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Roadside Revegetation

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MONITORING PROCEDURES<br />

◾◾<br />

Rectilinear areas – Associated with staging areas and material stockpiles<br />

◾◾<br />

Dispersed areas – Associated with planting islands, planting pockets, and clump<br />

plantings<br />

Each of these sampling designs has a set of procedures defining how transects and quadrats<br />

will be laid out. Section 12.8, Sample Size Determination, guides the designer through the<br />

methods for determining how many transects and quadrats to establish.<br />

12.1.3 WHAT IS THE OBJECTIVE BEHIND MONITORING?<br />

There are three basic reasons for statistical monitoring:<br />

◾◾<br />

Compliance – Were regulatory standards or project objectives met?<br />

◾◾<br />

Treatment differences – Are there differences between revegetation treatments?<br />

◾◾<br />

Trends – What degree of change is occurring over time?<br />

Monitoring for most projects will be conducted to determine whether standards were met<br />

(compliance) because this will be of most interest to the reviewing officials. There will be<br />

occasions, however, when it will be helpful to know if different revegetation treatments applied<br />

to the same area resulted in a different vegetative response. There might also be times when<br />

it will be important to know to what degree things have changed over time. It is important to<br />

discern which of these three objectives meet the intent of the monitoring.<br />

This chapter will provide a set of instructions that establish the following:<br />

◾◾<br />

Quadrat locations (see Section 12.7, Sampling Area Design)<br />

◾◾<br />

Quantity of quadrats to take (see Section 12.8, Sample Size Determination)<br />

◾◾<br />

Type of data collection at each quadrat (see Section 12.2, Soil Cover Procedure, Section<br />

12.3, Species Cover Procedure, Section 12.4, Species Presence Procedure, Section 12.5,<br />

Plant Density Procedure, and Section 12.6, Plant Attributes Procedure)<br />

◾◾<br />

Type of data analysis to perform (see Section 12.9, Statistical Analysis Using Confidence<br />

Intervals)<br />

12.2 SOIL COVER PROCEDURE<br />

Reestablishing grasses and forbs on disturbed sites is essential for erosion control. In general,<br />

erosion and sediment transport is a function of live or dead cover in contact with the soil<br />

surface. The following soil cover procedures can be used to determine the amount and type<br />

of cover existing on the surface after construction.<br />

The quadrat is the unit of area that is monitored for soil cover. Exact measurements are<br />

based on recording the surface soil attributes at 20 data points within each quadrat. In this<br />

assessment, a grid of 20 data points is placed on the surface of the soil; where each point hits<br />

the surface is where the soil cover attribute is recorded. For instance, the data recorded at<br />

the first quadrat shows that 5 points were rock, 10 points were live plant cover, and 5 points<br />

were soil. The results for that quadrat would be 25 percent rock, 50 percent live plant cover,<br />

and 25 percent bare soil.<br />

Quadrats are read in the field using a fixed frame (see Section 12.2.1, Sampling by Fixed<br />

Frame) or read later in the office from digital pictures of quadrats. A system for taking digital<br />

photographs of the surface, where the photograph itself becomes the quadrat, is described<br />

in Section 12.2.2, Sampling by Digital Camera.<br />

The sampling design for laying out transects and quadrats depends on the shape of the sampling<br />

unit (see Section 12.7, Sampling Area Design). The number of transects and quadrats depends<br />

<strong>Roadside</strong> <strong>Revegetation</strong>: An Integrated Approach to Establishing Native Plants and Pollinator Habitat<br />

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