N (de Visser et al., 1997
). Since N
redistribution occurs mainly in the form of amino acids (Ourry et al.,
1989
; Bigot et al., 1991
), a significant fraction of the
reserve-derived C influx in regrowing shoots may be associated with the
import of amino acids (Avice et al., 1996
). Thus, estimation of the
reserve-derived carbohydrate influx from C-labeling data alone would
lead to wrong conclusions, if transport of redistributed amino-C is not
accounted for. As yet, to our knowledge, dual steady-state labeling has
not been used to assess the actual contribution of reserve-derived C
and N to postdefoliation regrowth of plants. But, in a study with
3-month-old alfalfa plants, Avice et al. (1996)
used a 10-d-long
predefoliation labeling of C and N to assess the redistribution of
reserve-derived N and carbohydrates. In that study only 7% of the
(labeled) mobilized C accumulated in the regrowing shoot biomass. Much
of this was likely associated with amino acids, suggesting a
low contribution of reserve carbohydrates to shoot
regrowth.
Since the recovery of N uptake is retarded relative to the restoration
of photosynthetic activity (Richards, 1993
), the reserve dependence of
shoot growth may be longer for N than for C. In the growth zones of
expanding leaves of severely defoliated perennial ryegrass
(Lolium perenne L.), the transition from reserve- to current
assimilation-supported growth was more rapid for C than for N (de
Visser et al., 1997
). Similarly, in the study with alfalfa (labeled)
reserve-derived N was the main N source for an extended period after
defoliation (Avice et al., 1996
). Still, it was not clear from these
studies whether the influx of C or N was controlling regrowth of the
shoot and which roles carbohydrate and N reserves played in alleviating
potential limitations in the supplies of C and N.
In regrowth studies with grasses a recognition of the functional
heterogeneity of the "stubble" left behind after defoliation is
necessary (Davidson and Milthorpe, 1966a
; Volenec, 1986
; de Visser et
al., 1997
; Morvan et al., 1997
). The stubble includes fully expanded
leaf material (mainly leaf sheaths), as well as the (enclosed) basal,
immature parts of expanding leaves and leaf primordia formed by the
apex at the tiller base (Fig. 1A). The former may serve as a source for mobilized C and N, whereas the latter
generate the new foliage and may act as sinks for mobilized C and N. At
all times about two leaves are actively expanding in a vegetative grass
tiller, with the younger of the two not becoming visible until its tip
emerges above the whorl of encircling leaf sheaths. As the older of the
two reaches its final size, a new leaf starts to expand, with lamina
expansion preceding sheath expansion (Skinner and Nelson, 1994
). Thus,
at any time during postdefoliation regrowth three functionally distinct
categories of leaves may be found in a grass tiller: (a) (the residual
parts of) fully expanded leaves that completed growth before
defoliation (b) (parts of) fully expanded leaves that completed growth
after defoliation, and (c) currently growing leaves (compare with Fig. 1B). The latter (b and c) compose the regrowing part of the tiller (which is hereafter termed the "regrowing tiller"; Fig. 1) and both
include exposed (photosynthetically active) and enclosed (heterotrophic
immature or mature) leaf zones.

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| Figure 1.
Schematic representation of a vegetative perennial
ryegrass tiller at defoliation (A) and approximately one leaf
appearance interval after severe defoliation (B). The tiller is
composed almost entirely of leaf tissue (1-5). Daughter tillers may be
present in axils of fully expanded leaves (not shown). The TB includes
the apex, nodes, and unelongated internodes of the tiller. The
defoliation level marks the boundary between the exposed (grazed/mown)
foliage and stubble zones. At defoliation (A) leaves 1 and 2 had
reached full expansion, whereas leaves 3 and 4 were expanding ( ).
Defoliation removed all lamina tissue of leaves 1 and 2 and (the
exposed) part of the lamina of elongating leaf 3. Leaf 4 was not
touched, because its tip had not emerged above the defoliation level.
Foliage production (exposure of lamina tissue above the defoliation
level) during the interval A to B was due to expansion of leaves 3 and
4. At time B leaf 3 had reached its final size. Expansion stopped
shortly after the ligule was exposed above the defoliation level. Leaf
4 was still expanding at time B, and leaf 5 had started to expand.
Expansion and maturation of cells takes place in a zone (IM-AE) that
extends from the base of the expanding leaf to the location where leaf
tissue emerges from the encircling sheaths of older leaves (at
approximately defoliation level). The sheath was actively expanding in
leaf 4 at time B (note position of the ligule). Leaf 5 was still
completely enclosed and expanding as a function of lamina growth. At
any time during refoliation, the regrowing tiller can be divided into
five functionally distinct zones: the TB, the EX-AE, and the IM-AE
(leaves 4 and 5 in B [shaded area]) and the EX-FE and EN-FE, which
stopped to elongate after defoliation (leaf 3 in B). Leaves 1 and 2 had
stopped to expand before defoliation and, hence, do not form part of
the regrowing tiller, as defined here.
|
|
Growth (cell production and expansion) is confined to the (enclosed)
immature base of the expanding grass leaf (Volenec and Nelson, 1981
;
MacAdam et al., 1989
; Schnyder et al., 1990
), and the tissue that
emerges from the enclosing leaf sheaths is (almost) fully
differentiated and photosynthetically active (Wilhelm and Nelson, 1978
;
Boffey et al., 1980
; Dean and Leech, 1982
; MacAdam and Nelson, 1987
;
Gastal and Nelson, 1994
). Thus, cell production and expansion in the
immature zone gives rise to a flux of (almost) fully mature tissue to
the exposed zone of expanding leaves (Fig. 2). Furthermore, when a leaf stops to
expand, it is laterally displaced to the expanded leaf category (organ
flux). During undisturbed growth the tissue-bound efflux of C and N
from the immature zone is compensated by concurrent import of the
substrate. However, following severe defoliation of perennial ryegrass
both the fresh mass (i.e. volume) of the immature zone and the C mass
per unit fresh mass of the immature zone of expanding leaves decreased strongly, indicating that axial relative to radial expansion was transiently increased and that C influx was less than was necessary to
balance the tissue-bound efflux of C (de Visser et al., 1997
). The
latter may have been caused by the use of carbohydrates, which were
already present in the immature zone at defoliation (Davidson and
Milthorpe, 1966a
; Volenec, 1986
; Morvan et al., 1997
). However, reduced
synthesis of structural biomass per unit (volumetric) growth could also
contribute to a dilution of C in the immature zone. This possibility
has not been studied to date. However, because it would contribute to
sustaining the efflux (exposure) of photosynthetically active tissue at
reduced costs, such a mechanism could facilitate the recovery from
defoliation and the transition from reserve- to current
assimilation-dependent growth.

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| Figure 2.
Conceptual model of tissue and substrate (i.e.
assimilate) fluxes among functionally distinct zones of a regrowing
tiller of perennial ryegrass. Leaf expansion is confined to the basal
region of the IM-AE and gives rise to a flux of tissue to the EX-AE. As
leaves stop to expand, they are "displaced" to the expanded leaves
category (EX-AE EX-FE, IM-AE EN-FE). Tissue flux is mainly
in the form of structural biomass. Substrate flux is mainly directed
toward the immature zone, where cell production, expansion, and
maturation (including synthesis of proteins and secondary cell walls)
take place. Substrate fluxes to and from other plant parts are not
shown.
|
|
The aim of this study was to assess the relative importance of
reserve- and current assimilation-derived substrate supply in the
regrowing shoot and of putative mechanisms operating within the
regrowing shoot itself in controlling postdefoliation regrowth of a
defoliation-tolerant species, perennial ryegrass (L. perenne L.). To this end, we used steady-state labeling of all
postdefoliation-assimilated C and N, periodic sampling of regrowing
tillers, and analysis of WSC and of the mass and isotope composition of
C and N in functionally distinct zones of regrowing tillers.
 |
MATERIALS AND METHODS |
Plant Material, Growth Conditions, and
13CO2/12CO2 and
15N/14N Labeling
Details of the plant material, growth conditions, and
13CO2/12CO2 and 15N/N
labeling were described previously (de Visser et al., 1997
). Clonal
plants of two genotypes of perennial ryegrass (Lolium
perenne L.) were established in a greenhouse in a hydroponic
system in Wageningen (The Netherlands). Well-established vegetatively
growing plants (n = 100) of both genotypes were
transferred to and distributed randomly in two plant growth chambers
(model E15, Conviron, Winnipeg, Manitoba, Canada) in Bonn, Germany. A
16-h light period of 400 µmol m
2
s
1 PPFD at plant height was supplied by
cool-white fluorescent and incandescent lamps. Temperature was
controlled at 20°C/17°C and RH near 70%/85% during the light/dark
periods, respectively. Individual plants were held in 1.2-L pots with
aerated nutrient solution (de Visser et al., 1997
). Nutrient solutions
(with nitrate as the sole N source) were replaced when the nitrate
concentration, as determined by indicator strips (Merckoquant, 10020, Merck, Darmstadt, Germany), had declined to about 20% (i.e. 1.5 mM). All plants remained vegetative throughout
the experiment. After 13 d in the growth chamber the plants were
defoliated at 5 cm stubble height and redistributed equally among the
two chambers. Defoliation was performed shortly before the start of the
light period.
An open-system, steady-state
13CO2/12CO2-labeling
technique (Schnyder, 1992
; de Visser et al., 1997
) was used to label
all photosynthate fixed during the 14-d postdefoliation regrowth
period. Before defoliation both chambers received ambient air with a
CO2 partial pressure of approximately 36 Pa and a
13C value (
) of approximately
8.8o/oo.
Immediately following defoliation the
of the
CO2 in one of the two chambers was changed to
28.1o/oo (using CO2 of fossil organic
origin; Buse, Bad Hönningen, Germany) for the entire regrowth
period. Air with a CO2 partial pressure of 36 Pa
was supplied to the chamber at a constant 36 m3 h
1. This provided for a near-maximum expression
of C isotope discrimination (
) during labeling (de Visser et al.,
1997
), since CO2 was injected at >30 times the
rate of photosynthetic CO2 uptake by plants. Also, at the time of defoliation the plants in the labeling chamber were transferred from a standard nutrient solution with 0.3682 atom % 15N to a solution enriched to 1.00 atom % 15N in nitrate. In the other chamber (labeling
control), the isotope composition of both the N in the nutrient
solution and the CO2 supplied to the plants was
kept the same as during the predefoliation period. This was done to
allow for a determination of eventual defoliation-, genotype-, time-,
and zone-specific effects on C and N isotope discrimination (see below;
de Visser et al., 1997
). The other growth conditions were kept
identical in both growth chambers.
Sampling
Plants were sampled at 0, 1, 2, 5, 8, and 14 d after
defoliation. Sampling always started at the beginning of the light
period and was completed within 6 h. On each date four plants of
each genotype were randomly sampled from each of the growth chambers. Each plant had approximately 50 "mature" tillers. Mature tillers are defined as having at least one fully expanded leaf at the time of
defoliation and usually included one or two daughter tillers in the
axils of fully expanded leaves. The daughter tillers had no fully
expanded leaves at defoliation. A subsample consisting of eight mature
tillers was removed from each plant. Selected mature tillers were
divided into (a) leaf tissue that had reached full expansion before
defoliation (mainly sheath tissue), (b) daughter tillers, and (c)
tissue that experienced growth after defoliation. The latter fraction
represented the "regrowing tiller" and was dissected to yield the
functionally distinct zones shown in Figure 1, i.e. (a) the IM-AE (0-5
cm from TB); (b) the EX-AE (tissue above the 5-cm defoliation level);
(c) the EN-FE (0-5 cm from TB) and (d) the EX-FE (>5 cm); and (e) the
TB, consisting of the regrowing tiller's apex, nodes, and unelongated
internodes (Fig. 1B). Actively expanding leaves were defined as having
their ligule at
2 cm from the leaf base. Leaves with the ligule at >2 but
5 cm were arbitrarily assigned to the fully expanded leaves fraction (with tissue located between 0 and 5 cm of the TB added to the
EN-FE fraction and tissue >5 cm to EX-FE), since expansion was
confined to the sheath part of the leaf and the expansion rate was
slower and rapidly decreasing with time (compare with Schnyder et al.,
1990
). All plant material was kept on a cool surface (approximately
0°C) during dissection. Immediately following collection the
individual samples were weighed, freeze-dried, weighed again, ground to
homogeneity in a ball mill, and then stored at
30 °C until needed.
C, N, and Carbohydrate Analysis
Aliquots of the plant material were analyzed for the content and
isotope composition of C and N using an elemental gas chromatograph interfaced to a continuous flow isotope-ratio mass spectrometer (Roboprep TCD-Tracermass, Europa Scientific, Crewe, UK; de Visser et
al., 1997
). Since differences in C and N concentration (grams per gram
dry mass) and isotope composition were very small between replicates
(compare with Table I), the elemental and
isotope analyses were restricted to two of the four replicates sampled from each genotype and growth chamber (SD averaged 0.3
for
of C in the control and 0.5
in the labeling chamber and
0.001 atom % 15N in the control and 0.015 atom % 15N in the labeling chamber).
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|
Table I.
Average coefficients of variation (CV) for dry mass,
C and N concentration, and the fraction of predefoliation C and N in
regrowing tillers of perennial ryegrass
Average CV was calculated from the CVs of sampling date × genotype combinations.
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For analysis of WSC, 10 mg of ground dry material was weighed into
2.2-mL capped Eppendorf tubes and 2 mL of water was added. Tubes were
sealed immediately and transferred to a 95°C water bath for 10 min,
shaken for 30 min, and centrifuged at 10,000g for 10 min,
and the supernatants were removed with a pipette. Comparison with two
additional extractions demonstrated that
98% of the total WSC was
dissolved in the first extract. WSC were analyzed with a continuous
flow system similar to the one described by Wolf and Ellmore (1975)
. An
aliquot of the WSC extract was hydrolyzed in 0.1 M sulfuric acid for 25 min at 92°C. Reducing power of the hydrolyzed carbohydrates was detected photometrically at
425 nm after reduction of a potassium ferricyanide solution. Analysis
of reference Glc, Fru, Suc, and fructan (all biochemical grade from
Merck) yielded response factors of the individual carbohydrates, which
were proportional to the amount of hexose residues present in 1 g
of substrate.
Data Analysis
The C and N isotope data (
13C and atom % 15N)
were used to calculate the weight fractions
(fpre and
fpost, where
fpost = 1
fpre) of C and N derived from pre- and
postdefoliation assimilation. The fraction of predefoliation C
(fpre) in a sample was obtained from
P = fpre
PC + (1
fpre)
PL:
where
P is the
of a given sample
harvested from the labeling chamber,
PL is the
of the C assimilated from the labeling CO2,
and
PC is the
of the parallel (replicate)
sample collected from the control chamber. The
PL was not determined experimentally. But,
since C isotope discrimination is independent of the isotope composition of CO2 (Deléens et al., 1983
;
Farquhar and Richards, 1984
; Schnyder, 1992
),
PL was calculated as:
where
SU is the
of the labeling
CO2, and
is the genotype-, zone-, replicate-
and time-specific C isotope discrimination, as determined in the
parallel sample collected from the control chamber (de Visser et al.,
1997
). The mass of predefoliation C in a sample
(Cpre, milligrams per tiller) was
calculated as:
where W is the dry mass (milligrams per tiller) and
[C] is the C concentration (grams per gram dry mass) in the sample
(Cpost = C
Cpre, where C is total C mass
per tiller). Cpre and
Cpost were estimated for samples collected
from both the labeling and control chambers using their
replicate-specific fpre estimate (note that
fpre was a parameter that was derived from
paired samples collected from the labeling and control chambers and
included variation in both). Dry mass and C and N mass parameters did
not differ among the two chambers (P > 0.05), as was expected
since growth conditions were the same. For replicates in which
elemental concentrations and isotope composition were not analyzed,
estimates of pre- and postdefoliation C mass were obtained from their
original dry mass (W) and randomly assigned
fpre estimates and elemental concentrations
([C]), as determined in the other replicates.
N isotope data were evaluated accordingly, but N isotope discrimination
was neglected because it was insignificant relative to the enrichment
of the nitrate by 15N (de Visser et al., 1997
).
The masses of pre- and postdefoliation C and N in the total regrowing
tiller were calculated as the sum of masses present in the component
tiller zones (a-e; see above).
Accumulation rates of pre- and postdefoliation C and N (milligrams of C
or N per tiller per day) were calculated from the net changes in mass
of pre- and postdefoliation C and N in the regrowing tiller as observed
in the respective sampling intervals. For calculation of the
accumulation rates of C and N and estimation of the associated
variation, all replicates within a sampling date × genotype
combination were first ranked according to total tiller mass.
Accumulation rate was then calculated separately for the two genotypes
and data pairs with the same rank number. This procedure removed
variation associated with differences in initial tiller mass. Data from
the two genotypes were then combined since differences were
insignificant for the relationships studied here.
 |
RESULTS |
The Regrowing Tiller
Refoliation
Defoliation was severe, because it removed essentially all lamina
tissue and approximately 70% of total shoot biomass (data not shown).
Foliage production was assessed by following the total mass of C in
leaf tissue exposed above the defoliation level (foliage zone, compare
with Fig. 1). Foliage production rate was decreased on d 1 (
18%) and
d 2 (
31%) when compared with the rate at 1 week after defoliation,
but it increased strongly between d 2 and 5 after defoliation (Fig.
3).

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| Figure 3.
Foliage production rate in regrowing tillers of
perennial ryegrass during the first 8 d of regrowth after severe
defoliation. Foliage denotes all leaf (essentially lamina) tissue
exposed above the defoliation level. Rates were calculated as the net
change over time of C mass in foliage as observed during sampling
intervals (see ``Materials and Methods''). Vertical bars indicate
±SE (n = 16; eight tillers per
replicate).
|
|
C and N Accumulation Rates
The net C balance of the regrowing tiller was positive during d 1 (Fig. 4A), whereas the whole-plant C
balance was negative on that day (R. de Visser and H. Schnyder,
unpublished data). C accumulation (i.e. gross C influx less respiration
and export) on d 1 (86%) was mainly due to accumulation of
reserve-derived C (i.e. of predefoliation C imported from other plant
parts [roots and senescing sheaths]). The C accumulation rate of the
regrowing tiller increased strongly between d 1 and 5, and this was
related to a strong increase in the accumulation of currently (i.e.
postdefoliation) fixed C (Fig. 4A). During d 2 postdefoliation fixed C
already accounted for 63% of the total (i.e. pre- plus
postdefoliation) C accumulation; thereafter, postdefoliation C provided
more than 90% in the regrowing tiller.

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| Figure 4.
Net accumulation rate of total C ( ),
predefoliation C ( ), and postdefoliation C ( ) (A) and total N
( ), predefoliation N ( ), and postdefoliation N ( ) (B) in
regrowing tillers of perennial ryegrass during the first 8 d of
regrowth after severe defoliation. Rates were calculated as the net
change over time of C or N mass (total, predefoliation, and
postdefoliation) as observed during sampling intervals (see
``Materials and Methods''). The regrowing tiller included the TB and
all of the leaves that experienced growth after defoliation but not the
leaves that had stopped to expand before defoliation (compare with Fig.
1). Vertical bars indicate ±SE (n = 16).
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|
The N accumulation rate on d 1 was only moderately depressed when
compared with the rate at about 1 week after defoliation (Fig. 4B). The
high rate of N accumulation on d 1 was related to import of both
reserve-derived (predefoliation) and currently absorbed
(postdefoliation) N, with reserve-derived N contributing the bulk
(75%) of the accumulation.
Accumulation of N in the regrowing tiller was transiently depressed on
d 2, and this was due to decreased accumulation of both pre- and
postdefoliation-absorbed N. In relative terms the decrease was stronger
for post- than for predefoliation-absorbed N. Thus, the contribution of
current N uptake to N accumulation in the regrowing shoot was only 10%
on d 2. After d 2 the accumulation rate of N increased, which was
mainly due to increased accumulation of postdefoliation-absorbed N,
which became the dominant N source about 3 d after defoliation
(Fig. 4B).
C:N Ratio in Reserve- and Current Uptake-Derived Biomass
Accumulating in the Regrowing Tiller
The total (i.e. pre- and postdefoliation) biomass accumulating in
the regrowing tiller during d 1 had a C:N ratio of 4.5. However, the
biomass accumulating during d 2 closely matched the C:N ratio of the
whole-tiller biomass observed at defoliation and of the regrowing
tiller biomass at the end of the regrowth period (Fig.
5).

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| Figure 5.
C:N (w/w) ratio in total biomass ( ) and in pre-
( ) and postdefoliation biomass ( ) accumulating in regrowing
tillers of perennial ryegrass during the first 8 d of regrowth
after severe defoliation. Ratios were calculated from the daily net
rates of C and N accumulation presented in Figure 4 (compare with Fig.
4 for SE). Note that the strong increase in the C:N ratio
of postdefoliation biomass accumulating between d 1 and 2 resulted from
an increase in the rate of postdefoliation C accumulation and a
(concurrent) decrease in the rate of postdefoliation N accumulation.
The dotted line indicates the C:N ratio (8.9) of regrowing tiller
biomass at 14 d after defoliation, which was the same as in total
tiller biomass at defoliation.
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|
Predefoliation biomass accumulating on d 1 had a C:N (w/w) ratio of 5.2 (Fig. 5), which decreased steadily thereafter. Postdefoliation biomass
accumulating during d 1 was very rich in N, but on d 2 it contained
very little N. After d 2 the C:N ratio in new biomass derived from
postdefoliation assimilation rapidly approached an equilibrium value
near 9.
The Tiller Zones
C:N Ratio in Biomass
The biomass in the different zones of the regrowing tiller
exhibited large zone-specific differences in the C:N ratio (Fig. 6A) and in the changes over time of the
C:N ratio in pre- and postdefoliation biomass (Fig. 6, B and C). In all
of the zones the C:N ratio of total biomass decreased transiently after
defoliation (Fig. 6A). The C:N ratio in predefoliation biomass was
lowest in the immature zone and highest in the TB (Fig. 6B). In all of the zones, except for the TB, the C:N ratio of predefoliation biomass
decreased significantly between d 0 and 5 after defoliation. This
decrease was strongest in the immature zone.

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| Figure 6.
C:N ratio in total biomass (A), predefoliation
biomass (B), and postdefoliation biomass (C) in functionally distinct
zones of regrowing tillers of perennial ryegrass during the first
8 d of regrowth after severe defoliation: IM-AE ( ), EX-AE
( ), EN-FE ( ), EX-FE ( ), and TB ( ). For definition and
designation of zones, see the legends for Figures 1 and 2. Vertical
bars indicate ±2 SE (n = 16).
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|
Significant zone-specific differences were also evident in the time
course of the C:N ratio of postdefoliation-assimilated biomass. In the
IM-AE and EX-AE (compare with Fig. 1), the C:N ratio of postdefoliation
biomass followed the changes observed for the C:N ratio of
postdefoliation biomass accumulating in the entire regrowing tiller
(compare Figs. 5 and 6C). This was related to the high turnover of
biomass in these zones (generation of new tissue from current substrate
[Fig. 5]) and concurrent efflux of mature tissue (compare with Fig.
2; see ``Discussion''). The C:N ratio of the postdefoliation biomass
in other zones (TB, EN-FE, and EX-FE) changed more gradually over time
(Fig. 6C).
Fraction of Postdefoliation C and N
The rates of increase in the fraction of postdefoliation C and N
in biomass differed strongly among the different zones and were
different for C and N (Fig. 7). For
postdefoliation C the rate decreased in the order
IM-AE > EX-AE > EN-FE > EX-FE > TB (Fig. 7A).

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| Figure 7.
Time course of the fraction of postdefoliation C
(A) and postdefoliation N (B) in functionally distinct zones of
regrowing tillers of perennial ryegrass during the first 8 d of
regrowth after severe defoliation: IM-AE ( ), EX-AE ( ), EN-FE
( ), EX-FE ( ), and TB ( ). For definition and designation of
zones, see legends for Figures 1 and 2. Vertical bars indicate
±SD (n = 4).
|
|
The kinetics of postdefoliation N differed from the pattern observed
for C: In particular, postdefoliation N always represented a smaller
fraction of total N (Fig. 7B) compared with C (Fig. 7A). This effect
resulted from the longer duration of predefoliation N supply than of
predefoliation C supply to the regrowing tiller (Fig. 4). Furthermore,
there was a significant transient slowing down between d 1 and 2 in the
increase of the fraction of postdefoliation N in all of the zones,
demonstrating that decreased postdefoliation N accumulation in the
regrowing tiller on d 2 (Fig. 4B) affected N supply to all of the zones
(compare with Fig. 9C). Also, the kinetics of the increase of
postdefoliation N in the exposed zones did not differ from the enclosed
zones (Fig. 7B) in either the actively expanding or the fully expanded
leaf category.

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| Figure 9.
Masses of total N (A), predefoliation N (B), and
postdefoliation N (C) in regrowing tillers of perennial ryegrass and in
its component zones during the first 8 d of regrowth after severe
defoliation: IM-AE, EX-AE, EN-FE, EX-FE, and TB. Leaves that had
stopped to expand before defoliation are not included, because they did
not form part of the regrowing tiller as defined here. For definition
and designation of zones, see the legends for Figures 1 and 2. Vertical
bars indicate ±2 SE (n = 16).
|
|
Predefoliation Biomass
The zones of the regrowing tiller differed strongly in the
temporal changes of predefoliation C and N (Figs.
8B and 9B),
as calculated from the total masses of C and N (Figs. 8A and 9A) and
the fractions of postdefoliation C and N (Fig. 7). In the TB the masses
of predefoliation C and N changed little over time, whereas they
decreased rapidly in the immature zone. Rapid loss of predefoliation C
and N from the immature zone between d 0 and 2 was associated with
rapid accumulation in the exposed zone of expanding leaves. The latter,
however, was a transient feature with the masses of predefoliation C
and N in the EX-AE decreasing after d 5. Conversely, continuous
accumulation of predefoliation C and N was evident in both the EN-FE
and EX-FE (as a result of tissue/organ flux, compare with Fig. 2). At d
8 most of the predefoliation C and N present in the regrowing tiller
was contained in the expanded leaf zones (Figs. 8B and 9B).

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| Figure 8.
Masses of total C (A), predefoliation C (B), and
postdefoliation C (C) in component zones of regrowing tillers of
perennial ryegrass during the first 8 d of regrowth after severe
defoliation: IM-AE, EX-AE, EN-FE, EX-FE, and TB. Leaves that had
stopped to expand before defoliation are not included, because they did
not form part of the regrowing tiller as defined here. For definition
and designation of zones, see legends for Figures 1 and 2. Vertical
bars indicate ±2 SE (n = 16).
|
|
Since the immature zone had a strongly negative balance for
predefoliation C and N, the accumulation of predefoliation C and N in
the whole regrowing tiller between d 0 and 8 was much less than in its
component mature zones (EX-AE plus EN-FE plus EX-FE; Figs. 8B and 9B).
Accumulation of predefoliation C and N in the composite of mature zones
(EX-AE plus EN-FE plus EX-FE) was 2.5 and 1.5 times the accumulation of
predefoliation C and N in the entire regrowing tiller because of flux
of predefoliation C and N from the immature to the mature zones (Figs.
8B and 9B).
Postdefoliation Biomass
Accumulation of postdefoliation-absorbed C and N was evident in
all of the zones, but the distribution changed strongly with time
(Figs. 8C and 9C). Initially, the bulk of the postdefoliation C and N
was present in the IM-AE and EX-AE. However, because predefoliation C
and N in these zones were exchanged by postdefoliation-absorbed C and N
and their total masses changed little, the mass of postdefoliation C
and N in the IM-AE and EX-AE increased relatively little after d 5. After d 5 the bulk of the postdefoliation C and N accumulation occurred
in the zones of expanded leaves, which comprised an increasing proportion of the total regrowing tiller biomass (Figs. 8, A and C, and
9, A and C).
The Fractional Contribution of WSC-C to Tissue C
Except in the immature zone, WSC-C was a minor component of the
total C in the different zones (Fig.
10). WSC-C accounted for 14% of the
total C in the immature zone at defoliation. During d 1 the WSC
fraction in the immature zone decreased rapidly to a level that was
only 32% of that at defoliation. Subsequently, the WSC fraction in the
immature zone increased gradually to and above the level at
defoliation. In the exposed zones (i.e. the foliage) of both actively
expanding and fully expanded leaves, WSC-C accounted for less than 8%
of total tissue C throughout the 1st week after defoliation. In the
EN-FE the fractional contribution of WSC to tissue C was slightly
higher and increased substantially after d 5.

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| Figure 10.
Fractional contribution of WSC-C to the mass of C
in functionally distinct zones of regrowing tillers of perennial
ryegrass during the first 8 d after severe defoliation: immature
zone of actively expanding leaves (IM-AE, ), exposed zone of
actively expanding leaves (EX-AE, ), enclosed zone of fully expanded
leaves (EN-FE, ), and exposed zone of fully expanded leaves (EX-FE,
). For definition and designation of zones see Figures 1 and 2.
Vertical bars indicate ±2 SE (n = 16).
|
|
The concentration of starch in the different zones was not determined
in the present experiment. However, earlier studies of the two
genotypes showed low starch concentrations (<10% of total
nonstructural carbohydrates) in leaves. Also, in studies of perennial
ryegrass grown under conditions favoring nonstructural carbohydrate
accumulation, starch was a minor component of the nonstructural
carbohydrates (<15%) in both leaf blades and sheaths (Guerrand,
1997
).
The Concentrations of WSC and Structural Biomass in the Immature
Zone
In the immature zone the concentration (expressed as grams of C
per gram of tissue water) of both WSC and structural biomass (estimated
as total tissue C minus WSC-C, thus including protein C and possibly
trace amounts of starch) decreased transiently after defoliation (Fig.
11). The WSC concentration was very low 1 and 2 d after defoliation but increased rapidly thereafter. In
absolute terms the initial (0-1 d after defoliation) decrease in the
concentration of structural biomass was even larger (
6.3 mg C
g
1 tissue water) than the decrease in the WSC
concentration (
4.9 mg C g
1 tissue water).

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| Figure 11.
Concentration of WSC-C ( ) and structural C
( ) in the IM-AE of actively expanding leaves of perennial ryegrass
during the first 8 d after severe defoliation. Vertical bars
indicate ±2 SE (n = 16).
|
|
 |
DISCUSSION |
Zonal Heterogeneity in the Kinetics of Pre- and Postdefoliation C
and N
Steady-state labeling of postdefoliation-absorbed C and N in
combination with sequential sampling and separation of functionally distinct zones of the regrowing tiller demonstrated large zone-specific differences in the change over time of the fraction of postdefoliation C in total tissue C (Fig. 7A). The ranking of zones in terms of the
increase over time in the fraction of postdefoliation C
(IM-AE > EX-AE > EN-FE > EX-FE > TB) corresponded closely
to the gradient of (mean) age of tissue present in the different zones
(compare with Skinner and Nelson, 1994
). Thus, at all sampling times
the fraction of postdefoliation C in total C was lowest in the zones
that contained the oldest tissue and highest when the tissue was
youngest (immature zone).
Interpretation of these results requires a consideration of the factors
determining labeling kinetics, i.e. the specific rates and isotopic
composition of "tissue fluxes" among zones of a tiller (Fig. 2) and
"substrate in- and efflux" (turnover) of the plant part studied.
For instance, it is important to take into account that structural C
(estimated as total tissue C minus WSC-C) is largely immobile and
accounted for more than 90% of the C present in mature tissue zones
(except for the enclosed zone of expanded leaves at d 8; compare with
Fig. 10), in contrast to structural N (protein), which is highly mobile
(turnover rate up to 10% d
1; Bouma et al.,
1994
). Structural biomass (including protein) is synthesized mainly
when the leaf tissue is located in the immature zone (MacAdam and
Nelson, 1987
; Gastal and Nelson, 1994
; Maurice, 1997
). Accumulation of
structural biomass in the fully expanded leaf category and in the EX-AE
thus results from the tissue-bound efflux of structural C from the
immature zone. The first tissue to be exposed above the defoliation
level was (almost) fully differentiated at the time of defoliation and,
hence, its structural biomass was largely synthesized before
defoliation. The biomass in the immature zone is rapidly turned over
(Schnyder and Nelson, 1989
) and was rapidly depleted of predefoliation
C (Fig. 7A). Accordingly, the structural biomass formed within and
displaced from the immature zone after defoliation was progressively
depleted of predefoliation C. Hence, although structural biomass
accumulating in the zones of the fully expanded leaf category during
the first days was mainly composed of predefoliation C, the structural
biomass accumulating at later stages (and as a result of tissue flux
mainly) was primarily composed of postdefoliation C, thus causing the
apparent dilution of predefoliation C in the fully expanded leaf zones
(Fig. 7A).
Another important aspect of zonal heterogeneity is the distinction
between exposed leaf zones (foliage) and whole leaves or tillers. The
total mass of predefoliation C in foliage (EX-AE plus EX-FE) increased
significantly until d 5 after defoliation (Fig. 8B), although
(reserve-derived) predefoliation C accumulation in the regrowing tiller
was minimal after d 2 (Figs. 4A and 8B). This delayed accumulation of
predefoliation C in foliage was related to the time needed for
displacement of tissue from the immature zone to the (exposed) foliage
zone (up to approximately 12 d; compare with Schnyder et al.,
1990
). These relationships also explain why investigation of
predefoliation C and N accumulation in foliage overestimates both the
duration of reserve utilization in regrowth and the contribution of
reserves to refoliation: When assessed on the basis of the masses of
predefoliation C and N present in foliage at d 8, the reserve-derived C
and N accumulation in the entire regrowing tiller was overestimated by
102% and 55%, respectively (Figs. 8B and 9B). The rapid transition to
current assimilation-driven growth observed in this study contrasts
with findings from other studies, suggesting a major role of reserves for about 1 week (carbohydrates; Alberda, 1957
; Gonzalez et al., 1989
;
Johansson, 1993
) up to 2 weeks (N; Ourry et al., 1989
; Thornton et al.,
1993a
, 1993b
). In these studies reserve-derived substrate use in
regrowth was inferred from the kinetics of reserve mobilization in the
stubble (Alberda, 1957
) or from the accumulation of predefoliation N
(Thornton et al., 1993a
, 1993b
) or C (Johansson, 1993
) in foliage. Mobilization gives no proof of the actual use of mobilized substrate in
shoot regrowth, and accumulation of predefoliation C and N in foliage
overestimates the duration and contribution of reserve use in regrowth
due to neglect of tissue flux.
Differences in turnover rate (in- and efflux) of C and N in zones may
also contribute to variation in labeling kinetics. In a steady-state
labeling experiment with wheat, Gebbing et al. (1998)
found no evidence
for turnover of C in structural carbohydrates of fully expanded leaves.
But WSC pools (Borland and Farrar, 1988
) and proteins may be turned
over rapidly by currently assimilated C and N. However, WSC turnover
would not have a large effect on the C isotope composition of tissue in
mature zones (EX-AE, EX-FE, EN-FE), since WSC was a minor component of
tissue C (Fig. 10). However, the fraction of postdefoliation N in total
N of the exposed and enclosed zones of leaves increased at very similar
rates, although the tissue in these zones was formed at different
times. This phenomenon was the same in the actively expanding and fully expanded leaf categories and cannot be explained only by tissue-bound efflux of N from the immature zone. The relatively high rates of
protein turnover (Bouma et al., 1994
), N cycling within plants (Larsson
et al., 1991
; Laine et al., 1994
), and postemergence accumulation of
postdefoliation-absorbed N in exposed tissue (Maurice, 1997
) likely
contributed to this effect. More research is needed to clarify further
the relationships among tissue flux, substrate flux, and turnover of
the different C and N pools in the functionally distinct zones and
organs.
Control of Refoliation and Tiller Regrowth by Substrate Supply
Since photosynthesis and N uptake were severely depressed
immediately after defoliation (R. de Visser and H. Schnyder,
unpublished data), but all active shoot meristems and leaf growth zones
were left behind intact, one should expect that initial refoliation was
controlled by substrate supply. Indeed, the foliage production rate on
d 1 and d 2 after defoliation was approximately 25% less than 1 week
after defoliation (Fig. 3). This effect was related to a decreased
substrate supply to expanding leaves as reflected in the decreased C
and N accumulation rates in the regrowing tiller (Fig. 4) and in the
negative C balance of the immature zone during the first 2 d after
defoliation (Fig. 8A). The negative C balance of the immature zone on d
1 must have resulted from a higher tissue-bound efflux of C relative to
the concurrent net influx of substrate C in this zone (Fig. 2). Several
mechanisms contributed to rapid refoliation by an imbalance between
efflux of tissue C and influx of C substrate in the immature zone on d
1: (a) a promotion of longitudinal relative to radial expansion
(leading to an 18% decrease in the mass of tissue water contained in
the immature zone, de Visser et al., 1997
), (b) increased partitioning
of imported C to synthesis of structural biomass relative to deposition
of WSC, (c) mobilization of carbohydrates stored within the immature
zone, and (d) a decreased rate of synthesis of structural biomass
relative to growth-associated water influx into expanding tissue. The
decreases in the fractional contribution of WSC to tissue C content
(Fig. 10) and in the mass of WSC in the immature zone (
0.16 mg WSC-C) on d 1 were likely related to both decreased partitioning of imported carbohydrates toward WSC deposition and mobilization and use of the
WSC, which were already present in the immature zone at defoliation. Dilution by growth-associated water uptake in expanding cells and
consequent tissue-bound displacement of WSC to other zones (compare
with Fig. 2) could also contribute to the decrease in the WSC content
of the immature zone. However, the mass of WSC lost from the immature
zone on d 1 was 3 times larger than the amount of WSC accumulated in
the other leaf zones, demonstrating that mobilization of WSC was the
main cause for WSC loss in the immature zone. Notably, however, the net
loss of C from the immature zone on d 1 (
0.55 mg) was much larger
than could be accounted for by the loss of WSC (
0.16 mg). This
discrepancy was partially due to a dilution of structural C in the
immature zone (Fig. 11), which resulted from decreased synthesis of
structural biomass relative to growth-associated water influx into
expanding cells. A similar dilution of structural biomass in growth
zones of tall fescue leaves was observed during the dark period of
diurnal cycles, when growth-associated water influx into expanding
tissue was stimulated more than the synthesis of structural biomass
(Schnyder and Nelson, 1988
; Schnyder et al., 1988
). All of these
mechanisms contributed to decrease the C investment for leaf production
and foliage exposure when C supply to the regrowing tiller was low immediately after defoliation. Conversely, the concentration of N in
fresh mass of the immature zone did not change after defoliation (de
Visser et al., 1997
) and the total mass of N in the immature zone
decreased much less than the mass of C (compare with Figs. 8A and 9A),
showing that the balance between substrate import and tissue-bound
efflux was much closer for N than for C.
Foliage production rate appeared to be related to C rather than N
supply. Foliage production rate was least on d 2, 31% less than 1 week
after defoliation (Fig. 3). Also, N (
43%) and C (
45%) accumulation rates in the regrowing tiller were significantly less than
1 week after defoliation (Fig. 4). Moreover, the WSC concentration was
very low (Fig. 11), indicating no opportunity for carbohydrate
mobilization in the immature zone on d 2. Also, the concentration of
structural C was still low (Fig. 11), demonstrating that leaf
production continued with reduced investments of C in the synthesis of
structural biomass. The increase in foliage production after d 2 (Fig.
3) was associated with strong increases in the net rates of current
assimilation-derived C and N accumulation in the regrowing tiller (Fig.
4) and increasing concentrations of structural C and WSC in the
immature zone (Fig. 11). Whereas changes in WSC concentration in the
immature zone closely paralleled the changes in foliage production rate
(Figs. 3 and 11), such parallels did not exist for N (de Visser et al.,
1997
).
Preferential allocation of current assimilate to growing tiller tissue
has repeatedly been indicted as a mechanism contributing to rapid
refoliation (Richards, 1993
). The present data indicate that such
preferential allocation is related to a "priviledged" position of
the immature zone relative to the main source of current photosynthate
produced during the initial period after defoliation. The exposed parts
of the actively expanding leaf category (EX-AE) made up more than 82%
of the total foliage generated by the regrowing tillers until 2 d
after defoliation (Fig. 8A). Current photosynthate and reduced N
produced and exported by this tissue must pass the immature zone (Fig.
2), which is a strong sink for current photosynthate (Allard and
Nelson, 1991
) and reduced N (Gastal and Nelson, 1994
). Rapid turnover
of Suc in the immature zone by C fixed after defoliation (Morvan-Bertrand et al., 1999
) may be related to this effect.
Control by C or N Substrate Supply?
Whereas the relationships discussed above support the view that
refoliation was (at least partially) controlled by substrate supply, a
question remaining is whether this control was exerted by C or N or
both. Clearly, a balanced supply of carbohydrates and N is required for
optimal growth. Extensive studies with a range of
C3 species have consistently shown that during
early growth stages growth is maximum and colimited by the
availabilities of C and N, when the C:N (w/w) ratio in shoot biomass is
approximately 8.6 (Lemaire and Gastal, 1997
). This ratio is almost
identical to the C:N ratio of 8.9 of tillers at defoliation and of the
regrowing tillers 14 d after defoliation, indicating an optimal balance between the supplies of C and N during predefoliation undisturbed growth and after recovery from defoliation. The C:N ratio of 4.5 for
total (i.e. reserve- plus current assimilation-derived) new biomass
accumulating in the regrowing tiller on d 1 (Fig. 5A) suggests a
relative shortage of C and/or relative abundance of N as the substrates
for shoot growth. However, after d 1 the C:N ratio in total biomass
accumulating in the regrowing tiller always ranged between 8.3 and 8.9 (Fig. 5), indicating that, although substrate supply likely controlled
growth, the C:N ratio in the substrate available for growth was near
optimal balance. Thus, at least after d 1, tiller regrowth appeared to
be colimited by the supplies of C and N.
Role of Reserves Versus Current Assimilates
Transition from reserve- to current assimilation-dependent growth
was much faster than was suggested in studies in which steady-state labeling was not used to differentiate between the fluxes of reserve- and current assimilation-derived C and N to the regrowing shoot or in
which the functional heterogeneity of the grass stubble left behind
after defoliation was not recognized (see above). Reserve-derived
biomass accumulating in the regrowing tiller had a low C:N ratio (Fig.
5), supporting earlier evidence that much of the reserve-derived C
accumulation in regrowing tillers was in the form of amino-C (Avice et
al., 1996
; de Visser et al., 1997
). Using the assumptions that (a) all
predefoliation N was imported in the form of amino acids having a mean
C:N (w/w) ratio of 2.6 (Fisher and Macnicol, 1986
) and (b) that the C
associated with the reserve-derived N was all predefoliation C, we
estimated that the import of amino-C accounted for 50% and 75% of the
reserve-derived C accumulation in the regrowing tiller on d 1 and 2 after defoliation (Table II). Since
postdefoliation fixed C was the main C source already on d 2 (Fig. 4A)
and amino-C was the main component of reserve-derived C accumulation,
it was highly unlikely that reserve-derived carbohydrates were a
significant source of substrate for tiller biomass after d 1 (Table
II). However, these carbohydrates may have contributed indirectly to
tiller regrowth via energy supply in shoot respiration and maintenance
of root integrity and function.
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|
Table II.
Estimated contributions of predefoliation reserves
to accumulation of carbohydrate- and amino-C in regrowing tillers of
perennial ryegrass on d 1 and 2 after severe defoliation
Predefoliation amino-C accumulation rate was calculated as accumulation
rate of predefoliation N (Fig. 4B) times 2.6 (see text). The
accumulation rate of reserve-derived carbohydrate-C (CHO-C) was
estimated as the accumulation rate of predefoliation C (Fig. 4A) minus
the accumulation rate of predefoliation amino-C, as defined above.
|
|
The strong decrease in accumulation of postdefoliation-absorbed N
between d 1 and 2 (Fig. 4B) was a significant factor contributing to
the increased C:N ratio of postdefoliation-absorbed biomass accumulating in the regrowing tiller during d 2 (Fig. 5). Jarvis and
Macduff (1989)
and MacDuff et al. (1989) already noted that defoliation
entailed an inhibition of N uptake in perennial ryegrass plants, which
were well supplied with N before defoliation. However, inhibition of
nitrate uptake occurred with some delay, the rate declining over a
period of 15 h after defoliation. The present data show that this
lag in the response of root function had a direct effect on the supply
of postdefoliation-absorbed N to the regrowing tiller. However, as was
indicated by the near-optimal C:N ratio of total (reserve- plus current
assimilation-derived) new biomass accumulating in the regrowing tiller,
decreased supply of current uptake-derived N on d 2 was compensated by
the sustained supply of reserve-derived N (Fig. 5).
Reserve-derived N accumulation in the regrowing tiller was sustained
over a longer period than was the influx of reserve-derived carbohydrates (Fig. 4; Table II). As a consequence, the C:N ratio in
reserve-derived biomass accumulating in the regrowing tiller decreased
strongly over time (Fig. 5). This occurred while the C:N ratio in total
(i.e. reserve- and current assimilation-derived) biomass accumulating
in the regrowing tiller was almost constant at approximately 8.6 after
d 1. Thus, although the C:N ratio in reserve- and current
assimilation-derived biomass diverged strongly, the two sources were
highly complementary in terms of providing a substrate with an optimal
C and N composition. To our knowledge, such an effect has not been
observed before. It may reflect the operation of a mechanism working at
the plant level and balancing the fluxes of reserve- and current
assimilation-derived C and N among the regrowing shoot and the root
system. Such a mechanism may contribute to minimize trade-offs in
resource allocation (root versus shoot growth, maintenance, and
function) in the face of limited availability of both substrates. The
nature of the putative mechanism is not clear, but one hypothesis is
that substrate supply to sinks is demand driven, involving chemical
signaling (sugars: Frommer and Sonnewald [1995], Farrar [1996],
Koch [1996]; and/or plant growth regulators (hormones): Jackson
[1993], Munns and Cramer [1996] and Van der Werf and Nagel
[1996]). Also, the vascular architecture of the plant (compare with
the position of the immature zone relative to current assimilate
supply) may be involved.
In conclusion, the present study yields evidence for an important role
of several mechanisms in facilitating rapid refoliation in a
defoliation-tolerant grass species: (a) reduced C investment for leaf
expansion associated with both "spatial" (transient promotion of
longitudinal relative to radial leaf expansion, de Visser et al., 1997
)
and "chemical dilution" (reduced C investment per unit volumetric
leaf expansion, i.e. transient dilution of structural biomass in
immature zones), (b) utilization in regrowth of WSC, which were already
present in the immature zone at defoliation, (c) rapid transition to
current photosynthate (carbohydrate)-driven growth (which may be
partially related to a priviledged position of the immature zone of
expanding leaves relative to the main path of current photosynthate
produced during initial refoliation), (d) transient import of mobilized
assimilate (mainly N), and (e) rapid reestablishment of a balanced C:N
ratio in the new biomass produced in the regrowing tiller resulting
from complementarity in the supply of reserve- and current
assimilation-derived C and N. Rapid refoliation was likely due to a
high sink capacity and strength of the regrowing tiller, since none of
the expanding leaf tissue and shoot meristems were removed by
defoliation. Further research with a range of species differing in
defoliation tolerance and grown in contrasting conditions is needed to
assess the relative importance of each of the above mechanisms in
conferring or limiting tolerance to defoliation.
 |
FOOTNOTES |
1
This work was supported by the Commission of the
European Communities, Directorate General VI for Agriculture, Divison
for the Coordination of Agricultural Research, Brussels, Belgium (grant no. GT920078 to R.d.V.), and the Deutsche Forschungsgemeinschaft (grant
no. SFB 607).
*
Corresponding author; e-mail
schnyder{at}romeo.grass.agrar.tu-muenchen.de; fax 49-8161-713243.
Received August 10, 1998;
accepted January 7, 1999.
 |
ABBREVIATIONS |
Abbreviations:
EN-FE, EX-FE, enclosed and exposed zones of
leaves that had reached full expansion by the time of sampling but had
experienced growth after defoliation, respectively .
EX-AE, IM-AE,
exposed and immature (enclosed) zones of actively expanding leaves,
respectively.
TB, tiller base zone.
WSC, water-soluble
carbohydrate(s).
 |
ACKNOWLEDGMENTS |
We wish to thank Prof. W. Kühbauch (Universität
Bonn, Germany) and Siebe van de Geijn (AB-DLO, Wageningen, The
Netherlands) for continued support and Thomas Gebbing, Elisabeth
Huber-Sannwald, Markus Lötscher, and Rudi Schäufele (all at
Technische Universität München, Germany) for valuable
suggestions concerning the manuscript. Hanno Vianden, Sandra Beck,
Ludwig Schmitz (all at Universität Bonn), Riet de Kock
(AB-DLO), and Brigitte Schilling (Technische Universität
München) provided invaluable technical assistance.
 |
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