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Tree water relations and climatic variations at the alpine timberline: seasonal changes of sap flux and xylem water potential in Larix decidua Miller, Picea abies (L.) Karst.
and Pinus cembra L
Tommaso Anfodillo, Stefano Rento, Vinicio Carraro, Luca Furlanetto, Carlo Urbinati, Marco Carrer
To cite this version:
Tommaso Anfodillo, Stefano Rento, Vinicio Carraro, Luca Furlanetto, Carlo Urbinati, et al.. Tree
water relations and climatic variations at the alpine timberline: seasonal changes of sap flux and
xylem water potential in Larix decidua Miller, Picea abies (L.) Karst. and Pinus cembra L. Annales
des sciences forestières, INRA/EDP Sciences, 1998, 55 (1-2), pp.159-172. �hal-00883195�
Original article
Tree water relations and climatic variations at the alpine timberline: seasonal changes of sap flux
and xylem water potential in Larix decidua Miller,
Picea abies (L.) Karst. and Pinus cembra L.
Tommaso Anfodillo Stefano Rento Vinicio Carraro,
Luca Furlanetto Carlo Urbinati Marco Carrer
Dipartimento
Territorio e SistemiAgro
Forestali,University
of Padova,Agripolis,
Via Romea, 16, 35020
Legnaro
(PD),Italy
(Received 15January
1997;accepted
15September
1997)Abstract - Trees
growing
at thealpine
timberline very seldomundergo
severe water stressbecause of
high precipitation during
thevegetative period.
Since trees areadapted
to moist con- ditions, moderate water deficit may lead to a strong reduction intranspiration. Transpiration
and
xylem
waterpotential
were measured in two individuals each of Pinus cembra, Larix decidua and Picea abiesgrowing
at the timberline (2 080 m a.s.l.) in the north-eastern ItalianAlps.
FromJune to October 1996
predawn
waterpotential
was between -0.29 and -1.0 MPa with moderate differences amongspecies. Throughout
thegrowing period
L. decidua showed aprogressive
decrease in the minimum water
potential
(from -0.45 to -1.93 MPa); in P. abies and P. cembra variations were more correlated to weather conditions with minima (-1.2 and -1.49 MPa, respec-tively) during
a milddrought period.
L. decidua showed the meandaily
maximum sap flux den-sity
(about 3.3 dm3dm-2 h-1) while mean maximum values in P. abies and P. cembra wereabout 0.9 and 0.7,
respectively. High daily
fluctuations of sap flow were observed in relation torapid
variations in weather conditions,particularly
in L. decidua.Regardless
ofspecies
a veryhigh
stomatal
sensitivity
to vapour pressure deficit was recorded. The threespecies
seem to haveevolved different
drought
avoidancestrategies.
L. decidua maintained arelatively high transpi-
ration even
during
moderate water deficitperiods
because of itshigh
wateruptake capacity.
During
the samedrought period
P. abies and P. cembra showed an evident reduction in sap flux,suggesting
a watersaving
behaviour. These different responses should be taken into account whenconsidering
the effectsof global change
on timberline trees. (© Inra/Elsevier, Paris.)water relations / timberline /
drought
resistance / stomatalsensitivity
/ climatewarming
effects
*
Correspondence
andreprints
Tel: (39) 49 827 2697; fax: (39) 49 827 2686; e-mail:
anfodill@uxl.unipd.it
Abbreviations: Ψ:
xylem
waterpotential
(MPa); Ψm: minimumxylem
waterpotential
(MPa);Ψpd:
predawn xylem
waterpotential
(MPa); Fd: sap fluxdensity (dm 3
dm-2h -1 );
MWDP: mild waterdeficit
period;
HC:hydraulic
conductance(dm 3
dm-2 h-1Mpa -1 ).
Résumé - Relations
hydriques
des arbres et facteurs du climat à la limite forestièrealpine :
variations saisonnières du flux de sève et du
potentiel hydrique
chez Larix decidua Miller,Picea abies (L.) Karst. et Pinus cembra L. Les arbres situés à la limite forestière dans les
Alpes
sont rarement soumis à des contraintes
hydriques
sévères, car lesprécipitations
durant lapériode
de
végétation
sont élevées. Alors que ces arbres sontadaptés
à des conditions de forte humi- dité, une contraintehydrique
modérée peut conduire à une forte réduction de leurtranspiration.
La
transpiration
et lepotentiel hydrique
ont été mesurés sur deux individus de chacune desespèces :
Pinus cembra, Larix decidua et Picea abies dans la zone de la limite forestière(altitude 2 080 m), dans le nord-est des
Alpes
italiennes. Dejuin
à octobre 1996, lepotentiel hydrique
de base a varié entre -0,29 et -1,0 MPa, avec peu de différences entreespèces.
Aucours de la
période
devégétation,
L. decidua a montré une diminutionprogressive
de sonpotentiel hydrique
minimum(passant
de -0,45Mpa
à -1,93Mpa).
Chez P. abies etP. cembra, les variations de ce
paramètre
étaientplus
fortement corrélées aux facteursclimatiques,
les valeurs atteintes étantrespectivement
de -1,2Mpa
et de -1,49Mpa
pour ces deuxespèces,
lors d’unepériode
de sécheresse modérée. Les valeurs lesplus
élevées dedensité de flux de sève ont été observées chez L. decidua (environ 3,3
dm 3
dm-2h -1 ),
contre0,9 dm3 dm-2 h-1 chez P. abies et 0,7 dm3 dm-2h-1 chez P. cembra. Des fortes variations
journalières
de flux de sève ont été mises en évidence en relation avec les fluctuationsrapides
des conditions
climatiques,
notamment chez L. decidua. Une forte sensibilité des stomates audéficit de saturation de l’air a été observée pour chacune de ces
espèces.
Ces troisespèces
semblent avoir
développé
différentesstratégies
deréponse
à la sécheresse : L. deciduca amaintenu un taux de
transpiration
relativement élevé, même lors d’une sécheresse, en relationavec une forte
capacité
d’extraction de l’eau dans le sol. Au cours de la mêmepériode
de dessèchement, P. abies et P. cembra ont montré une nette réduction de leur flux de sève, cequi indiquerait
unestratégie
d’évitement. Ces différentesréponses
doivent êtreprises
en comptelorsqu’on
s’intéresse aux effets deschangements climatiques
dans cette zone de limiteforestière. (© Inra/Elsevier, Paris.)
relations
hydriques
/ limite forestière / résistance à la sécheresse /régulation stomatique
/réchauffement du climat
1. INTRODUCTION
The altitude of
alpine
timberline ismainly
controlledby
temperature[14].
However,
thegeneral
statement that heatdeficiency during
the short and cold grow-ing
season affects the carbonbudget
oftrees,
decreasing dry
matterproduction [31],
is ofteninadequate
toexplain why
the timberline occurs in different climatic
regions.
In continentalalpine
timberlines(e.g.
AustrianAlps)
anincomplete
devel-opment
of needle cuticlesduring
the shortgrowing period
seems toplay
the mostimportant
role indetermining
severedrought
conditions in thefollowing
winter[3, 12, 32].
Inarctic, temperate-maritime
and
tropical
treelines(Alaska, Washington Cascades,
VenezuelanAndes)
cold tem-peratures seem to have the
major impact
on
limiting physiological
processes: coldsoil,
frozen soil or vascular system, sub-freezing
temperaturesduring
both dor-mancy and
growth periods strongly
affectwater relations of treeline
species
deter-mining
severe stress conditions[13].
As there is a strong influence of abi- otic factors
(i.e.
temperature, wind, pre-cipitation)
onphysiological
responses oftrees at the timberline the effects of cli-
mate
warming might
beparticularly
pro- nounced[17].
There is sound evidence that climatic
changes
can affect the distribution ofplant
communities and shift the range of various
alpine species [21, 22]. Recently,
climatewarming
has beenthought
to be the causeof an altitudinal shift
upwards
inalpine plants [8]
and fordisplacement
of the arc-tic treeline as well as for an increase in
stem
growth
in the Krummholz zone[24].
Palynological
data have outlined the pos- siblemigrations
ofEuropean
flora in rela-tion to climatic variations
[15].
On the
contrary,
no evident effects ofrecent
higher
summertemperatures
on alti- tudinal range have been recorded inalpine
Pinus
sylvestris
and P. cembra[11].
Predictions of
possible impact
ofwarmer
temperatures
upon thephysiol-
ogy of
plants adapted
to cold climates should consider both the effective varia- tions inplant temperature (degree
of aero-dynamic coupling
between theplant layer
and free
atmosphere)
and differentaspects
of
temperature-mediated
processes(freez- ing resistance,
soil temperature and min- eral nutrientsupply, photosynthetic
rate,rate of cell
division,
rate of mitochondrialrespiration) [19].
Among these,
darkrespiration
couldbe crucial since
high
altitudeplants
exhibita much
higher respiration
rate than low-land
species do,
and unless acclimation occurs, this cannegatively
affect theplant
carbon balance
[23].
Further, predictions
are alsodependent
on the
type
of temperature values consid- ered: it isimportant
todistinguish annual, seasonal, daily
means and extremes[18].
Seasonal
monitoring
of the water status in timberline trees in the southernAlps
has allowed their
drought
resistance mech- anisms to be better defined and to makehypotheses
on somepossible
responses to climatewarming.
Our aim is to demonstrate
that, despite regularly
distributedprecipitation (about
400-500 mm between June and
Septem- ber),
trees at the timberline mayundergo
moderate water stresses
(i.e.
reduction instomatal
conductance)
due to theirhigh
stomatal
sensitivity
todrought.
Further-more, these moderate water deficits may
have a stronger
impact
onreducing
tran-spiration
inNorway
spruce(Picea abies)
and Stonepine (Pinus cembra)
than inEuropean
larch(Larix decidua).
The extent of
potential
assimilation reduction will alsodepend
on thechange
in
precipitation regime
associated with therising
temperature. Since the link betweenprecipitation
and temperature in theAlpine region
is not yetfully
understood[35]
and future scenarios are stillcontrasting,
thetrue effects of
higher
temperatures on the timberline are as yet uncertain.Nevertheless, higher
summer temper-atures may
lead,
in thelong
run, to a com-position change
of timberline forests dueto different
drought avoidance strategies developed
inAlpine
timberlinespecies.
2. MATERIALS AND METHODS
Experiments
were conducted on a timber-line ecotone at 2 080 m a.s.l. in the north-east-
ern Italian
Alps
(Dolomites, Cortinad’Ampezzo).
The site has S aspect and 30 %slope.
Here the timberline is formedby
rela-tively
young L. decidua, P. cembra and P.abies mixed stands
invading edges
ofrecently
abandoned pasture lands [7].
June-September
mean
precipitation
is about 450 mm.The
experiment
lasted from 29May-6
October 1996. Six similar-featured trees were
selected (two each of the above-mentioned
species).
In each tree asample
core was col-lected at 1.30 m and
height,
conventional age andsapwood
width were measured (table I).Differences among trees were
expected
as aresult of severe environmental conditions. A
quite good growing potential
of thespecimen appeared comparing
tree age and diameter.Xylem
waterpotential
(Ψ) was measuredweekly
with a pressure chamber on1-year-old
shoots in L. decidua and P. abies and on 1-
year-old
bundle needles in P. cembra. Foursamples
were collected at aheight
of 2 m (twoon the south- and two on the
north-facing
crown) on each treejust
before dawn(predawn
water
potential, Ψpd)
until sunset at 2-h inter-vals. Data were then
averaged
for eachspecies
since no statistical difference was recorded between the two trees and crown aspect.
Xylem
sap fluxdensity
(Fd, dm3 dm-2h -1 )
was measured in each tree
using 2-cm-long continuously
heated sap flowmeters [9]. Sen-sors were inserted into the
xylem
(NWaspect)
1.5-2 m
high
in the stem. Protection fromhigh
solar radiation was ensured both
by insulating
shields
placed
over the sensors and for P. abies and P. cembraby
the dense tree crowns, withground reaching
branches.No alterations in thermal
signal
due to resinemission or wood desiccation were recorded
over the whole
monitoring period. Sap
flowme-ters were heated from 14 June except for two
trees in which
heating began
20days
later.Measurements were taken every I min, aver-
aged
and stored every 15 mins.Sap
flux and waterpotential
data were usedto estimate the
global hydraulic
conductance roots-leaves.Neglecting
the stem-branchcapacitance
effect, theequation describing
sap transport between roots and leaves can be writ- ten as follows [6]:where r is the roots-leaves resistance.
Water
potential
when sap flux is null(Ψ 0 )
was deduced from
predawn
measurements orestimated with linear
regressions using
waterpotential
data and thecorresponding
sap flux values.Specific hydraulic
conductance (HC = 1/r dm3
dm-2 h-1
Mpa -1 )
was calculated as theslope
of the linearregression
of sap flux (Fd)versus the
drop
in the waterpotential
(Ψ)throughout
theday.
In L. decidua data devi- atedslightly
from theregression
line, indicat-ing
a low stem-branchecapacitance
[6]. InP. abies and P. cembra
loops
were widershowing
a less conservative water transport (as indicated from the loweraveraged
regres- sion coefficients - table II)Standard
meteorological
factors were mon-itored every minute,
averaged
and stored every 15 min with a datalogger (Campbell
Ltd CR10) connected to twomultiplexers (Camp-
bell AM32). Power was
provided by
a solarpanel
(Heliostechnology,
50 W) and batteries (140 Ah).Technical and
logistic
support was ensured from the Centre ofAlpine
Environment of theUniversity
of Padova located 20 km away in S.Vito di Cadore.
3. RESULTS
In this
Alpine
area summer is thewettest season
(mean precipitation
of thelast 30 years about 500
mm).
In1996,
dur-ing
the measurementperiod,
we recorded621 mm
(figure 1).
At the end ofJuly
therewas an unusual
dry period (10 days
withrain less than 0.4 mm
d -1
that we will call’mild water deficit
period’ MWDP)
sinceonly
four similarperiods
were recordedfrom 1960 to 1990.
The maximum mean air temperature
was reached at the
beginning
of June(about 16 °C),
followedby
asharp
decrease.
July
andAugust
were moder-ately
coldcompared
withprevious
years.3.1. Shoot water
potential
variationsFigure
2 shows the seasonal course of thepredawn
waterpotential (Ψpd)
ofselected trees
(no ecophysiological
mea-surements were made in the warmest
period).
L. decidua reached the
highest Ψpd (-0.29 MPa)
afterhigh precipitation
at theend of June
(day 174),
it then decreasedgradually
until the end ofAugust,
whenthe minimum was reached
(-1.0 MPa, day 237).
InSeptember
a new increase inΨpd
was recorded
according
with the variationin Ψm when
high precipitation, high
soilwater
availability
and low vapour pres-sure deficit
(VPD)
occurred.P. abies and P. cembra showed more
parallel
variations until the end of the MWDP. In P. cembraΨpd appeared
lower than the other two
species
exceptat the end of
July.
In contrast to L.decidua,
bothspecies
exhibited a reduc-tion
in Ψpd
in relation to the MWDP(about
0.3MPa)
and a slow recovery over 2-3 weeks.The minimum water
potential (Ψm)
curves in P. abies and P. cembra are well related to
precipitation
variations(fig-
ure
3).
The lowest values(-1.18
and-1.49
MPa, respectively)
occurred at theend of the
MWDP,
thehighest (-0.52
and-0.60
MPa)
on 22 June(day 174).
P. cem-bra also had lower Ψm values
probably
due to the
sampling
method(needles
instead oftwigs).
L. decidua showed a
completely
dif-ferent behaviour: Ψm decreased
regularly
from June
(-0.7 MPa)
to the end ofJuly (day 215), stabilizing
at about -1.9 MPa until the end ofAugust (day 237).
After- wards Ψmagain increased, reaching
thevalues of the
beginning
of the season. Inthis
species
no closerelationship
wasfound between short-term variations in
precipitation
and Ψm.3.2.
Daily
and seasonal variations in sap fluxdensity (Fd)
Examples
of Fd and Ψ coursesthrough-
out a
typical day
at thebeginning
ofAugust
are shownin figure
4.Due to
frequent
cloudiness variations athigh altitude,
air temperature(and VPD),
as well as solarradiation, change accordingly.
L. decidua
appeared strongly coupled
with the variations in VPD. Fd increases very
sharply reaching
thedaily
maximum(mean
maximum range 3-3.5dm 3 dm -2 h
-1
)
acouple
of hours after sunrise. Ψdecreases
rapidly
as well: 4 h later it can be1 MPa lower. Ψm is
normally
reachedafter noon and the recovery can be
quite
fast.
Fd in P. abies
began
later and the max-imum value is much lower than L decidua
(mean
maximum range 0.8-1.0dm 3 dm -2
h -1
).
Variations in Fd are lessdependent
on VPD and the course of Ψ
appeared
more
regular.
P. cembra had the lowest Fd values
(mean
maximum range 0.6-0.8dm 3 dm -2
h -1
).
Ψm is reachedjust
after noon butsubsequent
recovery is the slowest among the threespecies.
Fd
daily
sum variations and the average diurnal VPD(from
6 a.m. to 8p.m.)
werecalculated for the entire measurement
period (figure 5).
The mean VPD
throughout
thegrowing
season was
quite low,
asexpected
in atimberline environment. All
species
showed Fd variations
coupled
with VPDbut,
due tohigh
stomatalsensitivity (see below)
Fd is well correlated to VPDonly
below the treshold of 7-8 hPa. When VPD is
higher
stomatal conductance decreasesleading
to a reduction in theexpected
Fd.During
the MWDP nosignificant changes
in Fd were recorded in L.decidua. On
day
205(VPD
6.8hPa) daily
Fd was 33.5
dm 3 dm -2 d -1 ;
onday 210,
at the end of the MWDP
(VPD
5.8hPa),
about 32
dm 3 dm -2 d -1 .
These values wereclose to those recorded on similar
days (e.g. day
196 Fd =34; day
222 Fd =32.5), showing
no influence of the soildrying
out.
On the contrary, P. abies showed an
evident reduction in Fd
during
the MWDP(day
205 Fd = 10 versusday
196 Fd =12.5; day
210 Fd = 7.5 versusday
222 Fd=
11) reaching
about -35 % under thesame VPD conditions. The extent to which P. cembra Fd was influenced
by
MWDPappeared slightly
different from P. abies.At the
beginning
of the MWDP(day 205)
Fd seemed not reduced if
compared
withday
196: 8.5 versus9, respectively,
butafter some
days (day
210 versus222)
Fdappeared strongly
reduced(-35 %).
In order to better define the effect of MWDP on Fd of studied trees a compar- ison between the cumulated Fd over a 7-d wet
period
versus 7 dduring
the MWDPhas been made
(table III).
The effect of MWDP on cumulated Fd of the evergreenspecies
isexpressed
in relation to cumu-lated Fd in L. decidua which is the
only species
not affectedby
watershortage.
Fdis reduced
by
25 % in P. abies and 32 % inP. cembra.
The seasonal maximum in Fd was on
days
230-232 in allspecies, just
afterabundant rainfall even if very
high
tran-spiration
rates were also recorded inJuly.
Scattergrams
of Fddaily highest
val-ues versus VPD at the same time
high-
lights
therelationship
between the former and stomatal control(figure 6). Regard-
less of
species
and tree, Fd increases withincreasing
VPD from 0 to 4-5hPa,
thentends to stabilize and over 8 hPa no rele-
vant increase was recorded. The
shape
ofthe scatters showed
clearly
that astrong
stomatal control
occurred, suggesting
avery
high sensitivity
of thesespecies
towater deficit.
Differences between Larch #1 and #2
are
probably
due to theposition
of theprobes
in the stem. This may occurusing single probe
measurements[20].
3.3. Seasonal variation in
hydraulic
conductance
(HC)
Hydraulic
conductance showedlarge
variations
throughout
the season(figure 7).
The
highest
valuescorresponded
tohigh-
est
precipitation
at about the end of June when air temperature was alsoparticularly
low and soil
evaporation
wasprevented.
All three
species
showed a markeddepression
in HCduring
the MWDP. HCvalues in L. decidua were
always higher
than in the other two evergreen
species
except for two
days
after the end of the MWDP. In P. cembra and P. abies HCdropped
to minimum values at the end of the MWDP. With thefollowing precipi-
tation HC in P. cembra rose
quickly
whileP. abies needed 2 weeks to recover val-
ues
comparable
to thebeginning
of theseason.
4. DISCUSSION
Small variations in
Ψpd
and Ψm both in P. abies and P. cembra over the season are due to thehigh frequency
ofprecipi-
tation but also showed that
they
are able touse the available moisture in an econom-
ical way.
Values of Ψm in P. abies were
signif- icantly higher
than in other studies[25]
suggesting
that a morepronounced
watersaving
behaviour wasdeveloped.
More-over Ψm
appeared
to be muchhigher
thanthe turgor loss
point which,
at thealpine timberline,
was found to berelatively
con-stant
throughout
thegrowing
season atabout -2.8 MPa
[2].
Stomatal controltherefore occurred well above the thresh- old of both
incipient plasmolysis
and ofsignificant
loss ofxylem functionality
inconifers
(at
least 2.5 MPa[5]).
The
roughly
constant decrease inΨpd
and Ψm from the
beginning
of June untilthe end of
July
in L. decidua(figure 3),
followedby
the increase at the end of theseason could be due to an osmotic
adjust-
ment
(even
if it seems to have littleimpor-
tance in
conifers) [16]. Osmoregulation
should allow maintenance of
physiologi-
cal
activity (i.e.
turgormaintenance)
as Ψfalls
[28].
Hence, thespecies
enhanced itswater
uptake ability
in the mid-summer when it is morelikely
that moderate waterdeficit occurs. In L. decidua the value of
Ψm also
appeared
above the threshold forinducing xylem dysfunctions.
It is well known that L. decidua devel- ops a
deep
root system which allows itto utilize water sources in the
deepest
andwettest soil
layers
as also demonstratedusing hydrogen
stableisotope analysis [34].
As
expected,
undernon-limiting
soilmoisture
conditions,
L. decidua exhibiteda Fd
higher (up
to about threetimes)
than the other two evergreenspecies.
Thisdepends mainly
on its deciduous strategy, since the shorter assimilationperiod [26, 32]
must be associated with ahigher pho- tosynthetic capacity
and hence with a moreeffective stomatal gas
exchange.
A
high
level ofcoupling
betweencanopy and
atmosphere
was demonstrated for coniferous stands[27]
and this is par-ticularly
true in a less dense stand as occurs at the timberline. In our trees, VPDappeared
to be themajor
factor determin-ing Fd,
and among thespecies
L. deciduashowed the best
degree
ofcoupling (fig-
ure
4).
This may be due both to the less dense crown structure which determines a more efficient airmixing
and to the lowerstem-branch
capacitance (in
L. decidua and P. abies water is storedmainly
inbranches as demonstrated
by
Schulze etal.
[30]).
Infact,
if the stem and branches have littlecapacity
to store water and desaturate the reservoirs the variations in Fd measured at 1.3 m will bestrongly dependent
on stomatal behaviour. This is alsopartially
confirmedlooking
at thequite good
coherence between variationsin Ψ measured in shoots and Fd
(figure 4).
Less
variability
in Fd of P. abies andP. cembra also suggests a more efficient
water loss control. The lowest Fd are
found in P. cembra and this is consistent with the
widespread
belief that P. cembra is the mostdrought
resistantspecies (with
a water
saving strategy)
at thealpine
tree-line
[32].
Abigger
timelag
between thestart of sap flow and the
decreasing
oftwig
waterpotential
confirmed ahigher
stem-branche
capacitance
of the two ever-green
species.
The course of seasonal Fd
highlighted
a strong
impact
of MWDP on P. abies andP. cembra
(figure
5; tableIII).
Bothspecies
seemed unable to maintain an ade- quate watersupply
to the leaves after afew
days
without rainfall. This led to adecrease in the assimilation rate when the
supposed
most ’favourable’ weather con-ditions
(high
temperature andradiation)
occurred.Stomatal
sensitivity appeared particu- larly pronounced
since stomatal controlbegan
at 4-5 hPa VPD. Lowersensitivity
to soil
drought
andhigher drought
resis-tance has been demonstrated in lower ele- vation
species compared
tohigh
moun-tains
species [4, 25].
Values of HC in P.abies
appeared
similar to other measure-ments at the
same Ψpd
conditions[10].
During
the MWDP the HC decreasedsharply
in all threespecies
but remainedgenerally higher
in L. decidua. Since trees did notexperience xylem
waterpotential
below the threshold of
significant
loss ofxylem functionality
inconifers,
at least2.5 MPa
[5]
thedrop
in HC seemedmainly
to be due to an increase ofhydraulic
resistance between soil and rootinterface. Hence, it
appeared
that soilmoisture could
play
animportant
role indetermining
water stress conditions insome
species
at the timberline. Due to thelowering
of Ψm L. decidua was able to take up water in drier conditions than did P. abies and P.cembra,
whichappeared
more
susceptible
to watershortage.
Theresults showed that,
despite high precipi- tation,
soils athigh
altitude could becomephysiologically dry
becausethey
are shal-low,
discontinuous andhighly permeable.
High temperatures
and VPD not asso- ciated with anadequate
watersupply appeared
to have anegative
effect on P.abies and P. cembra
growth. Since,
in thiszone, the
growing period (considered
asa
period
of wood formation atDBH)
isabout 50 d
[1],
any break in assimilation processes could have a considerableimpact
on total annualgrowth.
Moreover,
since treesadapted
to coldclimates have a
relatively
low tempera-ture
optimum
forphotosynthesis (between
10 and 14 °C[33]) high temperatures
arenot necessary to
develop
maximum assim- ilation rate.In fact no
significant
variations in Fdwere recorded on
bright
and warmdays
as
compared
torelatively cloudy days.
Trees seemed unable to make the most of the fine weather conditions. The
early
stomatal control when VPD
approaches
4-5
hPa, irrespective
ofspecies studied, undoubtedly
affectsgrowth potential.
Thishigh
stomatalsensitivity
was alsoreported
in other spruce
species [13].
The different response recorded in P.
abies and P. cembra as
compared
with L.decidua allows us to
speculate
that in thecase of an increase in air
temperature (and VPD)
the latter could be favoured in com-petition against
the former. Predictionson a
change
in standcomposition
must becarefully
evaluatedconsidering possible
future scenarios of
precipitation
andcloudiness due to climate
warming
as wellas the effect of
higher CO 2
concentrationon tree
growth [29].
If
precipitation
rate,regimes
and cloudi-ness should
change
towards more xericconditions,
as has beenhypothesized [35],
in the
long
term, achange
inspecies
com-position
in timberline should not be exluded.ACKNOWLEDGMENTS
This research was carried out with the finan- cial support of the
Ministry
ofUniversity
andScientific and
Technological
Research (MURST) funds ex40 %. The authors wish to thank theRegole
of Cortinad’Ampezzo
forhaving
allowed thestudy
on their property.Special
thanks to Fausto Fontanella, Roberto Menardi and Giuseppe Sala of the Centre ofAlpine
Environment for theprecious
technical support. We also thank the Albertifamily,
owner of the 5 Torri
Refuge,
for the kind hos-pitality
offeredthroughout
the work.REFERENCES
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primi risultati di un’indagine nelle Alpi ori- entali, Proc. VII Congres S.It.E. Napoli, 1996, pp. 35-38.
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nelle relazioni idriche di rametti di abete rosso
lungo un gradiente altitudinale, in: Anfodillo T., Urbinati C. (Eds.), Ecologia delle foreste di alta quota, Proc. XXX Corso di Cultura in
Ecologia, University of Padova, 1993, pp.
143-171.
[3] Baig M.N., Tranquillini W., Studies on upper timberline: morphology and anatomy of Nor- way spruce (Picea abies) and stone pine (Pinus cembra) needles from various habitat conditions, Can. J. Bot. 54 (1976) 1622-1632.
[4] Barton A.M., Teeri J.A., The ecology of ele-
vational position in plants: drought resistance
in five montane pine species in Southern Ari- zona, Am. J. Bot. 80 (1993) 15-25.
[5] Cochard H., Vulnerability of several conifers to air embolism, Tree Physiol. 11 (1992) 73-83.