Wetland biodiversity protection in Kamanos Strict Nature Reserve, Lithuania

Year of issue
2025
Summary

Kamanos Strict Nature Reserve is the largest raised bog (2,434 ha) in the northern Lithuania region (a farming region) with ridge–pool complexes, numerous small lakes (over 120 pools each less than 2 ha in area) and surrounding wet forests. In 65 ha of selected bogs and meadows restored with 18.5 km of ditches dammed Kamanos Strict Nature Reserve. The measures were implemented in the frame of a larger UNDP-GEF project in 2004–2010. Further hydrological restoration was carried out under the LIFE WETLIFE2 project (2014–2018), blocking 37 km of drainage ditches and improving water conditions over 670 ha. These actions supported bog habitats and species like the Aquatic Warbler. The site is now part of the eLTER network, with ongoing ecological monitoring and climate data collection.

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Location
56.280151, 22.662279
Project
NWRM
National ID
Lithuania_03
Sector
Hydromorphology
Installation Date
2010
Implementation status
Ongoing

Overview

Location of the project
The Kamanos Strict Nature Reserve lies in the Akmenė District of Šiauliai County, northwestern Lithuania (approx. 56°16.3′ N, 22°47.3′ E), situated just a few kilometres west of Ašvėnai village. While surrounded by cultivated lands and forest, it is accessible only via local roads leading to the visitor centre in Akmenė II.
Country
Lithuania
NUTS2 Code
Latvija
Sponge measures implemented in the case study
Wetland restoration and management
Removal of dams and other longitudinal barriers
Forest riparian buffers
Objectives
Objective 1: Demonstrate improved in-situ wetland management at five globally significant wetland sites in Lithuania including Kamanos, addressing degradation threats such as drainage, overgrowth of meadows, and unsustainable land use.
Objective 2: Institutionalize best practices through a multisectoral mechanism (the "Multisectoral Wetlands Working Group") to replicate lessons learned across other wetland sites in Lithuania and integrate conservation principles into relevant sectoral policies (e.g., agriculture, forestry, tourism) for sustainable wetland management.
Involved partners
Authority type Authority name Authority role Comments Authority responsibility
NGO Nature Heritage Fund Initiation of the measure — —
Nature park Kamanos Srict Nature Reserve Implementation Strict Nature Reserve is an institution for the protection of Kamanos bog and neighbouring areas of conservative importance —
National water authority Ministry of Environment of Lithuania Initiation of the measure — Supporting

Site Information

Climate Zone
Warm temperate moist
Precipitation
585.00 mm
Temperature (°C)
6.74 °C
Elevation range
111
Groundwater level
In central (pristine) bog : 4.5 cm to 30 cm below the surface. In actively drained zones, fluctuations ranged from 8 cm to 51 cm.
Vegetation class
Sphagnum mosses
WFD Ecological status
Poor
WFD Chemical status
Failing to achieve good
Water quality status
This is water bosies status around the reserve, there is no info about the Kamanos reserve's waterbodies themselves.

Design and Implementation

Project scale
Micro
Project scale specifications
The restoration and conservation actions in the Kamanos Strict Nature Reserve focus on a clearly defined protected area (2,434 ha), involving localised hydrological interventions such as ditch blocking, habitat restoration, and biodiversity monitoring. All measures are site-specific and confined to the boundaries of the reserve, making this a typical micro-scale project.
Project area
1283
Area subject to Land use change or Management/Practice change (ha)
1218.00 ha
Size
18.50
Size unit
km

Financing

Total cost information
€1,520,701 for LIFE WETLIFE 2 (LIFE13 NAT/LT/000084) (2014-2018) Restoration of 670 ha of bog habitats; 37 km of ditches blocked; 300 dams built; monitoring and public awareness activities.

US $13,865,400 for UNDP-GEF (2004-2010) “Conservation of Inland Wetland Biodiversity in Lithuania”, Restoration of 65 ha of bogs and meadows; 18.5 km of drainage ditches blocked; development of reserve management plans.
Compensations
No

Policy and Governance

Policy description
Extensive drainage of the bog for agriculture and forestry, loss of biodiversity, change f habitat
Land ownership
The core area of the Kamanos Strict Nature Reserve is entirely state-owned, while its buffer zone includes both state-owned and privately owned parcels.
Policy targets
Runoff control
Increase Water Storage
Improved Biodiversity
Oher Societal Benefits
Part of a wider plan
Yes
Wider plan
Name Comments
Conservation of Inland Wetland Biodiversity in Lithuania’ National project
Public consultation
Yes
Consultation activities
Activity stage Activity type Comments
Design phase WETLIFE 2 project seminars 14 seminars and volunteer-based actions aimed at: Raising awareness of the importance of peatland ecosystems and the problems caused by drainage. Engaging local stakeholders directly in conservation activities.
Has contractual arrangements
No

Impacts and Monitoring

Monitoring System

Monitoring parameters
Groundwater/hydrological levels (post-restoration). As part of the WETLIFE 2 project, the reserve organized 14 seminars and volunteer-based maintenance or monitoring actions, contributing to active stakeholder engagement and localized stewardship.

Maintenance

Maintenance requirements
Maintenance is carried out by the Kamanos Reserve Directorate and includes regular inspection of water level control structures (e.g., dams) and ongoing hydrological monitoring to ensure restoration effectiveness.

Impact Assessment Methodology

Performance impact assessment method
Catchment outlet
Performance impact estimation information
Change of water table level in the bog

Socio-economic Impacts

Direct benefits
For all Lithuania's peatlands combined : Rewetting peatlands → ~€170M annual savings; drainage → ~€309M annual losses (6.6% of GDP)

Biophysical impacts: Hydrology

Information on increased groundwater level
Groundwater level rise: After damming drainage ditches (1–1.2 m deep), the groundwater table increased by 9.8 to 12.2 cm, with the effect detectable up to 980 m from the ditch. In extensively drained areas, water levels matched undrained (control) plots within 4 years; in more intensively drained zones, recovery to control levels is projected within 12 years
Information on Restoring hydraulic connection
Restored hydrological conditions (WETLIFE 2 project): 37 km of ditches were blocked, leading to restoration of 40 ha of bog lag zones, benefiting 670 ha of mire habitat

Biophysical impacts: Biodiversity

Improved biodiversity
Yes
Information on improved biodiversity
The sphagnum community is beginning to recover in places where it had been negatively impacted before. Mire habitats supporting species such as Eurasian golden plover (Pluvialis apricaria), wood sandpiper (Tringa glareola), black grouse (Tetrao tetrix), and woodpeckers (Dendrocopos leucotos, D. medius) are expected to benefit.

Biophysical impacts: Water & Soil Quality

Water quality overall improvements
N/A info
Soil quality overall improvements
N/A info

Biophysical impacts: Others

Information on ecosystem impact climate regulation
Improved storage of GHG in peatland.

Lessons Learned

Key lessons
• Mid-Term Evaluations should have stringent timing requirements.
All GEF projects should mandate that mid-term evaluations occur at a specific date in the project cycle. This should include recruitment of international expertise at least six months prior to the planned MTE date.

• Relatively small management teams can produce big results.
Successful implementation project with a relatively small full-time technical and management staff is an indication of the project benefiting from a contemporary, strategic approach; authentic stakeholders buy-in; an implementation environment with relatively good capacity; and capable, motivated leadership. The team also showed a willingness to identify and recruit necessary technical assistance.

• Valuable indicators measure impact and quality, not just production.
Projects should benefit from carefully designed indicators that provide an accurate measurement of the delivery of outputs but, more importantly, measure the impact delivery has on objective conservation values.

• Projects may benefit from continuity between PDF-B and implementation teams.
This project benefited from having the same strong team working from the beginning of the project through to implementation. Capacity, team building, partnerships, and project “historical perspective” were all enhanced with this consistency.

Barriers
Barrier type Barrier role Comments
Lacking financing sources Secondary barrier No financing for further implementation (building more dams)
Drivers
Driver type Comments
Other The goal should have been reached in the most cost effective measure. Small dams made of plastic were the best option. Construction costs were minimised, since no outsourcing was needed and SNR staff was able to build it.
Success factors
Success factor type Success factor role Comments
Attitude of decision makers Main factor —
Financing possibilities Main factor EU funding was a big help.
Available support tools Main factor During the MOMENT project, it was possible to gain knowledge about the similar retention ponds in Sweden. As this was one of the first (pilot) retention ponds in Lithuania, therefore, knowhow was very usefull.
Legal obligations Main factor —
Transferability
The measure is highly transferable to other degraded peatlands with similar ecological conditions. Its success depends on prior drainage intensity, local hydrology, and land ownership. Careful assessment of groundwater response, long-term maintenance needs, and stakeholder support is essential. Monitoring should go beyond water levels to include biodiversity and climate impacts.

Sources