Edited by: Felix Müller, Christian-Albrechts-Universität zu Kiel, Germany
Reviewed by: Simone A. Beichler, Leibniz-Institut für Gewässerökologie und Binnenfischerei, Germany; Paraskevi Drakopoulou, Hellenic Centre for Marine Research, Greece
This article was submitted to Marine Pollution, a section of the journal Frontiers in Environmental Science
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The assessment of ecosystem services, the benefits humans obtain from ecosystems, is a worldwide topic of growing interest, but examples addressing coastal and marine waters are still a small minority. In this study, we carry out an expert based ecosystem service assessment for a concrete case study, the Szczecin (Oder) Lagoon located at the German/Polish border in the Baltic Sea region. We analyze to what extent, in which step and how it can be applied for supporting Integrated Coastal Zone Management (ICZM), the ecological-social-economic assessment within System Approach Frameworks (SAF), and Marine Spatial Planning (MSP). The large, shallow Szczecin Lagoon is heavily eutrophied. Therefore, several alternative measures (scenarios) are under discussion to improve its water quality and its ecological status. Scenarios include a large-scale mussel farm; the establishment of a local mussel farm that removes nutrients via harvest and increases water transparency; artificial mussel beds; groins to reduce coastal current velocities, favor sediment accumulation, and promote the enlargement of macrophyte beds and other measures to enlarge macrophyte belts and coverage. We adapt and apply a computer aided ecosystem service assessment and visualization tool (ESAT). Eight experts and two student groups apply this tool and carry out an assessment of each scenario compared to the present state of the lagoon. The results show that the scenario assuming measures to enlarge macrophyte belts is perceived as the one that generates the highest additional ecosystem service output. However, more importantly our approach can serve as tool to catch the views of experts, can extract disagreements between experts and misunderstandings in the setup of scenarios as well as services that have highest priority for further consideration. Further, the results are useful for preparing stakeholder discussions and workshops. However, the expert assessments are influenced by the spatial scale of the assessed scenarios. As consequence, the assessment results itself cannot be regarded as a reliable basis for decision making. Today, Integrated Coastal Zone Management ideas and approaches are well reflected and integrated into Marine Spatial Planning and we show that a comparative ecosystem service assessment can be applied in different steps of each concept.
Ecosystem services (ES) are defined as the benefits human obtain from ecosystems (Millennium Ecosystem Assessment,
In Europe, the Baltic Sea Region is leading with respect to strategies and actions for coastal and marine protection and sustainable development. The European Union Strategy for the Baltic Sea Region (EUSBSR) specifies three overall objectives: to save the sea, to connect the region, and to increase prosperity (European Comission,
The EU Maritime Spatial Planning Framework Directive (2014/89/EU) sets the legal framework for marine spatial planning in Europe. MSP identifies which areas of the ocean are appropriate for different uses or activities in order to reduce conflicts and achieve ecological, economic and social objectives (Douvere and Ehler,
Similar to the steps of a MSP process, as suggest by HELCOM-VASAB (
Coastal waters provide a wide range of services, but are under intensive human use, face degradation and are highly dynamic systems, where many changes will take place in the near future. This is especially true for large Baltic lagoons, like the Oder (Szczecin) Lagoon. In the Oder Lagoon, heavy eutrophication causes a degradation of some ES and hampers the socio-economic development. It is not possible to fight eutrophication via measures in the river-basin alone (Schernewski et al.,
The objectives of this article are to (a) define sets of five alternative environmental measures to improve the ecological status of the Oder Lagoon (scenarios); (b) assess changes in ecosystem service provision between the present state and hypothetical situations assuming the implementation of these scenarios based on experts; (c) analyse the potential role of ES assessments in stakeholder and expert involvement as well as; (d) discuss it in the context of the SAF, ICZM, and MSP.
For this purpose, we adapt and use an ecosystem services assessment tool and carry out comparative assessments involving experts. During the last decade, expert based ES assessments turned out to be a promising approach in environmental management (e.g., Beichler,
With a surface area of 687 km2, the Oder (Szczecin) Lagoon is one of the largest lagoons in Europe, shared between Germany (Kleines Haff, 277 km2) and Poland (Wielki Zalew, 410 km2) and intensively used by humans since the middle Ages (Figure
Location of the Oder (Szczecin) Lagoon and the focus area and pictures showing the south-western lagoon coast near the small resort Mönkebude.
Measures to reduce nutrient loads from the river basins into the lagoon are ongoing and show some success. Total nitrogen loads into the lagoon declined from about 80,000 t/a in the 1980s to <60,000 t/a between 2010 and 2014. In the same period, total phosphorus loads declined from 8,000 to <3,000 t/a (Friedland, pers. com.). According to the official German/Polish monitoring data, the total nitrogen (phosphorus) concentrations in the central Kleines Haff (western small lagoon) declined from about 220 μmol/l N (9 μmol/l P) in the 1980s to about 130 μmol/l N (5 μmol/l P) between 2010 and 2014. In the central Wielki Zalew (eastern large lagoon) the total nitrogen (phosphorus) concentrations declined from about 140 μmol/l N (7 μmol/l P) in the 1980's to about 130 μmol/l N (4 μmol/l P) between 2010 and 2014. Between the 1980's and today, in average, a 25% reduction of total nitrogen riverine loads to the lagoon caused a similar reduction of the total nitrogen concentration in the lagoon. With respect to riverine phosphorus loads, a more than 60% P load reduction between the 1980's and today caused a reduction of the total phosphorus concentration in the lagoon of nearly 45%. The chlorophyll-a concentrations in the Kleines Haff nearly remained on a level of 70 μg/l, but in the Wielki Zalew showed a decline from 70 μg/l in the 1980s to about 45 μg/l between 2010 and 2014. Averaging over the lagoon, we can assume a reduction of nearly 25%. During this period, water transparency showed a slight decline from 0.8 to 0.65 m in the Kleines Haff and an increase from 0.9 to 1.05 m in the Wielki Zalew. We can conclude that nutrient load reductions in the river basin had only a limited effect on algae concentrations and blooms and no effect on water transparency. The lagoon remained in a highly eutrophied status and a recovery of submerged macrophytes is still not observed.
The European Water Framework Directive (WFD, 2000/60/EC) classifies the ecological status of coastal waters based on biological quality elements, namely phytoplankton, macroalgae, and angiosperms as well as benthic invertebrate fauna. The assessment considers the biological deviation from reference conditions (high quality). The present status of the Oder Lagoon, which according to the German classification is regarded as a coastal water, still shows a major deviation from the reference state and its ecological status has to considered as poor. Therefore, an urgent pressure to implement suitable management measures in the river basin and the lagoon itself exists.
On 21st October 2015 a first workshop with 31 local stakeholders from diverse fields of interest such as local and regional authorities, fisheries, tourism and NGOs was organized in Ueckermünde (Figure
Map of the south-western lagoon (Kleines Haff) indicating the location of major human activities and the 4 scenarios. Pictures of the south-western lagoon: Goynes (pile rows), Zebra mussels (
On 6th September 2017, a second workshop with 26 participants took place in Ueckermünde, where the scenarios and possible environmental and socio-economic consequences were presented and discussed in more detail. The ES following expert assessments were used for the preparation of this workshop.
We adapted the Common International Classification on Ecosystem Services (CICES, version 4.3) (Haines-Young and Potschin,
Sub-division of ecosystem services into sections and classes as well as the associated indicators including units. The table is modified and extended based on CICES (Haines-Young and Potschin,
The application process required a clear spatial definition of the study area, as shown in Figure
Excerpt of the Ecosystem Service Assessment Tool (ESAT) showing the assessment of few provisioning ecosystem services. The numbers indicate the scores on indicator level and the automatic averaging process to obtain ES classes, groups, divisions, and sections. Below the relative scoring system used in the expert assessments. Scored are the changes resulting from the implementation of measures (scenarios), compared to the present situation.
In a first application, we carried out a comparison of the present state of the lagoon with the hypothetical assumption of an implementation of scenario 0. The assessment covered the entire lagoon and the coastal strip and involved two young scientists with broad and good knowledge relevant for the scenario. The experts worked independently, full time, without exchange and had about 2 weeks to finish the assessment. They had access to all available data and information about the lagoon.
In a second application, we provided four concrete, realistic, alternative scenarios covering different measures. Eight experts (including the authors) with different scientific background (biologists, ecologists, environmental scientists, geographer) and from different NGOs, universities, and scientific institutes (most hold a Ph.D. degree) were asked to carry out an assessment for all five scenarios and all 54 indicators describing the ES classes. The experts received the guidelines and ESAT and carried out the assessment independently at home within a period of 4 weeks. The experts based their assessment mainly on their existing knowledge and perception of the area. Additionally, two master-student groups with 4–5 persons each carried out an assessment during a 2 days course. The size and allocation of the scenarios was visualized on maps and explanations were provided to ensure a joint understanding. After the assessments, discussions with the experts took place to get a better understanding of their view and insight into their scoring. The experts were not allowed to change or adjust their scoring afterwards.
Our first application was carried out by two young scientists and related to scenario 0, the large scale mussel cultivation covering 50% of the lagoon surface. It formed the basis for the following guiding questions: To what extent does the spatial scale of a measure affects the result of an ES assessment? Is this extreme and controversial (scenario 0) perceived similar by both experts and are possible differences clearly reflected in the assessment? Is it possible to use the assessment to extract major points of disagreement and aspects that need deeper consideration or clarification? Do ES assessments provide a deeper insight, whether scenarios (set of measures) affect the potential state of and process toward sustainability on a regional (lagoon) level?
The experts found 26 out of 31 ES as relevant for this scenario. Expert 2 considered surface water for non-drinking purposes (P8) and animal based resources (P10) relevant and assumed a higher provision after the implementation of mussel cultivation, while expert 1 did not consider it as relevant. Background for the view are positive effects of mussels on water quality and transparency that may allow a water utilization in future. The potential use of shells as fertilizer and mussels for bio-energy production explains the choice and score of P10. For provisioning and regulating services in general, the average disagreement between both experts was about 1 unit and can be regarded as good (Figure
Comparison of the present state of the lagoon with the hypothetical assumption of an implementation of scenario 0, large scale mussel cultivation covering 50% of the lagoon surface. Provisioning (P), regulating and maintenance (R) as well as cultural ES (C). Positive scores indicate an increase in ES provision after the scenario implementation.
With respect to cultural ES, the disagreement (2 units in average) was much stronger. Expert 1 had a strongly positive opinion about the effects of a large mussel farm on cultural ES, while expert 2 assumed only minor positive changes. The experiential use of plants, animals and land-/seascapes in different environmental settings, indicated by the number of visitors taking part in activities related to biota, was perceived differently. While one experts considered mussel cultivation as a potential attraction, the other saw a negative impact on visitors. The cultural heritage (C4) indicated by the number of cultural and heritage sites was perceived differently, as well. One expert assumed mussels as a new local product with the potential to link new events to it, the other expert did not. With respect to aesthetics (C6), indicated by the number of pictures taken, both experts assumed an increase because higher water transparency increase attractiveness as well as farming and processing as attractions in itself that increase the number of pictures taken. However, the score strongly differs between both experts and it is questionable if an increase in the number of pictures related to farming and processing is still reflecting the aesthetics of the landscape as an ecosystem service. The effects of large scale mussel cultivation on symbolic (C7), namely the number of Red List and iconic species, were perceived differently. While one expert assumed that the zebra mussel may become an iconic species and that mussel farming might provide new habitats for red list species, the other expert had an opposite view. One expert assumed an increase in the number of religious events (C8), because the area might increase in tourist attractiveness, resulting in a higher number of weddings by visitors. Different opinions with respect to the extent of marine protected areas (C10) seemed to be a misunderstanding, because most of the lagoon is already under Natura 2000 protection.
The large agreement with respect to provisioning and regulating services makes it possible to use the assessment to extract major points of disagreement and aspects that need deeper consideration or clarification. With respect to cultural services, a clear joint vision between both experts was lacking. Comparable concrete experiences with mussel cultivation of this size and spatial extent do not exist and a supporting visualization was hardly possible. The scores depended on the virtual pictures the experts had in mind when carrying out the assessment. In general, the experts do not assume a relevant overall change in provisioning and regulating ES, but a clear overall increase in cultural ES. The large-scale utilization of the lagoon for mussel cultivation was perceived surprisingly positive and there is no indication that the scale of the mussel farm had a negative effect on the ES assessment. Major concern of both experts was that a large scale mussel cultivation has negative on key market fish species. This concern clearly indicates the need for further discussions and deeper considerations because a possible negative effect is scientifically highly uncertain.
In the second application, the four concrete, realistic, alternative local scenarios were assessed by eight experts with different background and two master-student groups. Beside the questions raised before, we wanted to know, according to their personal opinion and experience, what would be the consequence of the implementation of each of the four local scenarios on the ES provision of the lagoon would be. Additional guiding questions for us were: do we get more stable and similar results if the measures are more concrete and realistic? Do comparable, alternative scenarios force evaluators to think more deeply about the scores and will the results become more reliable and stable? How does the number of involved experts affects the variability of scores? What is the optimal number of experts and how does their background affect the results?
Figure
Comparison of the present state of the lagoon with the hypothetical assumption of an implementation of 4 concrete, realistic, alternative scenarios. The assessment was carried out by 8 experts (GS, SD, RF, NS, KR, MI, AZ, MB) and 2 master-student groups (S1, S2). Abbreviations indicate provisioning (P), regulating and maintenance (R) as well as cultural ES (C).
Comparing the scenarios 1–4, the experts in average assumed that the small mussel farm would cause the highest increase in provisioning ES, followed by macrophyte beds. Macrophyte beds were considered to increase the regulating ES most, followed by mussel beds (scenario 2) and with respect to cultural ES, the scenarios are perceived largely similar. The highest increase in the overall ES provision was assumed for macrophyte beds followed by the small mussel farm. However, the number of ES considered by the experts as relevant differed between the scenarios and one expert did not assess scenarios 3 and 4. Therefore, an alternative measure is the average increase for all considered ES. Here as well, the macrophyte beds followed by the mussel farm show the highest value of 1.9 compared to 1.65. However, all scenarios are considered to increase the overall ES provision and are therefore beneficial. These assumed high overall increases in ES provision clearly show that experts relate their assessment to the area covered by the measure and its immediate surrounding and not to the area provided as assessment background.
Figure
While with respect to scenario 2 (mussel beds) only two ES showed a strong disagreement between experts (difference in scores of 6 and more). With respect to scenario 1 (mussel farm), this is the case for 10 ES. Scenario 1 obviously is much more controversial. Therefore, the assessment results can serve as basis for addressing controversial scenarios in more detail, similar to addressing controversial ES.
The high variability of scores, the obvious differences in the perception of scenarios and scale problems are some reasons why even the averaged assessment of all eight experts for each scenario does not reflect more than a tendency and can hardly be used for assessing whether one scenario is more sustainable than another one. Systematic differences between the scenarios are hidden by the variability of scores between experts within a scenario. Lesson learnt is that the ES assessment is more suitable for supporting and guiding a participation and discussion process, rather than delivering crisp results.
During our second workshop with 26 stakeholder on 6th September 2017, several scenarios and possible environmental and socio-economic consequences were presented and discussed in more detail. The ES assessments helped to focus on most important aspects when presenting and discussing the scenarios. Between the expert assessments and the meeting, the spatial location and definition of scenarios were modified and a presentation of the expert assessment itself did not make sense. Therefore, the ES assessment tables and figures were not explicitly used in this workshop. However, based on the experience gained during the workshop discussions, we learnt that time restriction and participants being not familiar with ES concepts, require simplified presentations and visualizations of ES results. To meet this demand ESAT allows an aggregation (averaging) of ES class results to higher hierarchical levels like ES groups and divisions (Figure
More important, in this context was the question, how ES assessments in general could be used in an ICZM and MSP planning context, especially in stakeholder participation. How to extract suitable and simplified information from complex assessments, as presented in Figures
Median scores for each ecosystem service, their relevance (% of evaluators that considered the service as relevant for this scenario) and the resulting importance (score*importance/10).
In our case, most important ES to be addressed in scenario 1 (mussel farm) are animal outputs (P1), animal aquaculture (P3), material for processing (P6), materials for agriculture (P7), non-drinking water (P8), mass flow (R4), pest control (R7), and scientific and educational aspects (C3). The most important ES differ between the scenarios and the number of important ES can be regarded as indication of the complexity of a scenario. While scenario three (pile rows) has only three important ES, scenario 4 (macrophyte beds) has 10. This approach allows selecting a limited number of ES classes to be address during a workshop. During the preparation of a meeting, the results allow to compile background information specifically for the selected important ES. Further, it allows preparing explanations and information for ES classes, where obvious misunderstandings or misperceptions between the experts occurred and where similar problems could be expected during the stakeholder meeting, as well. During the stakeholder workshop, we think that an improved preparation and the focus on important ES would enable a more target-oriented, effective discussion in the restricted timeframe.
Most existing systems for ES assessment have the aim to quantify ES provision. Common to most is, that they require lots of resources, expertise, are time consuming and contain subjective elements. Simplified approaches like the one by Burkhard et al. (
To avoid this problem, the application of ESAT by experts and student groups was merely meant to support planning and management processes by increasing awareness about potential measures, supporting the development of joint future development scenarios, visualizing positive and negative consequences of measures as well as possible interactions between ongoing activities. The view that ES assessment could serve “as a tool to improve cooperation between natural and social sciences, experts, stakeholders, and decision makers” and may support “effective implementation and action” is supported by studies of Jacobs et al. (
In general, the ES assessment provided insights into the sustainability of measures compiled into the scenarios. One could assume that a higher overall provision of services can be considered as a more sustainable situation. However, in detail and for each ES this is questionable. Are higher landings of fish, which are favored by eutrophication, desired and sustainable? Is an increased N-fixation, which counteracts riverine nutrient load reductions and favors eutrophication, positive and sustainable? Further, we have to be aware of the limitation of an ES assessment. Examples are weaknesses in the indicators and their representation of ES classes or that services often are not independent of one another, exhibit complex interactions and generate tradeoffs in the delivery of different services (Lester et al.,
Campagne and Roche (
A major benefit of the assessment with multiple experts is to systematically catch their opinions and perceptions, analyze what is important, and where disagreements exist. It shows where deeper considerations and discussions or clarifications are required. This knowledge can support a guided stakeholder process. However, ESAT would need a simplification to be suitable as a tool during a stakeholder workshop. As it is, it requires scientific and good local knowledge and is too complex and time-consuming.
If local measures are assessed against the framework of the entire lagoon, its effect on ES provision should hardly be measurable. It means a local measure (scenario) should better be assessed against the affected local area. Further, more concrete local measures allow providing a more realistic picture as basis for the assessment. However, we observed that experts, when carrying out an ES assessment, implicitly consider only the potential area covered by a measure and its immediate surrounding and not the area that was provided in the background information as focus area. The ES assessment by expert does not reflect the spatial scale of a measure in relation to the spatial scale of the focus area. Therefore, small scale measures are with respect to their effect on ES changes overestimated.
Based on our data, we are not able to answer the question whether assessments are more stable and show lower standard deviations when scenarios are more concrete, realistic, and local. However, our impression is that our concrete local scenarios helped the experts to develop a clear and joint idea of how a system would look like after a scenario implementation. Further, we think that comparable, alternative scenarios make an assessment easier and more reliable, because it allows experts an easy reiteration of scores after going through all scenarios.
Figure
The potential role of ecosystem service assessment in Integrated Coastal Zone Management (ICZM) and Systems Approach Frameworks (SAF) as well as in Marine Spatial Planning (MSP) (according to HELCOM-VASAB,
In the early ICZM and SAF phases, an ES assessment can provide a basis for a better joint understanding of the ecological-social-economic interactions and dependencies. After the implementation of measures, a repeated ES assessment allows a comparison with the initial assessment and an evaluation, to what degree the measures were successful and reached the objectives. A strong increase in the overall ES provision afterwards could, with the discussed limitations, indicate how sustainable a measure is. In this respect too ESAT is a suitable tool, because it provides a classified semi-quantitative assessment, reflecting changes that took place between two points in time or between alternative scenarios. Advantages of an application are that a more objective, unified view can be obtained and that ecosystem services with different units can be directly compared. The allocation into classes in ESAT means that a concrete value often is not required, but just the knowledge into which class observed changes fall. This allows a relatively fast assessment, compared to other approaches. For the assessment, a broad spectrum of information can be utilized, ranging from concrete data to expert knowledge. Further, the system is spatially expandable and transferable.
Usually MSP focusses on an international, national, or regional spatial scale and provides a framework, while ICZM focusses on a more local to regional spatial scale and deals with more concrete management issues. However, in coastal waters, MSP and ICZM show a strong overlap in objectives and approaches. Scotlands National Marine Plan is a nice recent example for it. It sub-divides the Scottish coastal waters into 12 marine regions that cover major bays, like Clyde, Moray Firth or Forth, and Tay (Scottish Government,
In MSP in the Baltic, it becomes obvious that aspects of ICZM are included in MSP, as well. HELCOM-VASAB (
HELCOM-VASAB (
Our comparative ES assessment by local experts shows that it can serve as a tool to catch the views of an expert on a certain measure or development scenario that it can extract disagreements between expert opinions and misunderstandings related to scenarios or measures, as well as define services of highest priority. The results can be used for guiding expert discussions and for harmonizing views. Further, they are valuable for preparing stakeholder discussions and workshops. However, it requires the involvement of experts with good local knowledge and it seems too complex, knowledge demanding and time-consuming to carry it out with a larger number of stakeholders during one event, like a workshop. It needs to be tested, if simplified ES assessments may make sense and could be used in this respect. Comparative assessments, measuring relative change between different scenarios or measures, are less sensitive to common ES problems e.g., that indicators insufficiently reflect certain services or the high degree of uncertainty associated to ES assessment. However, it requires a thorough preparation, description, and visualization of the alternative scenarios and their spatial extent. We observed that experts, when carrying out an ES assessment for a local measure implicitly consider the immediate surrounding as reference area and not the provided spatial definition. As consequence, expert ES assessment seem scale dependent. Recent developments and examples show that formerly independent concepts, like ICZM and MSP, are largely merged. Today, ICZM ideas and approaches are well reflected and integrated in MSP. This is especially true for public participation and stakeholder involvement. As consequence, a comparative ES assessment can be used in different steps of each concept.
The study does not require an ethics approval according to German regulations or according to the European Commission guideline Ethics for researchers 2017. The experts involved in the ecosystem service assessment got the Ecosystem Service tool via email. In this email they were informed about its purpose and that the results shall become part of a publication. Later, the experts received the final paper via email and were explicitly asked, if they have any objections or comments on the results that reflect their expert assessment (Figure
GS the project leader, developed the article concept, took care of the analyses and did the article writing. MI provided the assessment tool, graphical visualizations and coordinated the expert evaluation. YN carried out the ES assessment in the Oder Lagoon.
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
We like to thank Martynas Bučas, Sven Dahlke, Rene Friedland, Kasimierz Rabski, Nardine Stybel, Anastasija Zaiko for supporting the evaluation and for providing data and information, Simon Paysen for contributing to the graphical visualization and Johanna Schumacher for corrections and comments on the manuscript.