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2009
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11 pages
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Calibration of the self-thinning frontier in even-aged monocultures is hampered by scarce data and by subjective decisions about the proximity of data to the frontier. We present a simple model that applies to observations of the full trajectory of stand mean diameter across a range of densities not close to the frontier. Development of the model is based on a consideration of the slope s = ln(N t /N t-1 )/ln(D t /D t-1 ) of a log-transformed plot of stocking N t and mean stem diameter D t at time t. This avoids the need for subjective decisions about limiting density and allows the use of abundant data further from the selfthinning frontier. The model can be solved analytically and yields equations for the stocking and the stand basal area as an explicit function of stem diameter. It predicts that self-thinning may be regulated by the maximum basal area with a slope of -2. The significance of other predictor variables offers an effective test of competing self-thinning theories such Yoda's -3/2 power rule and Reineke's stand density index.
2.4. Analysis of a model with three constraints on population growth • • • • • • • • • 2.5. Effect of a reduction in illumination on population trajectories in a two-constraint model ••••• 3. 1. Typical dynamic behavior of the simulation model •• 3.2. Variations in the self-thinning trajectory due to stochastic factors in the simulation model ••• 3.3. Effect of the allometric power, p, on the self-thinning 1 i ne • • • • • •. • •. .. • 3.4. Effect of the density of biomass in occupied space, d,. .
Ecological Monographs, 1987
The self-thinning rule predicts that for a crowded even-aged plant population a log-log plot of average plant mass vs. plant density will reveal a straight "self-thinning" line of slope-%. The rule is supported by examples from many individual populations, and by the existence of an interspecific relationship that yields a line of slope-% in a loglog plot displaying average mass and density data from many populations of different species. I examined and reanalyzed the evidence to evaluate the strength of support for this widely accepted rule. Some problems in fitting thinning lines and testing agreement with the rule have no truly satisfactory solution, but three improvements on commonly used methods were made: the analysis related stand biomass density to plant density because the alternative of relating average plant mass to plant density is statistically invalid; principal components analysis was used rather than regression, because regression relies on unrealistic assumptions about errors in the data; and statistical tests of hypotheses were used to interpret the results. The results of this reanalysis were that 19 of 63 individual-population data sets previously cited in support of the thinning rule actually showed no significant correlation between stand biomass density and plant density, and 20 gave thinning slopes significantly different (P < .05) from the thinning rule prediction. Four other analyses provided additional evidence against a single quantitative thinning rule for all plants: slopes of the thinning lines were more variable than currently accepted, differed significantly among plant groups, were significantly correlated with shade tolerance in forest trees, and differed among stands of the same species. The same results held for the intercepts of self-thinning lines. Despite the failure of the thinning rule for individual populations, the combined data for all populations are still consistent with an interspecific relationship of slope-3/,; therefore, the existence of the interspecific relationship does not necessarily support the withinpopulation thinning rule. The within-population and interspecific relationships are apparently different phenomena that may arise from different constraints, so the two relationships should be tested and explained separately.
Journal of Ecology, 2005
1Many theoretical models have been proposed to explain the empirical self-thinning relationship given by Yoda et al. in 1963 for even-aged, monospecific stands of plants, but the models are inadequate to allow consensus on the processes driving variation in density-dependent mortality and self-thinning.2Most non-individual based models (non-IBMs), and many IBMs, employ a common representation of competition in which a finite amount of potential crown area remains completely allocated throughout self-thinning, making stand density inversely proportional to mean projected crown area.3This representation entails four assumptions regarding the competition process: the population is adequately represented by the mean plant; total stand resource utilization is constant throughout self-thinning; competition is a horizontal packing process; and differences in initial stand conditions may affect the rate of competition but not the process itself.4Reviewing published empirical data, the competition literature and the logical implications for the self-thinning process shows that all four assumptions are untenable as generalizations. Unfortunately, their application provides neither a mortality-inducing mechanism nor insight into the relationship between stand growth and mortality.5Explaining the observed variation in self-thinning relationships therefore requires improved representation of the competition process. This improvement is likely to require IBMs that explicitly represent variation in plant size or resource acquisition, two-dimensional stand distribution, dynamic rather than static stand resource utilization, and, perhaps, explicit three-dimensional stand development. Most importantly, the requirement for explicitly modelling mortality mechanisms implies that whole plant models may be insufficient for insight into the self-thinning process.6The review reinforces the need to assess mechanistic models for more than their ability to reproduce a single, high-level pattern. Such models should be assessed for their ability to simultaneously reproduce multiple features selected from the levels of both the modelled mechanisms and the high-level patterns.7Progress in understanding the observed variation in self-thinning currently requires a shift from searching for universal insight into the modelling of specific mechanisms for specific plant types, eventually leading to a broader theory explaining how variation in plants affects the competition process.Many theoretical models have been proposed to explain the empirical self-thinning relationship given by Yoda et al. in 1963 for even-aged, monospecific stands of plants, but the models are inadequate to allow consensus on the processes driving variation in density-dependent mortality and self-thinning.Most non-individual based models (non-IBMs), and many IBMs, employ a common representation of competition in which a finite amount of potential crown area remains completely allocated throughout self-thinning, making stand density inversely proportional to mean projected crown area.This representation entails four assumptions regarding the competition process: the population is adequately represented by the mean plant; total stand resource utilization is constant throughout self-thinning; competition is a horizontal packing process; and differences in initial stand conditions may affect the rate of competition but not the process itself.Reviewing published empirical data, the competition literature and the logical implications for the self-thinning process shows that all four assumptions are untenable as generalizations. Unfortunately, their application provides neither a mortality-inducing mechanism nor insight into the relationship between stand growth and mortality.Explaining the observed variation in self-thinning relationships therefore requires improved representation of the competition process. This improvement is likely to require IBMs that explicitly represent variation in plant size or resource acquisition, two-dimensional stand distribution, dynamic rather than static stand resource utilization, and, perhaps, explicit three-dimensional stand development. Most importantly, the requirement for explicitly modelling mortality mechanisms implies that whole plant models may be insufficient for insight into the self-thinning process.The review reinforces the need to assess mechanistic models for more than their ability to reproduce a single, high-level pattern. Such models should be assessed for their ability to simultaneously reproduce multiple features selected from the levels of both the modelled mechanisms and the high-level patterns.Progress in understanding the observed variation in self-thinning currently requires a shift from searching for universal insight into the modelling of specific mechanisms for specific plant types, eventually leading to a broader theory explaining how variation in plants affects the competition process.
Research Letters in Ecology, 2007
The constancy of biomass density was considered in an entire plant population p by combining two adjacent populations p 1 and p 2 for which the self-thinning rule is assumed to be satisfied independently and each biomass density is also assumed to be the same constant value. Under these assumptions, the biomass density d in a population p was formulated as d = c((km −α + 1)(km + 1)/(km 1−α +1)(k+1)), where c is biomass density of p 1 and p 2 , and k and m are stand area and density ratio of p 1 to p 2 , respectively, and α is the self-thinning slope. In the case of m = 1, the value of d in the above equation is always larger than unity. This fact indicates that the biomass density in a combined population p is not equal to the biomass density c in each population p 1 or p 2 because of systematic error.
Ecology, 1987
The -3/2 power rule of self-thinning, which describes the course of growth and mortality in crowded, even-aged plant stands, predicts that average mass is related to plant density by a power equation with exponent -312. The rule is widely accepted as an empirical generalization and quantitative rule or law. Simple geometric models of space occupation by growing plants yield a power equation, but the exponent can differ from -3/2 when realistic assumptions about the allometric growth of plants are considered. Because such deviations conflict with the empirical evidence for the -3/2 value as a lawlike constant, the geometric models have not produced an accepted explanation and the thinning rule remains poorly understood. Recent studies have concluded that thinning exponents can deviate more widely from -3/2 than previously thought, motivating the present re-evaluation of the geometric explanation. I extend the simple models to predict the relationships of the thinning exponent to allometric exponents derived from commonly measured stand dimensions, such as height, average mass, average bole diameter at breast height (DBH), and average bole basal area. If the form and exponent of the thinning equation arise from the geometry of space filling, then thinning exponents should be systematically related to the exponents of allometric equations relating average height to average mass, average height to average DBH, and average height to average basal area. I also predict some values for the slopes and intercepts of regression lines relating thinning exponents to the allometric exponents. The predictions are verified by statistically comparing the thinning exponents and allometric exponents of self-thinning populations. The expected negative correlations are present and statistically significant (P 5 .05), and the slopes and intercepts of linear regressions relating thinning exponents to allometric exponents are near the predicted values. These results support the hypothesis that the thinning equation arises from the geometry of space filling, but recognition that thinning exponents differ from -3/2 as predicted by simple geometric considerations weakens the case for a quantitative rule or law.
Ecology and Evolution
Size-density relationships are essential for understanding and predicting core ecological processes. These relationships highlight how the number of individuals in a population decreases with the progression of time, or more specifically as the individuals increase their average size. Therefore, a size-density relationship is a fundamental result of highly dynamic competition and mortality processes. This concept is an essential aspect of many ecological disciplines including forest (Jack & Long, 1996), wildlife (Jonsson, 2017), and fisheries ecology (Elliott, 1993). Self-thinning results from a frontier relationship between stand density and tree size (Bi et al., 2000). That is,
The American Naturalist, 1989
In a plot of the logarithm of average plant mass versus the logarithm of plant density, measurements of crowded stands of different plant species form a linear band of slope -% that extends over 7 orders of magnitude of plant density and almost 10 orders of magnitude of average plant mass White , 1985;; Westoby 1984). The existence of such a simple relationship across plant species ranging from mosses to trees has been judged remarkable and cited as strong support for the self-thinning rule, which states that the temporal progress of growth and mortality within an individual crowded, evenaged stand will trace a line of slope -% in the same double-logarithmic plot (
Silva Fennica, 2002
Pukkala, T., Miina, J. & Palahí, M. 2002. Thinning response and thinning bias in a young Scots pine stand. Silva Fennica 36(4): 827-840.
2015
This study examines tree and stand response to a gradient of commercial thinning intensities and nitrogen fertilization (200 kg N ha −1) in nine jack pine (Pinus banksiana) stands of Eastern Canada over a period of 14 years. Thinning intensity ranged from 0% basal area removal in control plots to 64% in thinned plots. Tree diameter increment, absolute and relative volume increment and mean volume increased with thinning intensity and were higher in fertilized plots. Individual tree response depended on tree diameter, with smallest trees exhibiting highest relative volume increment to thinning intensity. Stand basal area increment was positively associated to initial stand basal area and negatively to stand age. In thinned and fertilized plots, stand volume increment was higher and natural mortality lower than in fertilized only and unfertilized control plots over the 5-14 year period after thinning. However, the positive effect of fertilization on tree volume increment decreased with thinning intensity. Despite positive individual tree growth responses to thinning and fertilization, residual stand volume increment decreased with increased thinning intensity in both fertilized and unfertilized plots. While total cumulative stand volume (harvested + residual) also decreased with thinning intensity in unfertilized plots, comparable total
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