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Mixedwood Growth Model
Features/Functions


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OverviewReturn to top of page

The Mixedwood Growth Model (MGM) is a deterministic, distance-independent, individual tree-based, stand growth model that can summarize both tree and stand characteristics. Summaries are provided in the form of yield tables portraying averages and totals for the conifer and hardwood tree species. The stand, including juvenile stands (<1.3m height), to be grown may be provided as a tree list or stand table or trees may be simulated based on an assumed tree diameter distribution. The primary focus of the model is on white spruce and aspen, typically growing together in varying degrees of mixture. Lodgepole pine and black spruce are also included but less emphasis has been placed on development of relationships for these species.


Stand volume per hectare is a primary model output for management purposes. It is determined based on the stand density, the species composition, diameters, and the tree heights. Mortality and growth relationships are used to predict these changes as the stand age increases. Both tree (e.g. species diameter, height, and relative tree size) and stand characteristics (e.g. site index, density, and basal area) influence these predictions. Most variables are maintained separately for each major species group.

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How MGM WorksReturn to top of page

Growth Relationships

The MGM stand growth simulator software consists of several Microsoft Excel workbooks and the user interface. The "MGM.xls" and related workbooks ("MGM Crop Plans.xls", and "MGM Records.xls") allow the analyst to compose, execute, and save crop plans and results of growth simulations for one or more stands or management scenarios.

MGM uses crop plans (Crop Plan, Design and Test) to control simulations. A crop plan is a sequence of "events" that determine the source and characteristics of the stand, the growth schedule, and the timing and method of other activities like thinning, harvest, and regeneration. Then, following the growth schedule, the tree list and other stand characteristics are repeatedly projected 1 year into the future by updating tree diameters, heights, and densities to reflect increment and mortality. At the end of each projection period, a stand yield summary report is prepared. This cycle continues until the growth schedule is completed.

The interface adds an MGM Toolbar to the Microsoft Excel interface. The toolbar controls the simulation by invoking dialogs to construct and execute crop plan "events". The interface also allows you to save crop plans and simulation results for one or more stands or management scenarios.

In the earlier versions, the model was primarily based on diameter rather than age and height as is typical with many whole stand (yield table) models. Age was not used in estimating any stand characteristics or in predicting growth or mortality. Age was provided only as an approximate stand age, a calendar year, or as elapsed time since the projection began. It was the responsibility of the analyst to interpret the meaning of the age label.

This version includes preliminary relationships that link growth and mortality to site index as well as the earlier relationships based on variables other than age. Tree age is maintained for each tree, and it is not the same as stand age (elapsed time since harvest or disturbance). Mean annual increment based on stand age is provided as part of the yield report.

Many growth relationships for older trees are based on variables other than age (Huang and Titus 1993, Burkhart et al 1972, Curtis at el. 1981, Wykoff et al. 1982). The seedling (juvenile stand) model allows linking the age variable needed when producing yield tables with a stand growth model that may not require age. The juvenile stand model is also useful in simulating the tree height until it reaches a 1.3 metre height. At that point diameter at breast height is available and can be used in other tree growth relationships (Huang and Titus 1993, Arabatzis and Burkhart 1992, Wang and Hann 1988).

Database

All basic growth relationships were derived from data collected in Alberta. Tree volume and height-diameter estimation is based on regional relationships developed by the Alberta Environment, Land and Forest Service and the British Columbia Ministry of Forests.

Model Components (Interface)

Input

Stand simulation input can be a tree list or stand table, or trees may be simulated based on an assumed tree diameter distribution. MGM requires both region and tree species variables as input. Three regional classification are recognized: the Alberta Sampling Region (VSR), the Natural Region of Alberta, and two British Columbia Bio-geo-climatic Ecological Classification (BEC) zones, Boreal White Spruce (BWBS), and Sub-Boreal Spruce (SBS). It uses 16 individual tree species grouped into 4 major groups: white spruce, pine, aspen, and black spruce Creating and Importing Stand Data.

The growth simulation process requires a growth schedule and the stand data to be projected. The growth schedule is a list of the intervals between yield reports and the stand consists of five information items: name, year, site, tree list, and treatment parameters

Output

Stand summary reports are generated according to the Schedule and include: stand age, total density/ha, average DBH, average height, total basal area/ha, total volume/ha, and mean diameter volume increment (total volume/ha divided by average DBH) Figure 1. These characteristics are presented for two broad species groups: coniferous and deciduous.

Stand summary statistics are computed based on all trees at or above the minimum utilization DBH. Total volume/ha is estimated using the tree volume function and merchantability settings. At present, no deductions are made for defect or breakage. If necessary, regional height/diameter relations (Huang, et al.1992 and Huang 1994) are used to predict tree height. MGM yield tables summarize tree and stand characteristics as species averages and totals.

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Applications and LimitationsReturn to top of page

Applications

MGM generates yield tables for white spruce and aspen, and black spruce and lodgepole pine mixedwood stands and supporting graphics for:

  • stand level crop planning; and
  • forest level planning for long term timber supply projections of boreal mixedwood stands .

Limitations

MGM 2001B was reviewed and evaluated by exploring model behavior across a wide range of conditions ( FARNDEN 2002). Model comparison with remeasured BC MOF PSPs data also indicated model strengths and weaknesses ( HARPER 2002). As a result, a number of recommendations for operational use have been suggested ( BC USE RECOMMENDATIONS - MGM 2001B).

The following information provides additional limitations and model specifications for the recent MGM 2001B release:

  1. Growth and mortality relationships are based only on Alberta PSP data.

  2. Site index and taper functions are based on BC equations. BEC regions SBS and BWBS equations are implemented.

  3. BC species codes are applicable if the regional variant is set to BC.

  4. The upper limit of stand data for site index is around 21 m at 50 years.

  5. The upper limit of stand data for density is slightly less than 20,000 per ha.

  6. Juvenile and small tree data is limited to a small sample of stands covering a limited range of conditions. This is indicated in the Establishment Dialogs.

  7. All species other than white spruce, lodgepole pine, aspen and black spruce are pooled into one of these four. See the MGM help files.

  8. Some growth and mortality relations for black spruce are based on limited data.

The following are some of the limitations and additional guidance for usage of MGM in northeastern British Columbia (Titus, 1998):

  • Interpretation of MGM simulations should be tempered by professional experience and knowledge of local conditions.
  • Application of MGM in FIZ zones other than "L" is not recommended.
  • Where possible, MGM yield projections should be compared with plot data.
  • Other than taper functions used for tree volume estimation, there is not differentiation of growth relationships by BEC zone. All growth relationships were developed with data from outside British Columbia.
  • Pure (100%) species composition for spruce and aspen may provide overestimates of volume. This tendency has not been verified because of difficulty in obtaining data for completely pure stands of these species. It is recommended that at least 10% of stand density be included for the typical complementary species.
  • Estimates of yield beyond 150 years are subject to greater uncertainty than those below that age.
  • Starting values for stand characteristics obtained from plot averages can be inappropriate if the plot averages have been computed only for merchantable trees. For example, if height data for plots is based on top height or D/DC height, then the input height should be lower than this to approximate the average of all trees.
  • When comparing plot data summaries with MGM projections, definition of terms must be consistent or allowances must be made in interpreting the output graphs and statistics. For example, MGM reports average height while the VDYP database uses top height or D/DC height.

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Last Modified: 2002 OCT 25. Ministry Contact: Mario di Lucca
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