Difference between revisions of "Erythranthe washingtonensis"
Phytoneuron 2012-39: 39. 2012. (as washingtoniensis)
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|place=2012-39: 39. 2012 | |place=2012-39: 39. 2012 | ||
|year=2012 | |year=2012 | ||
| + | |other_info_on_pub=(as washingtoniensis) | ||
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|common_names=John Day or Washington monkeyflower | |common_names=John Day or Washington monkeyflower | ||
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|label=Endemic | |label=Endemic | ||
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| − | |basionyms={{Treatment/ID/ | + | |basionyms={{Treatment/ID/Basionym |
|name=Mimulus washingtonensis | |name=Mimulus washingtonensis | ||
|authority=Gandoger | |authority=Gandoger | ||
| + | |rank=species | ||
| + | |publication_title=Bull. Soc. Bot. France | ||
| + | |publication_place=66: 218. 1919 | ||
}} | }} | ||
|synonyms= | |synonyms= | ||
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|elevation=700–1300 m. | |elevation=700–1300 m. | ||
|distribution=Oreg. | |distribution=Oreg. | ||
| − | |discussion=<p>Erythranthe washingtonensis is considered to be extirpated in Washington by the Washington Natural Heritage Program.</p> | + | |discussion=<p><i>Erythranthe washingtonensis</i> is considered to be extirpated in Washington by the Washington Natural Heritage Program.</p> |
|tables= | |tables= | ||
|references= | |references= | ||
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-->{{#Taxon: | -->{{#Taxon: | ||
name=Erythranthe washingtonensis | name=Erythranthe washingtonensis | ||
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|authority=(Gandoger) G. L. Nesom | |authority=(Gandoger) G. L. Nesom | ||
|rank=species | |rank=species | ||
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|publication year=2012 | |publication year=2012 | ||
|special status=Endemic | |special status=Endemic | ||
| − | |source xml=https:// | + | |source xml=https://bitbucket.org/aafc-mbb/fna-data-curation/src/2e0870ddd59836b60bcf96646a41e87ea5a5943a/coarse_grained_fna_xml/V17/V17_1307.xml |
|genus=Erythranthe | |genus=Erythranthe | ||
|species=Erythranthe washingtonensis | |species=Erythranthe washingtonensis | ||
Latest revision as of 19:29, 5 November 2020
Annuals, fibrous-rooted or filiform-taprooted. Stems erect to ascending, straight or geniculate at nodes, usually many-branched, terete, 5–25 cm, moderately puberulent-glandular to villous-glandular, hairs 0.1–0.8 mm, flattened, sometimes vitreous, distinctly multicellular, gland-tipped. Leaves cauline, basal not persistent; petiole 2–14 mm; blade palmately veined, deltate or ovate to ovate-lanceolate, 4–16(–23) × 2–11(–16) mm, base rounded to cuneate or truncate, margins denticulate or entire, apex acute, surfaces moderately puberulent-glandular to villous-glandular, hairs 0.1–0.8 mm, flattened, sometimes vitreous, distinctly multicellular, gland-tipped. Flowers herkogamous, 1–6, from proximal to distal nodes. Fruiting pedicels divergent at nearly right angles, 20–50 mm, densely, minutely stipitate-glandular. Fruiting calyces greenish, ridge-angled, tubular, weakly inflated, 6–8 mm, margins distinctly toothed or lobed, densely, minutely stipitate-glandular, lobes pronounced, erect. Corollas yellow with small reddish brown dots, abaxial limb with 2 white patches (abaxial ridges), bilaterally symmetric, strongly bilabiate; tube-throat funnelform, 8–10 mm, exserted beyond calyx margin; limb expanded 7–10 mm, lobes obovate-oblong, apex rounded to rounded-cuneate. Styles hispid-hirtellous. Anthers included, glabrous. Capsules included, 5–8.5 mm. 2n = 32.
Phenology: Flowering May–Sep.
Habitat: Shallow basalt gravel in narrow channels and intermittent streams, sandy stream banks, open slopes, rocky shelves near seeps.
Elevation: 700–1300 m.
Discussion
Erythranthe washingtonensis is considered to be extirpated in Washington by the Washington Natural Heritage Program.
Selected References
None.