Figure 1.

Figure 2.

Summary of the relationships between the groups of ecosystem services identified in the publications analysed
| Ecosystem services | Cultural | Provisioning | Regulating | |||
|---|---|---|---|---|---|---|
| trade off | synergy | trade off | synergy | trade off | synergy | |
| Cultural | 1 | 1 | 1 | 13 | ||
| Provisioning | 11 | 10 | 22 | 22 | 79 | 42 |
| Regulating | 1 | 6 | 27 | 2 | 35 | 18 |
| Sum | 12 | 17 | 49 | 25 | 114 | 73 |
Summary of research between the groups of ecosystem services identified in the publications analysed
| Ecosystem services | Cultural | Provisioning | Regulating |
|---|---|---|---|
| Cultural | 1 | 2 | 13 |
| Provisioning | 12 | 27 | 72 |
| Regulating | 7 | 24 | 45 |
| Sum | 20 | 53 | 130 |
Summary of the relationship between carbon storage and timber production in the publications analysed
| ES „A” | ES „B” | Study area | Age of stand | Species composition | Time scale | Spatial scale | Relationship between ecosystem services | Source | |
|---|---|---|---|---|---|---|---|---|---|
| trade off | synergy | ||||||||
| 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 |
| Carbon storage | fuelwood production | Finland | n/d | Picea A. Dietr. | 2012–2100 | 1425 km2 | x | Akujärvi et al. 2021. | |
| Finland, Germany, Norway, Slovenia, Spain | n/d | n/d | n/d | survey | x | x | Peters et al. 2015 | ||
| Carbon storage | timber production | Sweden | 70 | Picea A. Dietr. | 2100 | virtual forest stand | x | Zanchi, Brady 2019 | |
| Sweden | n/d | Pinus sylvestris, Picea abies, Betula spp. | 2106 | NFI plots | x | Blatertt et al. 2020 | |||
| Germany | n/d | Picea A. Dietr., Pine, Beech, Quercus L., Betula L., Pseudotsuga menziesii (Mirb.) Franco | 14 simulations of future climate (2011–2045) plus five simulations of historical climate (1971–2005) | 10.37 million hectares | x | Gutsch et al. 2018 | |||
| Central Europe | n/d | Fagus sylvatica L., Picea A. Dietr. | 120 years | Stands | x | Duncker et al. 2012 | |||
| USA | different | Acer saccharum, Fagus grandifolia, Tsuga canadensis, Betula alleghaniensis | 100 years | 533 randomly located site | x | Schwenk et al. 2012 | |||
| Austria | n/d | Picea abies, Pinus sylvestris | 100 | Private forests, 248.7 ha | x | Seidl et al. 2007 | |||
| Europe (exc. North Europe) | n/d | n/d | 2010–2030 | n/d | x | Verkerk et al. 2014 | |||
| Germany | n/d | Pinus L., Picea A. Dietr. | 100 years | 2 study areas: 78,000ha, 53,000 ha | x | Schwaiger et al.. 2019. | |||
| Lithuania, Ireland, Netherlands, Germany, Slovakia, Italy, Portugal, Sweden, Portugal, Turkey | n/d | different stands | 2050 or 2100 | 15–3734 ha | x | Biber et al. 2020 | |||
| Spain | n/d | Pinus L. | 2016–2100 climate model | 40,000 | x | Morán-OrdóĖez et al. 2020 | |||
| Carbon storage | timber production | Sweden | n/d | Pinus sylvestris, Picea abies, Betula spp. | n/d | NFI plots | x | Blatertt et al. 2020 | |
| Finland | n/d | different stands | n/d | 48770 ha | x | Eyvindson et al. 2018 | |||
| Switzerland | Pole or Mature stands | Fagus sylvatica L., Picea A. Dietr. | 2016–2101 | forest subcompartment | x | Mey et al. 2022 | |||
| Italy | 50 | conifer stand | 210 years | subcompartment | x | Sacchelli 2018 | |||
| Fuelwood production | carbon sequestration in soil | Sweden | different | Picea A. Dietr., Pinus L., Betula L., Fagus sylvatica L. | 400 000 km2 | x | Gamfeldt et al. 2013 | ||
| Carbon storage | timber production | USA | Pinus L. | x | Stokely’ego et al. 2021 | ||||
Summary of the relationship between biodiversity and timber production in the publications analysed
| ES „A” | ES „B” | Study area | Age of stand | Species composition | Time scale | Spatial scale | Relationship between ecosystem services | Source | |
|---|---|---|---|---|---|---|---|---|---|
| trade off | synergy | ||||||||
| 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 |
| Timber production | biodiversity | Czech Republic (simulation) | 30 years | Quercus L., beech | 60 years | 332 ha | x | Sedmák et al. 2020 | |
| Europe (Spain, France, Belgium, Germany, Sweden, Finland) | different | different | n/d | NFI plots – extrapolating | x | van der Plas et al. 2017 | |||
| Central Europe | 0 | beech, Picea A. Dietr. | 120 years | stands | x | Duncker et al. 2012 | |||
| USA | different | Acer saccharum, Fagus grandifolia | 100 years | 533 randomly located site | x | x | Schwenk et al. 2012 | ||
| Tsuga canadensis, Betula alleghaniensis | |||||||||
| Norway | n/d | coniferous and boreal deciduous forest | n/d | landscape level | x | Schroter et al., 2014 | |||
| Austria | n/d | Picea abies, Pinus sylvestris | 100 | private forests, 248.7 ha | x | x | Seidl et al. 2007 | ||
| Europe | n/d | n/d | 2010–2030 | n/d | x | Verkerk et al. 2014 | |||
| Europe (20 case studies located in Bulgaria, France, Germany, Ireland, Italy, Lithuania, Netherlands, Portugal, Slovakia, Sweden) | n/d | depends on country | 30 years | 600–1,000,000 ha | x | x | Biber et al. 2015 | ||
| Lithuania, Ireland, Netherlands, Germany, Slovakia, Italy, Portugal | n/d | different stands | 2050 or 2100 | 15–3734 ha | Biber et al. 2020 | ||||
| Sweden, Portugal | n/d | x | Biber et al. 2020 | ||||||
| Turkey | n/d | x | Biber et al. 2020 | ||||||
| Timber production | biodiversity | Spain | n/d | Pinus nigra Arn. subsp. Salzman-nii, Pinus sylvestris L. | 2001–2100 | ca. 40000 ha | x | Morán-Ordóñez et al. 2020 | |
| Switzerland | n/d | Different stands | 2013–2106 | NFI plots | x | Blatertt et al. 2020 | |||
| Finland | n/d | Pinus L., Picea A. Dietr., Betula L. | 50 years | 68700 ha | x | Triviño et al. 2016 | |||
| Finland | n/d | different stands | n/d | 48,770 ha | x | Eyvindson et al. 2018 | |||
| Sweden | n/d | Pinus L. | n/d | 117 field plots | x | Strengbom 2017 | |||
| Switzerland | mature stand | Fagus sylvatica L., Picea A. Dietr. | 2016–2101 | Forest subcompartment | x | Mey et al. 2022 | |||
| Biodiversity | timber production (expected) | USA | Pinus L. | x | Stokely’ego et al. 2021 | ||||
| Fuelwood production | biodiversity | Sweden | n/d | Pinus sylvestris, Picea abies, Betula spp. | 2106 | NFI plots | x | Blatertt et al. 2020 | |
| Finland, Slovenia | n/d | n/d | n/d | Survey | x | Peters et al. 2015 | |||
| Germany, Norway, Spain | n/d | n/d | n/d | Survey | x | x | Peters et al. 2015 | ||
| Fuelwood production | dead wood | Sweden | different | Picea A. Dietr., Pinus L., Betula L., Fagus sylvatica L. | 400 000 km2 | x | Gamfeldt et al. 2013 | ||
Summary of the relationship between regulating and cultural ecosystem services in the publications analysed
| ES „A” | ES „B” | Study area | Age of stand | Species composition | Time scale | Spatial scale | Relationship between ecosystem services | Source | |
|---|---|---|---|---|---|---|---|---|---|
| trade off | synergy | ||||||||
| Spiritual and religious values | biodiversity | Europe | n/d | n/d | n/d | n/d | x | Motiejūnaitė et al. 2019 | |
| Socioeconomic functions | biodiversity | Europe (20 case studies located in Bulgaria, France, Germany, Ireland, Italy, Lithuania, the Netherlands, Portugal, Slovakiaand Sweden) | n/d | depends on country | 30 years | 600–1,000,000 ha | weak (region-specific) | weak (region-specific) | Biber et al. 2015 |
| Culturally interesting plants | temperature regulation, carbon storage, nitrification potential | Germany | 53 forest type | dominating forest types in Central Europe | n/d | 150 forest plots of 100 m × 100 m / NFI to predict | x | Simons et al. 2021 | |
| Recreation | carbon sequestration | Italy (mountain forests) | n/d | Picea abies, Larix decidua Mill, Pinus sylvestris L., Fagus sylvatica L. | n/d | n/d | x | Häyhä et al. 2015 | |
| Biodiversity | recreation | Europe (exc. North Europe) | n/d | n/d | 2010–2030 | n/d | x | Verkerk et al. 2014 | |
| Regulating ES | recreation | Europe (exc. North Europe) | n/d | n/d | 2010–2030 | n/d | x | Verkerk et al. 2014 | |
| Recreation/aestheti values | carbon storage/biodiversity | Denmark | n/d | n/d | n/d | n/d | x | Sántha, Bentsen, 2020 | |
Summary of the relationship between non-timber products and timber production in the publications analysed
| ES „A: | ES „B” | Study area | Age of stand | Species composition | Time scale | Spatial scale | Relationship between ecosystem services | Source | |
|---|---|---|---|---|---|---|---|---|---|
| trade off | synergy | ||||||||
| Timber production | Vaccinium vitis-idaea L. | Finland | different | Pinus L., Picea A. Dietr. | 2001–2012 | whole country | x | x | Turtiainen et al. 2013 |
| Biomass (Pinus L.) | Vaccinium myrtillus L. | Sweden | different | Picea A. Dietr., Pinus L., Betula L., Fagus sylvatica L. | 400,000 km2 | x | Gamfeldt et al. 2013 | ||
| Amount of game meat (humting) | Vaccinium myrtillus L. | x | |||||||
| Biomass | Vaccinium myrtillus L. | x | |||||||
| Potential amount of game meat | biomass | x | |||||||
| Timber production | beekeeping | Spain | n/d | mediterranean shrubs and trees species andalmonds | n/d | 1 km × 1 km | bundle | García-Nieto et al. 2013 | |
| Production of feed for wild ungulates | timber production | USA | Pinus L. | x | Stokely’ego et al. 2021 | ||||
| Biodiversity and non-wood production | timber production | Finland | n/d | different stands | n/d | 48,770 ha | Eyvindsona et al. 2018 | ||
| Timber production | Vaccinium myrtillus L. | x | |||||||
| Timber production | milk production | Germany/Netherlands | 241/219 km2 | x | Hölting et al. 2020 | ||||
| Timber production | Resin | x | |||||||
| Timber production | Vaccinium myrtillus L., Vaccinium vitis-idaea L. | x | Kurttila et al. 2018 | ||||||
| Thinning | lichens, Vaccinium myrtillus L. | Sweden | n/d | Pinus L. | n/d | 117 field plots | x | Strengbom 2017 | |
| Timber production | Vaccinium vitis-idaea L. | Finland | 18 forest stands (app. 3 ha each) | x | Granata et al. 2018 | ||||
| Timber production | Vaccinium myrtillus L. | x | |||||||