Lathyrus bijugatus, drypark pea
Abrahamson, Ilana L., compiler. 2026. Species Brief: Lathyrus bijugatus, drypark pea. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Missoula Fire Sciences Laboratory (Producer). Available: https://research.fs.usda.gov/feis/species-briefs/latbij
This Species Brief is a concise summary of the biological, ecological, and fire‑related characteristics of an individual species derived from a Fire Effects Information System (FEIS) Species Review. Table 1 is derived from a standardized template and highlights these characteristics.
| Attribute | Characteristic | Justification | Source |
|---|---|---|---|
| Biological characteristics | |||
| Life form | Forb | Drypark pea is a perennial, leguminous forb. Its stems may vine, but vining is less pronounced than in legumes with more developed tendrils, so it is treated as a forb. | FEIS: Botanical Description [1] |
| Typical lifespan | Insufficient information | The source does not provide explicit information about typical lifespan. | FEIS [1] |
| Life cycle | Perennial | Drypark pea is a perennial, leguminous forb. It desiccates in fall and sprouts again in spring. | FEIS: Botanical Description; Seasonal Development [1] |
| Drought tolerance | High* | Drypark pea prefers dry soils and open sites. Soil moisture on sites where it occurs is reported as dry, but drought tolerance is not explicitly stated. | FEIS: Site Characteristics [1] |
| Rooting depth | Deep* | Rooting depth is not stated directly, but inferred from the root type. Lathyrus species have caudices, taproots, fibrous horizontal roots, and slender rhizomes growing from the taproot. | FEIS: Botanical Description [1] |
| Bark thickness at maturity | N/A | This attribute applies to trees. | FEIS [1] |
| Sheds low branches | N/A | This attribute applies to trees. | FEIS [1] |
| Reproduction and Regeneration | |||
| Adventitious buds | Rhizomes; Caudex* | Drypark pea sprouts from its rhizomes. It may also sprout from its caudex after top-kill, although this is not documented. | FEIS: Vegetative Regeneration; Botanical Description [1] |
| Time to reproductive maturity | Insufficient information | The source does not provide explicit information about time to reproductive maturity. | FEIS [1] |
| Soil seed bank longevity | Insufficient information | Lathyrus species have a soil-stored seed bank, but the long-term viability of drypark pea seed is not documented. | FEIS: Seed Banking [1] |
| Serotinous cones | N/A | This attribute applies to conifers. Drypark pea fruit is a two-valved pod bearing 6 to 12 seeds. | FEIS: Botanical Description [1] |
| Seed dispersal mechanism | Insufficient information | Information on seed dispersal, viability, and seedling establishment of drypark pea was not available in the literature. | FEIS: Regeneration Processes [1] |
| Seed dispersal distance | Insufficient information | Information on seed dispersal, viability, and seedling establishment of drypark pea was not available in the literature. | FEIS: Regeneration Processes [1] |
| Optimal conditions for seedling establishment | Insufficient information | Information on seed dispersal, viability, and seedling establishment of drypark pea was not available in the literature. | FEIS: Regeneration Processes [1] |
| Successional Status | |||
| Shade tolerance | Shade intolerant* | Drypark pea occurs on open sites and is rare in late-successional conifer forests, but shade tolerance is not stated directly. | FEIS: Successional Status [1] |
| Successional status | Early* | Drypark pea occurs on open sites, including clearings, and is rare in late-successional conifer forests, but its successional status is not stated directly. | FEIS: Successional Status [1] |
| Fire | |||
| Primary fire response(s) or adaptation(s) | Recover/Resprout | Fire probably top-kills drypark pea, and it likely sprouts from its rhizomes and/or caudex afterward. It likely survives because perennating buds are insulated by soil. One study suggests that fires of low or high intensities may not substantially affect its abundance. | FEIS: Immediate Fire Effects; Fire Adaptations and Plant Response to Fire [1] |
| Germination is fire stimulated | Insufficient information | Little is known of drypark pea's germination requirements, and no fire cue for germination is described. | FEIS: Germination [1] |
| Flowering/fruiting is fire stimulated | Insufficient information | The source does not provide explicit information about fire-stimulated flowering or fruiting. | FEIS [1] |
| Season when it is most sensitive to fire | Insufficient information | Information was not available about seasonal differences in drypark pea's fire sensitivity. In the only available fire study on the species, drypark pea abundance 1-3 years after a fall prescribed fire was similar to prefire abundance. | FEIS: Fire Adaptations and Plant Response to Fire |
| Plant flammability | Low* | Because it is rare even where it occurs, drypark pea does not substantially contribute to fine fuels. Flammability is not measured directly. | FEIS: Fuels [1] |
| Early colonizer/recolonizer of burned or disturbed sites | Insufficient information | The single study found cover and frequency similar on unburned plots and plots burned under low or high intensity, but no evidence describes colonization of newly burned or disturbed sites. | FEIS: Fire Adaptations and Plant Response to Fire [1] |
| Effect of fire exclusion on population | Possible decrease | Because drypark pea occurs in open plant communities, fire exclusion could reduce its abundance, especially in conifer woodlands and forests. | FEIS: Fire Management Considerations [1] |
| Is this species typically managed with prescribed fire? | Rarely/No* | Only one study documented drypark pea after fire, where it was incidental to prescribed burns applied to logged ponderosa pine. | FEIS: Fire Adaptations and Plant Response to Fire [1] |
| Predominant historical fire frequencies of ecosystem where it most commonly occurs | Frequent; Mid-frequency | Drypark pea grows in open conifer forests, Palouse prairies, mountain grasslands, and on the edges of big sagebrush communities. The open ponderosa pine, Douglas-fir, and western larch forests historically experienced mostly frequent, low-severity fires. Historical fire intervals in big sagebrush communities were likely over 25 years. | FEIS: Fire Regimes [1] |
| Predominant historical fire severity where it most commonly occurs | Low; Mixed*; Replacement* | The open conifer forests historically experienced mostly frequent, low-severity fires. Western larch and subalpine fir stand types experienced some mixed-severity and some stand-replacing fire, and big sagebrush communities experienced mostly high-severity fire. | FEIS: Fire Regimes [1] |
| Predominant historical fire regime group where it most commonly occurs | 1; 4* | The source does not assign fire regime groups directly, but open ponderosa pine, Douglas-fir, and western larch forests had mostly frequent, low- to mixed-severity fires (group 1), and big sagebrush communities historically had mid-frequency, stand replacing fire (group 4). | FEIS: Fire Regimes [1] |
| Alters historical fuel characteristics of ecosystems where it occurs | Rarely/No | Because it is rare even in the plant communities where it occurs, drypark pea does not substantially contribute to fine fuels. | FEIS: Fuels [1] |
1. Fryer, Janet L. 2021. Lathyrus bijugatus, drypark pea. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Missoula Fire Sciences Laboratory (Producer). Available: https://research.fs.usda.gov/feis/species-reviews/latbij