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For bond release sampling with belts, sufficient samples must be collected to insure <br />adequacy of the effort (to facilitate valid testing) in accordance with one of the three <br />methods under either Rule 4.15.11 (2), or Rule 4.15.11 (3). Depending on the selected <br />protocol, care must be taken to collect at least the minimum number of samples indicated <br />(15, 30, 40, or 75, depending on the procedure utilized). <br />The second method, total enumeration, may be employed for monitoring when the size of <br />a unit is less than approximately one to two acres in size. Total enumeration shall be the <br />typical method utilized for bond release purposes unless shrub patches are too large (e.g., <br />greater than 10 to 15 acres) to practically utilize this technique (in which case belts will <br />be utilized). This method involves total counts of woody plant populations as opposed to <br />estimates of mean densities through statistical sampling. Implementation of the total <br />count technique would involve circumscribing the boundaries of a target polygon with <br />hip chain thread or similar visible designation. Once a unit is circumscribed in this <br />manner, a team of two or more biologists walking shoulder-to-shoulder traverse the plot <br />enumerating each plant by species. The person farthest inside the line of observers trails <br />hip chain thread, or other means, to mark their path to prevent missing or double counting <br />specimens on subsequent passes. The distance between observers should be 15 to 20 feet <br />or less depending on the height of grasses and the presence of low growing taxa such as <br />rose or snowberry. Each internal observer should also "zigzag" as the team progresses, <br />occasionally turning to view the area just passed to ensure visual coverage of the entire <br />survey path. Constant communication among crew members precludes double counting <br />or missing of plants located along the margins of observed paths. Results from total <br />enumeration efforts can be compared directly with success criteria without statistical <br />testing. <br />Determination of Seedling Emergence <br />At each emergent density sample point (revegetation monitoring only), five one-square <br />foot quadrats should be blindly tossed to the ground and the number of emergents rooted <br />within the perimeter of each shall be recorded accordingly into one of five classes: <br />perennial grass, perennial forb, shrub, annual grass, or annual forb. Where possible <br />recognizable taxa may be recorded by species. Efforts with 1- 2 perennial emergents per <br />ft2 are considered to be fair, 2-3 perennial emergents per ft2 are considered to be good, <br />while 3-4 perennial emergents per ft2 are considered very good. Five or more perennial <br />emergents per ft2 are considered to be excellent. <br />Sample Adequacy Determination <br />Sampling within each monitored unit shall be conducted to a minimum of 5, 15 or 20 <br />samples as necessary. Sampling within each unit under consideration for bond release <br />shall start with a minimum of 15 (reference area) or 20 samples (revegetated area) and <br />continue until a statistically adequate sample (if necessary) has been obtained in <br />accordance with Section 4.15.11 (2) (a). From initial sampling efforts, sample means and <br />standard deviations for total non-overlapping vegetation ground cover, production, and <br />woody plant density will be calculated. For bond release applications, the typical <br />procedure is that sampling continues until an adequate sample, nmi,,, has been collected in <br />4.15-32 Revision Dater 3/14/08 <br />Revision No.: TR-72