Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Bio-based and Applied Economics BAE Copyright: © 2024 Eichhorn, T., Schaller, L., Hamunen, K., & Runge, T. Open access, article published by Firenze University Press under CC-BY-4.0 License. Firenze University Press | www.fupress.com/bae Citation: Eichhorn, T., Schaller, L., Hamunen, K., & Runge, T. (2024). Explor- ing macro-environmental factors influ- encing adoption of result-based and collective agri-environmental meas- ures: a PESTLE approach based on stakeholder statements. Bio-based and Applied Economics 13(1): 49-71. doi: 10.36253/bae-14489 Received: March 3, 2023 Accepted: August 30, 2023 Published: May 20, 2024 Data Availability Statement: All rel- evant data are within the paper and its Supporting Information files. Competing Interests: The Author(s) declare(s) no conflict of interest. Guest Editors: Stefano Targetti, Andreas Niedermayr, Kati Häfner ORCID TE: 0000-0002-4286-3272 LS: 0000-0002-8313-8798 KH: 0000-0003-2188-782X TR: 0000-0002-8366-4392 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures: a PESTLE approach based on stakeholder statements Theresa Eichhorn1,*, Lena Schaller1, Katri Hamunen2,3, Tania Runge4,* 1 Institute of Agricultural and Forestry Economics (AFO), Department of Economics and Social Sciences, University of Natural Resources and Life Sciences, 1180 Vienna, Austria 2 Natural Resources Institute Finland (LUKE), Bioeconomy and Environment, Yliopis- tokatu 6 B 80100 Joensuu, Finland 3 Stora Enso, Keskuskatu 14, 81100 Kontiolahti, Finland, since August 2022 4 Coordination Unit Climate, Soil, Biodiversity, Thünen Institute, Braunschweig, Germany *Corresponding authors. E-mail: tania.runge@thuenen.de; theresa.eichhorn@haup.ac.at Abstract. To promote more environmentally friendly and cost-effective agri-environ- mental-climate measures in the European Union, novel approaches such as result- based and collective schemes are advocated. This study explores macro-environmental factors facilitating or impeding the adoption of such schemes. By means of a PESTLE analysis and based on a survey of 85 stakeholders from Austria and Germany, we iden- tify major adoption factors within the political, economic, social, technological, legal, and environmental domains. Our results indicate that economic, legal, and social fac- tors are the most influential, with fair payment, clear contract design, and social rela- tions being the most commonly mentioned. Moreover, the unpredictability of nature is a major impediment to the adoption of result-based schemes, while social dynamics and farmers’ attitudes are key factors for a successful implementation of collective con- tracts. Overall, the study provides strategic and practical insights that can support the design and implementation of novel agri-environmental-climate measures under the Common Agricultural Policy. Keywords: agri-environmental contracts, German and Austrian stakeholders, survey, acceptance. JEL Codes: Q15, Q18. 1. INTRODUCTION A more sustainable agricultural system in the European Union (EU) is not only a societal demand, but also an ecological necessity to tackle climate change, counteract biodiversity loss, and protect the EU’s natural resources. By providing public funding, the legal framework of the European Common Agricultural Policy (CAP) has a prominent role in fostering agriculture’s https://doi.org/10.36253/bae-14489 http://www.fupress.com/bae https://doi.org/10.36253/bae-14489 https://orcid.org/0000-0002-4286-3272 https://orcid.org/0000-0002-8313-8798 https://orcid.org/0000-0003-2188-782X https://orcid.org/0000-0002-8366-4392 mailto:tania.runge@thuenen.de mailto:theresa.eichhorn@haup.ac.at 50 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. transition to sustainability. Contracts for Agri-Environ- ment-Climate Measures (AECMs) under the second pil- lar of the CAP are pluriannual commitments, specifical- ly designed to reduce the negative impacts of agriculture on the environment and to mitigate the effects of climate change (European Commission, 2017). The main chal- lenge for AECMs is to ensure an efficient use of funds in addition to delivering the intended environmental effects. AECMs are facing multifaceted criticisms in this regard, such as the lack of empirical evidence supporting their effectiveness, imprecise targeting through insuf- ficient consideration of the heterogeneity of farms and their local circumstances (European Court of Auditors, 2011), as well as missing (financial) incentives for farm- ers to produce the best environmental result through their entrepreneurial activity (WBAE, 2020). New pathways within the design of AECMs are required: approaches such as result-based payments or collective implementation can contribute to a more effective and efficient design of AECMs. Result-based schemes aim at providing environmental improvement through paying for the achievement of specific environ- mental objectives instead of prescribing and compen- sating management practices to farmers. Consequently, farmers can flexibly decide how they want to achieve environmental improvement (Burton & Schwarz, 2013). Collective approaches have the objective to activate land managers to jointly provide agri-environmental-climate public goods (AECPGs), often accompanied by formal- ised cooperation (Runge et al., 2022). In fact, result- based and collective AECMs were eligible for receiving EU co-financing within the past CAP period (2014- 2022), although they have been applied to a very lim- ited extent in the Member States (WBAE, 2020). In the new CAP Strategic Plans Regulation ((EU) 2021/2115), Article 70(5), it is recommended that: “Member States may promote and support collective schemes and result- based payment schemes to encourage farmers or other beneficiaries to deliver a significant enhancement of the quality of the environment at a larger scale or in a measurable way.” (European Parliament and the Coun- cil of the European Union, 2021). Moreover, Recital 71 of Regulation (EU) 2021/2115 states that “[s]upport under payments for management commitments may also be granted in the form of (…) result-based interventions”. Result-based payment schemes are further specifically mentioned in the EU’s biodiversity strategy 2030 (Euro- pean Commission, 2020). With the new emphasis on environmental performance in the CAP, result-based schemes gain importance as a fast-evolving and distinc- tive approach. For illustration, at the time the survey was conducted, a result-based pilot project for nature conservation (biodiversity) was implemented in Austria, which, in the meantime, has been transferred into a fully eligible measure under the Austrian agri-environmental programme for the period 2023-2027 (AMA, 2023). Also in Germany, already in the previous CAP period some Federal States had programmed result-based measures for extensive permanent grassland which now led to the programming of a respective eco-scheme measure targeting flowering species (BLE, 2022). As regards col- lective approaches, they may operate as an extension of many other forms of contracts aiming at a more effec- tive delivery of environmental goods and services, e.g. at a landscape scale. While in the last CAP period only the Netherlands made extensive use of collective implemen- tation for its agri-environmental schemes, in the new programming period (2023-2027) there are also other countries offering collective measures with CAP fund- ing, e.g. Ireland (DAFM, n.d.) and Germany in the Fed- eral State of Brandenburg (MLUK, 2023). Still, despite their potential positive impacts on the environmental effectiveness of AECMs, several factors can hinder the implementation and uptake of collec- tive and result-based approaches. The implementation of result-based schemes may be impeded by (i) elevat- ed administrative and transaction costs compared to action-based systems due to the requirement for result measurement, limited experience, and often small-scale experimental designs (Eichhorn et al., 2022; Schwarz et al., 2008), (ii) difficulties in determining accurate indica- tors for measuring environmental progress (Allen et al., 2014; Burton & Schwarz, 2013); and (iii) potential con- flicts with WTO regulations (Matthews, 2019; Melèn- dez-Ortiz et al., 2009). Factors hampering farmers’ will- ingness to participate are (i) the fear among farmers of lacking sufficient knowledge and skills to successfully perform result-based schemes (Massfeller et al., 2022), (ii) general scepticism towards novel approaches (Stolze et al., 2015), (iii) difficulties in understanding how these contracts work in practice (Wezel et al., 2018), (vi) per- ceived higher risk due to environmental uncertainty, and (vii) no secured remuneration (Derissen & Quaas, 2013). Also collective approaches face hurdles, such as lack of farmers’ willingness to cooperate (Franks, 2011), insuffi- cient coordination (Olivieri et al., 2021), and missing of pre-existing networks or lack of capacity (Prager, 2022). Up to now, the state of knowledge on factors sup- porting or hindering the implementation of novel schemes is largely based either on case studies investi- gating mostly single or few contract solutions in a spe- cific context (e.g. Birge et al., 2017; de Sainte Marie, 2014; Derissen & Latacz-Lohmann, 2013; Prager, 2022; Zabel, 2019), on farmers’ surveys mainly addressing farmers’ 51 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures intention to perform such novel schemes (e.g. Massfeller et al., 2022; van Dijk et al., 2015), or on studies con- centrating on contract related factors, such as contract design features (contract length, payment mode etc.) (Bredemeier et al., 2022; Schulze & Matzdorf, 2023). What is still missing, however, is a structured gath- ering of knowledge about macro-environmental factors influencing the adoption of result-based and collective agri-environmental measures. This is where this study comes in. Macro-environmental factors (such as tech- nological, political, natural factors) refer to external forces and conditions that can have a significant impact on a business or organisation’s operations and perfor- mance and are beyond the control of the business, but can influence its success or failure (Kotler et al., 2018). In our case, we looked at factors, which cannot be influ- enced by farmers directly, but have an impact on farm business decisions. A PESTLE analysis framework was used to identify these macro-environmental factors that promote or hinder the implementation of novel contract types in a holistic, structured and multidisciplinary way (Yüksel, 2012). Our analysis is based on an online survey of 85 stakeholders from Austria and Germany conducted in spring 2021. Within this survey, stakeholders identi- fied a comprehensive set of factors based on six PESTLE categories (Political, Economic, Social, Technological, Legal, and Environmental). The survey targeted a wide range of stakeholders involved in the promotion, design, implementation and control of AECMs, with actors from government agencies, environmental organisations, agri- cultural associations, and private sector companies. By including policy makers/administrators/advisors from local up to national level, we were able to gather strate- gic, as well as practical (phenomenological) knowledge (Raymond et al., 2010). The importance and originality of this study is that it (1) compares two novel contractual AECM approaches in one analysis, (2) strongly focuses on the opinion of stakeholders on external factors, which are much less examined within the agriculture policy literature and (3) provides a structured analysis of the external factors by applying the PESTLE approach, a strategic tool from business analysis, for the first time to study AECMs. 2. DATA AND METHOD Our study aimed at identifying topics potential- ly affecting the adoption of result-based or collective contracts in their operational environment. For this purpose, the PESTLE approach was applied. This stra- tegic planning tool is regularly used to analyse exter- nal macro-environmental factors that may impact an organisation or industry (Gupta, 2013). It is often used in marketing as well as for strategic business decisions (Theobald 2019), however, also in other fields the PES- TLE tool (or its previous model PEST) is gaining impor- tance (Achinas et al., 2019; Gupta, 2013; Rambaree et al., 2021). “PESTLE” represents the initial letters of the six factor categories considered, namely Political, Economic, Social, Technological, Legal, and Environmental factors. The main advantages of the PESTLE approach are, that it (1) enables a holistic, multidisciplinary analysis of the external factors inhibiting or promoting the feasibility of result-based or collective contract solutions before they are put into practice (precondition analysis) (Yüksel, 2012), (2) improves decision-making by systematically providing valuable information (in our case phenomeno- logical and strategic stakeholder knowledge) and thereby encourages strategic thinking (Nitank & Treivdi, 2016) and (3) enhances risk assessment, by identifying poten- tial risks that impact the feasibility and implementation of new types of contracts, thereby helping to take actions to avoid or minimise their effect (Nitank & Treivdi, 2016). 2.1 Questionnaire and data Surveys were conducted in Austria and Germa- ny between end of April and mid-May 20211 to assess stakeholders’ knowledge of external factors impacting the implementation of novel AECMs. The surveys were administered online via LimeSurvey. Potential partici- pants were contacted via email and provided with an online-link to access the survey. We aimed to reach key stakeholders and actors (e.g. involved in the promo- tion, design, implementation and control of AECMs), targeting respondents acting in different roles or hav- ing different areas of interest from both the public and private sector and with different backgrounds, at local, regional, and state levels. In Austria, 80 stakeholders were contacted and 34 questionnaires completed, in Germany, 142 persons were contacted and 51 completed surveys were received. This led to a total of 85 surveys considered in the analysis. Among the stakeholders, due 1 Within the CONSOLE project, a stakeholder survey with PESTLE questions about the result-based contract was carried out in 12 countries. However, only Germany and Austria also conducted a PESTLE survey for collective contracts. In this contribution, we will, therefore, solely refer to the survey results from Germany and Austria. For more information on the PESTLE results for the 12 countries, see Hamunen et al. (2023): Deliverable 3.3 “Synthesis of opinions to implement suggested contract solutions and lessons learned” on the CONSOLE-website at www.console-project.eu. http://www.console-project.eu 52 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. to the still rather experimental nature of such schemes, an overall low level of familiarity with result-based and collective approaches was assumed. Connected to this, and for ensuring some common understanding amongst respondents, a short description of result-based as well as collective contract solutions was included in the sur- vey (see appendix A). The questionnaire was structured into three parts: the first part contained questions on the respondent’s backgrounds, such as affiliation, areas of interest, and responsibilities. The PESTLE approach was then implemented using two blocks of questions (one for result-based and one for collective approaches). The PESTLE block began with the overarching ques- tion of what external factors in the farm environment inhibit or promote the adoption of (a) result-based or (b) collective contracts? For a better understanding, participants were shown the six main PESTLE catego- ries in a figure (see Fig. 1). Additionally, PESTLE cat- egories were described by including short examples/ descriptions: namely 1) environmental factors such as emissions and climate change, 2) political factors such as administration and regulations, 3) economic factors such as purchasing power and income, 4) socio-cultural factors such as demographic development and societal demands, 5) technological factors such as digitalization and innovations, 6) legal factors such as environmental and competition law. The procedure of the survey was then as follows: Starting with result-based and in a second round con- tinuing with collective contracts, participants were asked to (1) name 5 particularly important factors impacting on implementation/adoption, which can’t be influenced by farmers directly, but have an impact on farm deci- sions. As participants were informed about the PESTLE categories beforehand, they certainly kept them in mind when answering, but they were not asked to name the factor nor to assign their responses to any category. (2) Using the symbols “+” or “-”, participants were asked to indicate whether the mentioned factors promote or hin- der implementation. (3) In a final ranking exercise, par- ticipants were then asked to select the most important factor out of the 5 answers they had given. This resulted in 5 responses for each contract type, of which one each was selected as most important for both result-based and collective contracts. There was no word limit for the free answers but participants were asked to answer in short sentences, supplemented by the note: “the more concrete the infor- mation, the better”. In addition, participants were forced to provide five responses, otherwise they were not able to continue the survey. The approach used is illustrated exemplarily in Table 1 in appendix A. 2.2 Data analysis The analysis of the PESTLE results was carried out in excel and by using a three-step approach: First, the factors named by the stakeholders were assigned to the 6 PESTLE categories. This was done separately for the two contract types. (Thereby, statements which referred to the design of the contracts themselves, such as contract terms, duration etc. were assigned to the legal category.2) Second, factors representing a similar content were grouped, examined and subcategories were built. Thereby, a minimum of 3 associated responses were required to form a subcategory. To ensure quality and improve objectivity, the allocation of single factors to the subcategories was conducted via several rounds of exchanges between the Austrian and German researchers involved in the study. Third, codes and short summarising descriptions were assigned to the subcategories, whereas codes represent the PESTLE cat- egory and a consecutive number (e.g. “Ec” for Economic factor and “04” for the fourth subcategory). As several identical factors were mentioned by the stakeholders for both types of contracts, subcategories were summarised under identical descriptions where possible. Differences in subcategory descriptions between the two contract types are underlined in Table 1 for ease of identification and 2 Several contract-related responses, in most cases targeting particular contract features, were given by the stakeholders, therefore the legal category was expanded to include them. Figure 1. PESTLE categories; figure showed in the survey. 53 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures – whenever the descriptions differ partly or completely – abbreviations, CO for collective and RB for result-based, are added to the respective codes (e.g. Ec04RB)). Differ- ences in subcategories are often closely related to the spe- cificities of the two contract solutions under considera- tion.3 When responses couldn’t be assigned to one specific subcategory – either because they highlight interfaces or because they address aspects belonging to two differ- ent subcategories – a double-code was given (e.g. Ec01/ L06), but they were only assigned (and counted) within the first code. For the case that stakeholders’ answers directly repeated the pre-set PESTLE category, (e.g. stake- holders stated that economic factors influence adoption), such responses were counted into the respective PESTLE category, but were not assigned to any subcategory and marked “00”. To reduce the complexity of the interpreta- tion of the external factors we formulated descriptions of the subcategories neutrally or positively. 3. RESULTS 3.1 Descriptive statistics of stakeholder characteristics Among the Austrian respondents, most participating stakeholders (64.7%) were active on a national level. In Germany mainly regionally (56.3%), and nationally active stakeholders (29.2%) participated in the survey. With regard to the field of activity, “agricultural activity” is in first place in both countries, followed by “environmen- tal protection and nature conservation” and “forestry”. In Germany 68.6% and in Austria 60.4% of the surveyed stakeholders are employed in these three fields of activity, whereby multiple answers were possible (Figure 2). While in Austria many participating stakeholders (30%) were representatives of the private sector, a large share of German stakeholders were representing state organisations (22.9%). Furthermore, representatives of public companies, non-governmental organisations, sci- entific institutions, non-profit organisations, associa- tions and civil society took part in the survey. In both countries, “advice or provision of information for farm- ers” was the most important task or field of interest for the participating stakeholders. Thus, 23.3% of the stake- holders in Austria and 21.2% in Germany were active in this area. For 21.6% and 14.7% of stakeholders in Austria and Germany, respectively, this task was also the most important field of activity. In Austria, “support in the design of contract solutions” (21.4%) and “provision of 3 This is most evident for the social category, where the responses of stakeholders were assigned to different headings with one exception (see Table 1). information to the public” (19.4%), were the second and third most important areas of activity, both of which were selected by 20.6% of the respondents. Also, in Ger- many, these tasks were named second and third most frequently, however in reverse order (for more details on stakeholder characteristics please see Appendix B). 4.2 PESTLE Results For result-based contracts, a total of 376 responses could be assigned to the six PESTLE categories, of which 147 came from Austrian and 229 from German stake- holders. For collective contracts, a total of 3334 responses could be assigned to the six categories (131 from Aus- tria, 202 from Germany). Table 1 summarises the main findings: The title of each section represents the PES- TLE category. Subcategories (codes and descriptions) are assigned to each category, with differences between result-based and collective contract types being under- lined. For each category, between four and six subcat- egories have been formed. Table 1 also serves as basis for the results presented in chapters 4.2.1 and 4.2.2. A more detailed description of the results is provided in Table 4 in Appendix C, which, in addition to the descriptions for all subcategories, also indicates the frequency of mentions and the factors selected in the ranking exercise as most important. In addition, it is indicated if the fac- tor mentioned was marked as promoting or hindering. Figure 3 shows how the factors identified for result- based and collective contracts are distributed across the six categories and among the two countries. The total number of responses per country and contract type is 100%, distributed across the six PESTLE categories. 4 The different amount of answers between collective and result-based schemes can be explained by the fact that only those factors which can’t be influenced by farmers themselves while having an impact on farm decisions were included. Furthermore, within the collective part (the third part of the survey) a few participants decided to just write “no additional idea/answer” into the field. 0% 10% 20% 30% 40% 50% Food sector Training and advice Municipal development Water management Research and development Public administration Land use policy and planning Forestry Environmental protection Agriculture Germany Austria Figure 2. Stakeholders’ fields of activity in Austria and Germany. 54 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. In general, the figure reveals that stakeholders from both countries have given similar preferences to certain PESTLE categories per contract type, resulting in a simi- lar distribution of the responses. Results also show that general differences exist between the importance of specific PESTLE categories Table 1. PESTLE categories and subcategories built based on the survey responses POLITICAL ECONOMICAL P01 Advice and support to farmers for implementation Ec01 Payment calculation, appropriate remuneration for participation in the contracts P02 Political will to support farmers in delivering environmental services Ec02RB Availability of sufficient funding for contract payments Ec02CO Availability of sufficient funding for contract payments and for coordination / measure planning P03 Low level of bureaucracy and administrative burden Ec03 Income / revenue security and little financial risk for farmers P04 Longer-term stable political framework Ec04RB Reliability of demand for and value chains to sell the agricultural products Ec04CO Sharing of remuneration between farmers when participating in the contracts P05 Assistance in contract implementation by qualified authorities and intermediaries Ec05 New income opportunities for farmers by participating in contracts Ec06 Limited time and financial effort for implementation SOCIAL TECHNOLOGICAL S01 Social appreciation, recognition for the environmental services provided by farmers T01RB T01CO Existence of appropriate technologies for measuring the results achieved Existence of appropriate technologies for measuring the achievements S02RB SO2CO Attitudes of farmers, consideration of cultural norms and traditions Attitudes of farmers and sensitivities of farmers T02 Determination of appropriate indicators for monitoring S03RB S03CO Societal and consumers’ demand and interest for environmental services Involvement of further stakeholders (interest groups, ...) T03 Easy to implement and no time-consuming monitoring / documentation S04RB S04CO Willingness to work together (interest groups, neighbours, farmers’ associations) Content of cooperation T04RB T04CO Access to technology / machinery, technical practicability Access to technology / machinery, distribution of work S05RB S05CO Farmers’ awareness of environmental topics and knowledge Farmers’ awareness of environmental topics and knowledge exchange T05RB Sufficient knowledge about the environmental effects of the farming practices S06CO Group dynamics LEGAL ENVIRONMENTAL L01RB L01CO Contract characteristics: voluntariness, flexibility, clear goal(s), possibility of influencing Contract characteristics: voluntariness, flexibility, clear goal(s), entry and exit conditions, responsibilities En01 Impacts of climate change and perceived need for action L02RB L02CO Simplicity and comprehensibility of the contract Conditions of participation for farmers (number, setting) En02 Unpredictability of nature and the limited ability of farmers to have an influence on it L03 Clarity and consistency of the legal framework of the contract En03 Spatial and regional environmental conditions L04 Compatibility of the contract with existing laws, programs and EU policies En04 Interplay of action and impacts on nature and environment L05 Practical achievability of the contract goals L06 Transparent and comprehensible controls and sanctions Note: PESTLE category = title; Subcategories including codes (category and a consecutive number e.g. Ec01, if different: CO= col- lective; RB= result-based, deviating wording is underlined). 55 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures with respect to specific contract types: For result-based contracts, most stakeholder responses belonging to this contract type fall into the legal category, with 25.8% for Germany, respectively 29.3% for Austria. The economic category with around 20% is placed second, social third and political fourth. For collective contract solutions, stakeholder responses belonging to the social category take the big- gest share with 35.5% of the responses from Germany, respectively 33.1% from Austria, followed by the legal category on the second, and economic on the third place. Differences between both countries amongst cat- egories become obvious only for the political category in respect to collective contracts, which is considered as more important by German than by Austrian stake- holders. Also, for collective contracts concerning the technological category some variance occurs: here Ger- man stakeholders evaluate technological aspects as less important than the Austrian respondents do. When looking at the responses which were ranked as most important and their distribution amongst the six PESTLE categories, differences between the two con- tract types become even more explicit (see Figure 4). For result-based contracts, the economic category received the highest number of responses marked as “most important”. 34% of the German and 31.3% of the Austrian stakehold- ers selected a response belonging to the economic catego- ry. For result-based contracts, the legal category follows on the second place with 24% of the German, respectively 25% of the Austrian responses ranked first. In sum, more than 50% of the responses ranked as most important for result-based contracts belong to those two categories. For the collective contract the dominance of the social cate- gory is outstanding, with 54.2% of the answers from Ger- many and 62.1% of the Austrian answers ranked as most important. At a great distance follows the economic cat- egory with less than 20% in both countries. 4.2.1 External factors in result-based contracts In the following section, all six PESTLE categories impacting on result-based contracts are described, fol- lowing the PESTLE order5. However, since economic, legal and social factors were mentioned most frequently for result-based contracts and since these are also the factors differing most when comparing the responses for result-based and collective contract solutions, more emphasis is put on these factors. An overview of the most mentioned subcategories in result-based contracts can be found in Table 2 at the end of this sub-chapter. – Political factors impacting result-based contracts In the political PESTLE category for result-based contracts, the subcategory low level of bureaucracy and administrative burden (P03) includes 11 indi- vidual stakeholder statements. Within these 11 state- ments, the factors “administrative effort”6 and “bureau- cracy” have been mentioned four times each. One stakeholder, for example, expressed concerns that result-based contracts would lead to an increase in bureaucracy due to the customization required for each contract to match the specific environment. Nine 5 Due to the very similar response behaviour of the stakeholders, an evaluation in chapter 4.2.1 and 4.2.2 is carried out without differentiation between the two countries. However, where there are visible differences in response behaviour between Austria and Germany, this is addressed and highlighted in the result section. 6 All translations of the responses from German to English by the authors. Figure 3. Breakdown of all stakeholder responses to the six PESTLE categories per contract type and country. Note: The six PESTLE cat- egories for each contract type by country sum up to 100%. Figure 4. Breakdown of the responses ranked as most important by the stakeholders to the six PESTLE categories per contract type and country. Note: The six PESTLE categories for each contract type by country sum up to 100%. 56 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. statements were summarised under the subcategory of political will to support farmers in delivering envi- ronmental services (P02). One stakeholder stated that the “contents of the contracts must have political con- sensus”. In the third place, with 8 statements, the sub- category of advice and support to farmers for imple- mentation (P01) emerged. Advice, including technical guidance, and access to training are considered pro- moting factors. One stakeholder for example stated the need for “support in understanding what is worth pro- tecting and why”. – Economic factors impacting result-based contracts In the economic PESTLE category, the subcategory of payment calculation, appropriate remuneration for participation in the contracts (Ec01) was built on a sum of 28 statements, representing the subcategory based on most stakeholder responses within the whole PESTLE analysis for result-based contracts. Also, for the factors ranked as most important, this subcategory received the highest number (12 mentions). The payment level itself has been mentioned several times as an important fac- tor for participation (“It must pay off for the farmer”). At the same time, it was critically noted that the payment calculation is “demanding”. Also costs and time required for the payment calculation have been mentioned as economic factors. Listed as encouraging was that result- based contracts allow for a “reward for higher environ- mental standards” and also that the “payments are posi- tively dependent on management/commitment”. Specifi- cally, a “ fair design of payment” is called for, and this was made even more explicit in the response that “ fair compensation creates acceptance and reliability.” In this sense, one stakeholder suggests a combination of “basic remuneration plus performance payment (participation + success)”, while another participant advocates “grada- tions in the achievement of intermediate targets”. In the economic category, 12 statements could be assigned to the subcategory of new income opportunities for farm- ers by participating in contracts (Ec05) placed second. On the third place, out of 10 statements, the subcategory income / revenue security and little financial risk for farmers (Ec03) emerged. While the former subcategory focuses on economic opportunities, the latter focuses on the risks associated with result-based contracts. Sev- eral times, economic profitability was mentioned in Ec05, with seven factors being ranked as most impor- tant under this subcategory. Thereby, the environmental performance to be provided was also considered. One statement explained that “It must be possible to realize a financial and ecological profit that can be economical- ly influenced on the basis of entrepreneurial decisions.” Price fluctuations or the price level of the cultivated crops, but also production-related mistakes are men- tioned as factors that can put at risk the income for par- ticipating farmers. – Social factors impacting result-based contracts In the social PESTLE category compiling factors with relevance for result-based contracts, the subcategory of social appreciation, recognition for the environmental services provided by farmers (S01) is based on 20 state- ments. Thus, it became clear that public perception or appreciation is classified as promoting. One statement in this respect exclaimed “noticeable (!) social recognition” as a factor, and another marked that “the performance should be made visible to the people”. In addition, there were also a few sceptical voices about result-based con- tracts in the social context namely that “The more dif- ferentiated the requirements are, the more difficult it is to argue ‘externally’ the funding level or to explain to the consumer what exactly is being done”. The importance of outreach to improve social recognition was highlighted in four responses. For example, one statement said that “society needs to be made aware of this important work of the farmer through the media”. 15 further statements have been compiled under the subcategory of farmers’ aware- ness of environmental topics and knowledge (S05RB). As promoting factors, farmers’ own initiative and respon- sibility in result-based contracts have been mentioned: For example, one statement was that “ farmers are granted expertise/partners in nature conservation”. In the social category, the attitudes of farmers, consideration of cul- tural norms and traditions (SO2RB), but also the will- ingness to work together (interest groups, neighbours, farmers’ associations) (SO4RB) and the societal and con- sumers’ demand and interest for environmental services (SO3RB) further emerged from the stakeholders’ answers. Even if result-based contracts are implemented on the level of individual farms, peer pressure or social pres- sure from other farmers can have both positive and nega- tive effects. An answer expressing positive impacts in this respect was for example that “experience of other farmers with result-oriented contracts influences the acceptance and willingness to participate of interested parties”. – Technological factors impacting result-based contracts In the technological PESTLE category for result- based contracts, existence of appropriate technolo- gies for measuring the results achieved (T01RB) has emerged as the only subcategory addressed more fre- quently, assembling 13 responses. Participants suggest- ed new technologies, such as drones, remote sensing or aerial photography. One answer says for example that 57 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures “a possible documentation of results by the farmer could be facilitated by an app”, another recognizes that “by all means use digitalization for knowledge creation and control, certainly motivates the majority”. In the techno- logical category, reliability of outcome measurement, the choice of easily measurable indicators, and the availabil- ity of technology, both for monitoring and for measure implementation are further crucial factors. One sugges- tion in this respect was that “easy-to-use tools should be available for documentation/monitoring”. Another answer going in the same direction by telling that, “it is also important that technological means are promot- ed and made available to farmers through appropriate knowledge transfer on advantages and disadvantages”. Opportunities are further seen in digitalization and the use of special technology. – Legal factors impacting result-based contracts Within the legal PESTLE category, the subcategory of contract characteristics (L01) was highly important for the stakeholders, being represented by 22 statements. Here, voluntariness, flexibility and clear goals were named as promoting factors. The importance of achievable goals or a form of co-determination in the setting of goals becomes clear with these two answers: “objective benefit of the goals should be evident to the contracting parties” and “if farmers can influence the selection of the desired ecological goals, this promotes acceptance”. Also, “quanti- tative and qualitative specification of the results (criteria, indicators)” is seen positively. This requirement is closely related to suitable technical feasibility and was coded twice accordingly (L01RB/T02). Another subcategory within the legal PESTLE category, which was built on 20 statements is transparent and comprehensible controls and sanctions (L06). While sanctioning is seen as a factor hindering the implementation of result-based contracts, controls and controllability were rated both positively and negatively. Annual fluctuations, especially with regard to biodiversity, insects, etc., are seen as critical for the assess- ment of results. In this regard, one question raised was “What happens if, for example, no species settle/no results can be shown?” As possible solutions, “easy to control (simple success criteria)” as well as “conciliation in case of differing assessments of success” were mentioned. The third important subcategory within the legal category, with 18 statements as basis, is clarity and consistency of the legal framework of the contract (L03). “Legal certain- ty” and “planning security” were mentioned particularly often with 6, respectively 4 responses. The 2 subcatego- ries of compatibility of the contract with existing laws, programmes and EU policies (L04) and practical achiev- ability of the contract goals (L05) were built on 14 and 12 statements, respectively. In connection with legal regula- tions, restrictions due to requirements from the fertilizer regulation and the prohibition of double funding were mentioned. Demands such as “achieving the agreed results Table 2. Result-based contracts – subcategories with at least ten mentions. Code Subcategory Sum + - 1. P Ec S T L En 1 Ec01 Payment calculation, appropriate remuneration for participation in the contracts 28 21 7 12 2 En02 Unpredictability of nature and the limited ability of farmers to have an influence on it 27 3 24 8 3 L01 Contract characteristics: voluntariness, flexibility, clear goal(s), possibility of influencing 22 21 1 4 4 L06 Transparent and comprehensible controls and sanctions 20 8 12 3 5 S01 Social appreciation, recognition for the environmental services provided by farmers 20 17 3 2 6 L03 Clarity and consistency of the legal framework of the contract 18 12 6 4 7 S05 Farmers’ awareness of environmental topics and knowledge 15 14 1 4 8 L04 Compatibility of the contract with existing laws, programmes and EU policies 14 5 9 3 9 T01 Existence of appropriate technologies for measuring the results achieved 13 11 2 2 10 Ec05 New income opportunities for farmers by participating in contracts 12 10 2 7 11 L05 Practical achievability of the contract goals 12 10 2 4 12 P03 Low level of bureaucracy and administrative burden 11 4 7 3 13 Ec03 Income / revenue security and little financial risk for farmers 10 1 9 1 Sum = number of responses in total assigned under this heading/factor; + = responses framed positively as well as assigned as promoting factor; – = responses framed negatively as well as assigned as hindering factor; 1. = number of responses, stated as most important factor for result-based contracts by stakeholders in the survey = ranking exercise; categories: P = Political ; Ec = Economical; S = Social; T = Tech- nological; L = Legal; En = Environmental. 58 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. must not lead to sovereign protection!” or “no obligation to continue after termination of the contract” point to exist- ing legal uncertainties in ecological successes. – Environmental factors impacting result-based contracts The environmental PESTLE category assembles the second most statements for result-based contracts under the subcategory of unpredictability of nature and the limited ability of farmers to have an influence on it (En02). This subcategory was built based on 27 state- ments in total, and 8 statements ranked as most impor- tant. Weather conditions and extreme weather events such as lack of precipitation have been mentioned, which can negatively influence the results and thus jeopardize the success of the measures implemented. Also addressed are uncertainties in natural processes, population trends, as well as already good ecological status as a baseline, which can make further environmental improvements difficult. From the point of view of the stakeholders, dealing with these uncertainties is crucial for a successful implementation of result-based contracts. This became clear e.g. in the demand that “in case of extreme weather, the farmer must also be compensated” (En02 / Ec01) or in the question on “liability in case of non-achievement of goals (capricious weather, ...)” (En02 / L06). The double coding indicates that regulations in this regard are highly relevant from an economic as well as a legal perspective. The subcategory of impacts of climate change and per- ceived need for action takes a special position within the environmental PESTLE category (En01). Climate change was explicitly mentioned as a factor relevant for result-based schemes, so one statement was for example that “effects of climate change are felt by every farmer and increase the willingness to deal with the topic of soil”. One stakeholder commented that “paid environmental or eco- system services are farm diversification and increase resil- ience in climate change.” 4.2.2 External factors in collective contracts For collective contracts, we again structured the results along the six PESTLE categories. A clear domi- nance of social factors became obvious for collective contracts. Also, legal and economic factors were men- tioned often, therefore we describe these three categories in more detail. Table 3 at the end of the chapter provides an overview of the twelve subcategories with most state- ments assigned to collective contracts. – Political factors impacting collective contracts As in the case of result-based contracts, within the political PESTLE category for collective contracts, the subcategory low level of bureaucracy and administra- tive burden (P03) was the only category to be built on the basis of more than 10 stakeholder statements. Hereby arguments concerning efficiency and effort have been raised: Stakeholders mention that in collective con- tract solutions “control effort for [the] authority could be reduced”, and that “public admin costs are reduced and increased within the group, but more efficient”. Also men- tioned positively was that “administration has fewer indi- vidual applications to deal with”. However, there are also a number of responses indicating the risk of even more bureaucracy for this contract type. This shows that the contractual arrangement will be decisive for the amount of bureaucracy. In the ranking process two responses within this category have been selected as most impor- tant, namely that “good information in advance about the measure, its practical implementation and about ecological bases” needs to be provided (within subcategory P01) and “political will must be present” (within subcategory P02). – Economic factors impacting collective contracts The most important subcategory within the eco- nomic PESTLE category impacting on the adoption of collective approaches is the fair sharing of remunera- tion between farmers when participating in the con- tracts (Ec04CO): Many statements take up the issue of fair payment distribution and how this can be organ- ized. One stakeholder for example raised the question “how is the compensation and the distribution within the group realised?” and one respondent put his/her fears in a nutshell as follows: “distribution of payment – when it comes to money, friendship ceases”. Other stakeholders suggested a “distribution formula” as well as the “distri- bution of money via third parties” or a “pre-allocation of the remuneration” in order to avoid disputes. But there were also comments regarding how to consider differ- ences in cost structure amongst participating farms and how to distribute money fairly. Besides fair remu- neration, two further economic aspects, summarised in the subcategories payment calculation, appropri- ate remuneration for participation in the contracts (Ec01) (13 statements) and new income opportunities for farmers by participating in contracts (Ec05) (11 statements) revealed to be of high importance for suc- cessful collective contracts. Of the 13 answers on pay- ment calculation, 9 came from Austria, one of the rare situations with a clear country difference in the response behaviour. As in the case of the result-based contracts, statements on the payment amount and “proper finan- cial incentive” dominate; there is also the demand for “payment also for the additional organisational effort” in the case of collective measures. In the ranking process, 59 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures for collective contracts 16 statements in the economic category were selected as most important, while for the result-based contracts 28 statements in the economic category were chosen. Amongst the most important fac- tors were the requests for “financing a coordination func- tion” and “coordination must not be at the expense of remuneration”. – Social factors impacting collective contracts In the ranking of all PESTLE categories, for collec- tive contracts social subcategories take the second to fourth place. This clearly demonstrates the outstanding relevance given to them by the stakeholders inquired (see Table 3). 30 statements have been assigned to the subcategory of attitudes and sensitivities of farmers (S02CO). Moreover, 13 stakeholders ranked statements in this subcategory as the most important, bringing it in the first position. For example, a good neighbourly rela- tionship, “past experiences of cooperation between farm- ers” and the “alliance of farmers with the same goal” are mentioned as conducive. However, a number of inhibit- ing factors are also mentioned. For example, the willing- ness of farmers to cooperate and exchange is doubted, one answer in this respect was that a “ farmer is rather a loner”. But also, envy and jealousy between farmers or “difficulty in finding a group” have been mentioned. Trust between farmers, fairness, willingness to commu- nicate and the ability to work in a team are mentioned as prerequisites for the successful implementation of col- lective contract solutions. The subcategory of content of cooperation (S04CO) follows in third place with 29 statements, of which the positive mentions slightly out- weigh with 16 answers. 10 responses within this sub- category were ranked as most important by the stake- holders. Particularly the setting of common goals was mentioned several times as an important success factor, thereby e.g. two answers stated that “the group focuses on a few or a common goal” and “ farmers can achieve this effectively and on a large scale as a group with a com- mon goal”. Coordination and communication efforts within the “collective” are seen as obstacles to be over- come, answers underlying this statement are e.g. that a “common basis for discussion between all participants at equal level” is needed, or, formulated differently, that there must be “no dependencies / power imbalances with- in the group”. An “equitable distribution of duties and benefits in the collective” is seen as a success factor and it was suggested to offer “mediation and conflict resolu- tion training”. It was noted that “if collective structures already exist, this simplifies the process”. The possibil- ity of exchanging experiences among each other is seen positively, but also that in collective contracts syner- gies can arise. Group dynamics (S06CO) were consid- ered as a separate subcategory, as 21 responses explicitly refer to it, 9 of which were ranked as most important. In total, this term was used six times by the respond- ents, of which it was negatively evaluated five times. For example, group dynamics are described as a “stumbling block” and there is a fear that solutions are endangered “if individual participants crossfire”; there are also ques- tions about how to deal with social conflicts within the group as well as with “difficult characters”. Specifi- cally addressed is the concern that “individual interests or political opinions of group members differ greatly or diverge” and “ free-riding” is mentioned as a further problem. Promoting factors are if the “group [is] already sufficiently long established”, the presence of group mem- bers who have an “exemplary character for other partici- pants” and the emergence of a “we-feeling”. In the case of the subcategory of social appreciation, recognition for the environmental services provided by farmers (S01), with one exception, only promoting factors are men- tioned. One statement explains that “as a group it is eas- ier to present interests to the outside world (public, poli- tics)”, and also the “example setting for third parties out- side the group” is mentioned. For the success of collec- tive contracts, the involvement of further stakeholders (S03) besides farmers is important. Hereby, advisors and agricultural associations were explicitly mentioned, but also cooperation with environmental administrations/ authorities was suggested. With regard to the involve- ment of nature conservation associations, answers were more reserved with a “distrust of environmentalists” being mentioned and the potential for conflict that this may entail. – Technological factors impacting collective contracts Within the technological PESTLE category, even though none of its subcategories was amongst the top twelve, stakeholders raised a number of concrete sugges- tions: For example, “technical devices that facilitate the application or the implementation of measures” or tech- nical solutions for the “clear breakdown of services and rewards” and for the “verifiability of results and alloca- tion to individual farmers” are seen as beneficial. One stakeholder calls for “suitable (digital) tools for the docu- mentation of the measures implemented”. Also, the use of GPS “can positively influence coordination within the collective”. – Legal factors impacting collective contracts For collective contracts, amongst the legal PESTLE category, the subcategory contract characteristics: vol- untariness, flexibility, clear goal(s), entry and exit 60 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. conditions, responsibilities (L01CO) was in first place with 34 stakeholder statements belonging to it. The contractual regulation of responsibilities and account- abilities, as well as clear rules and a clear distribution of tasks are named as promoting factors. Stakeholders ask questions such as “how is the contract with the agen- cy structured?”, “who selects criteria for performance”, “who evaluates which achievements with distribution of funds?”, “how is the division of labour organized within the group”, or “who is liable if an individual from the collective fails to perform”. Several answers in this sub- category refer to the legal protection in case of changes in the group composition or if one or more participants want to leave. The necessity of a clear formulation of goals is further stated, also that this is more difficult in the case of collective contracts as it requires “contractu- al clarification between farmers”. The risk for disputes is mentioned as an inhibiting factor, either “in the in the contract negotiations”, or because of “unfulfilled require- ments of individuals” or regarding “the payout”; in this regard, there is a suggestion to establish an “internal control system in the collective”. 14 stakeholder state- ments built the legal subcategory of clarity and consist- ency of the legal framework of the contract (L03). As with result-based contracts, also with collective solu- tions legal and planning certainty are addressed, and there is the concern about “legal dispute(s) when draft- ing the contract.” In addition, 10 statements were addressed to the subcategory of transparent and comprehensible con- trols and sanctions (L06), classified under legal aspects even though being relevant from economic perspec- tive too. Central is thereby the question of “how is the cooperation regulated, what happens if repayments would have to be made”. In the same direction goes the state- ment that the “collective must be secured in terms of a control and sanction system”. There is also concern about the “risk of sanctions or assumption of liability for mis- takes made by other farms”. At the same time, another stakeholder points to an advantage of collective con- tracts with the answer “no feeling as an individual to be at the mercy of the control system”. – Environmental factors impacting collective contract solutions In the environmental PESTLE category for collective contracts, in contrast to the result-based contracts, no subcategory made it into the top twelve. Beneficial fac- tors addressed in this category are however the “higher effectiveness of measures” and that “regional concerns can be better addressed”. Mentioned is moreover the possibil- ity for implementing measures in a larger area through collective contracts and that the “integration of struc- tures such as wind belts etc. [is] more easily possible”. Qualifying, one response reads “suitable only for meas- ures that have a landscape effect and not just an area- specific effect.” One comment is “if it is clear what char- acterises a region and what is worth protecting, everyone is on board”. Table 3. Collective contract solutions – subcategories with at least ten mentions. Code Subcategory Sum + - 1. P Ec S T L En 1 L01 Contract characteristics: voluntariness, flexibility, clear goal(s), entry and exit conditions, responsibilities 34 18 16 4 2 S02 Attitudes and sensitivities of farmers 30 9 21 13 3 S04 Content of cooperation 29 16 13 10 4 S06 Group dynamics 21 8 13 9 5 Ec04 Sharing of remuneration between farmers when participating in the contracts 18 3 15 4 6 L03 Clarity and consistency of the legal framework of the contract 14 8 6 3 7 Ec01 Payment calculation, appropriate remuneration for participation in the contracts 13 11 2 1 8 Ec05 New income opportunities for farmers by participating in contracts 11 10 1 2 9 S03 Involvement of further stakeholders (interest groups, ..) 10 8 2 2 10 S01 Social appreciation, recognition for the environmental services provided by farmers 10 9 1 3 11 P03 Low level of bureaucracy and administrative burden 10 4 6 3 12 L06 Transparent and comprehensible controls and sanctions 10 5 5 0 Sum = number of responses in total assigned under this subcategory/factor; + = responses framed positively as well as assigned as promot- ing factor; – = responses framed negatively as well as assigned as hindering factor; 1. = number of responses, stated as most important factor for collective contracts by stakeholders in the survey = ranking exercise; categories: P = Political ; Ec = Economical; S = Social; T = Technological; L = Legal; En = Environmental. 61 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures 5. DISCUSSION AND CONCLUSIONS This work addresses macro-environmental factors impacting on the success of result-based contracts, and of contracts fostering collective implementation, both aiming for an improved provision of agri-environmen- tal-climate public goods. So far, to the knowledge of the authors, only little literature can be found on hindering or facilitating external factors affecting the implementa- tion of these novel AECMs. Therefore, this study aimed to investigate political, economic, social, technological, legal as well as environmental factors by using the PES- TLE approach. The analysis was based on a stakeholder survey conducted in Germany and Austria. The application of the PESTLE approach has demon- strated its efficacy as a valuable tool for structuring and classifying the varied responses elicited from a diverse set of stakeholders. It could be demonstrated that stake- holders possess the ability to provide input within the established categories/factors. Nevertheless, the practical application of the PESTLE approach within this particu- lar context has encountered certain limitations. First, it is important to recognize that the quality of the results obtained is highly depending on which stakeholders finally participate in the survey. Despite successfully engaging a significant number of stakeholders in both countries, it is important to note that the sample is not representative in terms of their regional level (e.g., with a bias towards regional and national stakeholders), back- ground organisation, and other stakeholder character- istics (see Appendix B). Second, our study specifically addressed factors that are beyond the direct control of farmers, yet exert influence on their business decisions. Under the CAP, AECM contracts are standardized and not subject to bilateral negotiations, thereby restricting individual contractors from negotiating specific elements of contract design within the legal framework. Conse- quently, various “internal” design elements arise within the “external” legal category (e.g. L01 contract charac- teristics), rendering the precise differentiation between “external” and “internal” factors somewhat challenging. Third, a lack of clear demarcation between external and internal factors was observed within the social category. While there are distinct external social factors such as social appreciation, this category also encompasses sub- groups that can be regarded as internal, namely farmers’ awareness and attitudes. Taking a broader perspective, it can be argued that the external social environment plays a pivotal role in shaping and influencing farmers’ aware- ness and attitudes. Fourth, in the case of collective con- tracts, the introduction of a third social interaction in the form of the “group dynamics” of course represents a significant differentiation within the subcategories of collective and results-oriented contracts (e.g. S04CO “content of cooperation” and S06CO “Group dynam- ics” versus S04RB “willingness to work together (interest groups, neighbours, farmers’ associations”). This has led to significant distinctions within the social category for result-based and collective contract solutions and to dif- ferent subcategory headings, with one exception. The results of this analysis shall now be discussed along the main external factors revealed for both con- tract types (see table 2 and 3). Starting with the fac- tors/subcategories that exhibit congruence across both contract types, we will conclude with those factors that demonstrate the most significant variations in terms of statements and subcategories. Navigating uncertainty in the new CAP period – political factors During our PESTLE analysis, conducted in the midst of the new Common Agricultural Policy (CAP) strategic planning discussions, it became evident that the upcoming CAP period has resulted in considerable uncertainty among German and Austrian stakeholders. The respondents frequently highlighted the importance of having a clear and consistent legal framework for the contracts, as well as ensuring that the contracts are com- patible with existing laws, programs, and EU policies. Specifically, legal certainty, planning security, ongoing legal changes, and the potential issue of double funding were identified as key concerns. Fair payment structures and new income opportunities – economic factors The economic category plays a crucial role in both result-based and collective schemes. The appropriate remuneration for participation and the potential for new income opportunities are perceived highly positive and important for farmers’ engagement among stake- holders in both types of contracts. AECMs represent- ing an additional income opportunity is a well-known motivational factor among famers in classical schemes, but was also already confirmed in novel schemes (e.g. Barghusen et al., 2021). The calculation of payments, however, is a concern for stakeholders in result-based contracts due to the challenge of compensating appro- priately for the environmental improvements achieved. Literature recommends tailoring the payment structure to the environmental objective and the level of partici- pation desired (Herzon et al., 2018). Stakeholders suggest 62 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. incorporating intermediate targets or offering graduated payments for various levels of success. The importance of fair economic incentives in introducing existing and novel contract types is widely acknowledged (Lastra-Bra- vo et al., 2015; Pavlis et al., 2016; Ruto & Garrod, 2009; Wilson & Hart, 2000), and should also cover risks in the introductory phase (Prager & Posthumus, 2010). In col- lective contracts the fair distribution of payments in line with the management efforts is particularly relevant for adoption. In addition, a “collective bonus” could serve as a reward for the additional effort of the farmers to inte- grate their business orientation into a specialised (collec- tive) concept (DVL, 2021). Beyond money: the power of social recognition in incentiv- izing environmental services by farmers – social factors In addition to economic incentives, social apprecia- tion and recognition for the environmental services pro- vided by farmers are perceived as strong promoting fac- tors in both result-based and collective schemes. Farm- ers react to societal demand when delivering AECPGs, but this usually goes along with higher / additional workload. Making farmers’ work visible, for example through media or public relations work, helps improv- ing the image of agriculture and is perceived as a strong promoting external factor. Result-based schemes, in addition, provide an opportunity to report clear envi- ronmental results to society. Furthermore, farmers themselves have also emphasized the importance of social recognition (Russi et al., 2016), which was mir- rored by our stakeholder responses. Stakeholders expressed concerns about specific contract design elements, with clearly differentiated requirements for result-based and collective contracts – legal factors In line with the reticence and concerns expressed by stakeholders, there are recommendations pertaining to the legal aspects of contract design. While in result- based schemes, voluntariness, flexibility, and clear goals are key aspects, for collective schemes, entry and exit conditions as well as responsibility issues are particu- larly relevant. This finding is consistent with previous research suggesting that collective incentive schemes should have clearly defined participation criteria and organisational structures (Barghusen et al., 2021; Franks, 2011). Additionally, stakeholders emphasized the impor- tance of fair distribution of remuneration among farm- ers participating in collective schemes, and a third-party distribution system or pre-allocation of the remunera- tion were suggested as means to increase trust and fair- ness. The legal category also revealed that stakehold- ers call for legal protection in case of changes in group composition. In literature, result-based schemes promote higher flexibility in farmers’ management decisions (de Sainte Marie, 2014; Klimek et al., 2008; Matzdorf & Lor- enz, 2010; Russi et al., 2016; Sabatier et al., 2012), and this was also deemed important by the stakeholders. In addition, result-based schemes require clear targeting, which involves a precise definition of the results that farmers can achieve and the ability to influence them, according to our stakeholders. Nature’s unpredictability poses a significant hindrance to result-based agri-environmental schemes – environmental factors According to the results of our study, the unpredict- ability of nature and the limited influence of farmers on it emerged as a major hindering external factor for the adoption of result-based contracts. This issue is very spe- cific to result-based schemes, where linking payments to measurable environmental improvements makes the influence of nature more salient, particularly in direct comparison to the dominating action-based payments. Also, for collective contract solutions it was seen as less relevant. Already existing literature has identified this issue as a potential risk factor for result-based payments (de Snoo et al., 2013; Derissen & Quaas, 2013; Olivieri et al., 2021; Wezel et al., 2018), our study provides evidence of its significance in stakeholders’ perception: In the survey, stakeholders identified and mentioned various environmental factors that can influence the ecological outcome, including extreme weather events, seasonal/ regional weather phenomena/conditions, shifts in animal and plant communities, climatic conditions, soil con- ditions, and the current ecological status. Thus, stake- holders acknowledge that the achievement of ecological results is not solely in the hands of farmers. Social dynamics and farmer attitudes: Key factors in collec- tive contracts – social factors For collective contracts, social relationships between participating farmers and the related difficulties are dominating stakeholders’ perceptions when thinking about hindering and facilitating external factors. This resulted in “attitudes and sensitivities of farmers” being the aspect with the most statements, and it also ranked first in the list of factors rated as most important. Farm- er-to-farmer relationships and the social dimension of 63 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures such engagements were frequently mentioned. Promot- ing factors included past positive experiences of cooper- ation between farmers, good neighbourly relations, and an existing basis of trust. Hindering factors included a lack of willingness to cooperate, jealousy, traditions, and the perception of farmers as “loners”. The stakeholders’ predominantly pessimistic view of farmers’ willingness to cooperate is also mirrored in a study by Rommel et al. (2022). Already Sutherland et al. (2012) concluded to take farmer co-ordination with caution, especially with regard to social characteristics and assumptions about trust between farmers. They also noted that it seems use- ful to build on existing structures. Franks (2011) stated that the success of collective contracts depends on clubs of like-minded members with similar views and beliefs who are willing to cooperate and have a low level of con- flict between the members. Stakeholders in our study specifically addressed group dynamics as a crucial fac- tor. They identified difficulties in bundling diverse interests and managing larger groups but saw positive aspects in knowledge exchange, developing a group feel- ing (“together we protect!”), and possible social control. Other studies have shown that farmers are motivated to join a group for knowledge exchange, learning from peers, and socializing with other farmers (Prager, 2022). Also Barghusen et al., (2021) confirmed social norms as an motivation factor. 6. CONCLUDING REMARKS AND OUTLOOK To sum up, the objective of this study was to inves- tigate the factors that are outside the sphere of influence of the individual farmer impacting the adoption of novel agri-environmental schemes, specifically result-based and collective schemes, using the PESTLE analysis frame- work. This approach was conducted to provide a system- atic analysis of the macro-environmental factors affect- ing the implementation of such schemes and to offer in- depth insights. The study adopted a stakeholder survey approach and collected precise, multidisciplinary, and holistic insights into most important external factors. The findings of this study can support the decision-making of Austrian and German policymakers in the design and implementation of the two novel contract types by con- sidering relevant promoting factors, including practi- cal requirements for result-based and collective contract approaches from the outset. Furthermore, the study iden- tified hindering factors that could be used as a basis for risk assessment, and scheme designers could act to mini- mize or avoid their impact. Overall, this study shows the suitability and practicality of the PESTLE approach for analysing the external factors influencing agri-envi- ronmental policy measures. This is becoming even more important under the current CAP with its new green architecture that gives greater flexibility at Member State level in the choice and design of measures targeting the environment and climate. Further research opportunities are seen within the framework of the approach adopted in this study. One pathway to follow in future investigations could be the examination and comparative analysis of responses from further countries and assessing the differences amongst them. Moreover, it would be important to quantitatively analyse more in depth the differences between external factors for result-based compared to external factors for collective contracts. Another promising area for future research is to look more closely at the stakeholders and actors, their background and their activities at different levels and how this influences their response behaviour. ACKNOWLEDGMENT This work was supported by the European Commis- sion’s Horizon 2020 project CONSOLE (Grant Agree- ment No. 817949). The content of this article does not reflect the official opinion of the European Commission. The views expressed in this article are solely those of the authors. REFERENCES Achinas, S., Horjus, J., Achinas, V., & Euverink, G. J. W. (2019). A PESTLE analysis of biofuels energy indus- try in Europe. Sustainability (Switzerland), 11(21), 1–24. https://doi.org/10.3390/su11215981 Allen, B., Hart, K., Radley, G., Tucker, G., Keenleyside, C., Oppermann, R., Underwood, E., Menadue, H., Poux, X., Beaufoy, G., Herzon, I., Povellato, A., Van- ni, F., Prazan, J., Hudson, T., & N, Y. (2014). Biodiver- sity protection through results based remuneration of ecological achievement. December, 167. AMA. (2023). ÖPUL 2023 – Ergebnisorientierte Bewirtschaftung (Issue September 2022). Barghusen, R., Sattler, C., Deijl, L., Weebers, C., & Matz- dorf, B. (2021). Motivations of farmers to participate in collective agri-environmental schemes: the case of Dutch agricultural collectives. Ecosystems and People, 17(1), 539–555. https://doi.org/10.1080/26395916.202 1.1979098 Birge, T., Toivonen, M., Kaljonen, M., & Herzon, I. (2017). Probing the grounds: Developing a payment- https://doi.org/10.3390/su11215981 https://doi.org/10.1080/26395916.2021.1979098 https://doi.org/10.1080/26395916.2021.1979098 64 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. by-results agri-environment scheme in Finland. Land Use Policy, 61, 302–315. https://doi.org/10.1016/j.lan- dusepol.2016.11.028 BLE. (2022). GAP kompakt 2023. Bredemeier, B., Herrmann, S., Sattler, C., Prager, K., van Bussel, L. G. J., & Rex, J. (2022). Insights into inno- vative contract design to improve the integration of biodiversity and ecosystem services in agricultural management. Ecosystem Services, 55(April), 101430. https://doi.org/10.1016/j.ecoser.2022.101430 Burton, R. J. F., & Schwarz, G. (2013). Result-oriented agri-environmental schemes in Europe and their potential for promoting behavioural change. Land Use Policy, 30(1), 628–641. https://doi.org/10.1016/j. landusepol.2012.05.002 DAFM. (n.d.). What the difference is between ACRES General and ACRES Co-operation. Retrieved Febru- ary 10, 2023, from https://www.gov.ie/en/service/ f5a48-agri-climate-rural-environment-scheme- acres/#what-the-difference-is-between-acres-general- and-acres-co-operation de Sainte Marie, C. (2014). Rethinking agri-environmen- tal schemes. A result-oriented approach to the man- agement of species-rich grasslands in France. Journal of Environmental Planning and Management, 57(5), 704–719. https://doi.org/10.1080/09640568.2013.763 772 de Snoo, G. R., Herzon, I., Staats, H., Burton, R. J. F., Schindler, S., van Dijk, J., Lokhorst, A. M., Bullock, J. M., Lobley, M., Wrbka, T., Schwarz, G., & Musters, C. J. M. (2013). Toward effective nature conservation on farmland: Making farmers matter. Conservation Letters, 6(1), 66–72. https://doi.org/10.1111/j.1755- 263X.2012.00296.x Derissen, S., & Latacz-Lohmann, U. (2013). What are PES? A review of definitions and an extension. Eco- system Services, 6, 12–15. https://doi.org/10.1016/j. ecoser.2013.02.002 Derissen, S., & Quaas, M. F. (2013). Combining perfor- mance-based and action-based payments to provide environmental goods under uncertainty. Ecologi- cal Economics, 85, 77–84. https://doi.org/10.1016/j. ecolecon.2012.11.001 DVL. (2021). DVL-Empfehlungen Überbetriebliche Gemeinschaften – Mehrwert für den Natur- und Kli- maschutz in der Agrarlandschaft Inhalt. Eichhorn, T., Kantelhardt, J., Schaller, L., Bartollini, F., Berzina, I., Bradfield, T., Cosgrove, M., Dupraz, P., Dzelzkaleja-Burmistre, M., Gatere, D., Haltia, E., Hamunen, K., Hennessy, T., Iglesias, A., Issanchou, A., Kurttila, M., Le Gloux, F., Leppänen, J., Majewski, E., … Zavalloni, M. (2022). Deliverable 2.6, CON- SOLE Project (No. 817949): Catalogue of updated factsheets of European in-depth case studies. European Commission. (2017). Agri-environmental schemes: impacts on the agricultural environment. In Science for Environment Policy (Issue 57). https://doi. org/10.2779/633983 European Commission. (2020). EU Biodiversity Strategy for 2030 – Bringing nature back into our lives. In COM(2020) 380 final. European Court of Auditors. (2011). Is agri-environ- ment support well designed and managed? In Special Report No 7. European Parliament and the Council of the European Union. (2021). Regulation (Eu) 2021/2115 of the Euro- pean Parliament and of the Council. Official Journal of the European Union, 2021(November), 435/1-435/186. Franks, J. R. (2011). The collective provision of environ- mental goods: A discussion of contractual issues. Journal of Environmental Planning and Management, 54(5), 637–660. https://doi.org/10.1080/09640568.201 0.526380 Gupta, A. (2013). Environmental and pest analysis : An approach to external business environment. Interna- tional Journal of Modern Social Sciences, 1(2), 34–43. Herzon, I., Birge, T., Allen, B., Povellato, A., Vanni, F., Hart, K., Radley, G., Tucker, G., Keenleyside, C., Oppermann, R., Underwood, E., Poux, X., Beaufoy, G., & Pražan, J. (2018). Time to look for evidence: Results-based approach to biodiversity conservation on farmland in Europe. Land Use Policy, 71(Decem- ber 2017), 347–354. https://doi.org/10.1016/j.landuse- pol.2017.12.011 Klimek, S., Richter gen. Kemmermann, A., Steinmann, H. H., Freese, J., & Isselstein, J. (2008). Rewarding farm- ers for delivering vascular plant diversity in managed grasslands: A transdisciplinary case-study approach. Biological Conservation, 141(11), 2888–2897. https:// doi.org/10.1016/j.biocon.2008.08.025 Kotler, P., Armstrong, G., & Opresnik, M. O. (2018). Principles of Marketing (17th ed.). Pearson Education Limited. Lastra-Bravo, X. B., Hubbard, C., Garrod, G., & Tolón- Becerra, A. (2015). What drives farmers’ participation in EU agri-environmental schemes?: Results from a qualitative meta-analysis. Environmental Science and Policy, 54, 1–9. https://doi.org/10.1016/j.envs- ci.2015.06.002 Massfeller, A., Meraner, M., Hüttel, S., & Uehleke, R. (2022). Farmers’ acceptance of results-based agri- environmental schemes: A German perspective. Land Use Policy, 120(August 2021), 106281. https://doi. org/10.1016/j.landusepol.2022.106281 https://doi.org/10.1016/j.landusepol.2016.11.028 https://doi.org/10.1016/j.landusepol.2016.11.028 https://doi.org/10.1016/j.ecoser.2022.101430 https://doi.org/10.1016/j.landusepol.2012.05.002 https://doi.org/10.1016/j.landusepol.2012.05.002 https://www.gov.ie/en/service/f5a48-agri-climate-rural-environment-scheme-acres/#what-the-difference-is-between-acres-general-and-acres-co-operation https://www.gov.ie/en/service/f5a48-agri-climate-rural-environment-scheme-acres/#what-the-difference-is-between-acres-general-and-acres-co-operation https://www.gov.ie/en/service/f5a48-agri-climate-rural-environment-scheme-acres/#what-the-difference-is-between-acres-general-and-acres-co-operation https://www.gov.ie/en/service/f5a48-agri-climate-rural-environment-scheme-acres/#what-the-difference-is-between-acres-general-and-acres-co-operation https://doi.org/10.1080/09640568.2013.763772 https://doi.org/10.1080/09640568.2013.763772 https://doi.org/10.1111/j.1755-263X.2012.00296.x https://doi.org/10.1111/j.1755-263X.2012.00296.x https://doi.org/10.1016/j.ecoser.2013.02.002 https://doi.org/10.1016/j.ecoser.2013.02.002 https://doi.org/10.1016/j.ecolecon.2012.11.001 https://doi.org/10.1016/j.ecolecon.2012.11.001 https://doi.org/10.2779/633983 https://doi.org/10.2779/633983 https://doi.org/10.1080/09640568.2010.526380 https://doi.org/10.1080/09640568.2010.526380 https://doi.org/10.1016/j.landusepol.2017.12.011 https://doi.org/10.1016/j.landusepol.2017.12.011 https://doi.org/10.1016/j.biocon.2008.08.025 https://doi.org/10.1016/j.biocon.2008.08.025 https://doi.org/10.1016/j.envsci.2015.06.002 https://doi.org/10.1016/j.envsci.2015.06.002 https://doi.org/10.1016/j.landusepol.2022.106281 https://doi.org/10.1016/j.landusepol.2022.106281 65 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures Matthews, A. (2019). Introducing a Development Policy Perspective into CAP Strategic Plans (Issue 0319). http://www.europarl.europa.eu/sides/getDoc. do?pubRef=-//EP//NONSGML+COMPARL+PE- Matzdorf, B., & Lorenz, J. (2010). How cost-effective are result-oriented agri-environmental measures?-An empir- ical analysis in Germany. Land Use Policy, 27(2), 535– 544. https://doi.org/10.1016/j.landusepol.2009.07.011 Melèndez-Ortiz, R., Bellmann, C., & Hepburn, J. (2009). Agricultural subsidies in the wto green box: Ensur- ing coherence with sustainable development goals. 16, 1–675. https://doi.org/10.1017/CBO9780511674587 MLUK. (2023). Förderung kooperativer Maßnahmen zur Verbesserung des Klimaschutzes und der Biodiversität auf landwirtschaftlich genutzten Flächen. https://mluk. brandenburg.de/mluk/de/service/foerderung/land- wirtschaft/foerderung-kooperativer-massnahmen- klimaschutz/# Nitank, R., & Treivdi, M. K. (2016). Pestle Technique – A Tool To Identify External Risks In Construction Pro- jects. International Research Journal of Engineering and Technology, 03(01), 384–388. Olivieri, M., Andreoli, M., Vergamini, D., & Bartolini, F. (2021). Innovative Contract Solutions for the Provi- sion of Agri-Environmental Climatic Public Goods: A Literature Review. Sustainability, 13(12), 6936. htt- ps://doi.org/10.3390/su13126936 Pavlis, E. S., Terkenli, T. S., Kristensen, S. B. P., Busck, A. G., & Cosor, G. L. (2016). Patterns of agri-environ- mental scheme participation in Europe: Indicative trends from selected case studies. Land Use Policy, 57, 800–812. https://doi.org/10.1016/j.landuse- pol.2015.09.024 Prager, K. (2022). Implementing policy interventions to support farmer cooperation for environmental ben- efits. Land Use Policy, 119(May), 106182. https://doi. org/10.1016/j.landusepol.2022.106182 Prager, K., & Posthumus, H. (2010). Human dimensions of soil and water conservation: A global perspective. Human Dimensions of Soil and Water Conservation, 1–404. Rambaree, K., Sundström, A., Wang, Z., & Wright, S. A. I. (2021). Qualitative stakeholder analysis for a swed- ish regional biogas development: A thematic network approach. Sustainability (Switzerland), 13(14), 1–20. https://doi.org/10.3390/su13148003 Raymond, C. M., Fazey, I., Reed, M. S., Stringer, L. C., Robinson, G. M., & Evely, A. C. (2010). Integrat- ing local and scientific knowledge for environmental management. Journal of Environmental Management, 91(8), 1766–1777. https://doi.org/10.1016/j.jenv- man.2010.03.023 Rommel, J., Schulze, C., Matzdorf, B., Sagebiel, J., & Wechner, V. (2022). Learning about German farmers’ willingness to cooperate from public goods games and expert predictions. Q Open, August. https://doi. org/10.1093/qopen/qoac023 Runge, T., Langlais, A., & Cardwell, M. (2022). Legal aspects of contract solutions to foster the provision of agri-envi- ronment- climate goods. Summary for stakeholders. 1–18. Russi, D., Margue, H., Oppermann, R., & Keenleyside, C. (2016). Result-based agri-environment measures: Market-based instruments, incentives or rewards? The case of Baden-Württemberg. Land Use Poli- cy, 54, 69–77. https://doi.org/10.1016/j.landuse- pol.2016.01.012 Ruto, E., & Garrod, G. (2009). Investigating farmers’ pref- erences for the design of agri-environment schemes: A choice experiment approach. Journal of Environ- mental Planning and Management, 52(5), 631–647. https://doi.org/10.1080/09640560902958172 Sabatier, R., Doyen, L., & Tichit, M. (2012). Action ver- sus result-oriented schemes in a Grassland agroeco- system: A dynamic modelling approach. PLoS ONE, 7(4). https://doi.org/10.1371/journal.pone.0033257 Schulze, C., & Matzdorf, B. (2023). The institutional design of agri-environmental contracts – How stake- holder attitudes can inform policy making. The Euro- pean Agricultural and Applied Economics Publications Foundation, 4–7. (prepublished version) Schwarz, G., Moxey, A., Mccracken, D., Huband, S., & Cummins, R. (2008). An analysis of the potential effectiveness of a Payment-by-Results approach to the delivery of environmental public goods and services supplied by Agri-Environment Schemes. Report to the Land Use Policy Group, UK, November, 108. Stolze, M., Frick, R., Schmid, O., Stöckli, S., Bogner, D., Chevillat, V., Dubbert, M., Fleury, P., Neuner, S., Nitsch, H., Plaikner, M., Schramek, J., Tasser, E., Vin- cent, A., & Wezel, A. (2015). Result-oriented Measures for Biodiversity in Mountain Farming Result-oriented Measures for Biodiversity in Mountain Farming A Pol- icy Handbook. Sutherland, L. A., Gabriel, D., Hathaway-Jenkins, L., Pas- cual, U., Schmutz, U., Rigby, D., Godwin, R., Sait, S. M., Sakrabani, R., Kunin, W. E., Benton, T. G., & Stagl, S. (2012). The “Neighbourhood Effect”: A mul- tidisciplinary assessment of the case for farmer co- ordination in agri-environmental programmes. Land Use Policy, 29(3), 502–512. https://doi.org/10.1016/j. landusepol.2011.09.003 van Dijk, W. F. A., Lokhorst, A. M., Berendse, F., & de Snoo, G. R. (2015). Collective agri-environment schemes: How can regional environmental coopera- http://www.europarl.europa.eu/sides/getDoc.do?pubRef=-//EP//NONSGML+COMPARL+PE- http://www.europarl.europa.eu/sides/getDoc.do?pubRef=-//EP//NONSGML+COMPARL+PE- https://doi.org/10.1016/j.landusepol.2009.07.011 https://doi.org/10.1017/CBO9780511674587 https://mluk.brandenburg.de/mluk/de/service/foerderung/landwirtschaft/foerderung-kooperativer-massnahmen-klimaschutz/# https://mluk.brandenburg.de/mluk/de/service/foerderung/landwirtschaft/foerderung-kooperativer-massnahmen-klimaschutz/# https://mluk.brandenburg.de/mluk/de/service/foerderung/landwirtschaft/foerderung-kooperativer-massnahmen-klimaschutz/# https://mluk.brandenburg.de/mluk/de/service/foerderung/landwirtschaft/foerderung-kooperativer-massnahmen-klimaschutz/# https://doi.org/10.3390/su13126936 https://doi.org/10.3390/su13126936 https://doi.org/10.1016/j.landusepol.2015.09.024 https://doi.org/10.1016/j.landusepol.2015.09.024 https://doi.org/10.1016/j.landusepol.2022.106182 https://doi.org/10.1016/j.landusepol.2022.106182 https://doi.org/10.3390/su13148003 https://doi.org/10.1016/j.jenvman.2010.03.023 https://doi.org/10.1016/j.jenvman.2010.03.023 https://doi.org/10.1093/qopen/qoac023 https://doi.org/10.1093/qopen/qoac023 https://doi.org/10.1016/j.landusepol.2016.01.012 https://doi.org/10.1016/j.landusepol.2016.01.012 https://doi.org/10.1080/09640560902958172 https://doi.org/10.1371/journal.pone.0033257 https://doi.org/10.1016/j.landusepol.2011.09.003 https://doi.org/10.1016/j.landusepol.2011.09.003 66 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. tives enhance farmers’ intentions for agri-environ- ment schemes? Land Use Policy, 42, 759–766. https:// doi.org/10.1016/j.landusepol.2014.10.005 WBAE. (2020). Designing an effective agri-environment- climate policy as part of the post-2020 EU Common Agricultural Policy (Issue December 2019). Wezel, A., Vincent, A., Nitsch, H., Schmid, O., Dub- bert, M., Tasser, E., Fleury, P., Stöckli, S., Stolze, M., & Bogner, D. (2018). Farmers’ perceptions, prefer- ences, and propositions for result-oriented meas- ures in mountain farming. Land Use Policy, 70(May 2017), 117–127. https://doi.org/10.1016/j.landuse- pol.2017.10.020 Wilson, G. A., & Hart, K. (2000). Financial Imperative or Conservation Concern? EU Farmers’ Motivations for Participation in Voluntary Agri-Environmental Schemes. Environment and Planning A: Economy and Space, 32(12), 2161–2185. https://doi.org/10.1068/ a3311 Yüksel, I. (2012). Developing a Multi-Criteria Decision Making Model for PESTEL Analysis. International Journal of Business and Management, 7(24). https:// doi.org/10.5539/ijbm.v7n24p52 Zabel, A. (2019). Biodiversity-based payments on Swiss alpine pastures. Land Use Policy, 81(February 2018), 153–159. https://doi.org/10.1016/j.landusepol.2018.10.035 APPENDIX A DESCRIPTIONS OF RESULT-BASED AND COLLECTIVE CONTRACTS AS PROVIDED WITHIN THE PESTLE SURVEY Result-based contract In a result-based contract, land managers receive a payment only for the delivery of environmental or cli- mate results (e.g. water protection, landscape improve- ment, increasing biodiversity of carbon sequestration). Land managers are free to decide about the management practices, with which they want to achieve these envi- ronmental or climate improvements. Selected indicators and scoring systems to monitor environmental or climate results are often used, and they will be exactly defined in the contract. Land managers have access to advice or training when they participate in this contract and they can voluntarily engage in the monitoring activity. Contract with collective implementation Land managers become members of a group who applies jointly for compensation in order to implement environmental or climate activities, e.g. water protec- tion, carbon sequestration, biodiversity or landscape improvement. A minimum number of group members (e.g. 5) from the region is required to collaborate in order to get a payment. The group members decide about the implementation and locating the measures, and the dis- tribution of the payment. Within the group, peer land managers and advisors share knowledge and support the achievement of the environmental objectives. https://doi.org/10.1016/j.landusepol.2014.10.005 https://doi.org/10.1016/j.landusepol.2014.10.005 https://doi.org/10.1016/j.landusepol.2017.10.020 https://doi.org/10.1016/j.landusepol.2017.10.020 https://doi.org/10.1068/a3311 https://doi.org/10.1068/a3311 https://doi.org/10.5539/ijbm.v7n24p52 https://doi.org/10.5539/ijbm.v7n24p52 https://doi.org/10.1016/j.landusepol.2018.10.035 67 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures (1) Short introduction into the PESTLE task (2) Overarching question of the PESTLE survey stated (3) Introduction of the six PESTLE factors including short descriptions and the PESTLE figure 1 (4) Short contract solution descriptions for result-based contract and contract with collective implementation provided (5) Participants are asked to name five 5 important aspects, influencing the implementability, in short concrete statements (example given) Please name 5 important aspects that, in your view, influence the implementability of RB/CO contracts , in short concrete statements. A free text 1 B free text 2 C free text 3 D free text 4 E free text 5 (6) Participants are asked to decide for each response given if it is promoting or hindering and to finally select the response considered as most important (example) Your list of aspects (transferred from above A - E) Is the aspect promoting or hindering the adoption? The most important (only one) promoting + hindering - 1. A free text 1 þ o o B free text 2 o þ o C free text 3 þ o o D free text 4 o þ o E free text 5 o þ þ Table 1. Approach used within the PESTLE survey, exemplarily illustrate for RB schemes. 68 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. APPENDIX B – CHARACTERISTICS OF THE AUSTRIAN AND GERMAN STAKEHOLDERS Table 2. Characteristics of the Austrian and German stakeholders. Characteristics Germany frequency (%) Austria frequency (%) Regional level of the respondent National 29,2 64,7 Regional 56,3 20,6 Local 14,6 0 International 0 14,7 Background organisation Civil society / Private individual 4,2 0 Public enterprise 8,3 17,6 Non-governmental organisation 8.3 8,8 Academic (e.g. university, research institute) 8,3 17,6 Non-profit organisation (e.g. foundation, association) 14,6 11,8 Private company 18,8 32,4 Governmental organisation 22,9 8,8 Other (e.g. professional associations) 14,6 2,9 Special area of responsibility (multiple answers allowed) Agriculture 41,9 28,1 Environmental protection / nature conservation 18,1 19,8 Forestry 8,6 12,5 Land use policy and planning 7,6 4,2 Public administration 6,7 5,2 Research and development 6,7 6,3 Water management 4,8 4,2 Community development 2,9 0 Training and advice 1,9 9,4 Food sector 1,0 10,4 Role or areas of interest (multiple answers allowed); in bracket selection of “most important” Provider of information/advice to farmers 21,2 (21,6) 23,3 (14,7) Provider of information to the public 19,2 (13,7) 19,4 (20,6) Assistance for public funding of land management 1,9 (2,0) 4,9 (0) Support in the design of contract solutions 14,4 (17,6) 21,4 (20,6) Equipment and/or tool provision 7,7 (0) 2,9 (2,9) Providing/leasing land to land managers 2,9 (0) 4,9 (5,9) Providing finance to land managers/owners/workers 5,8 (2) 3,9 (0) Regulation and enforcement 6,7 (5,9) 2,9 (0) Lobbying, campaigning 13,5 (17,6) 6,9 (2,9) Community leader 1,9 (2) 1,9 (2,9) Supervisory authority 1,9 (2) 3,9 (0) Product certification body (e.g. organic, …) 0 (0) 0 (0) Processor of agricultural products 1 (2) 3,9 (2,9) Trade with agricultural products 1,9 (0) 0 (0) No selection “most important” (15,7) (26,5) 69 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures Table 3. Federal state from which the participants originate (in %). Germany Stakeholder Austria Stakeholder Baden-Württemberg 5,9 Burgenland 6,06 Bavaria 13,7 Lower Austria 12,12 Berlin 5,9 Upper Austria 6,06 Brandenburg 2,0 Salzburg 0 Hamburg 3,9 Styria 3,03 Hesse 5,9 Tyrol 0 Mecklenburg-Western Pomerania 5,9 Vorarlberg 0 Lower Saxony 5,9 Vienna 30,30 North Rhine-Westphalia 21,6 Across the federal states 42,42 Rhineland-Palatinate 7,8 Saarland 0 Saxony 2,0 Saxony-Anhalt 2,0 Schleswig-Holstein 7,8 Across the federal states 9,8 APPENDIX C Table 4. Detailed overview of subcategories mentioned within the PESTLE approach. Code Subcategory CT Sum + - 1. P E S T L E P00 Political category – without specification RB 5 2 3 1 CO 6 0 6 0 P01 Advice and support to farmers for implementation RB 8 7 1 1 CO 8 8 0 3 P02 Political will to support farmers in delivering environmental services RB 9 8 1 1 CO 3 3 0 1 P03 Low level of bureaucracy and administrative burden RB 11 4 7 3 CO 10 4 6 3 P04 Longer-term stable political framework RB 6 3 3 0 CO 4 2 2 0 P05 Assistance in contract implementation by qualified authorities and intermediaries RB 7 6 1 2 CO 5 4 1 0 P06RB Extensive communication of the measures to the public and to farmers RB 7 7 0 0 Ec00 Economical category – without specification RB 8 5 3 4 CO 7 4 3 4 Ec01 Payment calculation, appropriate remuneration for participation in the contracts RB 28 21 7 12 CO 13 11 2 1 Ec02RB Availability of sufficient funding for contract payments RB 4 3 1 2 Ec02CO ... and for coordination / measure planning CO 8 6 2 2 Ec03 Income / revenue security and little financial risk for farmers RB 10 1 9 1 CO 6 5 1 3 Ec04RB Reliability of demand for and value chains to sell the agricultural products RB 6 4 2 1 (Continued) 70 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Theresa Eichhorn et al. Code Subcategory CT Sum + - 1. P E S T L E Ec04CO Fair sharing of remuneration between farmers when participating in the contracts CO 18 3 15 4 Ec05 New income opportunities for farmers by participating in contracts RB 12 10 2 7 CO 11 10 1 2 Ec06 Limited time and financial effort for implementation RB 8 2 6 1 CO 6 2 4 0 S00 Social category – without specification RB 7 6 1 0 CO 6 4 2 2 S01 Social appreciation, recognition for the environmental services provided by farmers RB 20 17 3 2 CO 10 9 1 3 S02RB Attitudes of farmers, consideration of cultural norms and traditions RB 9 5 4 2 S02CO Attitudes of farmers and sensitivities of farmers CO 30 9 21 13 S03RB Societal and consumers’ demand and interest for environmental services RB 8 5 3 2 S03CO Involvement of further stakeholders (interest groups, ...) CO 10 8 2 5 S04RB Willingness to work together (interest groups, neighbours, farmers’ associations) RB 5 1 4 1 S04CO Content of cooperation CO 29 16 13 10 S05RB Farmers’ awareness of environmental topics and knowledge RB 15 14 1 4 S05CO … and knowledge exchange CO 8 7 1 2 S06C Group dynamics CO 21 8 13 9 T00 Technological category – without specification RB 7 7 0 1 CO 3 3 0 0 T01RB Existence of appropriate technologies for measuring the results achieved RB 13 11 2 2 T01CO Existence of appropriate technologies for measuring the achievements CO 8 7 1 1 T02 Determination of appropriate indicators for monitoring RB 5 3 2 0 CO 1 1 0 0 T03 Easy to implement and no time-consuming monitoring / documentation RB 3 2 1 0 CO 1 1 0 0 T04RB Access to technology / machinery, technical practicability RB 7 3 4 1 T04CO Access to technology / machinery, distribution of work CO 6 4 2 1 T05RB Sufficient knowledge about the environmental effects of the farming practices RB 4 2 2 1 L00 Legal category – without specification RB 7 1 6 2 CO 5 4 1 0 L01RB Contract characteristics: voluntariness, flexibility, clear goal(s), possibility of influencing RB 22 21 1 4 L01CO … and entry and exit conditions, responsibilities CO 34 18 16 4 L02RB Simplicity and comprehensibility of the contract RB 9 5 4 0 L02CO Conditions of participation for farmers (number, setting, ...) CO 6 1 5 1 L03 Clarity and consistency of the legal framework of the contract RB 18 12 6 4 CO 14 8 6 2 L04 Compatibility of the contract with existing laws, programmes and EU policies RB 14 5 9 3 CO 2 0 2 0 Table 4. (Continued). (Continued) 71 Bio-based and Applied Economics 13(1): 49-71, 2024 | e-ISSN 2280-6172 | DOI: 10.36253/bae-14489 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures Code Subcategory CT Sum + - 1. P E S T L E L05 Practical achievability of the contract goals RB 12 10 2 4 CO 3 3 0 2 L06 Transparent and comprehensible controls and sanctions RB 20 8 12 3 CO 10 5 5 0 En00 Environmental category – without specification RB 5 3 2 1 CO 4 3 1 0 En01 Impacts of climate change and perceived need for action RB 4 2 2 0 CO 2 2 0 0 En02 Unpredictability of nature and the limited ability of farmers to have an influence on it RB 27 3 24 8 CO 5 2 3 0 En03 Spatial and regional environmental conditions RB 3 0 3 0 CO 7 5 2 1 En04 Interplay of action and impacts on nature and environment RB 3 2 1 1 CO 3 2 1 0 Note: Table 4 shows categories and subcategories including sum of all answers, indication of promoting or hindering assessed answers, weighting exercise answers with number of weighted as most important: Sum = number of responses in total assigned under this subcat- egory/factor; + = responses framed positively as well as assigned as promoting factor; – = responses framed negatively as well as assigned as hindering factor; 1. = number of responses, stated as most important factor for collective or result-based contracts by stakeholders in the survey = ranking exercise; categories: P = Political ; Ec = Economical; S = Social; T = Technological; L = Legal; En = Environmental. Table 4. (Continued). _Hlk60054323 _Hlk104829823 _Hlk128742463 _Hlk104830529 _Hlk127347111 _Hlk128647880 _Hlk128647635 _Hlk128646517 _Hlk128649491 New pathways for improved delivery of public goods from agriculture and forestry Stefano Targetti1,*, Andreas Niedermayr2, Kati Häfner3, Lena Schaller2 Assessing the Landscape Recovery Scheme in the UK: a Q methodology study in Yorkshire, UK Emmanouil Tyllianakis Upscaling environmental incentives in the Common Agricultural Policy: an assessment of the potential of transfers from the first to second pillar Fanny Le Gloux1,2,*, Pierre Dupraz1 Exploring macro-environmental factors influencing adoption of result-based and collective agri-environmental measures: a PESTLE approach based on stakeholder statements Theresa Eichhorn1,*, Lena Schaller1, Katri Hamunen2,3, Tania Runge4,* Innovative contract solutions for the Agri-Environmental-Climate Public Goods provision: Which features meet the farmers’ approval? Insights from Emilia-Romagna (Italy) Riccardo D’Alberto1,*, Meri Raggi2, Davide Viaggi3 The use of innovative contracts to provide agri-environmental public goods: Comparing attitudes between Ireland and other European countries Tracy Bradfield1,*, Thia Hennessy1, Riccardo D’Alberto2, Emmi Haltia3