Wind and remnant tree sway in forest cutblocks. III. a windflow model to diagnose spatial variation

https://doi.org/10.1016/S0168-1923(98)00121-XGet rights and content

Abstract

Root-mean-square tree sway angle (σθ) can be related to the r.m.s. value (σu|u|) of the wind `force' u|u|, specified nearby. Therefore the spatial pattern of wind statistics over the landscape, if known, arguably maps the relative risk of windthrow – suggesting a wind model can provide the basis to interpret spatial patterns of windthrow, and guide strategies with respect to that concern. To test this idea, we adopt a simple flow model able to describe both the mean wind (U) and kinetic energy of the turbulence (k), viz. Reynolds' equations closed using eddy-viscosity Kλk1/2, where λ is the turbulence lengthscale. We first compare this model with others' measurements of wind near forest edges, then simulate our own observations, which spanned arrays of cutblocks and intervening forest blocks in the Boreal forest (periodic spacing 1.7h or 6.1h, where h is mean tree height). We show that the model predicts well the spatial variation of the mean windspeed and turbulent kinetic energy, these being the wind statistics having greatest impact upon tree sway. Model-implied spatial patterns of r.m.s. wind force (σu|u|) agree closely with those observed, and in conjunction with a tree-motion model, imply tree sway (σθ).

Introduction

Management trials in the boreal mixedwood forest of northern Canada are evaluating felling practises that, at the time of aspen harvest, preserve the spruce understory (`released spruce') for later cutting. It is considered necessary to leave uncut or partially-cut forest strips to shelter the selectively-cut zones, because the previously-sheltered remnant spruce are very vulnerable to windthrow. An overall description of this long-term, practically-oriented project, which is being carried out near Manning (Alberta) by Forestry Canada and partners, is given by Navratil et al. (1994). The work we report here (and in companion papers, Flesch and Wilson, 1999aFlesch and Wilson, 1999b) was initiated in the hope of interpreting the observed spatial variation of tree windthrow across such arrays of cutblocks, so as to permit generalisation. It involves our own measurements of turbulence and tree sway in two cutblocks, each the leeward member of a periodic series; an analysis of the response of instrumented trees to the wind forcing; and, in this paper, an attempt to establish a framework for generalisation of our findings by numerically modelling the winds.

The link between tree sway statistics and wind statistics is discussed at length by Flesch and Wilson (1999b). Briefly, we treated the tree as a rigid rod, free to swing about a ground-level pivot in response to the wind force, but under the moderation of an angular spring and damper. We derived a transfer function relating the short-term power spectrum Sθ of tree angular displacement (θ) to the concurrent power spectrum Su|u| of the wind force u|u|, where u is the instantaneous alongwind velocity component, measured nearby. By `short-term' statistics, we mean statistical properties (standard deviations of tree sway angle σθ and of wind force σu|u|, variance spectra Sθ, Su|u|, etc.) defined by a sample taken over about 15 to 60 min., such intervals being sufficiently short that `external' or large-scale conditions are roughly constant, but sufficiently long that many `cycles' of the rapid turbulent variations are captured. Thus the `view' of our windthrow analysis consists of (say) 30 min. snapshots, from which a longer-term view may be constructed by integration; and the fluctuating (turbulent) variables, e.g. the alongwind velocity u, are decomposedu(x,y,z,t)=U(x,y,z)+u′(x,y,z,t)into sums of the average (in this case, the mean alongwind velocity U, a function of position only) and the instantaneous deviation (or fluctuation, here u′) from it. This terminology (upper-case for mean values; prime for fluctuation from average) will apply throughout our paper.

Returning to our tree sway model, the wind-force spectrum Su|u| was observed not at the `subject' remnant tree, but merely, at the same alongwind location relative to the upwind edge of the cutblock, and at a convenient, arbitrary height (9 m). We found that normalized wind force spectra Su|u|/σ2u|u| were similar at all points across the cutblocks (i.e. practically invariant), so that the sway (σθ) of a tree, no matter where located, could be definitively related to σ2u|u| at that point. But in turn, the force-variance σ2u|u| can be determined from the lowest order statistics of the windσ2u|u|≈σ2uu≡σ4uKtu−1+4Uσu2+4UσuSkuwhere the right-hand equality is exact. Within our framework then, the wind statistics governing root-mean-square (r.m.s.) tree sway are: mean U, variance σ2u, skewness Sku, and kurtosis Ktu. A sensitivity analysis (see Appendix A) indicates that under conditions typical of the flow in our Manning cutblocks (Sku  1, Ktu  4), spatial modulation of the wind-force variance (and thus of σ2θ) is controlled, in order of importance, by spatial variation in the velocity variance σ2u (one component of the turbulent kinetic energy1), and in the mean velocity U. Thus for the remainder of this paper, our focus is on modelling the spatial variation, around and about forest edges, of these principal wind and turbulence statistics, U and k. As regards the connexion of our method to the practical issue of tree windthrow, by hypothesizing that the spatial pattern of wind statistics implies the corresponding spatial pattern of windthrow, we obviously are assuming that the key factor in the cross-landscape variation of treefall susceptibility is the wind forcing, rather than any systematic variation in soil conditions, rooting depth, tree health, etc. It is also implicit that we presume extreme tree displacements (or wind forces) scale with the standard deviation σθ (or with σu|u|).

Having motivated our focus on mean wind (U) and turbulence (k) in forest clearings, we now review previous efforts to model forest edge flows; describe a numerical windflow model, developed by Wilson et al. (1998) specifically for the description of disturbed canopy winds; compare simulations using that model against others' observations of forest-edge flows; and finally simulate the spatial pattern of the wind and turbulence in our cutblocks at Manning for comparison with our observations.

Section snippets

Windflow across forest boundaries, and models thereof

We have elsewhere (Flesch and Wilson, 1999a) discussed the experiments to date on forest edge flows, in comparison with our own. Here we consider only the issue of whether or not one might expect to see universal patterns across such experiments.

Shinn (1971) analysed his own and others' experiments on forest edge flow. His observations of wind in uniform canopies are also important: he showed that due to the Coriolis force there occurs a large swing (about 80°) in mean wind direction between

Windflow model

We consider only flows whose mean properties are constant along an axis (y) oriented parallel to forest edges, and assume the mean wind is oriented approximately perpendicularly across the edges, i.e. along the x-axis. When we apply our model to simulate our cutblock flows at Manning, that symmetry assumption is not exactly valid, for if XC, YC denote the alongwind- and crosswind-widths of the cutblocks, then the aspect ratio YC/XC was not very large (3, 15 for the wide and narrow cutblocks,

Simulation of Raynor's forest-edge flow

Raynor (1971) reported mean profiles of horizontal windspeed at various distances from the upwind edge of a pine forest, during periods of flow at near-normal incidence to the forest edge. We simulated Raynor's experiment with the full model (i.e. including a full PBL, with Coriolis forces and the transverse component V) described in Section 3. Our motivation in doing so was to determine whether the excellent simulations of Raynor's experiment given by Li et al. (1990) rested in any essential

Simulation of wind-tunnel clearing-edge flow (Abbott's booby study)

In a study concerned with nesting habits of birds near forest clearings, Raupach et al. (1987) (hereafter RBG) measured mean windspeed and turbulence statistics across clearings of widths 4.3h and 21.3h in a model canopy, within a wind tunnel. The same canopy was later used in the `Furry Hill' experiments (Finnigan and Brunet, 1995), but some unexplained and possibly important differences are evident between the respective equilibrium flows (i.e. between dimensionless flow properties upstream

Simulation of periodic forest cutblocks (Manning, Alberta)

We now arrive at the issue motivating this paper: can a flow model sufficiently well diagnose wind and turbulence within forest cutblocks as to provide (via the wind statistics/tree sway connection established by Flesch and Wilson, 1999b) a useful indication of implied (remnant) tree sway – an issue to be tested by comparison of our model, which we have argued is as well-tested and as successful as any earlier effort to describe flow in irregular forests, against observations in the Manning

Model investigation of the effect of forest border width

As an example of the potential of a windflow model to evaluate strategies for minimising windthrow, we shall investigate the consequence of using forest strips of reduced width, XF = 3h or XF = 1h, to shelter remnant spruce in cutblocks of unaltered width Xc = 6.1h.

The sole difference between the simulations required for these three cases (XF/h = 6.1, 3, 1) is the distribution of forest-drag. We made no changes to the grid distribution, to the location of the large upstream `reference clearing' wherein

Conclusions

Our aim has been to combine a high-resolution (order 1 m) wind and turbulence model, with a tree-motion model, to infer statistics of remnant tree sway in forest clearings. To that end we have adapted the K-theory closure of Wilson et al., (1998; WFR), tested it against our own and others' observations of forest-edge flows, and showed it performs at least as well as the more-complex models of earlier authors. With appropriate choices of domain size, resolution, etc., simulations show quite good

Acknowledgements

Funding was provided by the Manning (Alberta) Diversified Forest Trust Fund, and Forestry Canada; and JDW acknowledges research grants from NSERC (Natural Sciences and Engineering Research Council of Canada) and Environment Canada. We are grateful to Dr. S. Navratil and L. Brace for helping us initiate the project, and to T. Thompson for his help in the field.

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