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Andrena cryptanthae

Authority: Timberlake

Assessment

Least Concern

Date: 3/24/2025

Justification:
Andrena cryptanthae is a solitary bee species that occurs in California, United States, and Baja California Norte, Mexico. It is known from nearly 200 observations, and has been recorded as recently as 2024. Using all records of the species, the extent of occurrence is 284,244 km2. Observations since 2014 come from seven distinct localities. The species is a dietary specialist, collecting pollen from the plant genus Cryptantha (Boraginaceae) for pollen. It has been recorded in grassland, shrubland, and forests. Across the range of the species, land use change has contributed to habitat loss, fragmentation and degradation. The species is also likely impacted by climate change, which alters the quality and quantity of available forage. These threats are likely acting on the species at local levels. More information is needed to understand the population dynamics of this species, and the degree to which threats act on it. Because the species is relatively widespread, occurs in several habitat types, and has been recently observed in several localities, it is unlikely that it is threatened with extinction at this time. As such it is assessed as least concern for now.

Distribution

Country Occurrence:
United States: California
EOO:Unknown
AOO:188.00 km²
Map Notes:The map was created by generating a polygon around all records, generalizing it, and clipping it to the North American continent to remove areas of uninhabited habitat, such as the Pacific Ocean.

Population

Trend:Unknown
Generation Length:1.00 years

Habitats and Ecology

Food habits comment: Andrena cryptanthae is a dietary specialist that collects pollen from the genus Cryptantha (Boraginaceae) (LaBerge 1986). Habitat comment: This species has been recorded in grassland, shrubland, and forest between 82 and 2325 m. Reproduction comment: This species likely nests underground like all other Andrena (Danforth et al. 2019), but nests from this species have not been described. Nest cells from other members of this genus are located at the ends of the lateral burrows, which are typically lined with a waxy Dufour’s gland secretion (Cane 1981) that serves to both isolate the provision from pathogens in the surrounding soil and to regulate water uptake from the soil atmosphere (Cane and Love 2021). Females provision each cell with a ball of pollen moistened with nectar on which they lay a single egg (Michener 2007). Phenology comment: Records of this species come from February to July, with most records from April (Chesshire et al. 2023). Adults are assumed to emerge annually (Danforth et al. 2019).

Habitat Types

Use and Trade

This species is not known to be utilized commercially.

Threats

Threat comments: Specific threats to the species have not been identified. This species may be threatened by drought, which has been severe in its range. Since 2000, the Southwest U.S. has seen the worst drought in 1200 years (Williams, Cook, and Smerdon 2022). Drought can reduce the abundance of flowering plants on a landscape scale, and also reduce pollen and nectar quality (Wilson Rankin, Barney, and Lozano 2020). Drought conditions have been shown to reduce the diversity and abundance of native bees (Minckley, Roulston, and Williams 2013; Hung et al. 2021). . Because Andrena cryptanthae has a short adult life stage, emerges in spring, and appears to be a narrow pollen specialist of the plant Cryptantha which blooms in response to winter rain, it may be at further risk from winter droughts within its range. This species occurs in California coastal sage scrub habitat, one of California's most threatened vegetation types, which is globally imperiled (NatureServe 2024). This habitat is highly threatened by modification, fragmentation, and loss due to urban and suburban growth. Nearly half of California’s residents live in the coastal California counties where this habitat occurs, which is less than 10% of the state’s land area (Riordan and Rundel 2013). Less than 20% of this habitat remains (Davis, Stine, and Stoms 1994), and the existing fragments are considered some of most valuable real estate in California. This contributes to considerable development pressure on remaining fragments, and their high real estate value makes their conservation costly. Coastal sage scrub has also been modified significantly in the past 100 years due to exotic annual grass invasion, which has been facilitated by increased wildfire frequency (Minnich and Dezzani 1998; Talluto and Suding 2008). These factors also contribute to a feedback where increased grass cover increases fire frequency, leading to grassland conversion. This habitat conversion may limit the availability of host plants used by Andrena cryptanthae and alter other abiotic factors important for this species. Certain aspects of this species' biology may make it more vulnerable to some threats. Andrena cryptanthae is a ground nesting species, and nests may be harmed by certain agricultural practices such as tilling, which can kill bees nesting close to the surface (Williams et al. 2010). This species is a dietary specialist, which has been linked to higher risk of extinction due to reduced host plant availability, especially under climate change scenarios (Roberts et al. 2011) and reduced effective population sizes (Packer et al. 2005). Additionally, Andrena have been reported to have low reproductive output because of the short adult life span, and a low rate of brood cell provisioning (reviewed in Danforth et al. 2019). Other threats to bees generally include habitat loss or modification, climate change, pesticide use, exposure to pathogens from managed bee species, and competition with honey bees (Brown and Paxton 2009; Potts et al. 2010; Wojcik et al. 2018; Grab et al. 2019; Raven and Wagner 2021). Threats Threats:
Code Threat Timing Scope Severity
1 Residential & commercial development - 1.2. Commercial & industrial areas Ongoing Majority (50-90%) Slow, significant declines
1.1 Residential & commercial development - Housing & urban areas Ongoing Majority (50-90%) Slow, significant declines
1.2 Residential & commercial development - Commercial & industrial areas Ongoing Majority (50-90%) Slow, significant declines
7 Natural system modifications - 7.1. Fire & fire suppression -> 7.1.2. Suppression in fire frequency/intensity Ongoing Minority (<50%) Slow, significant declines
7.1.1 Natural system modifications - Increase in fire frequency/intensity Ongoing Minority (<50%) Slow, significant declines
8 Invasive and other problematic species, genes, and diseases - 8.1 Invasive non-native/alien species/diseases -> 8.1.2. Named species Ongoing Minority (<50%) Slow, significant declines
8.1.2 Invasive and other problematic species, genes, and diseases - Named species Ongoing Minority (<50%) Slow, significant declines
9 Pollution - 9.3 Agricultural and forestry effluents -> 9.3.3 Herbicides and Pesticides Ongoing Minority (<50%) Slow, significant declines
9.3.3 Pollution - Herbicides and Pesticides Ongoing Minority (<50%) Slow, significant declines
11 Climate change & severe weather - 11.3.Temperature extremes Ongoing Minority (<50%) Slow, significant declines
11.1 Climate change & severe weather - Habitat shifting & alteration Ongoing Majority (50-90%) Slow, significant declines
11.2 Climate change & severe weather - Droughts Ongoing Minority (<50%) Slow, significant declines
11.3 Climate change & severe weather - Temperature extremes Ongoing Minority (<50%) Slow, significant declines

Conservation Actions

Conservation needs No known conservation actions are in place for this species. Protected/Managed area comment: Observations of this species are known from Bureau of Land Management (BLM), U.S. Fish and Wildlife, National Park Service, and U.S. Forest Service land, but this does not confer any specific protections to the species. Management comment: Specific conservation needs for this species have not been identified. Due to the importance of supporting wild bee populations for pollination services, general conservation practices are recommended including, restoring, creating, and preserving natural high-quality habitats to include suitable forage and nesting sites; limiting pesticide use on or near suitable habitat, particularly during the adult bee’s flight period; promoting farming and urban practices that increase pollinator-friendly plants in margin space; minimizing exposure of wild bees to diseases transferred from managed bees; and lastly, avoiding honey bee introduction to high-quality native bee habitat.

Actions Needed

Research Needs

Research need comment: More information is needed about the population status, population trend, existing threats, range limits, habitat, and ecology of this species. Surveys targeting this species are needed throughout its range to determine its persistence throughout its historic range.

Taxonomic Notes

(a. any taxonomic concerns about the validity of the species? b. any taxonomic revisions underway that would require a species reassessment.