Xyletinus longitarsis
Key Details
| Taxonomic Groups: | Invertebrate > insect - beetle (Coleoptera) > Wood boring beetle or ally |
| Red List Status: | Vulnerable (Not Relevant) [VU(nr)] |
| D5 Status: | Included in the baseline Red List Index for England (Wilkins, Wilson & Brown, 2022) |
| Section 41 Status: | (not listed) |
| Taxa Included Synonym: | (none) |
| UKSI Recommended Name: | Xyletinus longitarsis |
| UKSI Recommended Authority: | Jansson, 1942 |
| UKSI Recommended Qualifier: | (none specified) |
| Red List Citation: | Alexander, 2017 |
| Notes on taxonomy/listing: | (none) |
Criteria
| Question 1: | Does species need conservation or recovery in England? |
| Response: | Yes |
| Justification: | Vulnerable, based on a decline from 26 hectads pre-1990 to now 8 hectads at the time of red-listing; it is known from 8 locations (8 tetrads) and has an Area of Occupancy of 32 square km. The species formerly occurred across much of central, southern and eastern England, with old records as far west as South Devon, and north as the Derbyshire/Yorkshire border. Modern records are very few and the range appears to have contracted somewhat. The West Midlands (Herefordshire, Worcestershire and Shropshire) remain a stronghold, with other modern records coming from East Sussex, Buckinghamshire and Lincolnshire. |
| Question 2: | Does recovery/ conservation depend on species-specific actions? |
| Response: | Yes |
| Justification: | Minimum intervention management will not provide conditions suitable for the development of successive generations of veteran trees, and well-planned tree planting remains the exception rather than the rule. |
| Question 3: | At a landscape scale, would the species benefit from untargeted habitat management to increase habitat mosaics, structural diversity, or particular successional stages? |
| Response: | No |
| Justification: | Site issue. |
Species Assessment
| Current step on the Species Recovery Curve (SRC): | 4. Autecology and pressures understood |
| Recovery potential/expectation: | Low - Relict or natural rarity |
| National Monitoring Resource: | Opportunistic - insufficient |
| Species Comments: | Found in very brittle and powdery white-rotten deadwood of oak, usually large old hulks in open parkland. |
Key Actions
Key Action 1
Proposed Action: Research to characterise the ecology of the beetle, in terms of the species, size, condition, situation and management of host trees
Action targets: 4. Autecology and pressures understood
Action type: Scientific research
Duration: 3-5 years
Scale of Implementation: ≤ 5 sites
High priority sites: Moccas Park (Herefordshire), Grimsthorpe Park (Lincolnshire), Eridge Park (Kent)
Comments: Enforcing better record keeping upon detection will go a long way to understanding the issues here.
Key Action 2
Proposed Action: At sites where the species occurs document age structure for potential host veteran trees and future veterans, to determine whether there is an adequate rate of replacement. Also assess requirements for management of the veteran tree stock to reduce the risk of wind throw, by undertaking tree surgery to reduce the crown of excessive bough weighting.
Action targets: 4. Autecology and pressures understood
Action type: Targeted monitoring
Duration: 2 years
Scale of Implementation: ≤ 10 sites
High priority sites: To be determined based on the results of Action 1
Comments: The conservation of saproxylic invertebrates relies on continuity in the availability of dead wood resources, which can take centuries to develop, so there is a need to identify if there is insufficient recruitment of younger trees at sites where the species occurs. In general the loss of veteran trees at protected sites and in the wider landscape exceeds rates of recruitment.
Key Action 3
Proposed Action: At sites where the species occurs, plant oak trees or promote natural regeneration where there has been insufficient recruitment of younger trees.
Action targets: 7. Best approach adopted at appropriate scales
Action type: Habitat management
Duration: >10 years
Scale of Implementation: ≤ 5 sites
High priority sites: Prioritisation is subject to assessment of tree age structure on all occupied sites
Comments: Either planting or natural regeneration should not be allowed to create crown competition or cast shade on existing veteran trees. If there is no space within a site to achieve this, then planting on adjacent land may also be a priority.
Acknowledgment:
Data used on this website are adapted from Threatened species recovery actions 2025 baseline (JP065): Technical report and spreadsheet user guide (Natural England, 2025). Available here.