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Guidelines on the Implementation of Nature-based Solutions (NbS) to Combat the Negative Impact of Climate Change on Forestry

Azerbaijan, Kazakhstan, Kyrgyzstan, Tajikistan, Türkiye, Turkmenistan and Uzbekistan









Başsüllü, Ç., Belen, I. & Kaptanoğlu, E. 2023. Guidelines on the Implementation of Nature-based Solutions (NbS) to Combat the Negative Impact of Climate Change on Forestry – Azerbaijan, Kazakhstan, Kyrgyzstan, Tajikistan, Türkiye, Turkmenistan and Uzbekistan. Ankara, FAO. 





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    For effective forest biodiversity monitoring in FAO Sub-regional Office for Central Asia (SEC) countries (Azerbaijan, Kazakhstan, Kyrgyzstan, Tajikistan, Turkmenistan, Uzbekistan and Türkiye), it is important to develop cost-effective and efficient monitoring methods. The main purpose of the guidelines on forest biodiversity monitoring methodologies is to support FAOSEC countries in their efforts to detect changes in forest biodiversity and to ensure that appropriate measures are taken for sustainable forest management. The monitoring process begins with the assessment of monitoring requirements and the establishment of specific goals for the subsequent development of the monitoring approach. Subsequently, essential factors such as indicators, methods and tools for monitoring, team composition, frequency of monitoring, and data management are identified to shape the monitoring initiative, integrating aspects related to the state, impact, and response. The monitoring process is then concluded through the practical implementation of the program via field investigations, analysis and interpretation of the gathered information, and dissemination of resultant reports to pertinent stakeholders. The guidelines for forest biodiversity monitoring methodologies employ this comprehensive five-step monitoring cycle as a foundation for crafting an efficient forest biodiversity monitoring program. The guidelines on forest biodiversity monitoring methodologies are designed to take into account the changes in pressure, state and response indicators especially for biodiversity monitoring with the contributions of subject-matter experts. This study uses the "Pressure-State-Response" framework that has been frequently used in different global, regional, and national monitoring programs. In the guidelines, monitoring targets for species, habitats, ecosystem services, and forestry practices are defined for each monitoring component by using relevant indicators. Using Türkiye’s national biodiversity database (Noah’s Ark Database) and its monitoring tables as samples, the indicators are tabulated with detailed information on the following topics: • Monitoring Level • Monitoring Period and Frequency • Monitoring Area • Monitoring Method • Monitoring Team/Expertise • Target / Success Criteria For effective implementation of the guidelines, a governance mechanism is also proposed for the participation of regional and national stakeholders. The guidelines serve as a comprehensive framework for monitoring forest biodiversity in FAOSEC countries with the aim of providing practical guidance and recommendations for establishing effective forest biodiversity monitoring systems in those countries. The guidelines also emphasize the importance of harmonization and standardization of biodiversity indicators and methods across countries, enhancing comparability and facilitating regional and global reporting.
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    The Aral Sea, formerly the fourth largest inland lake located in Central Asia, has reduced dramatically as it lost most of its volume due to the large-scale water withdrawal for the cultivation of irrigated crops starting from the 1960s. The desiccated seafloor has become a source of salt, sand, and dust transfer to the adjacent regions, negatively affecting human health and the environment by inhibiting the survival and growth of the vegetation. In response, to stabilize the saline sand blowing from the Aral seabed, multiple domestic and international efforts have been performed to establish vegetation cover with indigenous trees of Haloxylon species as well as other salt- and water-stress tolerant woody and herbaceous plants of the region. As part of the afforestation project supported by the Korea Forest Service (South Korea) in Kazakhstan, field studies examined the impacts of the afforestation on carbon stock and soil quality. The summarized findings are as follows: 1) growth of planted seedlings indicates the measurable sequestration of carbon, which ultimately help to estimate its contribution to climate change mitigation by calculating the atmospheric greenhouse gas reductions; 2) afforestation increased the soil organic matter content which is closely related to soil fertility; 3) afforestation improved soil chemical properties for plants and soil microbes; 4) soil amelioration effects by the afforestation were statistically similar to those by natural vegetation succession. However, the soil conditions in the natural succession area improved after almost 50 years versus about 15 years in the afforested area. This signifies the relative efficiency of afforestation activities and thus helps justify the investments made. Based on the studies, we recommend further research to raise the efficiency of afforestation in arid areas, thereby reinforcing ecosystem restoration and climate change mitigation. Keywords: Aral Sea; afforestation; desertification; climate change; restoration; soil amelioration; carbon stock ID: 3615605
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    This handbook has been prepared for the training workshop on innovative methods of amelioration and use of salt-affected soils, which takes place in Kharkiv, Ukraine, in September 2017. This workshop is conducted within the framework of the Implementation Plan of the Eurasian Soil Partnership, which is a sub-regional affiliation of the Global Soil Partnership. The main goals of the Global Soil Partnership (GSP) and Regional Soil Partnerships (RSPs) include the development of global and regional plans of action for the sustainable management and monitoring of limited soil resources as a key element, as well as the maintenance of food security and ecological services of soils. The RSPs rely on the existing regional networks that connect the national and local networks, partners, projects and measures to ensure that the interests of all member countries of the partnership are taken into account. A RSP should give directives for the development of regional targets, priorities and ìrequred mechanisms of implementation and also undertake regular assessments of progress in reaching goals and accomplishing the tasks. The Eurasian Region covers Eastern Europe, Central Asia and Caucasus and includes the following countries: Armenia, Azerbaijan, Belarus, Georgia, Kazakhstan, Kyrgyzstan, Moldova, Russia, Tajikistan, Turkey, Turkmenistan, Ukraine and Uzbekistan. The Eurasian Region is diverse in terms of climatic conditions, soils, flora and fauna, land use and human activities. Soil degradation is a serious problem within this region, with its most destructive consequences including salinization, erosion, loss of soil organic matter, nutrients and biodiversity as well as soil compaction. Soil salinization presents a serious challenge that requires co-ordination between countries that share common water and land resources. International co-operation is also needed to attract and manage investment into water and land resources. It should be emphasized that salinization is both the cause and the result of other agricultural problems. Combating salinization should, together with other measures for achieving the sustainable intensification of agriculture, be considered as a basis for food security.

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