How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment?

Biber, Peter; Borges, José G.; Moshammer, Ralf; Barreiro, Susana; Botequim, Brigite; Brodrechtová, Yvonne; Brukas, Vilis; Chirici, Gherardo; Cordero-Debets, Rebeca; Corrigan, Edwin; Eriksson, Ljusk Ola; Favero, Matteo; Galev, Emil; Garcia-Gonzalo, Jordi; Hengeveld, Geerten; Kavaliauskas, Marius; Marchetti, Marco; Marques, Susete; Mozgeris, Gintautas; Navrátil, Rudolf; Nieuwenhuis, Maarten; Orazio, Christophe; Paligorov, Ivan; Pettenella, Davide; Sedmák, Róbert; Smreček, Róbert; Stanislovaitis, Andrius; Tomé, Margarida; Trubins, Renats; Tuček, Ján; Vizzarri, Matteo; Wallin, Ida; Pretzsch, Hans; Sallnäs, Ola

doi:10.3390/f6051666

Open AccessArticle

How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment?

by

Peter Biber

^1,*

,

José G. Borges

^2,†

,

Ralf Moshammer

¹,

Susana Barreiro

²,

Brigite Botequim

²

,

Yvonne Brodrechtová

³,

Vilis Brukas

⁴,

Gherardo Chirici

⁵

,

Rebeca Cordero-Debets

⁶,

Edwin Corrigan

⁷,

Ljusk Ola Eriksson

⁸,

Matteo Favero

⁹,

Emil Galev

¹⁰,

Jordi Garcia-Gonzalo

²,

Geerten Hengeveld

¹¹,

Marius Kavaliauskas

¹²,

Marco Marchetti

¹³,

Susete Marques

²

,

Gintautas Mozgeris

¹²,

Rudolf Navrátil

^14,15

,

Maarten Nieuwenhuis

⁷

,

Christophe Orazio

⁶

,

Ivan Paligorov

¹⁰,

Davide Pettenella

⁹

,

Róbert Sedmák

^14,15

,

Róbert Smreček

¹⁴,

Andrius Stanislovaitis

¹²,

Margarida Tomé

²

,

Renats Trubins

⁴

,

Ján Tuček

¹⁴,

Matteo Vizzarri

¹³,

Ida Wallin

⁴,

Hans Pretzsch

¹

and

Ola Sallnäs

^4,† Show full author list Hide full author list

¹

Chair of Forest Yield Science, Technische Universität München, Hans-Carl-von-Carlowitz-Platz 2, Freising 85354, Germany

²

Forest Research Center, School of Agriculture, University of Lisbon, Tapada da Ajuda, Lisbon 1349-017, Portugal

³

Department of Economics and Management of Forestry, Faculty of Forestry, Technical University in Zvolen, T.G. Masaryka 24 Zvolen 960 53, Slovakia

⁴

Southern Swedish Forest Research Centre, Swedish University of Agricultural Sciences, Box 49, Alnarp 23053, Sweden

⁵

Department of Agricultural, Food and Forestry Systems, Università degli Studi di Firenze, Via San Bonaventura, 13, Firenze 50145, Italy

⁶

Atlantic European Regional Office of the European Forest Institute—EFIATLANTIC, Cestas cedex 33612, France

⁷

UCD Forestry, School of Agriculture & Food Science, UCD, Belfield, Dublin 4, Ireland

⁸

Department of Forest Resource Management, Swedish University of Agricultural Sciences, Umeå 901 83, Sweden

⁹

Dipartimento Territorio e Sistemi Agro-Forestali, Università di Padova, Agripolis, v.le dell'Università 16, Legnaro I-35020, Italy

¹⁰

University of Forestry, 10 Kliment Ohridski blvd., Sofia 1756, Bulgaria

¹¹

Forest and Nature Conservation Policy Group, Wageningen University, and Alterra—Vegetation, Forest and Landscape Ecology, Drovendaalsesteeg 3, Wageningen 6708PB, The Netherlands

¹²

Aleksandras Stulginskis University, Studentu 11, Akademija, Kaunas Distr. LT-53361, Lithuania

¹³

Dipartimento di Bioscienze e Territorio (DiBT), Università degli Studi del Molise, Contrada Fonte Lappone, Pesche 86090, Isernia, Italy

¹⁴

Department of Forest Management and Geodesy, Technical University in Zvolen, T.G. Masaryka 24 Zvolen 960 53, Slovakia

¹⁵

Faculty of Forestry and Wood Sciences, Czech University of Life Sciences Prague, Kamýcká 1176, 165 21 Prague 6—Suchdol, Czech Republic

Show full affiliation list

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^*

Author to whom correspondence should be addressed.

^†

These authors contributed equally to this work.

Forests 2015, 6(5), 1666-1695; https://doi.org/10.3390/f6051666

Submission received: 8 January 2015 / Revised: 17 April 2015 / Accepted: 21 April 2015 / Published: 13 May 2015

(This article belongs to the Special Issue The 24th IUFRO World Congress: Session 118 Providing Ecosystem Services under Climate Change: Community of Practice of Forest Decision Support Systems)

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Abstract

:

While sustainable forestry in Europe is characterized by the provision of a multitude of forest ecosystem services, there exists no comprehensive study that scrutinizes their sensitivity to forest management on a pan-European scale, so far. We compile scenario runs from regionally tailored forest growth models and Decision Support Systems (DSS) from 20 case studies throughout Europe and analyze whether the ecosystem service provision depends on management intensity and other co-variables, comprising regional affiliation, social environment, and tree species composition. The simulation runs provide information about the case-specifically most important ecosystem services in terms of appropriate indicators. We found a strong positive correlation between management intensity and wood production, but only weak correlation with protective and socioeconomic forest functions. Interestingly, depending on the forest region, we found that biodiversity can react in both ways, positively and negatively, to increased management intensity. Thus, it may be in tradeoff or in synergy with wood production and forest resource maintenance. The covariables species composition and social environment are of punctual interest only, while the affiliation to a certain region often makes an important difference in terms of an ecosystem service’s treatment sensitivity.

Keywords:

ecosystem services; scenario analysis; European forests

1. Introduction

For a long time, the general consensus in Europe was that forest ecosystem services beyond wood production would be sufficiently provided as mere side effects of the latter, a concept that was well outlined by the term wake theory [1]. In the present, however, they have emancipated, and their relative importance is subject to partly heated societal debates from the local to the pan-European scale. The emergence of the Helsinki Criteria for sustainable forest management [2,3] marks an important milestone in this process. Consequently, important questions are how far ecosystem service provision is sensitive to forest management, and to what extent different ecosystem services are conflicting or compatible.

Although local case studies have contributed to these questions, there is no synthesis available yet. Furthermore, while the vulnerability of ecosystem service provision due to climate change has been investigated on a European level [4,5,6]), silvicultural steering possibilities were not fathomed on such a large scale. Existing studies were limited to single ecosystem services only and did not follow a regionally tailored bottom-up approach (cf. [7,8]). This is remarkable, as meanwhile most of Europe’s forests are covered by management-oriented forest growth simulation models—partly even embedded in decision support systems (DSS)—that enable such a scrutiny.

The European Union project INTEGRAL [9], a collaboration of 21 research groups from 13 European countries, asks how different policies influence forest managers’ behavior in terms of silvicultural treatment and how this would influence the provision of ecosystem services in a time frame of about 30 years (assuming constant climate conditions during that time span). To this end, mostly two representative case study areas have been selected per country, where, in a so far unprecedented collaboration of social and natural scientists, sets of policy scenarios have been developed and translated into forest owner-specific management scenarios that were able to drive up-to-date forest growth simulators and DSS containing such simulators, respectively. An important part of the research was to identify each region’s most relevant forest ecosystem services and to design and/or implement appropriate quantitative indicators for benchmarking ecosystem service provision in the forest growth scenarios. As a result there exists for each case study a set of policy scenarios with interlinked forest management scenarios and corresponding simulation results that show timelines of ecosystem service provision.

While the broad scope of the project results, from policy to ecosystem services, will be reported in other publications, it seems worthwhile to have a closer look at the silvicultural scenarios—without considering which policies triggered them—and the resulting ecosystem service provision expected from forest simulations. While forest ownership structure is crucial for management decisions in a given policy framework, it is not considered an influence variable in the study on hand. We focus on the management and its influence on ecosystem services; but we do not ask who decided on a given management option and why. The character of this work is explorative as there is no pre-defined set of hypotheses or theoretical framework we could test. Rather, we would like to contribute to the formation of hypotheses as a background for further studies.

Thus, this study uses the existing results for asking:

-: What kind of ecosystem services are important throughout Europe and which are relevant on a regional level only?
-: Can ecosystem services be meaningfully controlled by forest management, and is this different across Europe?
-: Which ecosystem services are conflicting, neutral, or positively correlated?

Based on this synthesis we discuss the steering potential for Europe’s forests.

2. Material and Methods

2.1. Case Study Areas

The 20 case study areas underlying this study were selected in the INTEGRAL project’s framework in order to represent typical forest landscapes for each country, the term “typical” concerning tree species composition, site conditions, and management paradigms, but also socioeconomic frame conditions for forestry. In the project, they were assigned to six European forest regions, namely Eastern Europe, Central Western Europe, North Western Europe, Southern Europe, Western Europe, and Northern Europe, each of these regions having a distinctive ecological, socioeconomic, and political context [10] (Table 1, Figure 1).

Figure 1. Geographic locations of all INTEGRAL case study areas. See Table 1 for the full case study names.

Table 1. The INTEGRAL case studies used in this work, selected group affiliations, and key properties. The table is sorted by country and case study name (alphabetical order).

**Table 1.** The INTEGRAL case studies used in this work, selected group affiliations, and key properties. The table is sorted by country and case study name (alphabetical order).
Country	Case Study Area (CSA)	CSA Acronym	Forest Region	Species Composition	Social Environment	Latitude	Longitude	Total Area (ha)	Forest Area (ha)
Bulgaria	Teteven	TET	Eastern Europe	broadleaf	rural	42°55′ N	24°25′ E	27,400	10,100
Bulgaria	Yundola	YUN	Eastern Europe	conifer	rural	42°01′ N	23°06′ E	10,100	3700
France	Pontenx	PON	Central Western Europe	conifer	rural	44°12′ N	00°55′ W	101,000	66,700
Germany	Munich South	MUN	Central Western Europe	mixed	city near	48°08′ N	11°34′ E	60,000	43,200
Germany	Upper Palatinate	UPP	Central Western Europe	mixed	rural	49°01′ N	12°05′ E	300,000	159,000
Ireland	Newmarket	NEW	North Western Europe	conifer	rural	52°12′ N	09°00′ W	75,100	13,500
Ireland	Western Peatlands	WES	North Western Europe	conifer	rural	53°48′ N	09°31′ W	1,000,000	116,000
Italy	Asiago	ASI	Southern Europe	mixed	rural	45°52′ N	11°31′ E	46,700	30,900
Italy	Etna	ETN	Southern Europe	broadleaf	city near	37°45′ N	14°59′ E	25,300	7000
Italy	Molise	MOL	Southern Europe	mixed	rural	41°40′ N	14°15′ E	600	600
Lithuania	Kazlu Ruda	KAZ	Eastern Europe	conifer	rural	54°45′ N	23°30′ E	66,000	36,800
Lithuania	Zemaitija	ZEM	Eastern Europe	mixed	rural	55°59' N	22°15′ E	38,000	11,700
Netherlands	South East Veluwe	SEV	Western Europe	conifer	city near	52°13′ N	5°58′ E	8000	6000
Portugal	Chamusca	CHA	Southern Europe	broadleaf	rural	39°21′ N	8°29′ W	74,600	53,000
Portugal	Leiria	LEI	Southern Europe	conifer	rural	39°45′ N	8°48′ W	75,200	44,400
Portugal	Sousa	SOU	Southern Europe	mixed	rural	41°04′ N	8°15′ W	48,900	22,000
Slovakia	Kysuce	KYS	Eastern Europe	mixed	city near	49°22′ N	18°44′ E	152,000	121,600
Slovakia	Podpol’anie	POD	Eastern Europe	broadleaf	rural	48°34′ N	19°30′ E	20,000	10,200
Sweden	Helgea	HEL	Northern Europe	conifer	rural	56°25′ N	15°42′ E	120,000	96,000
Sweden	Vilhelmina	VIL	Northern Europe	conifer	rural	64°55′ N	16°35′ E	850,000	530,000

The case study areas are located in 10 European countries; these are (in alphabetical order) Bulgaria (2 case studies), France (1 case study), Germany (2), Ireland (2), Italy (3), Lithuania (2), the Netherlands (1), Portugal (3), Slovakia (2), and Sweden (2). As shown in Table 1, they cover a range of northern latitudes between 38° (Etna, Italia) and 65° (Vilhelmina, Sweden) and longitudes between 9° W (Leiria, Portugal) and 24° E (Teteven, Bulgaria). The average total size and the forest area size of such a case study area amounts to about 160,000 ha and 70,000 ha, respectively. However, there is a large variance in the area sizes; the smallest case study area (Molise, Italy) is a forest biosphere reserve with slightly more than 600 ha only, while the largest (Western Peatlands, Ireland) covers an area of about 1,000,000 ha. For the purposes of this study, the case study areas (CSAs) were grouped into three tree species composition classes (Table 1). “Broadleaf” (4 CSAs) and “conifer” (9 CSAs) mean that the concerned area is dominated by deciduous species stands and conifer stands, respectively. The category “mixed” (7 CSAs) indicates a more or less balanced mixture of conifer and deciduous species in a given case study area at the stand level or on larger scales. Another simple grouping we called “social environment” considered if a case study area is located in an urban catchment (group name “city near”, 4 CSAs) or in a more rural landscape (“rural”, 16 CSAs, see Table 1).

2.2. Investigated Ecosystem Services

In total, 23 different ecosystem services have been investigated in the case study areas (Table 2). Some of them, e.g., biodiversity or harvested wood, were reported as important in each case study area; others, like the area available for reindeer herding, pine cone production or sub-specifications of harvested wood (e.g., eucalypt pulpwood, conifer sawlog production), were specific to certain case studies only (Table 3). For the purpose of this study we grouped the ecosystem services according to the six Helsinki criteria for sustainable forest management [3] as well as into the four categories suggested by the FORSYS COST Action FP0804 [11]. Both systems overlap; however, there are some important differences. The FORSYS categories only distinguish between wood products, non-wood products, and services, noting whether these products and services are traded on markets or not. The Helsinki criteria are more detailed concerning the forest services; however, they do not make a distinction between market or non-market products and services.

Concerning the Helsinki criteria, most reported ecosystem services (ESS) belong to the groups “protective functions” (7 ESS), and wood production (5 ESS), while according to the FORSYS categories the largest groups are “non-market services” (10 ESS) and “market wood products” (5 ESS). While standing wood volume was attributed to the Helsinki class “forest resources,” it was not attributed to any of the FORSYS categories because it is neither a product nor a service per se. See Table 3 for a complete list of the investigated ecosystem services by country and case study area. For each investigated ecosystem service, country-specific index calculation methods were used and partly newly developed in the INTEGRAL project (see Supplementary Information 2 for details), taking into account the specifically most important conditions. Being more difficult to compare than uniformly calculated index values, they ensure a high relevance on the spot.

Table 2. Forest ecosystem services (ESS) investigated in all case study areas together. The ESS were grouped (I) according to the Helsinki criteria [3]; and (II) according to the FORSYS categories [11].

**Table 2.** Forest ecosystem services (ESS) investigated in all case study areas together. The ESS were grouped (I) according to the Helsinki criteria [3]; and (II) according to the FORSYS categories [11].
Ecosystem Service	Helsinki Criterion No.	Helsinki Class	FORSYS Class
carbon sequestration	1	forest resource	non-market service
standing volume	1	forest resource
harvested wood	3	production (wood)	market wood product
conifer sawlog production	3	production (wood)	market wood product
cork oak fuelwood production	3	production (wood)	market wood product
eucalypt pulpwood production	3	production (wood)	market wood product
hardwood timber production	3	production (wood)	market wood product
cork production	3	production (non-wood)	market non-wood product
mushroom production	3	production (non-wood)	market non-wood product
pine cone production	3	production (non-wood)	market non-wood product
reindeer area	3	production (non-wood)	market non-wood product
biodiversity	4	biodiversity	non-market service
coastal protection	5	protective functions	non-market service
fire safety	5	protective functions	non-market service
natural dynamics protection	5	protective functions	non-market service
quality water provision	5	protective functions	non-market service
sand dunes embankment	5	protective functions	non-market service
water & soil protection	5	protective functions	non-market service
watershed protection	5	protective functions	non-market service
hunting	6	socioeconomic functions	market service
landscape aesthetics	6	socioeconomic functions	non-market service
recreation	6	socioeconomic functions	market service
tourism	6	socioeconomic functions	market service

Table 3. Investigated ecosystem services per country and case study area (CSA).

**Table 3.** Investigated ecosystem services per country and case study area (CSA).
Country	CSA Acronym	Ecosystem Service	Helsinki Class	FORSYS Class
Bulgaria	TET	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
		standing volume	forest resource
		tourism	socioeconomic functions	market service
Bulgaria	YUN	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
		standing volume	forest resource
		tourism	socioeconomic functions	market service
France	PON	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
		standing volume	forest resource
Germany	MUN	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		quality water provision	protective functions	non-market service
		recreation	socioeconomic functions	market service
Germany	UPP	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Ireland	NEW	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		quality water provision	protective functions	non-market service
Ireland	WES	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		quality water provision	protective functions	non-market service
Italy	ASI	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Italy	ETN	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Italy	MOL	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Lithuania	KAZ	biodiversity	biodiversity	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
		water & soil protection	protective functions	non-market service
Lithuania	ZEM	carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Netherlands	SEV	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		fire safety	protective functions	non-market service
		harvested wood	production (wood)	market wood product
		landscape aesthetics	socioeconomic functions	non-market service
		natural dynamics protection	protective functions	non-market service
Portugal	CHA	carbon sequestration	forest resource	non-market service
		conifer sawlog production	production (wood)	market wood product
		cork oak fuelwood production	production (wood)	market wood product
		cork production	production (non-wood)	market non-wood product
		eucalypt pulpwood production	production (wood)	market wood product
		pine cone production	production (non-wood)	market non-wood product
		recreation	socioeconomic functions	market service
Portugal	LEI	carbon sequestration	forest resource	non-market service
		coastal protection	protective functions	non-market service
		conifer sawlog production	production(wood)	market wood product
		recreation	socioeconomic functions	market service
		sand dunes embankment	protective functions	non-market service
		watershed protection	protective functions	non-market service
Portugal	SOU	carbon sequestration	forest resource	non-market service
		conifer sawlog production	production (wood)	market wood product
		eucalypt pulpwood production	production (wood)	market wood product
		hardwood timber production	production (wood)	market wood product
		recreation	socioeconomic functions	market service
Slovakia	KYS	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		hunting	socioeconomic functions	market service
		mushroom production	production (non-wood)	market non-wood product
		quality water provision	protective functions	non-market service
		recreation	socioeconomic functions	market service
		standing volume	forest resource
Slovakia	POD	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		hunting	socioeconomic functions	market service
		mushroom production	production (non-wood)	market non-wood product
		quality water provision	protective functions	non-market service
		recreation	socioeconomic functions	market service
		standing volume	forest resource
Sweden	HEL	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		quality water supply	protective functions	non-market service
Sweden	VIL	biodiversity	biodiversity	non-market service
		carbon sequestration	forest resource	non-market service
		harvested wood	production (wood)	market wood product
		recreation	socioeconomic functions	market service
		reindeer area	production (non-wood)	market non-wood product
		standing volume	forest resource
		tourism	socioeconomic functions	market service

2.3. Simulation Tools/DSS and Forest Data

Most of the simulation tools used in the case studies are single tree or stand level models (Table 4). While Table 4 gives the main references for these models, Supplementary Information 3 informs about their validity and applicability for the respective selected case study areas, and provides additional references. With a few exceptions (the Netherlands, Portugal), where partly process-based models were applied, these models were empirically or semi-empirically calibrated. In three countries (Ireland, Portugal, and Sweden), actual DSS with embedded simulation models were used. Thereby, the approach was to mirror different forest owners’ or manager groups’ attempts to optimize their target achievement within different policy frameworks. In the other cases, the simulations underwent no formal optimization. The forest data that were used to define the initial state for the scenario simulations mostly come from national and enterprise-level forest inventories or a combination of both. In France and Sweden remote sensing surveys also served as a forest data source.

Algorithms for calculating ecosystem service provision indices were either available as implemented in the simulation tools/DSS or were applied to the simulation results in a separate step following the scenario runs.

Table 4. Simulation tools/DSS and forest data sources used in the different countries.

**Table 4.** Simulation tools/DSS and forest data sources used in the different countries.
Country	Simulation Tool/DSS Type	Tool Name	Forest Data
Bulgaria	individual tree model	SIBYLA [12]	forest inventory
France	tree and stand level models embedded in a multi-model pool	Fagacées [13] and Maritime Pine Model [14], embedded in CAPSIS [15] with SIMMEM extension for landscape applications.	derived from aerial photographs and MODIS satellite images
Germany	single tree simulator	SILVA [16,17]	Forest enterprise inventories and German Federal Forest Inventory
Ireland	spatial DSS (including stand level models)	Remsoft Woodstock [18]	Landscape inventory data (forest and agriculture)
Italy	large-level matrix model	EFISCEN [19,20]	Stand wise forest management plan data
Lithuania	large scale stand-level forestry simulator	Kupolis [21]	Lithuanian stand wise forest inventory
Nether-lands	process based forest landscape simulation model (pixel or raster-based)	LandClim [22,23]	Detailed forest inventory (from 1981), projected to 2010 with a carefully checked spin-up run
Portugal	empirical and process-based individual or stand level models	SADfLOR toolbox [24,25]	Stand- and tree-level forest inventory data
Slovakia	individual tree model	SIBYLA [12,26]	Stand level inventory data from obligatory forest management plan
Sweden	DSS (including individual tree models)	Heureka [27]	National Forest Inventory Plots combined with satellite images

2.4. Forest Management Scenarios

The scenarios calculated with the above-mentioned tools originate from case-study specific policy analyses performed in the INTEGRAL project. Although this study utilizes these scenarios uncoupled from their political context, the original concept needs to be explained.

For each case study, several possible alternative socioeconomic scenarios for the coming decades were elaborated. As the forest area in most case studies belongs to different groups of owners, the probable forest management behavior of the different relevant owner types in the context of a given socioeconomic scenario was elaborated in detail. In order to make this information feasible for scenario calculations, owner behavior was translated into quantitative management rules and definitions, which were directly compatible with the specific simulation tools/DSS (see [28] for detailed explanations of the scenario building process). Although the applied simulation tools/DSS are very different, typical variables that defined forest management for simulation purposes were intensity and type of thinnings (e.g., thinning from above or below, selective thinning, etc.), thinning frequency, rotation length, and species preferences for harvesting and regenerating stands. Dependent on the specific simulation tool’s/DSS’s concept and the case studies’ frame conditions, such settings were in some cases applied in an overarching way for large forest landscape compartments, in other cases very detailed with specific settings for a broad spectrum of different forest stand types. On average, four different scenarios (max. 7, min. 3) were defined per case study area, amounting to 85 scenarios in total. In each case study, all scenarios started with the same initial forest state, and were applied immediately, i.e., possible transient phases from current concepts to the scenario conditions were neglected. The scenarios were simulated for three decades in most case studies; in some cases the simulations were extended to 50 years (Bulgaria, France, Netherlands), and 60 years (Lithuania). The central simulation outcomes were the case study-specific indicators for ecosystem service provision at the end of the simulation time span. Climate conditions were assumed to be constant at their present state.

While in the original INTEGRAL context the scenarios’ policy aspects are highly important, this study focuses on the treatment-dependency of ecosystem service provision. Thus, for the purpose of this work, a simple scenario grouping that could be meaningfully applied across all case studies was sought. As all case studies covered one scenario that could be interpreted as “business as usual” (or was explicitly called so), this was used as the reference for grouping. As the grouping criterion that could be applied in each case study while being relevant for this work as well, we chose forest management intensity. A scenario was termed “more intensive” or “less intensive” if it assumed a more intensive forest management on case study area level compared to business as usual. Precisely, “more intensive” means that on landscape level a higher wood production is strived for. This mainly comprises measures like increased felling budgets and rotation shortening, which are often accompanied by reduced stand densities, but also indirect measures like increasing the share of more productive tree species in the course of thinnings and stand regeneration (cf. [29]). Here, we made no difference between whether this is done evenly on the whole area or by a strong treatment segregation on stand level, as long as the overall goal—higher wood production at the landscape level—was the same. In addition to the scenarios “business as usual,” “more intensive,” and “less intensive,” we introduced a fourth group, called “near business as usual.” In this group, we pooled all scenarios that were comparable to business as usual in terms of management intensity, but resulted from another policy framework, which was not defined as the respective case study’s business as usual. This grouping resulted in 20 “business as usual,” 25 “less intensive,” 32 “more intensive,” and eight “near business as usual” scenarios (Table 5).

Table 5. Number of calculated scenarios by scenario category, country, and case study area (CSA).

**Table 5.** Number of calculated scenarios by scenario category, country, and case study area (CSA).
		# of Scenarios in Scenario Category
Country	CSA-Acronym	Business as Usual	Near b.a.u.	Less Intensive	More Intensive
Bulgaria	TET	1	0	1	1
Bulgaria	YUN	1	0	1	1
France	PON	1	1	2	2
Germany	MUN	1	0	2	1
Germany	UPP	1	0	1	2
Ireland	NEW	1	0	2	1
Ireland	WES	1	1	0	3
Italy	ASI	1	0	1	3
Italy	ETN	1	1	3	2
Italy	MOL	1	0	1	2
Lithuania	KAZ	1	0	1	2
Lithuania	ZEM	1	0	1	2
Netherlands	SEV	1	1	1	2
Portugal	CHA	1	1	0	2
Portugal	LEI	1	1	0	2
Portugal	SOU	1	1	2	0
Slovakia	KYS	1	0	2	0
Slovakia	POD	1	0	1	1
Sweden	HEL	1	1	1	2
Sweden	VIL	1	0	2	1
Sum		20	8	25	32

It is important to keep in mind that an overall reference scenario does not make sense. The case study-specific business as usual scenarios strongly reflect each country’s or forest region’s socioeconomic frame conditions for forestry. Evidently, they also depend on the current forest state in each case study area, which results from long-term feedback between the social economy and the forest state itself. The second INTEGRAL policy brief [10] denominates the socioeconomic context for each forest region, which ranges from “commodity-oriented forestry driven by strong forest industry, large forest area and globalized wood market” in Northern Europe to “amenity-oriented forestry influenced by small forest areas und urban society demands” in Western Europe (see Table 6 for a complete list).

2.5. Scenario Result Consolidation

As each country or case study had its own indices for given ecosystem services, a cross-country comparison based on the direct simulation results was not feasible. Instead, based on the expertise of each contributing research team, we classified each ecosystem service’s value on landscape level obtained at the end of a scenario simulation along an ordinal scale, expressed through the symbols “--”, “−”, “0”, “+”, “++”. Here, “0” means no meaningful change compared to the initial situation. The signs “+” and “−”, by contrast, indicate an increase or decrease, respectively, which is considered meaningful for the stakeholders in the case study area of interest, and “++” and “--” symbolize an increase or decrease that is considered particularly strong in the case study’s context. While inevitably losing quantitative information, this scaling overcomes the problem that in different regions meaningful changes of the same ecosystem service might imply different orders of magnitude.

Table 6. European forest regions, their current socioeconomic context, and representative countries in this study. Adapted from the 2nd INTEGRAL policy brief [10].

**Table 6.** European forest regions, their current socioeconomic context, and representative countries in this study. Adapted from the 2nd INTEGRAL policy brief [10].
Forest Region	Socioeconomic Context	Representative Countries
Eastern Europe	commodity-oriented forestry driven by transition to market economy, moderate role of forest industry and relatively large forest areas	Bulgaria, Lithuania, Slovakia
Central Western Europe	multifunctional forestry driven by a pluralistic society, market economy, moderate forest areas, and moderate role of forest industry	France, Germany
North Western Europe	plantation-oriented forestry driven by small forest area and market economy	Ireland
Southern Europe	partly low forest management driven by primacy of non-wood products and natural risks; partly plantation-oriented forestry driven by property fragmentation, forest industry, market economy, and natural risks	Italy, Portugal
Western Europe	amenity-oriented forestry influenced by small forest areas und urban society demands	The Netherlands
Northern Europe	commodity-oriented forestry driven by strong forest industry, large forest area, and globalized wood market	Sweden

The classification was performed in a combined bottom-up/top-down-approach. We communicated the above classification scheme to the contributing teams, and they reported their classification as well as the corresponding numerical simulation output. During the consolidation process we carefully checked and compared all group reports and called back in case of potential incongruities. Most important for the subsequent analyses was the comparison of the non-business-as-usual scenario outcomes with the related business as usual scenario. To this end, we assigned the numerical values −2, −1, 0, 1, and 2 to the ordinal scale “--”, “−”, “0”, “+”, and “++” in exactly this order. From each numerical ecosystem service value obtained in a given scenario we subtracted the corresponding business as usual value (e.g., subtracting “++” from “−” means −1 − 2 = −3, indicating a strong decrease in a given ecosystem service’s provision compared to business as usual). In order to avoid pseudo-precision, all such results greater or smaller than zero were assigned “+” or “−”, respectively, and all zero results were marked with “0.” Thus, “+” and “−” express a meaningful increase or decrease of an ecosystem service compared to business as usual at the end of the simulation time span, while “0” indicates no momentous difference.

2.6. Evaluating the Consolidated Results

Given the consolidated scenario outcomes described above, it was possible to scrutinize them for influences of the management scenario groups as defined above (“more intensive,” “less intensive,” “near business as usual”) on ecosystem service provision. Hereby the ecosystem services were grouped according to both the Helsinki criteria and the FORSYS-classification (see 2.2). In this context, ecosystem service provision is always understood as deviation from business as usual.

The case study-specific covariables forest region, species composition, and social environment were considered as well. Although technically possible, we refrained from testing effects statistically, as the simulation outcomes are not empirical but modeled data. As the backbone of our descriptive analysis we chose mosaic plots [30] as implemented in the R-package vcd [31]. A mosaic plot’s total area (Figure 4 may be taken as an example) represents the total amount of observations taken into account. This area is divided into tiles that display a specific combination of categorical properties (like scenario category, social environment, etc. in Figure 4) each. Each tile’s area represents the number of observations inside such a property combination. See Supplementary Information 1 for a detailed explanation of how to read mosaic plots.

3. Results

3.1. Ecosystem Services’ Pervasiveness

The choice of ecosystem services reported from the single case study areas gives an indication of their relevance and pervasiveness. For the Helsinki and FORSYS classifications, Figure 2 and Figure 3 show for how many case study areas a given ecosystem service category was reported. Concerning the Helsinki classes, across all regions, only wood production is reported in 20 out of 20 case study areas. Nearly the same is true for forest resource maintenance (19 out of 20). Socioeconomic functions (17 out of 20) and biodiversity (16 out of 20) show a high pervasiveness as well. Far less prominent are protective functions (9 out of 20) and non-wood production (4 out of 20). Although protective functions are reported for about half the case study areas only, they were dealt with in each of the forest regions (Figure 2). They are, however, a most diverse and region-specific group, ranging from fire protection in the Netherlands to coastal protection in Portugal, with water protection-related issues being the most prominent overall. Non-wood production-related ecosystem services are reported only for Southern, Eastern, and Northern Europe, which reflects the prominence of wood in the Western European countries’ forest products. From the FORSYS categories’ perspective, market wood products and non-market services are equally prominent throughout Europe and reported in each of the case study areas (Figure 3). Market services were not reported for Western Europe and North Western Europe.

Figure 2. Region-overarching and regional shares of reported ecosystem services categories grouped by the Helsinki criteria. Each sector represents the number of case study areas where a given ecosystem service category was reported.

Figure 3. Region-overarching and regional shares of reported ecosystem services grouped by the FORSYS classification. Each sector represents the number of case study areas where a given ecosystem service category was reported.

3.2. Management Sensitivity of Ecosystem Service Provision

3.2.1. Wood Production/Market Wood Products

As expected, the ecosystem services belonging to the Helsinki group “wood production” (equivalent to the FORSYS class “market wood products”) display a strong dependency on management intensity (Figure 4). More intensive management leads to marked increases in wood production, less intensive to marked losses. Taking forest region as a covariable (Figure 4, left panel), two exceptions become evident: in the Southern European case studies, less intensive management (similar to “near business as usual”) leads to almost no change compared to business as usual. In Central Western Europe, less intensive management sometimes leads to increased wood production, the reason being that accumulating standing wood volume forces managers to increase their harvest level after some decades, even in the framework of a less intensive management scenario.

Figure 4. Sensitivity of wood production in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue). “+” (green): decreased, unchanged, increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

Social environment (rural vs. near city, Figure 4, middle panel) does not show any influence as a covariable to management intensity. For species composition as a covariable (Figure 4, right panel), a similar lack of influence was observed. However, losses in wood production occur as a result of more intensive management in conifer-dominated forest landscapes (in Southern and Northern Europe) only.

Summary: Wood production (market wood product provision) clearly increases with management intensity with some region-specific exceptions. The social environment and species composition do not significantly impact on this relationship.

3.2.2. Forest Resources

The Helsinki class Forest Resources includes all ecosystem services related to carbon storage and standing volume. Thus, this class is closely related to the non-market services FORSYS class. As expected, we observe a clear, opposite trend to the one for wood production-related ecosystem services shown above. More intensive treatment reduces the standing volume and therefore also the carbon storage (Figure 5). There are, however, region-specific differences. Losses dominate with more intensive management in Southern Europe, Eastern Europe, and Central Western Europe (Figure 5, left panel). Massive gains are associated with less intensive management in Eastern Europe and Northern Europe, in contrast with the losses associated with more intensive treatment in the same regions. In Southern Europe, only a weak trend was found, with no gains at all with reduced management intensities; in Western Europe, we see no trend at all. In Central Western Europe, North Western Europe, and Southern Europe, losses do also occur when management is less intensive. This may be partly due to a more complex approach towards carbon modeling in some case studies, where C-storage in harvested wood products was included in the assessment.

Figure 5. Sensitivity of the Helsinki class Forest Resources in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue). “+” (green): decreased, unchanged, increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

In relation to the social environment (Figure 5, middle panel), a general trend—losses and gains associated, respectively, with more and less intensive management—is evident; however, there is no marked difference between rural and near city case studies. The same is true for species composition (Figure 5, right panel); however, only in mixed species settings did no losses in forest resources occur with reduced management intensity.

Summary: Forest resources are in general reduced with more intensive management, and less intensive treatment may lead to considerable gains in some regions. This general trend is most pronounced in mixed species settings.

3.2.3. Socioeconomic Functions/Market Services

Besides recreation and tourism, which solely define the FORSYS class of market services, the Helsinki class of socioeconomic functions also includes landscape aesthetics and hunting. As the latter two are only reported for a few case studies, the socioeconomic functions and market services classes are almost identical, which is also true in terms of the results obtained for both groups. Therefore, Figure 6, which depicts the outcomes for the socioeconomic functions class, represents the market services class as well.

Figure 6. Sensitivity of the Helsinki socioeconomic functions class in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue), and “+” (green): decreased, unchanged, and increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

Socioeconomic functions were not investigated in the North West European case studies, and only a few indices were reported from Northern Europe and Western Europe. In contrast, a strong emphasis was placed on these functions in Southern Europe and Eastern Europe (Figure 6, left panel). The results are quite region-specific. Less intensive management mainly does not change the provision of socioeconomic functions in Southern Europe, while in Eastern Europe it leads to no change or even an increase in two-thirds of cases only. In Central Western Europe, less intensive management decreases socioeconomic function levels more often than not. More intensive management drastically decreases the provision in Southern Europe, while in Eastern Europe the sensitivity to intensification is quite low. There, still more than half of the cases show no change or an increased provision under intensified management. In Central Western Europe, intensification increased provision in more cases than less intensive treatments. For the few cases in Western and Northern Europe, more intensive management leads to an increase or no change in the provision of socioeconomic functions compared to the levels provided by business as usual management.

In near-city environments, the frequency of losses in socioeconomic functions is the same for less intensive and more intensive management (~40% of the cases). However, in contrast to less intensive management, there are also a considerable number of cases where the provision of socioeconomic functions improves with management intensification (Figure 5, middle panel). These trends are reversed in rural environments. In most cases, less intensive treatment leads to no change or increased provision of socioeconomic functions. More intensive management increases the frequency of losses in the provision of socioeconomic functions substantially (nearly 50% of the cases).

Conifer-dominated forest landscapes exhibit improved provision of socioeconomic functions in 50% of the cases when less intensive management is applied; no case resulted in a reduced provision. In broadleaf-dominated areas less intensive management mostly leads to no change, although both increases and decreases in provision occur. The highest frequency of reducing the provision of socioeconomic functions with less intensive management comes in mixed species settings; this is due to the loss of attractive species mixtures in the course of reducing management intensity. More intensive management induces a decrease in the provision of socioeconomic functions in many of the coniferous species settings, but the majority of cases still results in no change or an improvement. In broadleaf-dominated areas, intensification increases the number of cases of reduced provision of socioeconomic functions to about 50%, while a few cases only result in a gain. Intensification in mixed species forest areas results in decreased provision in a majority of cases; near business as usual scenarios exhibit indifferent behavior in relation to treatment intensity and species composition.

Summary: The provision of socioeconomic functions (and therefore also market service provision) generally decreases with more intensive management. However, we observe strong region-specific differences that are due to regional forest history and societal perceptions and preferences. Social environment seems to matter, as less intensive management does not lead to an improved provision in any of the near-city cases while it frequently does in rural ones. In mixed species and broadleaf dominated regions, business as usual seems to be an optimum middle course.

3.2.4. Biodiversity

For the ecosystem services that belong to the Helsinki class biodiversity, there seem to be two opposing trends when related to the forest regions (Figure 7, left panel). The first is a clear trend towards biodiversity losses with more intensive management, which can be identified in Southern Europe, Eastern Europe, and Northern Europe. Second, in Central Western Europe and North Western Europe, losses prevail with less intensive management, while no change and increased provision dominate when management is more intensive. Only the results we obtained for Western Europe do not conform to either trend.

Figure 7. Sensitivity of biodiversity provision in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue), and “+” (green): decreased, unchanged, and increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

In the investigated rural regions (Figure 7, middle panel), there is a very pronounced trend; with less intensive management, biodiversity decreases only in a few cases while no change and, especially, increased provision dominate. More intensive management leads to lower biodiversity in about 60% of the cases, but no change and even improved provision also occurs. Near-city forest areas do not show such clear trends, with slightly more losses than gains in biodiversity associated with less intensive management, while there are no gains associated with near business as usual and more intensive management.

Management effects do not differ greatly for different species compositions (Figure 7, right panel). Across all species settings, losses in biodiversity are more frequent when management is intensified, while less intensive management produces more gains. Intensive management in mixed stands results in both losses and gains in more cases than for other species compositions.

Summary: The regional opposite trends in biodiversity provision as a result of different management intensities are not visible when considering social environment and species composition. In the latter two cases, more intensive management leads in most cases to biodiversity loss, while less intensive management results in many cases with a gain in biodiversity provision. This trend is most clear in rural environments and conifer and broadleaf species settings.

3.2.5. Protective Functions

As heterogeneous as the Helsinki group of protective functions is, so non-uniform are the outcomes associated with management intensity by regions (Figure 8, left panel). No trend with management intensity can be seen in the provision of protective functions in Southern Europe, Western Europe (comprising no change or improvement), and North West Europe (comprising no change or decline). In contrast, a strong trend was identified in Northern Europe and Central West Europe, where less intensive management leads to gains, and more intensive management leads to losses, in the provision of protective forest functions; a similar but weaker trend was identified for the Eastern European case studies.

Figure 8. Sensitivity of the provision of protective functions in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue), and “+” (green): decreased, unchanged, and increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

Less intensive management in near-city forests mostly leads to gains in protective functions, while no losses are found (Figure 8, middle panel). No change and gains in provision dominate (~80%) when management is more intensive. While less intensive management in rural areas mostly leads to gains or no change in the provision of protective functions, losses also occur. No change prevails with more intensive management, but the number of cases with a loss in provision increases considerably, while very few cases result in gains.

For broadleaved dominated regions, represented by only a few cases, both less and more intensive management results in gains in the provision of protective functions (Figure 8, right panel). A very strong trend exists for mixed species areas, where less intensive management is only accompanied by gains and more intensive management by losses in the provision of protective functions. Most results are available for conifer-dominated areas. Here, trends are weak; no change and gains in provision prevail when management is less intensive, almost no change is observed with near business as usual scenarios, and considerably more loss and less gain in the provision of protective functions occurs when treatment is more intensive.

Summary: Protective functions are regionally very different and, therefore, very different management effects exist by region. Near-city forests produce more gains than rural forests when management intensity is reduced. Losses in the provision of protective functions are more (and gains less) frequent when management is intensified in both social environments. The same trend occurs in conifer-dominated landscapes, while in mixed-species settings gains associated with less intensive management contrast with losses in provision associated with intensification.

3.2.6. Non-Wood Production/Market Non-Wood Products

Ecosystem services belonging to the Helsinki class of non-wood production, which is equivalent to the FORSYS class of market non-wood products, were only investigated in a few case studies (n = 13) in the Southern, Eastern, and Northern Europe forest regions. Mushroom production is included, as well as cork and pine cone production and reindeer herding.

In Southern Europe, where non-wood production was only investigated in near business as usual and more intensive management scenarios, the results show no difference between near business as usual and intensification (Figure 9, left panel). For the Eastern European case studies only a weak trend exists; while less intensive management results in no change or, more frequently to gains in non-wood production, more intensive management leads to increased production only. A weak relationship is also visible for Northern Europe. Less intensive management led either to losses or no change in non-wood production, while increased intensities did not result in non-wood production changes compared to the level associated with business as usual management.

Figure 9. Sensitivity of non-wood production in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue), and “+” (green): decreased, unchanged, and increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

In the few cases where results for near-city areas are available, information only exists for less intensive management, where non-wood production either increased or remained unchanged (Figure 9, middle panel). In rural areas, no change dominates in more intensive and near business as usual scenarios, with the non-wood production losses associated with less intensive management occurring only in the Northern European case studies.

The results for conifer-dominated areas (Figure 9, right panel) simply reflect those for Northern Europe (Figure 9, left panel). In broadleaf-dominated areas, less intensive management results in gains in non-wood production. For the other two treatment intensities no change is the most prominent outcome. For mixed species settings, the only available information is a balanced outcome between no change and increased non-wood production, when management is less intensive.

Summary: Due to the limited amount of available results, the trends related to non-wood production (equivalent to non-wood market product provision) have to be interpreted with caution. Obviously, their importance is not significant in many regions, especially Western Europe, North Western Europe, and Central Western Europe (Figure 2). Non-wood production does not seem to be highly sensitive to management intensity; almost exclusively no change and, less frequently, increases in provision were found as intensity changed.

3.2.7. Non-Market Services

In contrast to market non-wood products, the FORSYS class of non-market services is very large and prominent in all investigated European forest regions (cf. Figure 3). This class comprises biodiversity, carbon storage, landscape aesthetics, and all kinds of protection services. Although parts of the non-market services have been analyzed above in higher-resolution Helsinki classes, we also show the results for this aggregated class in order to be compatible with the FORSYS classification. When split into forest regions, we frequently find losses in non-market service provision being connected with more intensive management (Figure 10, left panel). The only exception is Western Europe, where intensification brings about unchanged or increased non-market service provision only. In Southern Europe we frequently observe losses with both less intensive and more intensive management. Except for Southern Europe and North West Europe, we observe a general trend towards fewer losses and more gains with lower intensity.

In near-city as well as in rural forest areas, unchanged and increased non-market service provision dominate when management is less intensive (Figure 10, middle panel). In both kinds of social environment, management intensification leads to a higher loss risk at the expense of gain chances, where the latter effect is far more pronounced under rural conditions.

Figure 10. Sensitivity of non-market services in relation to management intensity, by forest region, social environment, and species composition. Deviation from business as usual: “−” (red), “0” (blue), and “+” (green): decreased, unchanged, and increased ecosystem service provision compared to business as usual. Scenario Category: Less intensive (“less”), more intensive treatment (“more”), and near business as usual (“nbu”). Forest Regions: “SE”—Southern Europe, “EE”—Eastern Europe, “CWE”—Central Western Europe, “WE”—Western Europe, “NWE”—North Western Europe, “NE”—Northern Europe.

In mixed species areas lower non-market service provision with less intensive management is rare, while losses are dominating when management is intensified. The gains show exactly the reverse pattern. Broadleaf- and conifer-dominated case studies behave very similar to each other. In both kinds of settings non-market service provision is less treatment-sensitive compared to mixed species areas. The overall trend is, however, the same: Frequent losses with more intensive treatment come with less frequent gains.

Summary: Non-market services tend to show a higher loss risk when more intensive treatment is applied, albeit with region-wise exceptions. Often, gain chances are higher with less intensive treatment. Concerning species composition, non-market services are most treatment-sensitive under mixed species frame conditions.

3.2.8. Generalization

The previous analyses allow for the production of a generalized qualitative ranking of ecosystem service categories in terms of their sensitivity to management intensity (Table 7). Wood production (syn. market wood products), forest resources, and biodiversity react strongly to different management intensities. While wood production increases and forest resources decrease when management intensifies, biodiversity also reacts strongly, but both increased and decreased provision are possible, depending on the local forest history and cultural setting, as mentioned previously. The FORSYS class of non-market service provision reacts less strongly to management intensity changes than the three categories above, but change is still considerable. In general, provision tends to decrease with higher management intensity. Only a weak sensitivity was identified for the Helsinki classes of protective functions and socioeconomic functions, the latter being virtually identical to the market services FORSYS class. Non-wood production (syn. market non-wood production) levels do not, in general, show any clear relationship with management intensity.

3.3. Tradeoffs, Synergies

Based on the sensitivities of the ecosystem services to management intensity, as analyzed above and summarized in Table 7, a qualitative summary of tradeoffs and synergies is produced (Table 8). We use the term tradeoff for describing situations where a gain in one ecosystem service leads to a loss in another. In cases where a greater provision of one ecosystem service goes along with a greater provision of another, we use the term synergy.

Table 7. Generalized sensitivity of ecosystem service categories to management intensity. The signs “+” and “−” indicate whether the correlation with management intensity is in general positive or negative.

**Table 7.** Generalized sensitivity of ecosystem service categories to management intensity. The signs “+” and “−” indicate whether the correlation with management intensity is in general positive or negative.
Ecosystem Service Category	Sensitivity to Management Intensity
wood production/market wood products.	strong	+
forest resources	strong	−
biodiversity	strong	+ and − possible
non-market services	intermediate	−
protective functions	weak	−
socioeconomic functions/market services	weak	−
non-wood production/market non-wood products	none

Table 8. Tradeoffs (upper triangle, shaded light gray) and synergies (lower triangle, shaded dark gray) between the investigated ecosystem service categories. In case of analogies between FORSYS and Helsinki categories, the Helsinki category name is used in this table.

**Table 8.** Tradeoffs (upper triangle, shaded light gray) and synergies (lower triangle, shaded dark gray) between the investigated ecosystem service categories. In case of analogies between FORSYS and Helsinki categories, the Helsinki category name is used in this table.
	Wood Production	Forest Resources	Socioeconomic Functions	Biodiversity	Protective Functions	Non-Market Services
wood production		strong	weak	strong (region-specific)	weak	intermediate
forest resources				strong (region-specific)
socioeconomic functions		weak		weak (region-specific)
biodiversity	strong (region-specific)	strong (region-specific)	weak (region-specific)		weak (region-specific)	weak (region-specific)
protective functions		weak	weak	weak (region-specific)
non-wood production
non-market services		intermediate	weak	weak (region-specific)	weak

Wood production (syn. market wood products) displays a strong tradeoff with forest resources. In other words, it is very unlikely to have high wood production and large stocks of forest resources in the same area at the same time. A strong tradeoff as well as a great synergy between wood production and biodiversity can occur. This outcome is very region-specific (Table 7). Except for non-wood production (syn. market non-wood production), where neither a considerable tradeoff nor synergy is present, wood production in general is in a weak (socioeconomic functions/market services, protective functions) or intermediate (non-market services) tradeoff with the other ecosystem service categories when treatment intensity is changed.

Apart from wood production, most other ecosystem service categories show a weak synergy with each other. Dependent on forest region and history, biodiversity shows a tradeoff or a synergy with almost any other ecosystem service category, except with non-wood production (market non-wood production). The provision of the latter seems to be very elastic in relation to the provision levels of other ecosystem service categories as well as management intensity.

4. Discussion

Based on 20 case study areas throughout Europe, this study comes to statements about the relative importance of given ecosystem service categories and their sensitivity to the intensity of forest management. The latter was analyzed in the context of the covariables forest region, social environment, and species composition. Although these covariables partly correlate and thus must be interpreted with care, this allows us to make conclusions about management steering possibilities, tradeoffs and synergies, in terms of different ecosystem services’ provision, as presented above.

The ecosystem service categories that show a strong sensitivity to management intensity are wood production/market wood products (positive correlation), forest resources (negative correlation), and biodiversity. Surprisingly, biodiversity can react in both ways to management, negatively or positively. The latter finding agrees well with a recent meta-analysis [32], while the former disagrees with it. Our interpretation suggests that the former trend is prevailing in regions where the general development is from low intensity management to greater intensity, while the latter trend occurs in regions where there is a trend from plantation management to more close-to-nature forestry. Most other ecosystem service categories show only weak and negative correlations with management intensity. We could also identify different tradeoffs and synergies in the provision of different ecosystem services. A strong tradeoff exists between the maintenance of forest resources and wood production. Strong connections also exist between biodiversity and wood production and forest resources. Whether these connections are tradeoffs or synergies is region-specific. Remarkably, though, both are possible. An issue that is not fully covered by this study is the risk of calamities, especially in over-dense conifer stands, which may in some places result from low-intensity management and often bear an increased risk of storm or snow damage with subsequent insect attacks. Clearly undesired by forest owners who strive for a steady timber production, the consequences of such calamities for other ecosystem services’ provision are non-trivial.

Climate change and its possible effects were deliberately not considered in this study. The overwhelming majority of the contributing models are empirical, covering forest growth dynamics best under current climate conditions. Instead of burdening our study with the additional uncertainty of climate scenarios (cf. [33]), we chose simulation time spans, 30 years in most cases, which seemed short enough to assume no substantially different results under changing climate. Europe-wide forest growth and management scenarios including climate change usually take into account considerably longer time frames [4,5]. As a recent empirical study shows [34], past climate change (together with the fertilizing effects of increased N-immissions and CO₂ supply) has accelerated forest dynamics in Central Europe. Remarkably, though, this study hints that typical stand structures stayed virtually the same; only their progression accelerated. As most of the ecosystem services investigated in the study at hand are connected to structural forest properties, we take that as another argument for the stability of our results. To our knowledge, the study at hand is the only one covering such a broad spectrum of ecosystem services on the European level. Our outcomes, however, are not implausible in the context of other large-scale studies that focused on a smaller set of ecosystem services, often carbon budgets and wood supply, as summarized in [7].

Besides the wide range of ecosystem services investigated, methodological heterogeneity is a characteristic of this study. The forest growth models and DSS that were applied, and the forest data that were used for defining the initial state for the scenarios, included very different approaches across the contributing countries and case studies. The same is true for the indices that were taken as a measure for a given ecosystem service’s provision. This may seem problematic in terms of comparability on the one hand. On the other hand, however, this procedure ensured that in each case study the best available models and indices were used, which exactly fit into the regionally relevant information supply and demand (cf. [35,36]). As each model is built for being applied to the most important tree species in a given region, we are confident that a more precise and more relevant collection of forest development scenarios across Europe can hardly be achieved at the time being. However, we do not see the study at hand as a competitor to large-scale studies with one single model [8,37], more as a bottom-up complement to the usual top-down approach.

In two countries, namely Bulgaria and the Netherlands, the applied models (SIBYLA [12] and LandClim [22], respectively) have not been developed and formally validated with data from the relating case studies. However, in terms of natural conditions the Bulgarian case study regions are inside the range of applicability of the model SIBYLA; in addition, the simulation results were examined for plausibility and approved by local experts. The model LandClim is a process-based model that covers a broad range of natural conditions including the case study area where it has been applied, South East Veluwe. See Supplementary Information 3 for more details and literature.

It is important to state that the calculated management scenarios were not initially defined in order to assess ecosystem service provision against management intensity. They were derived from case study-specific societal and policy framework scenarios considered to drive forest managers’ behavior [9,12]. As such, they result from a so far rather unique collaboration between social scientists and forest growth and management modelers. Their definition, based on local stakeholder workshops as well as locally experienced social and natural scientists, ensured that the scenarios stayed in a plausible and therefore useful framework. However, aggregating the scenarios by treatment intensity as defined above for the purpose of this study turned out to be a straightforward procedure. Our confidence in this grouping is supported by the absolutely plausible behavior of wood production when related to treatment intensity.

As another important point to mention, the case study areas were not selected with the purpose of being representative in the sense of a forest inventory. Instead, the most important selection criterion was relevance for the respective country. Therefore, the case study areas represent situations where typical and relevant problems have to be dealt with. This fits well with the choice of models, indices, and data as discussed above. From that point of view, our study’s most prominent weakness—heterogeneity in methods and data—might be its most prominent strength.

5. Conclusions

At the European level, ecosystem service steering potential by forest management seems to be highest for wood production, forest resources, and biodiversity. Non-wood production, by contrast, where regional differences are high and our information base is smallest, seems to be very elastic when related to management intensity, at least as seen from a pan-European perspective. Strong tradeoffs were observed between the stocks of forest resources and wood production. Biodiversity may both, be in a strong tradeoff or in synergy with wood production, depending on a given region’s forest conditions and history. Except for non-wood production, almost any other ecosystem service group shows a weak tradeoff with wood production. The covariables species composition and social environment are of punctual interest only, while forest region often makes an important difference in terms of an ecosystem service’s treatment sensitivity. This confirms region-specific approaches to forest management in Europe.

Concerning the choice of methods, the coherent results of this study seem to justify a subsidiary approach—upscaling from local tools and data to the European level.

Acknowledgements

This project has received funding from the European Union’s Seventh Program for research, technological development and demonstration under grant agreement No 282887 (INTEGRAL).

Author Contributions

Peter Biber, José G. Borges, and Ola Sallnäs designed the study and interpreted the consolidated results. Peter Biber performed the analyses and wrote the paper. Maarten Nieuwenhuis, Ralf Moshammer, and Hans Pretzsch contributed to writing the paper. All authors contributed substantial data, meta-information, and result interpretation.

Conflicts of Interest

The authors declare no conflict of interest.

Supplementary Materials

References

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Biber, P.; Borges, J.G.; Moshammer, R.; Barreiro, S.; Botequim, B.; Brodrechtová, Y.; Brukas, V.; Chirici, G.; Cordero-Debets, R.; Corrigan, E.; et al. How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment? Forests 2015, 6, 1666-1695. https://doi.org/10.3390/f6051666

AMA Style

Biber P, Borges JG, Moshammer R, Barreiro S, Botequim B, Brodrechtová Y, Brukas V, Chirici G, Cordero-Debets R, Corrigan E, et al. How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment? Forests. 2015; 6(5):1666-1695. https://doi.org/10.3390/f6051666

Chicago/Turabian Style

Biber, Peter, José G. Borges, Ralf Moshammer, Susana Barreiro, Brigite Botequim, Yvonne Brodrechtová, Vilis Brukas, Gherardo Chirici, Rebeca Cordero-Debets, Edwin Corrigan, and et al. 2015. "How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment?" Forests 6, no. 5: 1666-1695. https://doi.org/10.3390/f6051666

APA Style

Biber, P., Borges, J. G., Moshammer, R., Barreiro, S., Botequim, B., Brodrechtová, Y., Brukas, V., Chirici, G., Cordero-Debets, R., Corrigan, E., Eriksson, L. O., Favero, M., Galev, E., Garcia-Gonzalo, J., Hengeveld, G., Kavaliauskas, M., Marchetti, M., Marques, S., Mozgeris, G., ... Sallnäs, O. (2015). How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment? Forests, 6(5), 1666-1695. https://doi.org/10.3390/f6051666

Article Menu

How Sensitive Are Ecosystem Services in European Forest Landscapes to Silvicultural Treatment?

Abstract

1. Introduction

2. Material and Methods

2.1. Case Study Areas

2.2. Investigated Ecosystem Services

2.3. Simulation Tools/DSS and Forest Data

2.4. Forest Management Scenarios

2.5. Scenario Result Consolidation

2.6. Evaluating the Consolidated Results

3. Results

3.1. Ecosystem Services’ Pervasiveness

3.2. Management Sensitivity of Ecosystem Service Provision

3.2.1. Wood Production/Market Wood Products

3.2.2. Forest Resources

3.2.3. Socioeconomic Functions/Market Services

3.2.4. Biodiversity

3.2.5. Protective Functions

3.2.6. Non-Wood Production/Market Non-Wood Products

3.2.7. Non-Market Services

3.2.8. Generalization

3.3. Tradeoffs, Synergies

4. Discussion

5. Conclusions

Acknowledgements

Author Contributions

Conflicts of Interest

Supplementary Materials

References

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