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Hiawatha National Forest Common Stand Exams Field Guide Revised 2019
HNF Common Stand Exams Field Guide
HNF Field Procedures Handbook for Common Stand Exam
Contents
| Hiawatha National Forest Common Stand Exams Field Guide | 1 |
| Section 1: General Information | 5 |
| Field Data Collection Procedures | 5 |
| Section 2: Setting | 6 |
| Project Name (25-character) | 6 |
| Region (2-digit) | 6 |
| Proclaimed National Forest (2-digit) | 6 |
| District (2-digit) | 7 |
| Location (compartment; 5-digit) | 7 |
| Stand Number (4-digit) | 7 |
| Ownership (4-character) | 7 |
| State (2-character) | 7 |
| County (3-digit) | 7 |
| Administrative Forest (2-digit) | 8 |
| Administrative Region (2-digit) | 8 |
| Date (8-digit) | 8 |
| Examination Level (4-digit) | 8 |
| Exam Purpose (2-character) | 9 |
| Existing Vegetation Reference Code (5-digit) | 9 |
| Existing Vegetation (2-character) | 9 |
| Structure (2-digit) | 9 |
| Acres (up to 4-digit) | 10 |
| Examiner (maximum of 12-letters) | 10 |
| Precision Protocol (maximum of 5 letters) | 10 |
| User Code (Size-density; 1-digit) | 10 |
| Setting Remarks (242-characters) | 11 |
| Stand Condition | 12 |
| Non-Forest Vegetation Types | 13 |
| Within Stand Features | 13 |
| Stand Prescription | 13 |
| Stand Damage Category/Agent/Severity | 13 |
| Damage Category (maximum 2-digit) | 13 |
| Damage Agent (maximum 3-digit) | 14 |
| Damage Severity (maximum 5-digit) | 14 |
| Section 3: Sample Design | 15 |
| Form Type | 15 |
| Sample Selection Method Type (3-character) | 15 |
| Sample Expansion Factor (maximum of 6 numbers) | 15 |
| Subpopulation Filter (8-character) | 15 |
| Subpopulation Variable (3-character) | 16 |
| Subpopulation Minimum Value (max of 6 numbers; may include 2 decimals) | 16 |
| Subpopulation Maximum Value (4,1- digit) | 16 |
| Sample Design Remarks (242-character) | 16 |
| Section 4: Plot Data | 18 |
| Plot Number (3-digit) | 18 |
| Plot Latitude (8-character) | 18 |
| Plot Longitude (8-character) | Error! Bookmark not defined. |
| Plot Existing Vegetation Composition Type (3-digits) | 19 |
| Plot Remarks (242-character) | 19 |
| User Code (3-digit) | 19 |
| Section 5: Tree Data | 20 |
| Overstory Plot Data | 20 |
| Understory Data Collection | 21 |
| Plot Number (3-digit) | 21 |
| Tag ID Number (4-digit) | 21 |
| Tree Status (1-character) | 21 |
| Tree Species (8-character) | 21 |
| Tree Count (3-digit) | 22 |
| DBH (Diameter at Breast Height) | 22 |
| Height (3-digit) | 22 |
| Tree Age (3-digit) | 22 |
| Wildlife Use (2-character) | 23 |
| Snag Decay (1-digit) | 23 |
| Tree Damage Category (2-digit) | Error! Bookmark not defined. |
| Tree Damage Agent (3-digit) | Error! Bookmark not defined. |
| Tree Damage Part (2-character) | Error! Bookmark not defined. |
| Tree Damage Severity (5-digit) | Error! Bookmark not defined. |
| Site Trees | 23 |
| User Field | 25 |
| APPENDICES | 26 |
| Appendix A: Existing Vegetation Codes (FSHR09) | 27 |
| Appendix B: Non-Forest Vegetation Codes (for use in Setting Remarks) | 30 |
| Appendix C: Timber Land Suitability Class (TLSC) Codes & Descriptions | 32 |
| Appendix D: Stand Prescription – Activity Codes and Descriptions | 33 |
| Appendix E: Within-Stand Features – Codes and Descriptions | 34 |
| Appendix F: Species Codes | 36 |
| Appendix G: Fixed Radius Plot | 37 |
| Appendix H: Variable Radius Plot | 39 |
| Appendix I: Damage Categories, Agents, Severity Ratings, and Tree Parts | 43 |
| Appendix J: Measuring DBH & DRC | 55 |
| Appendix K: Measuring Heights | 62 |
| Appendix L: Measuring Age | 66 |
| Appendix M: Glossary of Terms | 67 |
| Appendix N: FSVeg Spatial Editing Rules | 70 |
Section 1: General Information Field Data Collection Procedures Field data collection procedures are based upon national Common Stand Exam (CSE) protocols that have been modified for the Hiawatha National Forest. In general, Quick Plots with tree data only are collected on the Hiawatha. A complete listing of CSE data fields are available from the FS VEG web page: Comment by Brown, Laura - FS: A lot of this text is very wordy, maybe we can severely condense it to make it more easy to read http://fsweb.nrm.fs.fed.us/support/docs.php?appname=fsveg Quick Plot Definition –A quick plot exam may group trees by species, diameter, heights and/or damage classes on both large and small plots. These exams are designed to collect stand structural data in an efficient manner. Diameters of live trees are recorded by 2 inch DBH (Diameter at Breast Height) class and standing dead tree heights may be recorded by ocular estimated. Limited tree defect information is collected, growth data is not collected, and small tree measurements may be recorded in groups. The main uses of a quick plot are:
· Cover and stand structure estimates by vegetative layer
· Exams in single species or single storied stands
· Timber stand improvement inspections
· Post treatment examinations
· General surveys, such as mistletoe surveys
Section 2: Setting In the FSVeg database and the Common Stand Exam (CSE) program, a “setting” is usually a “stand”. The Setting ID data fields uniquely identify each setting. The date field is used to uniquely identify the Setting ID from multiple surveys from the same location over time. Complete one Setting Form for each setting.
Example of a Setting Record in CSE:
The highlighted fields are required.
Project Name (25-character) A project name is a useful way to group settings, for example ‘2019 Stocking Surveys’.
Region (2-digit) Record the proclaimed Region where the stand is located.
| 09 |
| Region Nine - Eastern Region (default) |
Proclaimed National Forest (2-digit) Record the proclaimed National Forest where the setting is located (default)
District (2-digit) Record the Ranger District number where the setting is located (default)
Location (compartment; 5-digit) Use leading zeros to complete the compartment code. Leading zeros are required Stand Number (4-digit) Use leading zeros to complete the setting code. Record the stand number consistent with the current vegetative polygon map layer, unless creating a new stand.
Ownership (4-character) Record the following ownership code:
| USFS |
| US Forest Service (default) |
State (2-character) Record the State in which the setting is located. A setting cannot cross state boundaries.
County (3-digit) Record the County in which the setting is located.
Administrative Forest (2-digit) Record the administrating National Forest where the setting is located.
Administrative Region (2-digit) Record the administrating National Forest where the setting is located.
| 09 |
| Region Nine - Eastern Region (default) |
Date (8-digit) Record the calendar month, day, and year the stand examination was completed. The format is MMDDYYYY. On personal data recorders, the current date will fill automatically.
Examination Level (4-digit) Record the examination level that identifies which exam protocol was used. The 1st number is for the tree form, and 2nd is for the vegetation form, the 3rd number is for the fuel form and the 4th number is for the ground form.
| 1xxx |
| Quick Plot (default) |
| 2xxx |
| Extensive examination |
| 3xxx |
| Intensive examination |
For example, a code of 1000 indicates the following:
| Tree Form |
| Veg. Composition |
| Down Woody Mat’l. |
| Ground Surface Cover |
| Quick (1) |
| Not taken (0) |
| Not taken (0) |
| Not taken (0) |
Down Woody & Ground Surface forms may only have values of zero (not taken) or 1 (taken).
Unless otherwise stated, HNF exam level will be “1000” (Quick Plot) Exam Purpose (2-character) Record the purpose of the exam. These codes are locally defined.
| SE |
| Stand Exam – Used to determine stand composition. |
| RE |
| Regeneration/Stocking – Used to determine stocking rates of stands or partial stands. If certifying stand, use “SE” code. |
| ID |
| Insect & Disease Exams – Used to verify types and severity of infestation as an aid in determining treatment needs. |
Existing Vegetation Reference Code (5-digit) Record the existing vegetation reference code.
| FSHR9 |
| Region 9 Forest Service Handbook (default) |
Existing Vegetation (2-character) Existing Vegetation (EV) refers to the Forest Type of the dominant vegetation. At plot level, record EV based on plot, as well as the immediate surrounding area. At setting level, record EV based on the overall stand. EV codes & descriptions for the Hiawatha are listed in Appendix A.
Structure (2-digit) Record the stand-level setting structure.
| SS |
| Single story - A single even canopy characterizes the setting. The greatest number of trees is in a height class represented by the average height of the setting; there are substantially fewer trees in height classes above and below this mean. |
| TS |
| Two-storied - Two relatively even canopy levels can be recognized in the setting. Understory or overtopped trees are common. Neither canopy level is necessarily continuous or closed, but both canopy levels tend to be uniformly distributed across the setting (e.g., overstory with regenerated understory). |
| MS |
| Multi-storied - At least three height size classes are commonly represented in the setting. Generally, the canopy is broken and uneven although multiple canopy levels may be distinguishable. The various size classes tend to be uniformly distributed throughout the setting. |
| MO |
| Mosaic - At least two distinct height size classes are represented and these are not uniformly distributed, but are grouped in small repeating aggregations, or occur as stringers less than two chains wide, throughout the setting. Each size class aggregation is too small to be recognized and mapped as an individual setting. |
| UA |
| Unknown/un-assessable - A structure classification was attempted, but the stand did not fit into one of the pre-defined categories. Note in the remarks column the reason the stand could not be classified. |
Acres (up to 4-digit) Record the total setting acres, round to the nearest whole acre.
Examiner (maximum of 12-letters) Record the individual(s) responsible for data collection. Use last name or last name and first initial. Example, for Tom Smith, use: Smith or Smith_T. Do not use reserved characters such as +, /, -, or * in this field. This field can be set up to default to the recorder’s name.
Precision Protocol (maximum of 5 letters) This field is used to indicate level of precision of the exam. Quick plot will be the most common (CSE_Q) User Code (Size-density; 1-digit) At the setting level, record the size-density code only after all plots have been completed. The basal area tally of trees recorded in Tree Data should be used as a guide.
Technique for size/density determination is different for stands below 5.0 inches DBH than for stands larger than 5.0 inches DBH. See the paragraphs following the codes for procedures. The following codes should be used:
| 0 |
| Nonstocked (less than 16% stocked) |
| 1 |
| Seedling-Sapling; Poor (16% - 39% stocked) |
| 2 |
| Seedling-Sapling; Medium (40% - 69% stocked) |
| 3 |
| Seedling-Sapling; Well (over 70% stocked) |
| 4 |
| Poletimber; Poor (16% - 39% stocked) |
| 5 |
| Poletimber; Medium (40% - 69% stocked) |
| 6 |
| Poletimber; Well (over 70% stocked) |
| 7 |
| Sawtimber; Poor (16% - 39% stocked) |
| 8 |
| Sawtimber; Medium (40% - 69% stocked) |
| 9 |
| Sawtimber; Well (over 70% stocked) |
Pole timber: Trees greater than 5 inch DBH, having at least one 8 foot stick Sawtimber: Trees greater than 9 inch DBH for softwood or 11 inch DBH for hardwood and aspen.
For stands that average less than 5.0 inches DBH, size-density is an estimate of stocking in seedling and sapling stands and is determined with a series of fixed acre plots. Here, a stocked versus non-stocked relationship is determined. For example, if 10 plots were taken and five were stocked, the stand would be 50% stocked or size density code = 2.
For stands which average 5.0 inches DBH and larger, generally consider only live trees with DBH of 5.0 or greater, regardless of the total number of trees recorded in plots. The exception would be if there are trees less than 5.0 inches DBH that are of truly acceptable growing stock. A general rule of thumb is that approximately 10 square feet of basal area represents 10% stocking.
This code is also recorded at the plot level.
Setting Remarks (242-characters) Record required items in this space, as well as remarks about specific observations on overall setting conditions. Remarks need to be understandable, complete and incorporate the various codes in Appendix D and E. If access to stand is obstructed (slope, wetlands, substandard bridge, etc.) enter extent of problem. Before leaving a stand, make a final check to be sure all important remarks have been recorded.
See Setting Remarks example below. Dashes and underscores are allowed. Up to 242 characters are allowed.
Setting Remarks Example:
TLSC500, YOR1929, SC6, A4151 - upland well-stocked NH with gaps and SM regeneration. Vernal pool in SW. F404, F440, F408. SI tree in plot 3. (if this were an opening, (ev codes 97, 98, or99), also include veg type. For example: VT51.)
Put remarks in the order in which they are listed below:
| Remark Type |
| When to Use |
| Format |
| Timber Land Suitability Class |
| Mandatory (See Appendix C); Record TLSC from the previous compartment record (or recommended changes if required) |
| TLSCnnn |
| Stand Year of Origin |
| Mandatory |
| YORyyyy |
| Stand Condition |
| Mandatory (See below) |
| SCn |
| Non-Forested Vegetation Type |
| Mandatory for non-forested stands (See below; Appendix B) |
| VTnn |
| Site Index tree Location |
| Mandatory |
| SI IN PLOT X. |
| Within Stand Features |
| If required, may vary by project (See below; Appendix E) |
| Fnnn |
| Stand Prescription |
| If required (See below; Appendix D) |
| Annnn |
| Stand Damage Category/Agent/Severity |
| Mandatory, if present (See below; Appendix I) |
| DCnn |
Year of Origin Year of origin (YOR) should be based off the oldest cohort of trees within the stand. Occasionally stands will have scattered remnant trees which are older than the rest. These trees should not be cored for YOR. A cohort of trees is a group of individuals that established at roughly the same time. In most cases the site index tree can be used for YOR in even-aged stands. For even-aged stands YOR could be more accurately be determined from compartment records or past stand exams. For uneven-aged stands, the site-index tree should NOT be relied on for an accurate YOR unless it’s truly from the oldest cohort.
Stand Condition Stand condition is based on species, age, size, quality, and stocking of trees Stand Condition - SCn
| 4 |
| Forest pest infestation |
| 7 |
| Low quality pole timber |
| 14 |
| Adequately stocked seedlings and saplings |
| 15 |
| Inadequately stocked / nonstocked |
| 16 |
| Group selection management |
| 17 |
| Individual tree selection management |
In Regeneration should be used for stands that were planted, seeded, or naturally regenerated that have yet to have be certified as meeting the minimum NFMA stocking requirements.
Sparse timber is defined as stands having less than 40 sq. ft. of basal area.
Low Quality timber has greater than 50% of the trees of low quality.
Low quality trees have the following characteristics:
1. Chlorotic/thin crowns
1. Dead branches in the upper crown
1. Crown is dying from the top down
1. Less than 30% live crown ratio
1. Crown only on 1 or 2 quadrants of the trees.
1. Bole is leaning, or has crooks, sweeps or forks
1. Signs of insects or disease
1. Has indicators of defect Mature timber is based upon the average rotation age for a given cover type. The table below describes that mature age for cover types across the forest. For a more detailed description of rotation age by management area, see the Hiawatha Forest Plan.
| Aspen |
| Paper Birch |
| Northern Hardwoods |
| Jack Pine |
| Balsam Fir |
| Black Spruce |
| White Spruce |
| Red/ White Pine |
| Cedar |
| Rotation Ages |
| 35-70 |
| 45-100 |
| 80-200 |
| 40-70 |
| 40-70 |
| 70-150 |
| 70-110 |
| 80-160 |
| 80-160 |
Non-Forest Vegetation Types Areas with less than 16 percent stocking of trees (which are not in the process of regenerating following a final harvest cut) are classified as one of the non-forested vegetation types listed in Appendix B. No overstory plots are needed in non-forested vegetation types, except in the savannah and orchard types.
Within Stand Features A 3-digit code that enables the examiner to record unique and important features of the stand that are not recorded elsewhere. These features include the presence of sensitive wildlife species, vegetative and geological features, recreational facilities and use, cultural resource sites and utilities. All within stand features that are observed anywhere in the stand by the examiner should be coded and recorded. Additional explanations can also be noted in Setting Remarks. Stand Feature Codes and Definitions are found in Appendix E.
Stand Prescription If required, prescription activities should be considered for every stand. If a stand will be ready for treatment within the next ten years, note in remarks, using the codes from Appendix D.
Stand Damage Category/Agent/Severity Damage category/agent/severity should be recorded in setting remarks if damage is present throughout the stand or if damage is seen within the stand, but not picked up at the Plot or Tree level.
Damage Category (maximum 2-digit) Use codes available under “Tree Data” or in Appendix I. Record as “DCnn”.
Example of codes and descriptions for Damage Category:
Damage Agent (maximum 3-digit) Record the damage agent associated with the category, if known. Use codes available under “Tree Data” or in Appendix I. Record as “DAnnn”.
Example of codes and descriptions for Damage Agent:
Damage Severity (maximum 5-digit) Record the damage severity associated with category and agent. Use codes available under “Tree Data” or in Appendix I. Record as “DSn”.
Example of codes and descriptions for Damage Severity:
| 4 |
| Defoliation 26-75%, no topkill |
Section 3: Sample Design Form Type Record the form type for each set of sample design data. In Exams, there is a separate page for each form type. Currently, only Tree Data is collected on the HNF. Valid form types are:
| VEGCOV |
| Vegetation cover form |
| SURCOV |
| Surface cover form |
| DNWDY |
| Down woody material form |
Sample Selection Method Type (3-character) Record the method by which trees, shrubs, grasses, or down woody material were selected. This field defines the type of each plot;
| BAF |
| Basal area factor for a variable radius plot. |
| FRQ |
| Frequency for fixed area plots or linear strip plots. |
| TRN |
| Fixed length transect line. |
Sample Expansion Factor (maximum of 6 numbers) This field corresponds to the Sample Selection Method Type and converts tree or piece data to a per-unit-area basis. This field defines the size of each plot: the BAF used with the variable radius plot, the size of the fixed area plot, or the transect length.
| Sample Selection Method Type |
| Code |
| Description |
| BAF |
| 10 |
| 10 basal area factor |
| FRQ |
| 1000 |
| The inverse of a 1/1000th acre plot or strip area |
| TRN |
| 27 |
| The horizontal length of a transect line to the nearest foot. |
Subpopulation Filter (8-character) Record the filter to define the sample subpopulation. This field is used to specify that only standing live, only standing dead, only stumps, only down, or both standing live and standing dead vegetation will be sampled. This field is not used for the surface cover form type. Use the following codes:
| ALL |
| Both live and dead standing |
Subpopulation Variable (3-character) Record the characteristic used to define the subpopulations sampled. This field defines which characteristic of the vegetation will be measured to see if it meets the sample criteria.
| DBH |
| Diameter at Breast Height |
| DRC |
| Diameter at Root Collar |
| CVR |
| Percent Vegetation Species Cover |
| SVC |
| Percent Surface Cover |
| DIA |
| Diameter at Midpoint or Intersection |
Subpopulation Minimum Value (max of 6 numbers; may include 2 decimals) Record the minimum value for the subpopulation variables. Default is 0. For example, if the subpopulation variable is set at “DBH,” this field defines the minimum DBH the vegetation must have in order to be sampled on the plot.
Subpopulation Maximum Value (4,1- digit) Record the maximum value for the subpopulation variables. Default is 999.9. For example, if the subpopulation variable is set at “HT,” this field defines the maximum height the vegetation must be in order to be sampled on the plot.
Sample Design Remarks (242-character) Record information to explain the sample design used. Remarks are available for each line in the sample design form.
Common Sample Designs:
Sample Design 1 – This is intended for multi-aged, multi-storied stands.
Sample Design 1 would typically be used in uneven-aged northern hardwood stands, mixed hardwood/conifer stands that have an established understory, two-aged stands, etc.
The examiner shall sample overstory trees for all plots on these types of stands using variable-radius 10-Basal Area Factor (BAF) to tally trees ≥ 2..0” DBH Sample Design 1 Example:
Sample Design 2 – This is intended for even-aged stands, such as CCC plantations and cedar swamps that have little or no understory. It may also be appropriate for younger, even-aged hardwood stands. In such stands, where regeneration is noted as patchy or sporadic, this may be reflected in Setting Remarks.
In very uniform, even-aged stands with minimal species variation and high average basal area, (pine plantations, cedar swamps, certain hardwood stands), examiner may opt to use a 20 BAF collection protocol, provided the examiner adjusts the Sample Design Form to reflect BAF 20. In these situation, sampling with a 10 or 20 factor prism should result in very little variation in average basal area.
Sample Design 2 Example:
Sample Design 3 - This is intended for openings, younger stands and regeneration surveys. For openings, there must be at least one Plot Data record, but the Tree Data table may have no entries. See table below for regeneration survey plot sizes.
Sample Design 3 Example:
Regeneration survey plot sizes
| Sample size |
| Radius |
| Purpose |
| 1/1000 acre |
| 3.7-foot |
| To determine stocking levels in uneven-aged hardwood stands (in gaps), non-plantation conifer regeneration, and plantations with target stocking levels of 1000 trees per acre or greater. |
To determine stocking levels in plantations with target stocking levels of 700-800 trees per acre. Typically used for red pine and jack pine plantations.
Section 4: Plot Data The Plot Data Form contains information about a sample plot or transect. This information is independent of the information collected in other sections. Record a separate set of plot data for each plot in the stand.
Example of a Plot Data Form:
Plot Number (3-digit) Record a plot number for each sample plot within a Setting. In Exams, plot numbers list automatically in the Plot Form.
The number of plots listed in the Plot Form MUST equal the number of actual plots taken on the ground. All plots listed in Exams must have field data entered into them – no “empty” plots.
For plots that have no trees (e.g. openings and regenerating clearcuts), plot data should indicate location (lat/long) and a “0” for the User Code (size density).
Plot Latitude & Longitude (8-character each) Record the plot latitude as measured by a Global Positioning System (GPS). Latitude consists of a 3-digit “degree”, a 2-digit “minute”, and a 3-digit “second”. The second value is in the form XX.X.
Plot Existing Vegetation Composition Type (3-digits) Record the dominant existing vegetation composition.
At plot level, Existing Vegetation is a combination of what is found on the plot (“plot trees”) as well as trees in the immediately surrounding area. See Appendix A for a complete list of existing vegetation composition codes.
Plot Remarks (242-character) Enter remarks relevant to the plot. Any within-stand features that fall within or near a plot should be recorded here; otherwise note in Setting Remarks.
User Code (3-digit) Record the size-density code for each plot. Use codes and procedures are detailed in Section 2, “Setting”.
HNF Field Procedures Handbook for Common Stand Exam
Section 5: Tree Data This section will cover how tree data is to be collected for quick plot protocols. The following table shows the fields required for all stand exams on the Hiawatha N.F.
| Header Information |
| Required |
| Site Tree |
| One site tree per stand |
| DBH |
| Trees ≥ 4.5 feet tall. |
| Height* |
| One site index tree/stand; all dead trees; |
and trees < 4.5 ft. tall
| Age |
| One site index tree/stand |
| Wildlife Use |
| As applicable |
| Tree Damage Category |
| As applicable |
| Tree Damage Agent |
| Required if Category is recorded. |
| Tree Damage Part |
| Required if Category is recorded. |
| Tree Damage Severity |
| Required if Category is recorded. |
| Treatment Option |
| Required if stand is ready for harvest. |
*For dead trees (snags), give an ocular estimate of the tree height. For Site Trees, height should be measured to the nearest foot.
Example of a Tree Data Form
Overstory Plot Data The overstory plot consists of gathering species, size and quality information using a Basal Area Factor plot (10 or 20). Record tally trees as required by the sample design.
When performing quick plots, all trees of the same species, diameter class and quality class can be recorded on the same line using the tree count field (except for the Site Tree, which must be measured to 1/10th of an inch DBH and recorded on a separate line).
Understory Data Collection A fixed- radius plot will be used to tally the number of seedlings of all woody species See table below for understory height requirements. In hardwood stands, count all seedlings taller than 1.5 feet but less than 1-inch DBH. In conifer stands, count all seedlings taller than 0.5 feet.
| Stand Type |
| Height Requirements (ft) |
Plot Number (3-digit) Record the plot number for each line of tree data if data is collected with a data recorder this is automatic.
Tag ID Number (4-digit) On each plot, start with ‘1’ (at true North) and increment one number for each tree record in a clockwise rotation. If using Exams, the program should automatically update the tag ID number.
The tag ID and plot number uniquely identifies each line of tree data. Each line may represent a single tree or a group of trees with the same characteristics – species, DBH, etc.
Tree Status (1-character)
| L |
| Live - includes all standing trees that have at least one green point of growth. This includes deciduous trees that have lost their foliage for the season, and trees that have recently lost their leaves to defoliators, but will reflush. |
| D |
| Dead - standing trees without a green point of growth. Note: many of the tree fields are not used if the tree is a dead tree. |
| S |
| Stump - woody base of a tree left in the ground less than 4.5 feet tall. Note: many of the tree fields are not used for stumps. |
| X |
| Down (may use if down woody material form is NOT used) - includes all trees (live or dead) that have their main stem lying on the ground, or are supported by branch wood. A tree is considered down if it is leaning more than 45 degrees from vertical, not self-supporting, and/or in contact with the ground. |
Tree Species (8-character) Record the species of every sampled tree and in BAF variable-radius plot. Refer to Appendix F or drop down list in the PDR.
Tree Count (3-digit) Record the number of sampled trees represented by each line of tree data. When determining “in” and “out” trees, measure from plot center to the face of the tree in question to determine the limiting distance. Record site trees individually.
Trees can be grouped by species, tree status, DBH, etc. For example, a plot can have 3-12” live red maple trees and 2- 14” live sugar maple trees.
Distinguishing characteristics may warrant further grouping or individual tree recording. Such characteristics include age, crown ratio, crown class, or tree damage.
DBH (Diameter at Breast Height) Record the DBH for each tree or group of trees. When measuring individual trees, measure them to the nearest 2 inches (quick plot). Examples of coding for quick plot exams are listed below. See Appendix J for examples on where to measure DBH.
*Exception: Site trees must be measured to 1/10th inch dbh.
Height (3-digit) Record tree height to the nearest foot from ground line on the up-hill side to the uppermost tip. See Appendix K for details on measuring tree heights.
Tree heights are required for the following trees when using the quick plot exam method:
Site Trees (measured tree height) Trees less than 4.5 feet tall (see table of height classes below) Dead trees/ snags (estimated tree height)
Example of height classes:
Tree Age (3-digit) Record the tree age, in years. This is required for site index trees. See Appendix L for details on how to determine tree age form increment borings.
Wildlife Use (2-character) Record stem characteristics that may indicate the presence of wildlife.
| NO |
| No wildlife characteristics observed |
| SC |
| Small cavities less than 3 inches in diameter |
| LC |
| Large cavities greater than 3 inches in diameter |
| FH |
| Foraging Holes/Flaked Bark: Antler Rubs, Porcupine feeding |
| NE |
| Nest in tree and not in cavity |
Snag Decay (1-digit) Record the condition of standing dead (snag) The pictures and descriptions below are adapted from "Wildlife Habitats in Managed Forests of the Blue Mountains of Oregon and Washington," by Jack Ward Thomas, Agriculture Handbook No. 553, USDA Forest Service, September 1979.
Site Trees One site tree per stand must be recorded. Site trees must be recorded individually, on their own line.
The age and height of site trees are used to determine site index, a measurement to describe the productivity of a site.
Site Tree Selection Criteria
1. Freedom from height growth suppression
· Choose dominants or co-dominants, depending on the specific site index curves used.
· No damage which could influence height growth
· No pronounced period of radial growth suppression
· No evidence of top damage, past or present.
2. Select trees from a locally defined species list (See species list below). Species preference is based on the quality of the associated site index-yield study.
3. Similar age class, preferably middle-aged, avoiding old growth and young age classes. Typically > 50 years and < 120 years.
4. If a suitable sample tree cannot be found on the plot, select the nearest suitable site tree to a sample plot. Use code “S” to designate site trees located on the plot. Use code “F” to designate off-plot site trees. If there are not any on-plot or off-plot trees that meet site tree criteria, do not select a site tree for the plot.
5. Measure DBH, age, and height on all site trees. Site tree DBH must be measured to 1/10th of an inch. Measure total tree height to the nearest foot. Age is determined from an increment boring made at DBH and is the annual ring count to the pith of the tree. See Appendix L for details on how to determine tree age form increment borings.
Site Species The following table describes which tree species may be used to determine site index in different forest types. To accurately reflect present stand productivity, select a site tree species which is a major component in the stand.
| Code |
| Appropriate Species for Site Index Tree |
| Existing Vegetation Code (Forest Type) |
| ABBA |
| Balsam Fir |
| 11, 13, 16, 18, 95 |
| ACRU |
| Red maple |
| 71, 72, 76, 79, 81, 82, 83, 84, 89 |
| ACSA3 |
| Sugar maple |
| 59, 81, 82, 85, 87, 89 |
| BEAL2 |
| Yellow birch |
| 5, 59, 81, 87, 89 |
| BEPA |
| Paper birch |
| 11, 19, 89, 91, 92 |
| FAGR |
| Beech |
| 81, 86, 87, 89 |
| FRAM2 |
| White ash |
| 41, 55, 83, 89 |
| PIBA2 |
| Jack pine |
| 1, 2, 3, 48, 49 |
| PIGL |
| White spruce |
| 16, 17, 95 |
| PIMA |
| Black spruce |
| 12, 17, 18, 19 |
| PIRE |
| Red pine |
| 1, 2, 3, 49 |
| PIST |
| Eastern white pine |
| 2, 3, 4, 5, 41 |
| POBA2 |
| Balsam poplar |
| 91, 94, 95 |
| POGR4 |
| Bigtooth aspen |
| 11, 19, 93 |
| POTR5 |
| Quaking aspen |
| 11, 19, 91, 95 |
| PRSE2 |
| Black cherry |
| 55, 83, 89 |
| QUPA2 |
| Northern pin oak |
| 48, 49 |
| QURU |
| Northern red oak |
| 41, 48, 49, 55, 56, 59 |
| THOC |
| Northern white cedar |
| 14, 18, 19 |
| TIAM |
| American Basswood |
| 55, 76, 81, 84, 89 |
| ULAM |
| American elm |
| 59, 71, 75, 79, 89 |
User Field When performing stocking surveys for stands that were planted, record N for natural, if it is naturally regenerated, or P for planted.
APPENDICES
HNF Field Guide for Common Stand Exam
Appendix A: Existing Vegetation Codes (FSHR09) Comment by Murawski, Chelsea -FS: Add codes 21 Mixed Northern Hardwoods, 30 Mixed Pines, and 85 Sugar maple The following table is grouped by broad forest types. Descriptions are provided to facilitate use of correct forest type. When entering the EV Code at Setting and Plot levels, two digits are required. For example: Jack Pine with an EV Code of “1” would be entered as “01”
| EV Code |
| Forest Type |
| Definitions |
| 1 |
| Jack Pine |
| At least 51% dominant or codominant trees being jack pine |
| 2 |
| Red Pine |
| At least 51% dominant or codominant trees being red pine |
| 3 |
| Eastern White Pine |
| At least 51% dominant or codominant trees being eastern white pine |
| 4 |
| Eastern White Pine - Hemlock |
| Eastern White Pine and Hemlock predominating in a fairly even mix. Different from EV 5 in that hardwoods are widely absent. |
| 5 |
| Hemlock |
| At least 51% dominant or codominant trees being hemlock |
| 6 |
| Scotch Pine |
| At least 51% of dominant and codominant trees being Scotch Pine |
| 7 |
| Norway Spruce |
| At least 51% of dominant trees being Norway spruce |
| 8 |
| White Spruce |
| At least 51% of dominant trees being white spruce. Different from EV 16 in that balsam fir is largely absent. |
| 11 |
| Balsam Fir - Aspen / Paper Birch |
| Balsam Fir - Aspen/Paper Birch mix. Different from EV 95 in that balsam fir is the featured species or is dominant in the overstory. |
| 12 |
| Black Spruce |
| At least 51% dominant or codominant trees being black spruce |
| 14 |
| Northern White Cedar |
| At least 51% dominant or codominant trees being northern white cedar in lowlands |
| 15 |
| Tamarack |
| At least 51% dominant or codominant trees being tamarack |
| 16 |
| White Spruce - Balsam Fir |
| White Spruce and Balsam Fir predominating in a fairly even mix. |
| 17 |
| Upland Black Spruce |
| At least 51% dominant or codominant trees being upland black spruce |
| 18 |
| Mixed Swamp Conifers |
| Mixed swamp conifers including white spruce, black spruce, tamarack, balsam fir and northern white cedar in lowlands. |
| 19 |
| Northern White Cedar - Aspen / Paper Birch |
| Northern White Cedar and Aspen/Paper Birch predominating in a fairly even mix. NWC is the featured species or is dominant in the overstory. |
| 20 |
| Northern Hardwoods - Hemlock |
| Hardwoods and Hemlock predominating in a fairly even mix. Different from EV 4 in that white pine is largely absent. Different from EV 5 in that hardwoods are widely present. |
| 21 |
| Mixed Northern Hardwoods |
| Sugar maple and red maple predominating in an even mix. Other species present may include beech, paper birch, yellow birch, hemlock, white pine, white spruce and balsam fir. Different from EV 89, 84, and 76 in that red maple and sugar maple co-dominate. |
| 22 |
| Upland Northern White Cedar |
| Upland topography and at least 51% of dominant trees being northern white cedar. Different from EV 14 in that 14 indicates lowland topography. |
| 23 |
| White Spruce - Balsam Fir - Aspen |
| At least 51% of dominant trees being white spruce. Different from EV 16 in that balsam fir is less present and aspen is largely present. |
| 24 |
| Balsam Fir |
| At least 51% of dominant trees being balsam fir. Different from EV 11 in that aspen and paper birch are largely absent. |
| 30 |
| Mixed Pines |
| A farily even mix of red pine, white pine and/or jack pine. |
| 41 |
| Eastern White Pine - Northern Red Oak / White Ash |
| Eastern White Pine and Northern Red Oak / White Ash predominating in a fairly even mix. White pine is the featured species or is dominant in the overstory. |
| 43 |
| Oak - Eastern White Pine |
| Oak and white pine predominating in a fairly even mix, or WP slightly predominating. Different fro EV 3 or 4 in that oak is widely present. Different from EV 55 in that white pine is widely present. |
| 47 |
| Oak - Aspen |
| Oak and aspen predominating in a fairly even mix, or aak slightly predominating. Different from EV 11, 93 or 94 in that oak is widely present. Different from EV 55 in that aspen is widely present. |
| 48 |
| Jack Pine - Oak |
| Jack pine and oak predominating in a fairly even mix. |
| 49 |
| Red Pine - Oak |
| Red pine and oak predominating in a fairly even mix. |
| 55 |
| Northern Red Oak |
| At least 51% dominant or codominant trees being northern red oak |
| 60 |
| Oak - Hardwoods |
| Oak and other hardwoods predominating in a fairly even mix, or oak slightly predominating. Different from other hardwood forest types in that oak is widely present. Different from EV 55 in that other hardwoods are widely present. Different from EV 80 in that hardwoods other than sugar maple are widely present. |
| 70 |
| Sugar Maple - Black Cherry |
| Sugar maple and black cherry predominating in a fairly even mix. Different from EV 81, 85 and 89 in that black cherry is widely present. Different from EV 83 in that sugar maple is widely present. |
| 71 |
| Black Ash - American Elm / Red Maple |
| Black ash and American elm / red maple predominating in a fairly even mix. Black ash is the featured species or is dominant in the overstory. |
| 74 |
| White Ash |
| At least 51% of dominant and codominant trees being white ash. |
| 76 |
| Red Maple (wet site) |
| At least 51% dominant or codominant trees being red maple on a wet site. |
| 77 |
| Green Ash |
| At least 51% green ash |
| 79 |
| Mixed Lowland Hardwoods |
| Mixed lowland hardwoods can include red maple, ash, elm, paper birch, yellow birch and aspen dominating over confirs in lowlands. |
| 80 |
| Sugar Maple - Northern Red Oak |
| Sugar maple and oak predominating in a fairly even mix. Different from EV 81, 85 and 89 in that oak is widely present. Different from EV 55 in that sugar maple is widely present. Different from EV 60 in that sugar maple is dominant (non-oak) hardwood. |
| 81 |
| Sugar Maple - Beech/ Yellow Birch |
| Sugar maple - beech/yellow birch mix. Sugar maple is featured species or dominant in the overstory. Different from EV 89 in that ash and paper birch are less common. |
| 82 |
| Sugar Maple - Basswood |
| Sugar Maple and Basswood predominating in a fairly even mix. |
| 84 |
| Red Maple (dry site) |
| At least 51% red maple on a dry upland site. |
| 85 |
| Sugar Maple |
| At least 51% dominant or codominant trees being sugar maple. |
| 86 |
| Beech |
| At least 51% dominant or codominant trees being beech |
| 88 |
| Black Locust |
| At least 51% dominant or codominant trees being black locust |
| 89 |
| Mixed Upland Hardwoods |
| Different from EV 81 in that red maple, ash and paper birch are more prevalent than sugar maple, beech, or yellow birch. |
| 90 |
| Sugar Maple - Beech/Basswood |
| Sugar maple and beech-basswood predominating in a fairly even mix. Different from EV 82 in that beech is or was widely present. |
| 91 |
| Quaking Aspen |
| At least 51% dominant or codominant trees being quaking aspen |
| 92 |
| Paper Birch |
| At least 51% dominant or codominant trees being paper birch |
| 93 |
| Bigtooth Aspen |
| At least 51% dominant or codominant trees being bigtooth aspen |
| 94 |
| Balsam Poplar |
| At least 51% dominant or codominant trees being balsam poplar |
| 95 |
| Aspen - White Spruce/ Balsam Fir |
| Aspen - white spruce / balsam fir mix. Different from EV 11 in that aspen is the featured stand or is dominant in the overstory. |
| 97 |
| Lowland Shrubs |
| Typically tag alder stands, Veg Type 66 (see Appendix B) |
| 98 |
| Upland Shrubs |
| Veg Type 53 and 55 (see Appendix B) |
| 99 |
| Open |
| Upland Vegtypes 51, 52, 54, 90, 95, 96, 97, 960 and 970 or Lowland Vegtypes 62, 63, 64, 65, 68, 70 and 80 (see Appendix B) |
HNF Field Guide for Common Stand Exam
Appendix B: Non-Forest Vegetation Codes (for use in Setting Remarks)
| Code |
| Description (For more detail, see below.) |
| Used Only With |
| 051 |
| Upland opening grass |
| EV code 99 |
| 052 |
| Upland opening forb |
| EV code 99 |
| 053 |
| Upland opening shrub |
| EV code 98 |
| 055 |
| Openings freshly cut that need follow-up work. |
| EV code 98 |
| 062 |
| Wetland sedge meadow |
| EV code 99 |
| 063 |
| Wetland shallow marsh |
| EV code 99 |
| 064 |
| Wetland deep marsh |
| EV code 99 |
| 065 |
| Wetland open water (= or < 10 acres) |
| EV code 99 |
| 066 |
| Wetland shrub swamp |
| EV code 97 |
| 068 |
| Wetland bog |
| EV code 99 |
| 070 |
| Water lake (open water > 10 acres) |
| EV code 99 |
| 080 |
| Water stream or river (undifferentiated) |
| EV code 99 |
| 090 |
| Nonvegetated; rocks, sand, mud |
| EV code 99 |
| 095 |
| Gravel pit |
| EV code 99 |
| 950 |
| Settlement |
| EV code 99 |
| 960 |
| Forested roads |
| EV code 99 |
| 970 |
| County, State roads |
| EV code 99 |
051 and 052 UPLAND OPENING - HERBACEOUS (grass/forb):
An upland supporting perennial grasses, forbs, and sedges with less than 16% stocking of trees and less than 10 percent crown cover of trees. Some dominant species of openings are kingbird, meadow vole, meadowlark and tree swallow. Grouse, wild turkey, and deer are dependent on this vegetation type in spring and summer.
053 UPLAND OPENING – SHRUB:
Low woody vegetation dominates and may include witch hazel, chokecherry, elderberry, juneberry, dogwoods, viburnums, sumac, and vaccinium. There is less than 20% stocking of forest tree species. This includes many of our turkey wintering areas that have been heavily planted with shrubs.
054 SAVANNAH:
Sparse (i.e. less than 16 to 39 percent stocked; less than 50 sq. ft. basal area) stands of black cherry, oak, other hardwoods, or pine that are valuable as forage areas for deer, turkey, deer mouse, and a variety of raptors. Bluebirds, red-headed woodpeckers, eastern moles, and masked shrews utilize savannahs.
056 ORCHARD:
A grassy opening with six or more fruit trees per acre. Characteristic wildlife species are downy woodpecker, sapsucker, cedar waxwing, chickadee, ruffed grouse, bluebird, kingbird, hummingbird, deer, black bear, and bees.
062 and 063 WETLAND - SEDGE MEADOW/SHALLOW MARSH:
Seasonally flooded areas, wet meadows, marshes, and swamps. Visible water ranges from very little up to 12 inches in depth. In most years water is present year round. The dominant vegetation includes rushes, sedges, cattails, and burreed. This vegetation type is utilized heavily by waterfowl, marsh birds, owls, amphibians, herons, sparrows, voles, and muskrats.
064 WETLAND - DEEP MARSH:
Wetlands containing 1 to 3 feet of water. Vegetation includes islands of cattails, reeds, bulrushes, spike rushes, and wild rice. This vegetation type is heavily used by waterfowl for feeding and nesting. The mink-muskrat-cattail ecology provides the nucleus for a rich wildlife community.
065 WETLAND - OPEN WATER:
Water depth is variable, but less than 10 feet in those areas classed as permanent open water. Emergent vegetation is restricted to a narrow belt around the edge and includes pondweeds, water lillies, coontail and wild rice. The edge may be a floating mat composed of sedges, spagnum, or laborador tea. This type is often used by broods of ducks, although brood cover is not usually well interspersed as in shallow marsh wetlands. This type is also important for attracting and holding migrating waterfowl.
Less than 10 acres will be classed as open water areas. Water areas larger than 10 acres will be classed as lakes. Deeper areas are excellent nurseries for pike, bass, and pan fish. These areas are important to geese, ducks, eagles, ospreys, terns, and gulls. Large beaver ponds are included in the open water classification.
066 WETLAND - SHRUB SWAMP:
Areas of saturated ground periodically covered with six inches or more of water. Typical vegetation includes alder, willow, arrowwood, and other shrubs. The use by waterfowl is low unless open areas occur within the dense thickets. Important habitat for woodcock. Grouse deer and herons may also use this vegetation type.
070 WATER LAKE:
Open water areas larger than 10 acres will be classified as lakes. Lakes serve as resting and feeding areas for loons, geese, ducks, eagles, and ospreys. A narrow band around the edge is often used for brood rearing if emergent vegetation is present: especially true for diving ducks.
080 WATER - STREAM – RIVER:
Slow moving streams and rivers, associated ox-bows and beaver dams provide important habitat for waterfowl, especially woodducks and mergansers.
090 NON-VEGETATED:
All areas naturally or artificially void of vegetation, includes extensive rock outcrops, talus, sand beach or dunes, mudflats, and cliffs.
095 GRAVEL PIT:
Active and inactive stone and gravel pits. Characterized by disturbed soils usually with cliffs and rock piles present.
Appendix B: NON-FOREST Vegetation Codes Appendix C: Timber Land Suitability Class (TLSC) Codes & Descriptions
| 100 |
| Non-meandered water (included as National Forest System ownership) |
| 200 |
| Non-forested land, including savannahs and orchards |
| 300 |
| Forested land withdrawn from timber production by Congress, the Secretary, or the Chief. Examples: Dukes Experimental Forest, Grand Island, and Dukes Research Natural Areas, wilderness areas and National Historical Register sites. |
| 500 |
| Forestland suited for timber production based on current technology. Reviewed by ID teams and determined to be suited for timber production. |
| 720 |
| Irreversible damage most likely to occur should harvest occur. Examples: Areas having steep slopes, unstable soils, unique ecosystems, etc. None was identified in the Hiawatha Forest Plan. |
| 740 |
| There is not adequate information to project responses to timber management practices. Examples: Areas having high water tables, low productivity (lands less than 20 cubic feet growth), etc. The Hiawatha Forest Plan identified 34,000 acres in this category. These acres are primarily lowland conifer/ hardwood types with productivity levels less than 20 cubic feet per acre per year of growth. |
| 800 |
| For land in which management objectives preclude timber production. Examples: Areas requiring resource protection to assure that objectives for riparian areas, wildlife habitat, vegetation, threatened and endangered species (eagle/osprey nest zones), etc, are achieved. |
| 801 |
| Unsuitable - other management objectives. |
| 803 |
| Dukes Experimental forest, harvests allowed. |
| 810 |
| For land proposed for resource uses that preclude timber production in order to achieve other multiple-use objectives. Example: Land allocated to management area 6.3 in the Hiawatha Forest Plan where timber production is precluded. |
| 820 |
| Land is not cost efficient in meeting forest objectives. Example: All forestlands within management area 9.1. Other lands that were tentatively suited but later identified by an ID Team as not cost efficient in meeting Forest objectives for timber production over the entire planning horizon (150 years). Simply, these are lands that are not needed to meet timber outputs during the planning horizon. |
| 880 |
| Lands under study pending Congressional, Chief, and/or Secretary of Agriculture action. Example: Wilderness study or roadless areas. On the Hiawatha these are: Candidate Wild and Scenic River (8.4), Candidate wilderness (9.2) and candidate Natural Research Areas. |
Appendix C: Timber Land Suitability Class Appendix D: Stand Prescription – Activity Codes and Descriptions Enter the codes as a 4-digit numeral, preceded by “A”, with no spaces between: “Annnn”.
Silviculturally-needed harvests in timbered stands
| 4111 |
| Acres |
| Patch Clear-cutting |
| 4112 |
| Acres |
| Strip Clear-cutting |
| 4113 |
| Acres |
| Stand Clear-cutting |
| 4114 |
| Acres |
| Salvage Clear-cutting, mortality |
| 4121 |
| Acres |
| Prep cut - Shelterwood |
| 4122 |
| Acres |
| Prep cut - Seed Tree |
| 4131 |
| Acres |
| Seed cut - Shelterwood |
| 4132 |
| Acres |
| Seed cut - Seed Tree |
| 4141 |
| Acres |
| Removal cut - Shelterwood |
| 4142 |
| Acres |
| Removal cut - Seed Tree |
| 4151 |
| Acres |
| Selection - Individual Tree (Uneven-aged NH) |
| 4152 |
| Acres |
| Selection - Group |
| 4210 |
| Acres |
| Improvement (Selection harvest without 3+ age classes) |
| 4220 |
| Acres |
| Commercial Thinning |
| 4231 |
| Acres |
| Selectively Salvage individual trees - mortality |
| 4232 |
| Acres |
| Selectively Salvage individual trees - sanitation |
Silviculturally-needed TSI in timbered stands
| 4431 |
| Acres |
| Planting - Full |
| 4432 |
| Acres |
| Planting - Fill in |
| 4492 |
| Acres |
| Site Preparation for Artificial Regeneration |
| 4493 |
| Acres |
| Site Preparation for Natural Regeneration |
| 4511 |
| Acres |
| Release - Individual Tree |
| 4512 |
| Acres |
| Release - Area |
| 4521 |
| Acres |
| Precommercial Thinning - Individual tree |
| 4541 |
| Acres |
| Control understory vegetation - prescribe burn |
| 4542 |
| Acres |
| Control understory vegetation - hand tools |
Opening needs in non-timbered stands
| 6720 |
| Acres |
| Opening needs improvement |
| 6725 |
| Acres |
| Burn upland opening |
| 6730 |
| Acres |
| Noncommercial clear-cut |
| 6734 |
| Acres |
| Remove residual stems |
| 6736 |
| Acres |
| Seed wildlife species |
| 6737 |
| Acres |
| Plant wildlife species |
| 6743 |
| Acres |
| Release mast trees or shrubs |
Appendix D: Stand Prescription – Activity Codes and Descriptions Appendix E: Within-Stand Features – Codes and Descriptions Record 3-digit code preceded by “F”: “Fnnn”.
Stand Feature Codes and Definitions marked with an asterisk (*) are described in greater detail in a second table that follows.
| 270 |
| Endangered plants or animals |
| 271 |
| Threatened plants or animals |
| 401 |
| Hemlock regeneration present |
| 402 |
| Hemlock component, widely scattered |
| 403 |
| White pine regeneration present |
| 404 |
| White pine component, widely scattered |
| 411 |
| Oak regeneration present |
| 412 |
| Oak component, widely scattered |
| 413 |
| Heavy beech brush (regeneration) |
| 415 |
| Shrubs interfering with regeneration of commercial species |
| 460 |
| Small opening (unmapped) |
| 614 |
| Undeveloped campsite* |
| 803 |
| Beaver dam - inactive |
| 900 |
| Cultural site (known or possible)* |
| 901 |
| Building or building remains* |
* Stand Feature Definitions are listed below for items with asterisks
| 614 |
| Undeveloped campsite - Unmapped dispersed recreation site, frequently used by camper vehicles, hunters or other visitors. |
| 900 |
| Cultural site (known or possible) - physical evidence of human occupation or use, i.e. artifacts, dumps, holes, pits, structures or foundations. |
| 901 |
| Building or building remains - standing or collapsed cabin, shack, or associated structure of wood, timbers, brick, concrete, etc. |
| 906 |
| Trash pile or dump - any surface debris scatter from human use, along roadsides, associated with old sites, or isolated in the woods. |
Appendix F: Species Codes R9SS = sensitive (Federal/Region 9); NOX = noxious Note: To find codes for other species, check the plants website at: USDA Plants Database
| Scientific Name |
| Common Name |
| Symbol |
| Status |
| Abies balsamea |
| Balsam Fir |
| ABBA |
| Acer pensylvanicum |
| Striped maple |
| ACPE |
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