Rötzer, T. Seifert, T. Pretzsch, H. (2009): Modelling above
and below ground carbon dynamics in a mixed beech and spruce stand influenced
by climate. Eur J Forest Res (2009) 128: 171-182
Abstract:
Tree growth and carbon dynamics
are important issues especially in the context of climate change.
However, we essentially lack knowledge about the effects on carbon
dynamics especially in mixed stands. Thus, the objective of this study
was to test the effects of climatic changes on the above and below
ground carbon dynamics of a mixed stand of Norway spruce (Picea abies [L.] Karst.) and European beech (Fagus sylvatica
L.) by means of scenario simulations. To account for the typical tree
interactions in a mixed-species stand a spatial explicit tree growth
model based on eco-physiological processes was applied. Three different
climate scenarios considering altered precipitation, temperature, and
radiation were calculated for an unthinned and a thinned stand. The
results showed significant changes of above and belowground biomass
over time, especially when temperature and radiation were increased
additionally to decreased precipitation. The reduction in biomass
increments of Norway spruce were more attenuated above than below
ground. In contrast, the results for beech were the opposite: The
belowground increments were reduced more. These results suggest a shift
in the species contribution to above and belowground biomass under
dryer and warmer conditions. Distinct effects were also found when
thinned and unthinned stands were compared. A reduced stand density
changed the proportions of above and below ground carbon allocation. As
a main reason for the changed growth reactions the water balance of
trees was identified which lead to changed biomass allocation pattern.
Pretzsch, H. (2009):
Re-evaluation of allometry. State-of-the-art and perspective regarding
individuals and stands of woody plants. Progress in Botany, Vol. 71., 2009 in
press
Abstract:
Allometry in its broader
sense is concerned with the size of organisms and its consequences for their
shape and functioning. Since the postulation of the allometric equation in the
1930s, allometry in a narrow sense refers to analysis and modelling of
logarithmic transformed bivariate size data by linear regression techniques.
This review first points
out that allometric research built up a valuable set of hypotheses and
biometrical methods for analysing size of organisms and its consequences for
their shape and functioning. Then, a summary of the knowledge about allometry
of woody plants and populations will unmask the search for overarching general
allometric exponents of shape and form development largely as a hunt for a
phantom. Tree size development and self-thinning processes in forest stands
give evidence that allometric exponents certainly lie in a narrow corridor but
are species specific and superimposed by site conditions, mechanical
disturbances, competition and other types of stress. The discussion states that
as long as allometry searches for universal constants to a certain extent it
stills our innate desire to reduce complexity and generalise. However, time is
ready to focus on and understand the differences between the species, sites
etc. in order to contribute to a better system understanding. It is concluded
that allometry has to draw attention both to the internal size-driven allometric
partitioning process and to the external factors which determine optimal
biomass allocation. And at best, allometric research should analyse both
factors in order to understand and integrate them. A systematic analysis,
ordering and causal explanation of allometric exponents, which reflects an
individuals’ tricks and traits of optimising fitness, may provide an important
link between plant genetics, physiology, plant biology and population biology.
In contrast, application of inaccurate and imprecise general scaling rules can
cause considerable flaws in modelling, prognosis and ecosystem management.
Wipfler, Ph. Seifert, T. Biber, P.
Pretzsch, H.
(2009): Intra-annual growth response of adult Norway spruce (Picea abies L.)
and European beech (Fagus sylvatica L.) to an experimentally enhanced, free-air
ozone regime. Eur J Forest Res (2009) 128: 135-144
Abstract:
Several
findings indicate an
impact of ozone on stem diameter growth leaving the question
unanswered, if and how the intra-annual growth pattern is changed. In
this study the hypotheses are tested, that (1) ozone will alter the
absolute growth and (2) alter and shift the period of growth activity
within a year. Our data originates from the free air ozone fumigation
experiment ‘Kranzberger Forst’ in a mixed stand of Norway
spruce and
common beech near Freising/Germany. Annual and intra-annual growth
reactions of a sample of five adult beech and five spruce trees,
exposed to double ambient ozone were examined and compared to the same
number of untreated reference trees. Diameter increments were measured
with plastic diameter girth bands and high-resolution, automatically
logging micro-dendrometers, mounted at breast height (1.3 m). We
used
the increment data from the growth periods 2000 to 2005. The
high-resolution micro-dendrometer data were examined by fitting a
Weibull function to the standardized annual growth profiles to obtain
curve parameters for statistical tests. We estimated the parameters
‘T’ which represents the point of time, when 63% of the
annual diameter increment is performed and the parameter
‘m’,
the Weibull module, which was used as an indicator for the span of time
needed to complete the annual growth. The statistical significance of
these curve parameters, together with the absolute diameter increment,
was tested by use of mixed regression models. The analysis of the
growth curve parameters revealed a significantly altered intra-annual
growth pattern of both species induced by ozone. Spruce under ozone
showed reduced absolute annual diameter increment and a preponed growth
activity compared to untreated trees. Beech’s absolute diameter
increment was not affected under ozone, but its growth activity was
delayed. For both species, ozone fumigation did not alter the
individual length of the annual growing season. These results are
discussed with respect to drought, tree ring anatomy and tree
allometry. The study shows that ozone is able to change growth
behaviour of trees even if increment losses are not obvious.
Pretzsch, H. Mette, T. (2008): Linking stand
level self-thinning allometry to the tree-level leaf biomass allometry. Trees 22:
611–622
Abstract:
Long-term experimental plots of Norway spruce and European beech are
investigated for a link between stand-level self-thinning and
tree-level leaf biomass allometry. Self-thinning refers to the finding
of Reineke (1933), who postulated for unthinned forest stands that

w
with β = −1.605; i.e. an increase of mean (quadratic) diameter d
q
by 1% results in a decrease of tree number N by 1.605%. On the individual tree level, leaf biomass (w
L) can be related allometrically to the tree diameter d: L = adα.
If we assume that (a) the stands have reached the ceiling leaf area,
(b) the specific leaf area (leaf area/leaf weight) is constant, and (c)
differences resulting from the use of mean quadratic diameter or
individual tree diameter are negligible, then the decrease in the
stands’ leaf biomass due to the trees lost in self-thinning must be
compensated by an equivalent increase in the remaining trees’ leaf
biomass. This means, the absolute slope of the individual trees’ leaf
biomass allometry α and the self-thinning allometry β would be equal
and just have the opposite sign: α = −β.
The analysis of the two long-term plots reveals that α is stronger than
β, both for spruce (β = −1.744, α = 1.840) and especially for beech
(β = −1.791, α = 2.181). The cause is traced back to a changing average
specific leaf area during stand development [assumption (b) is wrong].
The results do not only bridge a gap between tree and stand allometry,
but also emphasize an important effect for the understanding and
modelling of the resource allocations in trees and forests.
Seifert, T. (2007): Simulating the
extent of decay caused by Heterobasidion annosum s. l. in stems of Norway
spruce. Forest Ecology and Management 248: 95-106
Abstract:
Heterobasidion annosum (FR.) BREF. sensu lato causes severe economic
damage in stands of Norway spruce (Picea abies [L.] Karst). The primary
damage is the deterioration of timber by decay. Secondary damage can be
attributed to higher risks of windthrow and stem breakage, growth
reduction of infected trees as well as higher machining and handling
costs for decayed stems during grading and processing. Regardless of
the importance of this pathogen there are very few software tools which
support management decisions in red rot affected forests and none of
them are parameterised with data from Central Europe. The present study
aimed to develop a model which is able to spatially predict the extent
and degree of decay in the stem as well as its effects on the growth of
Norway spruce. This involves the integration of several sub-models into
a tree growth simulator: (i) diameter of decay, (ii) height of decay,
(iii) form of decay, (iv) degree of decay, and (v) feedback of the
pathogen on tree growth. The model is parameterised mainly from
published data of other authors. The input for the time of infection of
a tree is delivered from a separate model. A grading algorithm is used
to evaluate the impact of different scenarios on the revenue of
infected stands in typical stands of Norway spruce in Germany. This
integrated system of growth and red rot simulation is able to support
management decisions on various levels and documents that if red rot is
not taken into consideration in the affected stands, clear
misinterpretations and thus inaccuracies will arise in the economic
results from tree growth simulators. The need for further research was
identified especially in model validation and the tree-pathogen
interaction.
Pretzsch, H (2006b):
Species-specific allometric scaling under self-thinning: evidence from
long-term plots in forest stands. Oecologica (2006) 146:
572-583.
Abstract:
Experimental plots covering a 120 years’ observation period
in unthinned, even-aged pure stands of common beech (Fagus sylvatica),
Norway spruce (Picea abies), Scots pine (Pinus sylvestris), and common
oak (Quercus Petraea) are used to scrutinize Reineke’s (1933)
empirically derived stand density rule (

, N = tree number per unit area,

= mean stem diameter), Yoda’s (1963) self-thinning law based on Euclidian geometry (

= mean biomass per tree), and basic assumptions of West, Brown and Enquist’s (1997, 1999) fractal scaling rules (

w = biomass per tree, d
= stem diameter). RMA and OLS regression provides observed allometric
exponents, which are tested against the exponents, expected by the
considered rules. Hope for a consistent scaling law fades away, as
observed exponents significantly correspond with the considered rules
only in a minority of cases: (1) exponent r of

varies around Reineke’s constant −1.605, but is
significantly different from r=−2, supposed by Euclidian or
fractal scaling, (2) Exponent c of the self-thinning line

roams roughly about the Euclidian scaling constant −3/2, (3) Exponent a of

tends to follow fractal scaling 8/3. The unique dataset’s evaluation
displays that (4) scaling exponents and their oscillation are
species-specific, (5) Euclidian scaling of one relation and fractal
scaling of another are coupled, depending on species. Ecological
implications of the results in respect to self-tolerance (common oak
> Norway spruce > Scots pine > common beech) and efficiency of
space occupation (common beech > Scots pine > Norway spruce >
common oak) are stressed and severe consequences for assessing,
regulating and scheduling stand density are discussed.