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California Rapid Assessment Method for Wetlands - State Water ...

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<strong>Cali<strong>for</strong>nia</strong> <strong>Rapid</strong> <strong>Assessment</strong> <strong>Method</strong> <strong>for</strong> <strong>Wetlands</strong> v. 5.0.2 – Chapter 2<br />

2.3 Developmental Framework<br />

The CRAM developmental process consists of nine steps with distinct products organized into<br />

three phases: basic design, calibration, and validation (Table 2.1).<br />

Core Team<br />

Core and<br />

Regional<br />

Teams<br />

Table 2.1: Basic outline of CRAM development.<br />

Basic<br />

Design<br />

Phase<br />

Calibration<br />

Phase<br />

Validation<br />

Phase<br />

Develop conceptual models of wetland <strong>for</strong>m and function<br />

Identify universal Attributes of wetland condition<br />

Nominate Metrics of the Attributes<br />

Nominate descriptions of alternative states <strong>for</strong> each Metric<br />

Clarify and revise the Metrics and narrative descriptions of<br />

alternative states based on regional team input and inter- and<br />

intra-team comparisons<br />

Develop a checklist to identify stressors<br />

Test and select methods of scaling and weighting Attributes<br />

and Metrics<br />

Test and select <strong>for</strong>mulas <strong>for</strong> calculating Attribute scores and<br />

AA scores<br />

Validate Metrics and Attributes using Level 3 data<br />

Conduct independent peer review<br />

Provide outreach and training<br />

2.3.1 Basic Design<br />

This phase of CRAM development involved creating conceptual models of wetland <strong>for</strong>m and<br />

function, defining key terms, developing the wetland typology, identifying the attributes, and<br />

<strong>for</strong>mulating metrics that describe each attribute. The basic design work was done primarily<br />

through initial field-testing and feedback by Regional Teams and the Core Team. Version 2.0 of<br />

CRAM marked the completion of the basic design phase.<br />

Each CRAM attribute is represented by a set of metrics (Table 2.2 below), and each metric is<br />

represented by a set of mutually exclusive narrative descriptions of alternative states. In<br />

aggregate, the alternative states of all the metrics <strong>for</strong> any type of wetland represent its full range<br />

of visible <strong>for</strong>m and structure.<br />

An ef<strong>for</strong>t was made to separate assessments of condition from assessments of stress. This was<br />

done to explore correlations between stress and condition. For example, CRAM AAs can be<br />

grouped according to their associated stressors, and the groups can be compared based on their<br />

CRAM scores. The separation has been difficult to achieve, however, For example, the Plant<br />

Community metric of the Biotic Structure attribute includes a sub-metric about the relative<br />

abundance of non-native plant species, although biological invasion is usually considered a<br />

significant stressor. Some autocorrelation can there<strong>for</strong>e be expected between stress and<br />

condition as assessed using the current version of CRAM<br />

2.3.2 Calibration<br />

The calibration phase was used to determine if the draft wetland classification scheme, the<br />

attributes, the metrics, and the narrative descriptions of alternative states were (1) clear and<br />

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