Boxelder Page 1. Introduction: discussion of classification, seral assignment and monitoring. Page 2. Graph. Page 3. Instructions: plot setup and data collection using the Excel spreadsheet. Page 4. References. The Boxelder classification and monitoring system was developed using tree and shrub variables only. Herbaceous understory data were not collected for the Boxelder ecological type. Resource managers need to consider the herbaceous component when evaluating the overall ecological system. Caution Boxelder.xls is an Excel workbook containing the datasheet for field data collection. Copy the Excel file to a PDA. The .xls file will be converted to a Pocket Excel file with a .pxl extension. The file contains a spreadsheet with formulas that provide calculations necessary for classification of a site, using the variables defined for this ecological type. Be careful with the spreadsheet when loaded on a PDA. Although the formulas and cells are protected on the PC version of Excel, protection of spreadsheets/worksheets is not an option on the Pocket version of Excel. It is possible to erase formulas and stop the classification system. Be sure to make changes only within the empty cells, and not in any of the calculation or formula cells such as cov%, probabilities, etc. In addition, always: • Keep a backup copy of the original ‘Boxelder.pxl’ file on your PDA and, • Save the file under a new name after finishing data collection on each site, e.g. ‘Boxelder site1.pxl’, ‘Boxelder site2.pxl’…….. to avoid overwriting previous files with data. Monitoring Seral Stages in Boxelder-Hackberry-Snowberry Ecological Type Classification, seral assignment, and monitoring of Boxelder-Hackberry-Snowberry ecological type seral stages is according to the method of Uresk (1990). Statistical analysis of field-collected data indicates the presence of four seral stages: early, early intermediate (EINT), late intermediate (LINT) and late. A site is classified, and assigned to a seral stage by entering a set of key plant measurements into the set of canonical discriminant functions developed for this ecological type and estimating posterior probability for each seral stage (SPSS, 1995). The site monitored is assigned to the stage with the highest posterior probability (See Boxelder.xls program for methods). For the Boxelder-Hackberry-Snowberry ecological type the key variables are the basal area of trees in square feet per acre for Acer negundo (ACNE) and Celtis occidentalis (CEOC), and the percent canopy cover of Symphoricarpos occidentalis (SYOC), using Daubenmire’s (1959) canopy cover method. The seral stage assigned to a set of plant measurements is always associated with the greatest probability value. If that value is 1, then succession is at the middle of the assigned seral stage. If the greatest probability value is less than 1, then the second greatest probability value is used to determine the successional status relative to middle of the assigned stage. For instance, if the second greatest probability is associated with an earlier seral stage, succession is at the lower end of the assigned seral stage. On the other hand, if the second greatest probability is associated with a later seral stage, succession is at the upper end of the assigned stage (see example below). When permanent macroplots are established to assess the vegetational trend of a site, re-sampling and comparing the previously assigned seral stage to the current stage provides information about succession or retrogression. On a finer scale, within-stage changes in vegetation successional status can be quantified by comparing the probability values. For example, first-year field measurements collected for basal area of the two tree species and canopy cover of snowberry on a site resulted in the following values: ACNE=25, CEOC=31, and SYOC=17. Four years later the values obtained were: ACNE=27, CEOC=32, and SYOC=15. Calculating the probabilities, we find: ACNE CEOC SYOC LATE LINT EINT EARLY Stage Year1 25 31 17 .005 .780 .141 .075 LINT Year5 27 32 15 .003 .924 .033 .004 LINT Difference In both years, the site was classified and assigned to the late intermediate seral stage; the greatest probability values (.780 in Year1 and .924 in Year5) are associated with LINT. Placement within the late intermediate seral stage is at the lower end of the stage, as indicated by the second greatest probability values (.141 for Year1 and .033 for Year5) which are associated with an earlier seral stage (EINT). The site shows an upward successional change of about .14, which is the difference between the probabilities in Year1 and Year5. The figure to the right illustrates this example. These quantitative changes in the probabilities can be used to evaluate and monitor the effects of management alternatives. .144 Late Early Interm ediate Late Intermediate .78 Early Year 1 1.0 .5 Late 1.0 .5 1.0 Early Intermediate Late Intermediate .92 1.0 .5 Early Year 5 1.0 .5 Late 1.0 .5 1.0 Early Intermediate Late Intermediate .14 1.0 .5 Early Change 1.0 .5 1.0 .5 1.0 .5 1.0 Page 1 of 4 Monitoring Seral Stages in Boxelder-Hackberry-Snowberry Ecological Type Boxelder-Hackberry-Snowberry Ecological Type by Seral Stage 70 Boxelder Basal Area (ft2 /acre) Hackberry Basal Area (ft2 /acre) Snowberry (%cover) 60 Mean values 50 40 30 20 10 0 LATE L. INTERMEDIATE E.INTERMEDIATE EARLY Mean Values Boxelder BA (ft2/a) Hackberry BA (ft2/a) Snowberry cover (%) 58 8 6 29 47 7 18 11 33 5 4 3 Mean values of plant variables through four stages of succession in a Boxelder-Hackberry-Snowberry ecological type. Smoothed lines connect the means for each key plant variable at each stage. Graph provides a guide for an approximate mixture of species variables at each seral stage. Page 2 of 4 Monitoring Seral Stages in Boxelder-Hackberry-Snowberry Ecological Type DATA COLLECTION, SUMMARIZATION 30m OR AND 40m CALCULATIONS 10m 40m 20m Boxelder Overstory Basal CEOC DBH BA 5.1 20 9.2 66 5.4 23 6.7 35 6.3 31 12 113 4.7 17 15.8 196 3.3 9 7.9 49 8.4 55 11.6 106 9.4 69 11.4 102 5.3 22 1.5 2 ACNE 27 30m 30m VEG TYPE LIMITS ACNE DBH BA 4.5 16 8.9 62 2.3 4 2 3 1.1 1 3.2 8 10 79 11.7 107 5.6 25 4.4 15 5.8 26 6.8 36 3.5 10 6 28 13.8 149 2.9 7 2.7 6 2 3 3.1 8 2.3 4 1.9 3 10.7 90 4.6 17 2.4 5 7.1 40 3.6 10 40m 20m 30m Enter Daubenmire classes 1 through 6 Xsect CEOC 32 Frm 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 2 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 Mean cov% SYOC 3 1 4 1 1 2 5 6 4 1 1 5 3 1 1 4 1 3 3 1 4 1 2 2 5 2 TRANSECT 1. Within the Boxelder-Hackberry-Snowberry type, establish a permanent plot with an area of 800m2. Ideal plot dimensions are 20m x 40m; however, on some sites it may be necessary to use two 10m x 40m plots. Along the plot boundaries, establish two 30m transects, a minimum of 20m apart. (See figure above) Recommendations are to monitor two sites per section (640 acres) within the ecological type. Sites should be at least ¼ mile apart. 2. Using the ‘Boxelder.xls’ spreadsheet (see figure at left) installed on your PDA: Record the DBH in inches of each Acer negundo (ACNE) and Celtis occidentalis (CEOC) tree 1” or greater diameter within the 800m plot. Record canopy cover of Symphoricarpos occidentalis (SYOC) within a 20cm x 50cm quadrat at one-meter intervals along each transect (30 readings/transect) using Daubenmire (1959) class codes 1 through 6. Class Code 1 2 3 4 5 6 Cover Class >0 - 5% 5 - 25% 25 - 50% 50 - 75% 75 - 95% 95 – 100% Mid Point 2.5% 15% 37.5% 62.5% 85% 97.5% The spreadsheet calculates basal area for each tree and for the site, and mean percent canopy cover for snowberry for the site. It also provides classification probabilities by seral stage and the seral stage assignment. ‘Boxelder.xls’ Calculations 2 2 Basal area per tree (in inches) = DBH2 / 4 x 3.14. 1 SYOC 15 Seral Stage Classification Posterior Probability LATE LINT EINT ERLY 0.00 0.92 0.03 0.05 Assigned Stage LATE INTERMEDIATE PLOT LIMITS BA (ft2 / acre) = Sum basal of all trees on plot, divided by 144 to convert basal in inches to basal in feet. BA (ft) x 5.06 converts BA per 800m2 to BA per acre. Cover (%) = Sum of Daubenmire cover class midpoint values for Snowberry divided by 60. Page 3 of 4 Monitoring Seral Stages in Boxelder-Hackberry-Snowberry Ecological Type REFERENCES Daubenmire, R. 1959. A canopy-coverage method of vegetational analysis. Northwest Science. 33(1):43-64. SPSS 12.0 for Windows. 1989-2003. SPSS Inc. 444 N Michigan, Ave, Chicago, IL 60611. Uresk, D. W. 1990. Using multivariate techniques to quantitatively estimate ecological stages in a mixed grass prairie. J. Range Mgt. 43(4):282-285. Page 4 of 4