State 1
Reference

Community 1.1
Bigleaf Maple, Red Alder, Salmonberry, Thimbleberry, Western Swordfern, and Oregon Oxalis

Bigleaf maple – red alder / salmonberry – thimbleberry / western swordfern – Oregon oxalis

Structure: mature deciduous forest with a mix of shrubs in the understory

Bigleaf maple and red alder are the most dominant overstory species in the reference community. California laurel (Umbellularia californica), tanoak (Notholithocarpus desiflorus), and California live oak (Quercus chrysolepis) occur south of the Alsea River, at times quite prolifically (Pabst, 1999). Douglas-fir may also represent a portion of the overstory, however the frequency of flooding lends to hardwood regeneration. Conifer regeneration will increase in abundance further from the active stream channel (Wimberly, 2001). Regeneration is restricted by canopy cover and often limited to gaps where sunlight and exposed mineral soil is most available.
The reference community represents a lack of major flooding for at least 75 years, allowing the pioneering species to form a mature canopy. The lack of flooding also allows the growth of a robust understory of shrubs including salmonberry, vine maple, stink currant, thimbleberry, and snowberry (Symphoricarpos albus). Forbs such as western swordfern, false lily of the valley (Maianthemum dilatatum), ladyfern (Athyrium filix-femina), and Oregon oxalis are also common.
Common disturbances include small gap dynamics (1/2 acre openings or smaller) following the decline of the red alder canopy, minor scouring from flooding, and mass movement. Soil deposition following minor scouring from smaller scale and periodic flooding temporarily affects the understory community, but it does not alter the composition of the overstory. In addition, beaver (Castor canadensis) activity can by a significant driver in small scale disturbances, hydrologic morphology, and contribute to large woody debris in riparian edges and corridors.

Community 1.2
Red Alder, Salmonberry, and Coastal Hedgenettle

Red alder / salmonberry / coastal hedgenettle

Structure: Bare ground with scattered tree, shrub, and grass establishment

Community phase 1.2 represents a riparian forest that is undergoing regeneration or stand initiation immediately following flooding disturbance. The soil surface is gravelly and highly variable depending on the intensity, frequency, and aggradation of the flooding event (Fonda, 1974). There may be scattered remnant mature trees in some areas and an abundance of woody debris. Successful regeneration is dependent on the local seed source, adequate seed bed, and sufficient light and water (Nierenberg, 2000). Red alder has several competition advantages and can establish quickly, relative to conifers. Red alder can sprout and establish in full sunlight and fixes nitrogen in poorly developed alluvial soils providing an early competitive advantage (Villarin, 2009). In addition, the deciduous species seeds are light and can be transported long distances by wind and water, allowing for rapid recolonization. Salmonberry and coastal hedgenettle (Stacys chamissonis) are often established within this community phase.

Community 1.3
Red Alder, Bigleaf Maple, Salmonberry, Western Swordfern, and False Lily of the Valley

Red alder – bigleaf maple/ salmonberry / western swordfern – false lily of the valley

Structure: dense single story with diminished understory

Community phase 1.3 is an early seral forest in regeneration, possibly with scattered remnant mature trees. There is increased competition among individual trees for available water, light, and nutrients. Red alder tends to dominate the overstory, however red alder will begin to die between 40-70 years following disturbance and allow more light to penetrate the newly nitrogen rich soil (Naiman, 2009). If there is a presence of red alder regeneration within this community phase, it may be inferred that frequent minor flooding has been influencing site dynamics (Nierenberg, 2000). Shade tolerant forbs such as western swordfern and false lily of the valley establish during this phase.

Pathway 1.1A
Community 1.1 to 1.2

This pathway represents a stand replacing wildfire, catastrophic windstorm, a major 100 or 500-year flood event, or mass movement which scours the stream channel, removes understory and overstory vegetation, and may alter the stream flow. This type of disturbance may completely reconfigure sediment loads and dramatically reduce or eliminate the forest overstory.

Pathway 1.2A
Community 1.2 to 1.3

This pathway represents growth over time with no further major disturbance.

Pathway 1.3B
Community 1.3 to 1.1

Red Alder, Bigleaf Maple, Salmonberry, Western Swordfern, and False Lily of the Valley

Bigleaf Maple, Red Alder, Salmonberry, Thimbleberry, Western Swordfern, and Oregon Oxalis

This pathway represents growth over time with no further major disturbance.

Pathway 1.3A
Community 1.3 to 1.2

This pathway represents a stand replacing wildfire, catastrophic windstorm, a major 100 or 500-year flood event, or mass movement which scours the stream channel, removes understory and overstory vegetation, and may alter the stream flow. This type of disturbance may completely reconfigure sediment loads and dramatically reduce or eliminate the forest overstory.

State 2
Converted

Community 2.1
Managed Cropland or Hayland

Managed Cropland or Hayland

Structure: Annual or perennial non-native species

Community Phase 2.1 may consist of a range of crops, including annually planted species, short-lived perennials, and more permanent shrubby crops. Hayland and grass-legume silage crops are also included in this community phase.

Community 2.2
Non-Native Grassland and Shrubland

Non-Native Grassland and Shrubland

Structure: Annual or perennial herbaceous or shrubby species

Community phase 2.2 is characterized by a low level of agronomic or management inputs such as added fertility, intensive grazing management, regular mowing or weed control. This plant community is often dominated by introduced weedy species. Sites with extremely low fertility or heavy grazing pressure will have a higher proportion of annual, stoloniferous or rhizomatous species. Wetland areas are often dominated by non-native rhizomatous grasses. This plant community can include remnants of commonly seeded introduced pasture species.

Community 2.3
Managed Grassland

Managed Grassland

Structure: perennial herbaceous species

Community phase 2.3 receives regular agronomic inputs, including adding soil nutrients and other soil amendments such as lime, implementing grazing management plans, regular mowing, controlling weeds, and reseeding as needed. This plant community typically includes introduced perennial pasture and hay species that commonly are seeded. In areas of historic native grassland, mixtures of perennial and annual native species may be seeded and managed by appropriate agronomic and livestock management activities. Minor amounts of introduced species that commonly are in non-native grassland and shrubland communities (community phase 2.2) are in this phase.

Pathway 2.1A
Community 2.1 to 2.2

In the absence of the following agronomic and livestock management activities, seeds from surrounding weedy plant communities will be transported to the site through factors such as wind, flood water, animals or vehicle traffic where adapted species will become established. Management activities could include tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, planting the site to desirable herbaceous species and implementation of grazing management plans.

Pathway 2.1B
Community 2.1 to 2.3

Agronomic and livestock management activities such as tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, planting the site to desirable herbaceous species and implementation of grazing management plans.

Pathway 2.2B
Community 2.2 to 2.1

Agronomic activities such as tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, and planting the site to desirable crop species.

Pathway 2.2A
Community 2.2 to 2.3

Agronomic and livestock management activities such as tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, planting the site to desirable herbaceous species and implementation of grazing management plans.

Pathway 2.3A
Community 2.3 to 2.1

Agronomic activities such as tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, and planting the site to desirable crop species.

Pathway 2.3B
Community 2.3 to 2.2

In the absence of the following agronomic and livestock management activities, seeds from surrounding weedy plant communities will be transported to the site through factors such as wind, flood water, animals or vehicle traffic where adapted species will become established. Management activities could include tillage, addition of significant fertility or other soil amendments such as lime, mowing, burning, harvest or chemical control of vegetation, planting the site to desirable herbaceous species and implementation of grazing management plans.

Transition T1A
State 1 to 2

This pathway represents a change in land use. Land management changes include modifications to the hydrologic function to develop pasture and agriculture. Non-native seed disbursement is introduced (intentionally or unintentionally) which alters the reference community.

Transition T2A
State 2 to 1

This pathway represents a transition to restore the natural hydrologic function and native plant habitat. Native seed sources are necessary to restore the community as well as extensive brush and invasive species management and mitigation.