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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 5<br />

CHAPTER 5:<br />

GUIDELINES TO COMPLETE STRESSOR CHECKLISTS<br />

A. Definition: For the purposes of CRAM, a stressor is an anthropogenic perturbation within a<br />

wetland or its setting that is likely to negatively impact the functional capacity of a CRAM<br />

<strong>Assessment</strong> Area (AA). In contrast, disturbances are distinctly defined as natural phenomena,<br />

although they might have similar impacts as stressors.<br />

B. Rationale: Physical and biological processes connect wetlands to their environmental<br />

settings and thus help shape wetland conditions, which are there<strong>for</strong>e influenced by land use<br />

practices within the settings (Frissell et al. 1986, Roth et al. 1996, Scott et al. 2002). Wetland<br />

conditions can also be affected by stressors operating directly within the wetlands, although<br />

these tend to be less abundant than stressors originating in the surrounding landscape.<br />

The purpose of the Stressor Checklist is to identify stressors within a CRAM <strong>Assessment</strong> Area<br />

(AA) or its immediate hat might help account <strong>for</strong> any low CRAM scores. In some cases, a single<br />

stressor might be the primary cause <strong>for</strong> low-scoring conditions, but conditions are usually due to<br />

interactions among multiple stressors (USEPA 2002).<br />

There are four underlying assumptions of the Stressor Checklist: (1) stressors can help explain<br />

CRAM scores; (2) wetland condition declines as the number of stressors acting on the wetland<br />

increases (there is no assumption that the decline is additive (linear), non-linear, or<br />

multiplicative); (3) increasing the intensity or the proximity of the stressor results in a greater<br />

decline in condition; and (4) continuous or chronic stress increases the decline in condition.<br />

C. Seasonality: The Stressor Checklist is not sensitive to seasonality.<br />

D. Office and Field Indicators: The process to identify stressors is the same <strong>for</strong> all wetland<br />

types. For each CRAM attribute, a variety of possible stressors are listed. Their presence and<br />

likelihood of significantly affecting the AA are recorded in the Stressor Checklist Worksheet.<br />

For the Hydrology, Physical Structure, and Biotic Structure attributes, the focus is on stressors<br />

operating within the AA or within 50 m of the AA. For the Buffer and Landscape Context<br />

attribute, the focus is on stressors operating within 500 m of the AA. More distant stressors that<br />

have obvious, direct, controlling influences on the AA can also be noted.<br />

Table 5.1: Wetland disturbances and conversions.<br />

Is there evidence of a major disturbance<br />

flood fire landslide other none<br />

(select one best answer)<br />

If there is evidence of disturbance, how<br />

severe was it<br />

If the wetland has been<br />

converted from another<br />

type, what type was it<br />

not<br />

converted<br />

effects will last<br />

next 5 years<br />

effects will last<br />

3-5 years<br />

effects will last<br />

1-2 years<br />

depressional vernal pool<br />

vernal pool<br />

system<br />

non-confined<br />

riverine<br />

confined<br />

riverine<br />

seasonal<br />

estuarine<br />

perennial saline<br />

estuarine<br />

perennial nonsaline<br />

estuarine<br />

wet meadow<br />

lacustrine seep or spring playa<br />

91

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