Reptile
CEF
FCS

Species protection for the Sand lizard

Lacerta agilis

The sand lizard (Lacerta agilis) is strictly protected and listed in Annex IV of the FFH Directive. Because it colonises many human-influenced sites such as railway embankments, slopes and fallow land, it is one of the most common target species in the special species protection assessment. greeNature plans and delivers the required CEF and FCS measures from a single source, from mapping through reptile exclusion fencing and translocation to the creation and management of the replacement habitat in accordance with the BayKompV and § 44 BNatSchG.

Habitat of the Sand lizard: Semi-open, warm sites with loose, easily dug soil and a mosaic of basking spots and refuges, for example railway embankments, banks, dry grassland, sand and gravel pits, vineyards, field margins and woodland edges
Species profile

The Sand lizard at a glance

  • Habitat: Semi-open, warm sites with loose, easily dug soil and a mosaic of basking spots and refuges, for example railway embankments, banks, dry grassland, sand and gravel pits, vineyards, field margins and woodland edges
  • Threat status: Red List Bavaria: threatened (as at 2019), Germany: near threatened. Conservation status in the continental and alpine regions unfavourable to inadequate
  • Main causes: Loss and fragmentation of finely structured habitats, intensification of agricultural and forestry use
  • Protection status: Strictly protected under § 7 (2) BNatSchG, Annex IV of the FFH Directive, prohibitions under § 44 BNatSchG
  • Typical measure: Reptile exclusion fencing, capture and translocation to a prepared replacement habitat with basking spots, sand lenses for egg laying and frost-free winter refuges
Annex IV FFH Directive§ 44 BNatSchGstrictly protectedRed List Bavaria: endangered
Measures

Typical protective measures for the Sand lizard

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Reptile exclusion fencing and construction timing restrictions

Before construction begins, the project area is enclosed with temporary reptile exclusion fencing. This prevents animals from entering or returning to the construction area. Works are timed to match the sand lizard's period of activity, so that prohibited acts under § 44 BNatSchG are avoided.

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Capture and translocation (CEF)

Qualified personnel catch the sand lizards over several rounds during the active period and translocate them to a prepared replacement habitat. Capture continues until the project area is considered cleared and this is documented.

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Replacement habitat of stone, deadwood and sand

As an advance CEF measure, a habitat with a small-scale mosaic of structures is created. Stone piles and field-stone heaps serve as basking spots and frost-free winter refuges, deadwood piles as hiding places, and open sand patches as egg-laying sites. The habitat must be functional before translocation takes place.

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Habitat optimisation and habitat network connectivity (FCS)

Existing populations are enhanced through scrub clearance, sectional mowing and the creation of field margins and linear guide structures. Such FCS measures under § 45 (7) BNatSchG secure the favourable conservation status of the local population and connect partial habitats.

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Monitoring and management over the commitment period

Performance reviews document colonisation of the replacement habitat. The areas are kept open and managed for the duration of the commitment period set by the authority, so that the ecological function is permanently maintained. greeNature can take on the entire process on request.

Frequently asked questions

All about the Sand lizard

The sand lizard is strictly protected as a species listed in Annex IV of the FFH Directive. Because it colonises many human-influenced sites such as railway embankments, slopes, gravel pits and fallow land, it is frequently recorded in the vicinity of construction and infrastructure projects. Where this is the case, the access prohibitions under § 44 BNatSchG apply and avoidance, CEF or FCS measures are required.
CEF measures under § 44 (5) BNatSchG take effect before the project intervention. These include creating a replacement habitat and translocation, so that the ecological function of the breeding sites and resting places is maintained. FCS measures under § 45 (7) BNatSchG secure the favourable conservation status of the population and mainly come into play in connection with an exemption.
First, the replacement habitat is prepared with basking spots, sand patches, hiding structures and winter refuges, and must be functional before translocation. The animals are then caught over several rounds during their active period and moved. Reptile exclusion fencing prevents them from returning to the construction area.
The replacement areas must permanently fulfil their function. In addition to creation, this generally includes several years of establishment management, accompanying monitoring for performance review, and securing the site for the duration of the commitment period set by the authority. The specific duration follows from the species protection assessment and the permit.
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