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land Article Do Agricultural Advisory Services in Europe Have the Capacity to Support the Transition to Healthy Soils? 1 , 1 1 1 2 Julie Ingram *, Jane Mills , Jasmine E. Black , Charlotte-Anne Chivers , José A. Aznar-Sánchez , 3 4 2 5 6 Annemie Elsen , Magdalena Frac , Belén López-Felices , Paula Mayer-Gruner , Kamilla Skaalsveen , 6 3 Jannes Stolte and Mia Tits Countryside and Community Research Institute, University of Gloucestershire, Cheltenham GL504AZ, UK; firstname.lastname@example.org (J.M.); email@example.com (J.E.B.); firstname.lastname@example.org (C.-A.C.) Department of Economy and Business, Research Centre on Mediterranean Intensive Agrosystems and Agrifood Biotechnology (CIAIMBITAL), University of Almería, 04129 Almería, Spain; email@example.com (J.A.A.-S.); firstname.lastname@example.org (B.L.-F.) Soil Service of Belgium (Bodemkundige Dienst van België) W. de Croylaan 48, 3001 Leuven, Belgium; email@example.com (A.E.); firstname.lastname@example.org (M.T.) Institute of Agrophysics, Polish Academy of Sciences, Doswiadczalna ´ 4, 20-290 Lublin, Poland; email@example.com Soil Biology Department, Institute of Soil Science and Land Evaluation, University of Hohenheim, 70599 Stuttgart, Germany; firstname.lastname@example.org Department of Soil and Land Use, Division of Environment and Natural Resources, Norwegian Institute of Bioeconomy Research, NO-1431 Ås, Norway; email@example.com (K.S.); firstname.lastname@example.org (J.S.) * Correspondence: email@example.com Abstract: The need to provide appropriate information, technical advice and facilitation to support Citation: Ingram, J.; Mills, J.; Black, farmers in transitioning towards healthy soils is increasingly clear, and the role of the Agricultural J.E.; Chivers, C.-A.; Aznar-Sánchez, Advisory Services (AAS) in this is critical. However, the transformation of AAS (plurality, commer- J.A.; Elsen, A.; Frac, M.; cialisation, fragmentation, decentralisation) brings new challenges for delivering advice to support López-Felices, B.; Mayer-Gruner, P.; soil health management. This paper asks: To what extent do agricultural advisory services have Skaalsveen, K.; et al. Do Agricultural the capacity to support the transition to healthy soils across Europe? Using the ‘best ﬁt’ framework, Advisory Services in Europe Have analytical characteristics of the AAS relevant to the research question (governance structures, man- the Capacity to Support the agement, organisational and individual capacities) were identiﬁed. Analysis of 18 semi-structured Transition to Healthy Soils? Land 2022, 11, 599. https://doi.org/ expert interviews across 6 case study countries in Europe, selected to represent a range of contexts, 10.3390/land11050599 was undertaken. Capacities to provide soil health management (SHM) advice are constrained by funding arrangements, limited adviser training and professional development, adviser motivations Academic Editor: Amrakh and professional cultures, all determined by institutional conditions. This has resulted in a narrowing I. Mamedov down of access and content of soil advice and a reduced capacity to support the transition in farming Received: 9 March 2022 to healthy soils. The extent to which emerging policy and market drivers incentivise enhanced Accepted: 12 April 2022 capacities in AAS is an important area for future research. Published: 19 April 2022 Publisher’s Note: MDPI stays neutral Keywords: agricultural advisory services; soil health; governance; agricultural advisers; sustainable with regard to jurisdictional claims in soil management; soil policy; advice published maps and institutional afﬁl- iations. 1. Introduction Soil health has emerged as a priority for high level and national policy makers and Copyright: © 2022 by the authors. for agricultural communities. This is linked to the recognition of the multiple functions Licensee MDPI, Basel, Switzerland. that soils fulﬁl and the soil degradation processes closely linked to agriculture: erosion, This article is an open access article organic carbon decline, soil biodiversity decline, compaction, contamination, salinisation distributed under the terms and and acidiﬁcation [1,2]. Indeed, soil health is seen as “a key solution for our big challenges” conditions of the Creative Commons in the newly launched European Union (EU) Soil Strategy, which builds on the European Attribution (CC BY) license (https:// creativecommons.org/licenses/by/ Green Deal and the Farm to Fork Strategy [3,4]. For agricultural soils, soil health and 4.0/). managing soil sustainably are regarded as central to food system transition pathways Land 2022, 11, 599. https://doi.org/10.3390/land11050599 https://www.mdpi.com/journal/land Land 2022, 11, 599 2 of 26 such as agroecology and regenerative agriculture, managing carbon for climate change mitigation and adaptation and mitigating pollution for human wellbeing. However, the soil governance landscape (formal and informal institutions related to soil-related decision-making processes) continues to be highly fragmented. It is charac- terised by multi-level and multi-actor decision making, with no single body responsible at the EU or national levels  and could be described as a network mode of governance . A number of public and private mechanisms are applied that inﬂuence agricultural soil management decisions (directly or indirectly), reﬂecting the multiple functions (provi- sioning, ﬁltering of nutrients, carbon storage, ﬂood mitigation) and private and public good that soils provide . These include public cross-sectoral policy instruments (regu- latory and voluntary) at the EU, national and regional levels; market-led (food assurance schemes in the supply chain); and measures which are led by the farming industry and non-governmental organisations (NGO) (voluntary initiatives, partnerships and networks). This emphasis on soil health and its complex governance arena brings new challenges both for land managers and those that support them. The need to provide appropriate information, technical advice and facilitation to support farmers in transitioning towards sustainable soil management  has been identiﬁed by a number of researchers and policy makers at the international, European and national levels [8–13]. Agricultural Advisory Services (AAS) have always constituted an important part of farmer decision making with respect to soil management [14,15]. However, the increasing complexities of managing different soil functions and soil health at the farm scale  places new demands on these services. Soil health has been deﬁned as the capacity of soil to function as a vital living sys- tem ; however, the concept, and how it is operationalised, is still evolving . Conse- quently, there are many understandings of what constitutes good soil health management (SHM). There are multiple practices embodied in the soil health concept, such as the use of cover crops and residues and reduced tillage; however, there is no single message or set of advice that is relevant to all contexts. Emerging interest in soil health indicators, soil biological processes and soil carbon dynamics  and new farming approaches (e.g., regenerative agriculture, agroecology), requires increasingly specialist knowledge and understanding (metrics, sampling techniques and analysis, interpretation) [19–21] beyond the traditional territory of soil fertility and agronomy. Meeting famers’ knowledge needs, building their capacity and facilitating shared learning for SHM presents new imperatives for advisers . These challenges exist against a backdrop of a changing farming popula- tion operating in a volatile, competitive marketplace negotiating multiple drivers in the agri-food system. AAS have themselves been in transition, with privatisation and decentralisation oc- curring to different extents across Europe over the past 30 years . The diversity of actors, intermediaries and organisations from the private (The private farm advisory sector includes proﬁt and non-proﬁt enterprises. Prager et al.  distinguishes ‘private’ as the status of an organisation and ‘commercial’ as the activities carried out by the organisation (e.g., offering advisory services for a fee)) and public sectors and NGOs engaged in some way in offering advice that inﬂuences soil management has grown. In particular, there has been an increase in the number of private advisers (These include: commercial agronomists offering services as part of farm input sales; farm management consultants; independent advisers or technicians within the supply-chain, sector or industry body or employed by farmer-owned groups)  and those with commercial links to farmers [26,27]. There is debate about the impact of such diversity on governance with respect to the integration and fragmentation of advice, competition and cooperation and how on access to quality advice [24,28,29]. Arguments about the advantages and disadvantages of privatisation have also been well rehearsed [30–32]. The potentially negative impact of commercialisa- tion on public goods advice  and the limited investment in updating environmental knowledge for advisers has been highlighted . The powerful effect of new economic actors, such as those in the supply chain, on environmental objectives has also been demon- Land 2022, 11, 599 3 of 26 strated [26,27,35] and noted speciﬁcally for soil management [10,36,37]. Private sector providers who support production goals can promote practices detrimental to soil health (e.g., multiple ﬁeld operations with heavy machinery, a reliance on inorganic fertilizer, poor budgeting of organic inputs, harvesting in unsuitable conditions) . Meanwhile, resources for public sector advice to farmers on the mitigation of soil degradation processes have also been shown to be inadequate . Although there has been a requirement for all EU member states (since 2007) to establish a Farm Advisory System (FAS) (according to FAS, Regulation (EC) N 73/2009) to support farmers in meeting cross-compliance requirements, including soil management though Good Agricultural and Environmental Conditions (GAEC), the singular advisory focus on compliance has been to the detriment of other soil functions and soil health outcomes . The role of the individual adviser is also shifting, demanding greater professionali- sation in increasingly specialised sectors, technical expertise (subject-matter knowledge), facilitation skills and awareness of a number of policy instruments, innovations, industry demands, certiﬁcations and environmental objectives. In such an environment, the assump- tion is that advisers will pursue different knowledge and strengthen and broaden their suite of professional practices to suit the ‘new farming paradigm’ [41,42]. At the same time advisers need to stay abreast of the farming community’s growing informal soil knowledge networks, [43,44] and the different ways they negotiate their own microAKIS . How- ever, a body of evidence has been accumulating [10,14] suggesting a lack of specialist soil technical support and expertise in the advisory community, a poor understanding of the impact and externalities of their advice for soil, as well as varying motivations. Although studies show that farmers are deferring to advisers for their soil testing, largely in arable sectors [45,46], the lack of meaningful guidance for advisers regarding interpretation of these tests for soil health, especially for soil organic matter, and for speciﬁc farm conditions and management, is a concern [22,47]. There are a number of examples of effective soil advice across Europe ; however, it is clear that there are variable skill sets . These insights raise questions about the capacity of advisory organisations and the constituent advisers for supporting SHM. This paper asks: To what extent do agricultural advisory services have the capacity to support the transition to healthy soils across Europe? This addresses a recognised research gap, since understanding how the economic resources and strategies of advisory organisations determine the content of advice has received little (particularly for soil health) attention [26,30]. Equally, although soil literacy and societal engagement are central to the EU Soil Strategy and the implementation of the Mission for Soil and the European Soil Partnership, little has been done to understand the level of knowledge and expertise about soil health management in AAS. This question is addressed using an analytical framework which positions AAS within the wider Agricultural Knowledge and Innovation System (AKIS), in which AAS are a subsystem. The framework implies that a range of organisations and stakeholders are involved in agricultural innovations along agricultural value chains, as well as agricultural research, agricultural extension and agricultural education . Work conducted in the EU-funded SoilCare project underpins this analysis. 2. Concepts and Framework AAS can be deﬁned as sets of organisations that support and facilitate people engaged in agricultural production to solve problems and to obtain information, skills and tech- nologies by enabling farmers to co-produce farm-level solutions by establishing service relationships with advisers [30,32,49]. AAS comprise traditional advice providers (cham- bers of agriculture, public bodies, research institutes), farmer-based organisations (FBOs) (unions, associations, cooperatives), non-governmental organisations (NGOs), independent consultants as well as advisers working in upstream or downstream industries, supply chains and high-tech sectors. However, these distinct categories do not fully capture the dif- ferent arrangements and the new actors and roles emerging [23,26,27]. The term ‘pluralistic’ Land 2022, 11, 599 4 of 26 is used to describe the diversity of institutional options in providing and ﬁnancing AAS . AAS are characterised by a range of approaches, including one-to-one advice, facilitated interactive group approaches to foster peer-to-peer learning and mass dissemination. We have adapted the ‘best ﬁt’ (Birner ’s  framework was proposed for identifying modes of providing and ﬁnancing advisory services that ‘best ﬁt’ the speciﬁc conditions and development priorities of speciﬁc countries) framework developed by Birner, Davis, Pender, Nkonya, Anandajayasekeram, Ekboir, Mbabu, Spielman, Horna and Benin  to analyse the capacity of AAS for supporting SHM (Figure 1). Due to the multiple interacting dimensions of the AKIS and the AAS, it is difﬁcult to collect data to capture the full complexity and interdependence of the system . This framework provides a means of disentangling the different dimensions within the system. Here, we use selected key analytical categories in the framework relevant to the research questions. We deﬁne SHM as ‘where management maintains or enhances (and does not impair) the capacity of soil to function as a vital living system, and to provide supporting, provisioning, regulating cultural services’. SHM is underpinned by the following management principles identiﬁed in the SoilCare project: integrate crop rotation, maintain continuous soil cover, build organic matter, minimise soil disturbance, prevent soil compaction, manage water for soil, use soil-friendly weed/pest control and consider landscape-scale management. These were derived by scientiﬁc review  and experimentation , as documented in this Special Issue, and have proven soil health beneﬁts [54,55]. Figure 1. Framework—Blue shading represents the analytical characteristic investigated . The focus of this study is on Characteristics of the system of agricultural advisory services (C in blue in Figure 1) and the implications for SHM. Speciﬁcally, according to Birner, Davis, Pender, Nkonya, Anandajayasekeram, Ekboir, Mbabu, Spielman, Horna and Benin , we include: Governance structures: the roles of the public and private sectors and civil society in providing and ﬁnancing advisory services, the level of decentralisation and the linkages and partnerships among agents in the innovation system. Management, organisational and individual capacities: this refers to the expertise, training, motivations of the members of the advisory service as well as their incentives, professional and organisational culture. These were translated into characteristics relevant to SHM and framed the data col- lection. We understand that Governance (Usually deﬁned as the systems of institutional Land 2022, 11, 599 5 of 26 rules, policies and processes which govern how roles and responsibilities are delegated, managed and coordinated) structures enable and constrain organisational activities, in particular, the institutional options available for ﬁnancing and the extent of coordination, fragmentation and integration . Regarding the AAS Mmanagement, organisational and individual capacities to deliver SHM advice, organisational capacity is usually deﬁned in terms of the capacity to perform effectively or to fulﬁl a goal (e.g., as the set of processes, management practices or attributes that assist an organisation in fulﬁlling its mission ). This capacity also affects the individual. Previous work has shown, for example, that the back-ofﬁce support such as training and the organisation’s knowledge management impacts advisers’ capabilities . Regarding individuals, AAS studies recognise that certain individual competencies are necessary for organisations and their advisers to operate effectively, where competence is: to have sufﬁcient knowledge and skills that enable a person to act in a wide variety of situations and the ability to perform something efﬁciently and effectively (i.e., success- fully) [59,60]. These skills include technical skills, which relate to specialist understanding (knowledge, expertise), and process skills, which are soft skills and refer to the collective skills necessary for effective performance of the individual and their organisation. Technical skills with respect to SHM are foregrounded in this study; however, we recognise that the ‘soft’ skills of facilitators, intermediaries and network builders are important . This infrastructural approach to assessing AAS, which focuses on the presence and interaction of actors and the infrastructures that govern the behaviour of actors  also draws on selected criteria that Prager, Creaney and Lorenzo-Arribas  identiﬁed for evaluating a functional advisory system. This paper focuses its analysis on C to address the research question, and because these characteristics can be inﬂuenced directly by policy makers. However, data for Frame conditions (A), Characteristics of farmers/land managers and their knowledge needs (B), Characteristics in Performance (D), Evidence (E) and Impact (F) (Figure 1) were also collected and analysed. Frame conditions (A) are important contextual factors in shaping the AAS, particularly as these have implications for SHM, and these include: Policy environment; Capacity of potential service providers; Farming systems and socio- economic conditions. Equally, we acknowledge that Farmers’ knowledge needs (B) (which we inserted into the framework) are important for assessing the adviser ’s role. It is not the intention here to follow an impact chain approach to analyse the performance of agricultural advisory services (D,E,F). Assessing (Performance, D) and the quality of advice is challenging, since its measure is the outcome for the farmer and there are multiple factors that affect this [23,50,63]. 3. Methods Countries in Europe are highly diversiﬁed in terms of their AAS and AKIS, reﬂecting the structure of agriculture, farming systems, soils and productivity  and the extent to which AKIS are embedded in national institutions, laws and cultures . Six case studies (drawn from country partners in the SoilCare project) were selected to represent a range of AAS approaches and contexts: Norway, Belgium (Flanders) (Belgium (Flanders was the case study for Belgium) as Wallonia operates a different system), Spain, the UK (England) (As the UK’s four countries have different political structures and agricultural policies, the focus was on England), Germany and Poland. The selection was based on three broad criteria: ﬁrstly, AAS organisations (to ensure the dominant ones were represented); secondly, characterisation of the AKIS, according to strength of national inﬂuence and level of integration/fragmentation (based on the the PROAKIS project); and thirdly, to include a range of biogeographical and pedoclimatic zones, as already determined in the SoilCare case study selection process . This selection was informed by detailed AKIS descriptions for each of these coun- tries from a range of sources, including PROAKIS  and i2connect  project country reports [23,30,32,68–70], and previous reviews for soil . The dominant AAS are repre- Land 2022, 11, 599 6 of 26 sented in the case studies: Spain FBO; England (Private); Germany (Public/Private/FBO); Poland (Public); Norway (Private); and Flanders (Public) according to previous studies . The pedoclimatic zones represented are: Atlantic Central (Flanders, Germany, England), Nemoral/Boreal (Norway), Continental (Poland) and Mediterranean South (Spain). Semi-structured interviews (2–4) were conducted in each case study (a total of 18). Selection procedures and interviews were carried out in each case study by project partners using standardised guidance and protocols. Respondents were selected were: representa- tives of decision/policy makers at national and regional level or of AAS organisations who were knowledgeable about SHM. As this was a very limited pool of experts, a purposive sampling strategy was employed. Table 1 lists the respondents and their roles and afﬁliation and shows the range of AAS organisations represented. Table 1. The case study respondents and their roles and afﬁliations. Flanders Norway Spain England (UK) Germany Poland (Belgium) N1 ES1 GR1 Representative of BE1 Technical director Representative PL1 NLR (Norsk Land- UK1 Researcher and of agriculture and from the district Professor of bruksrådgivning) Independent extension worker research at administration, Agriculture Norwegian agricultural at Flemish association of Agricultural Ofﬁce Science (fruit and Agricultural consultant Research Station farmers and Baden- veg sector) Advisory Private independent Public livestock breeders Württemberg Public Private independent/ FBO Public FBO GR2 PL2 N2 ES2 UK2 Representative Company BE2 Representative of Professor of soil National farm from the district producing Adviser at the Soil NLR science and advice manager for administration, micro-organisms Service of Belgium Private independent/ agricultural a consultancy Agricultural ofﬁce, and organic Private independent FBO chemistry Public Private commercial Baden- grower Württemberg Private commercial Public ES3 GR3 P3 N3 BE3 Research Board member of Company adviser Representative of Representative of coordinator at agricultural for horticultural NLR Flemish Land research and cooperative, sector Private independent/ Agency transfer centre Brandenburg Private FBO Public Private FBO commercial commercial ES4 Researcher in agricultural research and transfer centre Private commercial The analytical categories (Figure 1) were translated into interview questions and topics as shown in Table 2. Interviews were recoded, transcribed and translated into English, then analysed thematically using Nvivo 12. The coding structure followed the analytical categories of the interview but was extended where other themes emerged inductively. In total, 18 interviews provided in-depth analysis of AAS capacities for supporting SHM. A list of abbreviations is provided. A full interview schedule is provided as Supplementary Materials. Land 2022, 11, 599 7 of 26 Table 2. Analytical categories translated into interview topics: example questions. Characteristics of AAS for Supporting SHM Governance Structures With respect to advice that supports or impacts soil management: the key actors and organisations providing advice; the key inﬂuencers; the roles of the public and private sectors and civil society in providing and ﬁnancing advisory services; the level of diversity, decentralisation, coordination, integration or fragmentation of these services; the extent of linkages and partnerships among actors. Management, organisational and individual capacities the extent of organisation/management/resourcing of advisory services for delivering advice on soil and the impact on advisers’ ability to provide soil advice; different advisers’ expertise for delivering SHM advice, quality of advice, level of soil management training; the attitudes and motivations of the different sorts of advisers and organisational cultures. 4. Results Where quotes are provided, the code refers to the notation in Table 1. A summary of the results is provided in Table 3. Table 3. Summary of AAS characteristics for case studies. Governance Flanders Norway Spain England (UK) Germany Poland Structure (Belgium) Synergies Private or FBOs Research Synergies exist, Horizontally Synergies exist, between public cooperate and institutes but some fragmented, but but some Integration/ ODRs and obtain support collaborate to conﬂict and partnerships tensions fragmentation private sector from public address soil tensions at farm work with between but bodies for SHM topics level shared goal individuals some tensions AAS capacity Good Good organisation Consultation competence and services are and capacity to Reliance on management in well equipped, Management deliver SHM short-term FBOs but Absence of good resources; Public sector and advice in NRL project funding limited in planning for the public under- organisation for reduces others necessary SHM provision has resourced SHM advice Staff continuity in skills and staff stafﬁng recruitment and SHM advice Culture of limitations retention is a short-term (Brandenburg) problem projects limits outlook Land 2022, 11, 599 8 of 26 Table 3. Cont. Governance Flanders Norway Spain England (UK) Germany Poland Structure (Belgium) Unequal distribution of Good quality Some shift in Commercial quality SHM advice in private adviser advisers more Public bodies advice consultation Level of activities to active than not very Good services, but advisers’ SHM environmental public advisers competent or knowledge Commercial scope could be knowledge and soil advice but ‘locked-in’ up to date, where advice and technical wider by company main role in linked to advisers Knowledge and Large range, goals supporting research emphasise Commercial practical some excellent fertilizer plans institutes and fertilizers advisers’ experience advisers Knowledgeable and subsidies, independent emphasis on (independent public advisers but high services but Big range in fertilization Soil fertility focus and in non- move to private standard of soil commercial SHM advice conﬂicts with commercial sector management in advisers have quality, poor advice for other Environmental initiatives) but the fertilizer focus quality linked soil functions shift commercial Organic sector independent to new but some shift Heterogeneity advisers have provides NRL untrained to supplying limited SHM high-quality advisers, good environmental knowledge SHM advice quality in advice organic sector Limited SHM training of Good Good In-service technical attendance at attendance at training in advisers dissemination dissemination Large range of ODRs Advisers’ Time and Need events events training training for resources for continuing courses, with All sectors need SHM advice soil training are education, as Limited time Good quality more offered in continuing often limited college training and resources CPD courses recent years education to inadequate for soil training but could be update college in all sectors more integrated training No uniﬁed certiﬁcation Horticulture Attitudes and Balancing Positive NRL High level of advisers’ A range of High level of motivations of commercial adviser personal commercial attitudes linked personal advisers and advantage and attitudes commitment to motivations can to advisers’ commitment to AAS farmer respect towards the soil SHM needed lead to low objectives SHM needed is important social value 4.1. Framing Conditions The case studies represent a range of biophysical, political, socio-economic and farm- ing contexts which determine the nature of the agri-food system, the distribution and intensity of production systems, the risk to the soil under agricultural management and public/private support. For example, in Norway, limited areas of arable land coupled with heavy rainfall, constrain timely tillage operations and has led to a national policy prioritising the reduction in the area under autumn ploughing in regions susceptible to soil erosion. In contrast, in Spain, low rainfall areas present challenges for farmers dealing with droughty soils. In Germany (Brandenburg), weather extremes mean water storage capacity, and water-saving cultivation methods are a priority. In both Flanders and Spain, specialised horticultural production systems put pressure on farmers’ businesses and, consequently, the soil, while elsewhere, extensive crops such as ‘soil friendly’ wheat have lower proﬁt margins. In England, arable farmers have expanded with more powerful machinery often implemented by contractors who do not always take account of soil conditions. Land 2022, 11, 599 9 of 26 With respect to the political context, in Norway and England, there are, to some extent, shared goals between the government and the farming industry (farmer unions and cooperatives) which allow farms to deliver on a range of policies including food production and environmental goals (water, biodiversity, climate, soil). In Spain, a dual system results where intensive horticulture is mainly driven by commercial interests while political interests of soil conservation are more present in extensive agriculture. In Germany, public district and regional ofﬁces identiﬁed a lack of direction about soil management from the federal government. From a socio-economic perspective, labour is expensive in Norway, and this affects farm proﬁtability; in Flanders, seasonal land leases hamper any investment in SHM, while strong manure regulations have implications for managing organic matter. Land leasing in Poland leads to exhausted soils, while in Germany (Brandenburg), the large number of cooperatives are well managed by expert agricultural scientists, although the farms themselves are struggling with liquidity. In family-based, non-horticultural farms in Spain, traditional knowledge about and habits concerning soil management continue to be passed on through generations. These variable contextual factors act as framing conditions for AAS for SHM. 4.2. Governance Structures 4.2.1. Governance Arrangements The six case-study countries have each evolved distinct AAS (and AKIS) in response to a range of framing conditions, with a different mix of public, private and farmer-based organisations (FBOs); non-governmental organisations (NGOs); and research institutes delivering advice that inﬂuences and impacts soil management in each (summarised in Box 1 from analysis of interviewee responses). The hybrid and dynamic nature of partnering and funding arrangements is notable across all the case studies. Consequently, there is a diversity and complexity of inﬂuencers on farmers’ decisions about soil management. The role of the public support varies across case studies. For most countries, the regional or district agricultural ofﬁces have been re-oriented away from technical ad- vice towards administration of subsidies and regulations, where the emphasis is on cross-compliance (GAEC) or supporting scheme applications. For example, in Baden- Württemberg (Germany), the soil service from district administration indirectly controls handling of soils according to the law. Other advice which directly or indirectly impacts SHM tends to be offered through a number of channels; it is often contracted out by the government to private companies, independent companies, FBOs and NGOs and focuses on aspects such as nutrient management and cross-compliance. Only the Soil Service of Belgium, an independent non-proﬁt organisation, is speciﬁcally dedicated to soil man- agement. Notably, a public face-to-face advisory service for soil is largely absent or very limited across the case studies. FBOs are signiﬁcant in Spain, where they are linked with technical soil advice in the production of high-value crops; in Germany, farmer associations are strong, and in Norway, which has a large independent membership organisation (NRL), soil advice is demand-led. The emergence and inﬂuence of the private sector is notable across the case studies. This encompasses a range of advisers working for input suppliers or independently. These advisers play an important on-farm role, where they support day-to-day farming operations. The powerful advisory role of private companies linked to input sales was characterised in some countries as the ‘commodiﬁcation of knowledge’, as one Polish respondent (PL3) remarked, “advice becomes more and more important, and knowledge becomes a commodity that can be bought or sold”. The role of FBOs and the private sector has implications for SHM advice as they respond to farmers’ production-oriented needs rather than public goods per se. Land 2022, 11, 599 10 of 26 Box 1. A summary of the main AAS governance arrangements relevant to SHM in each case study. Norway’s pluralistic advisory system comprises FBOs, public and commercial services. The Norwegian Advisory Service (Norsk landbruksrådgiving NLR) is a decentralised service which provides independent farm, phone and group advice through membership (most large cereal producers are members). NLR also receives subsidies for the organisation’s regional and local units to support public good objectives such as soil management and widening access. Other advice comes from advisers working for input companies, independent private consultants and agricultural business cooperatives (input and buyers). Governmental bodies, especially at the local and county levels, have a role in supporting fertilizer plans and subsidies, but there is limited governmental support and responsibility for advisory services. In Flanders, there are different forms of AAS and different sources of funding (regional and provincial funds, farmers’ contributions, industry). Public support is still important through funding of regionally embedded Research Stations (RS) which focus on physical and biological soil aspects and act as practical advisory centres, with group dissemination events linking research to farmers and advisors. The Soil Service of Belgium, an independent research and advisory institution, is the main RS for soil. Advisory services subsidised by the government include the CVBB (Coordination centre for education and guidance to sustainable fertilisation), with a focus on nutrient management, now replaced by B3W (Coaching service for a better soil and water quality), with a focus on improvement of soil and water quality. Provincial and regional ofﬁces manage administrative issues. FBOs (unions and associations, cooperatives), private consulting companies, Dutch advisors and upstream and downstream industries are a main AAS component and their attention is mainly on crop nutrition and fertilizers. In Spain, there are no public services that speciﬁcally provide soil advice on farm, although Agricultural and Fisheries Research and Training Centres hold ﬁeld events for crop nutrition advice, and regional agricultural ofﬁces offer technical advice and training to farmers but are mainly concerned with managing subsidies. Agricultural unions, universities, RDP and operational groups are also involved in advice initiatives. The dominant type of AAS in Spain is the FBOs, the OPAs and the Agro-Food Cooperatives, which are linked to high-value crops and hire their own agricultural technicians, supply companies, certiﬁcation bodies and have large and established structures. They also have innovation and development centres and provide training to farmers. Farmers with extensive low proﬁt systems (cereals and woody crops) have less access to technical soil advice at farm level. In England, the AAS is diversiﬁed and highly fragmented following privatisation. For on- farm advice, agronomists/consultants (independent or commercial) tend to dominate. Where there are commercial interests, historically the emphasis has been on fertilizer recommendations; however, consultants also provide agri-environmental services. Levy bodies (independent/FBOs) offer knowledge exchange for sector production support. Public supported advice has been linked to agri-environment schemes and catchment-based initiatives (soil management to manage diffuse pollution), where cross compliance was a key objective, delivered in partnership with government agencies, water companies and contractors through on-farm and group advice. The government is prioritising supporting public goods (with an emphasis on soil) post-Brexit. A range of NGOs have become increasingly important in facilitating initiatives relevant to all soil health functions. In Germany, there is a heterogeneous and decentralised governance structure where the Federal Government and the 16 Länder take an active role. Due to limited funds, most state services are becoming privatised. These are: (i) the state agricultural ofﬁces (free public extension providers) that engage in rural development and regulatory issues, and they also attend to local soil issues; (ii) the chambers of agriculture that offer free and charged advice, education and training; (iii) private consulting and advisory companies offer fee-based advice on specialised topics such as production and business management; (iv) numerous upstream and downstream companies also contribute, as do a broad range of actors who belong to FBOs (boundaries between private organisations and FBO are often ﬂuid). Privatised advisory companies play a key role in the eastern German states. In Poland, advisory services are provided by the state (Agricultural Advice Centres (ODRs)), agricultural chambers, private advisory organisations, companies and NGOs. The ODRs are in Brwinów (centre), branches and Voivodships and are responsible for the education, certiﬁcation and registration of advisers in Poland. They offer ﬁnancial and economic advice, while technological advice is limited, as well as organise training courses for farmers. Private agricultural organisations operate in the scope of the publicly funded measures under RDP and other national programmes. Commercial ﬁrms, which are extensive, supply advice as part of inputs sales and interact with ODRs. There are a large number of certiﬁed individual agricultural advisers who work for various institutions, private companies and farming communities under contract. There are also a large number of active FBOs, and Poland has a long history of agricultural production cooperatives. Land 2022, 11, 599 11 of 26 4.2.2. Integration/Fragmentation None of the case studies could be described as having an integrated framework for delivering soil advice. They exhibit different extents of integration and fragmentation in the AAS, which can be characterised by both cooperation and competition (for farmer clients and for project funds) between organisations. With respect to inter-organisational cooperation, in Norway, private or FBOs cooperate and receive support from public bodies for topics relevant to SHM which do not lend themselves to commercial services. In Flanders, increasing collaboration between the CVBB and B3W advisory services provides a good example of the joint effort of several research institutes to address soil topics. Meanwhile, in England, although the AAS is horizontally fragmented, with multiple uncoordinated actors, organisations and delivery activities concerned with advice for different soil functions, there are a number of partnerships and initiatives where organisations work together towards a shared goal for SHM and water quality (for example, Catchment Sensitive Farming initiative). Synergies were identiﬁed in Poland, where the public ODRs host training events which bring together large numbers of farmers and invite private-sector companies, who are knowledgeable about the technologies or products, to participate. However, in Spain, a duality of advice was described with a clear distinction between public and private services, which has implications for soil advice. There were different perspectives in Germany depending on experiences in the re- spective states: One respondent described few links between providers and competition between the different consultants and large companies. However, for another respondent (for Baden-Württemberg), the interaction between the state and private consultants at the agriculture ofﬁce level was a strong point, and they agreed that synergies deﬁnitely exist, while there may be tensions between individuals. In line with this viewpoint, the fragmented landscape and different objectives of public and private providers can have consequences for SHM at the farm level. In Spain, although most respondents did not identify tensions or conﬂicts in advisory service delivery, one respondent acknowledged that contradictions arise when there are commercial interests: The system is not fully integrated, this affects sustainable soil management negatively because conﬂicting advice is given, or conﬂicting objectives are pursued [ . . . .] when there are commercial interests, we do ﬁnd contradiction. ES2 As with Spain, in England, while advice is “theoretically joined up” (for example, a partnership will have shared goals), what actually matters is at an individual farm level, where farmers can be contacted by a number of advisers or projects ofﬁcers. One respondent (UK2) said, “I wouldn’t say that there’s contradictory advice now, but duplication”, and also noted that farmers have been advised to do things by a commercial company which are questionable with respect to SHM. A Polish respondent (PL3) also described tension and competition between companies providing agricultural products. Although, as another respondent explained, this depends on the company: There are companies whose approach is to sell their products, and there are companies that act for example together with associations promoting the welfare of the natural environment recommending the use a range of suitable products. PL2 Regarding vertical research–practice linkages in the soil context, these are considered strong for NLR in Norway which has good links with research; forexample, it is quite common for NLR and the research institute (NIBIO) to be cooperating in projects. This ensures good dissemination but also that projects are relevant to farmers. Researchers, farmers and advisers are also linked in Flanders, where research stations have strong outreach programmes, and in some states in Germany, where district agricultural ofﬁce carry out practical trials with farmers. In Spain, in the horticulture cooperative sector, there are strong links from research to farmers providing a comprehensive service to these particular farmers. In England, the perception is that research and practice are disconnected, Land 2022, 11, 599 12 of 26 and as the respondent UK2 said, “It’s actually the translation of that [research] into current farming practices, which is where the gap is”. 4.3. Advisory Services Capacity 4.3.1. Management and Organisation for Delivering Advice on SHM Some respondents considered that there is good organisation and management of AAS but that other limitations prevent effective delivery of SHM advice. For example, in Germany (Brandenburg), the AAS are thought to be well equipped and prepared in terms of technical capacity, with an excellent research infrastructure around Berlin, but lacking political guidance about soil from the federal government. In Spain, some respondents agreed that despite good organisation and management of advice, more information and knowledge transfer are needed for effective SHM advice to be achieved. In Norway, there was consensus from all three NRL (farmer membership organisation) respondents that they have both competence and capacity to deliver advice on SHM. Furthermore, they were optimistic that advice will improve as public funding is now available to increase the focus on soils. The capacity of public services, where they are provided, tend to be limited by re- source constraints, namely, staff and ﬁnancial. In Germany, there was a sense of good capacity and resourcing in the consultation services hosted by the state agricultural ofﬁce in Germany (e.g., Baden-Württemberg); however, respondents noted the stafﬁng limitations of public provision and the need for strong personal commitment. This is reiterated later in the analysis: From the public side, we in the agricultural administration are mostly limited by the staff capacities. That is an aspect, which has deteriorated dramatically everywhere in recent years, so if we want to work towards [soil] sustainability, it’s only possible through increased commitment beyond the actual working hours. GR1 Furthermore, the emphasis on inspection and regulation by state bodies in Germany limits their time and scope of work with a focus on inspection. As a consequence, farmers supplement public advice with consultations by private companies. The Polish state Agricultural Advisory Centres were described as working well to provide advisory services but not yet properly prepared to advise on soil protection, still being stuck in the “old structures and treatments” (PL1). They are also constrained by funding and often lose their best advisers to the private sector. The potential of private companies to ﬁll the gap left by public services was identiﬁed in Poland. There was consensus that private companies are more visible and accessible and able to meet market demand. Referring to horticultural crops and crop- and soil-borne diseases, this respondent (PL3) remarked: There are private companies that have appeared in the market and provide these services at a good level [ . . . . . . .].. The institutes [public] have the potential, equipment, experience and knowledge, but it seems that due to ﬁnancial and personnel constraints as well as other obligations, they are unable to respond to the very high market demand, and it is very large, while possibilities for conducting research are limited. Private companies, which are more and more visible on the market, are trying to ﬁll this gap, which is good, because such companies can provide services as part of, for example, soil or plant research projects. PL3 However, for private services, the business model is not always commensurate with build- ing capacity. In England, privatisation of the advisory services has introduced a profit incentive which impacts resourcing, as one respondent, who works for a consultancy, explained: We have to be a proﬁtable organisation, which means that we haven’t the luxury of an inﬁnite amount of time [ . . . ..] we do the very best we can with the resources we’ve got, but that some of the expectations of what it actually costs to deliver service are unrealistic. UK2 Land 2022, 11, 599 13 of 26 This is also a factor in Germany, where dealing with new issues, such as supporting the necessary transition to new cultivation systems or meeting the state policy requirements for environmental programmes, represents an added effort for the consultation services in terms of costs, time and energy. However, adaptation is seen to be essential to ensure future services: And every consultation service is required to adapt, to continuously improve, and to be up to date with the latest science and technology. I think that’s actually a very positive development [ . . . .]. But it is clear to them that if they do not consult their farms in the direction of sustainability, they will lose them completely in 10–20 years. GR1 This need to build capacity for the future is reiterated by a respondent (GR3) who works with large cooperatives south of Berlin, where the long-term nature of soil health has become the focus of attention amongst the scientists who advise on the farms. Private organisations also ﬁnd that they have to compete for project funding. In Flan- ders, although the quality of advice is good for soil in the government research institutes and the independent Soil Service, the resourcing of activities is seen to be constrained by a reliance on short-term project funding, reducing the chance to build strong and enduring relationships with farmers. The remark “True sustainable soil management advice does not exist to my knowledge, the Soil Service provide such integrated advices only as part of projects” (BE3) is insightful in that it indicates poor continuity, as well as a dependence of projects for funding. Staff recruitment and retention has implications for advisers’ expertise and experience in SHM and was mentioned across a number of countries. In Norway, it can be difﬁcult to recruit advisers who possess sufﬁcient knowledge about soil if, for example, an experienced adviser retires. High turnover of advisers due to a lack of job satisfaction or progression and ﬁnancial motivations exacerbates this. In Spain, advisers who belong to technical departments in FBOs (companies/associations) are seen to have more room for manoeuvre and are more organised and professionalised compared to commercial advisers. The absence of planning for the necessary skills and staff which may be needed in 2–4 years’ time was also raised as a limitation for SHM advice in England. Regarding an organisation’s culture, there was also recognition that advisory organi- sations themselves have some responsibility to rethink how they advise farmers who are overburdened, face severe economic pressures and are constrained in terms of investing in new equipment, new crop rotations or new fertilization methods. In this respect, the culture of the organisation is seen to be important in Germany, where every consultation service has a speciﬁc philosophy that is shaped by the organisations’ decision makers. 4.3.2. Level of Advisers’ Knowledge about SHM In the pluralistic advisory systems described here, it is difﬁcult to characterise the expertise or the quality of advice for soil overall and SHM speciﬁcally, as this can depend on the sector and systems they support. However, the following provides some insights. Knowledge and Practical Experience Practical experience is seen as indicative of good quality advice and private advisers are more likely to acquire this, compared to public advisers, due to their regular on-farm activities. For example, the quality of advice is considered high in consultation services in Germany, although the focus is limited, and wider aspects of SHM advice are not covered: I think, the quality of consultation is high [ . . . .] many of the consultants are running agricultural businesses themselves, so they have a certain practical background, or they have simply been working at an agricultural ofﬁce for many years, so they have a very high level of knowledge [ . . . .] so far,[this] has mostly been on crop protection and, I think, especially in terms of sustainability, sustainable soil management, crop rotation, intercropping, things like that—there is still room for improvement. GR2 Land 2022, 11, 599 14 of 26 Similarly, in Poland, private advisers were regarded as more effective and active than state advisers who, although knowledgeable, lack practical experience and the ability to follow up on advice to keep farmers up to date: A strong point of commercial services is that they have capable advisers. With regard to government institutions, their strong point is certainly their infrastructure and the preparation of speakers, i.e., advisors, who are very knowledgeable, but then somehow nothing happens. And this is the weak point, that there is a lack of continuity, on-site continuity, during on-site workshops. Often these advisers lack practical experience and [ . . . . ] are unable to keep up with these new solutions and products. PL2 Another Polish respondent (PL3) noted that, with the loss of good quality government advisers to the private sector, their expert knowledge now only reaches farmers who are customers of private companies. This unequal distribution of quality advice (including SHM) was also identiﬁed in Spain, where technicians with a good level of specialist expertise in horticultural production support intensive crop growers, but family-based businesses with extensive systems in other sectors in Spain have limited access to good quality advice on soil. Furthermore, pockets of high-quality SHM advice were described for advisers in the organic sector, as mentioned in Poland and in Spain, and for advisers selling products related to, for example, organic or sustainable management who “provide information about the nature of living soil, biodiversity or soil quality” (PL2). In Norway, governmental and public bodies, especially at the local and county levels, were described as not very competent or up to date, with a main role in supporting fertilizer plans and subsidies. However, the respondents all agreed that the standard of advice for soil management is high in the independent NRL, where the advisers are knowledgeable and have an increasing focus on soil health and environment. Soil Fertility Focus In all case studies, there was agreement that private advisers (working for input companies or as independents) are generally trained to advise on soil from the perspective of fertilization and crop nutrition and tend to look at crop management in the shorter term. This emphasis was noted by a respondent (PL3) in Poland who said, “My impression is that most advisers focus only on the composition of the soil, on just the chemical factors, but they ignore and totally undervalue the importance of soil microbiology”. A number of respondents called for a change in the mindset of advisers away from production-orientated to more holistic advice, with a shift in thinking from soil chemistry to a microbiological approach required, to show that “living soil can achieve more”. This focus on soil fertility and crop nutrition can have some negative implications. For example, in Flanders, commercial advisers were known to advise maximum fertiliser recommendations irrespective of crop requirements, which is contrary to good practice recommended by research organisations. This was also noted in Germany, where an emphasis on fertilization as part of an overall crop care package can lead to conﬂicts with advice for other soil functions. This respondent in Poland highlighted how some advisers are ‘locked-in’ by their company’s commercial imperatives despite being knowledgeable: Many advisers are enslaved by receiving payment from the company, so they have to advise according to the company’s offer, and this limits their freedom to act; they have the knowledge but they will necessarily be focused on bonuses, on a raise, on ﬁnances, and this restricts them. PL3 However, respondents did not think commercial advisers purposely provide negative advice, although they may be slightly less inclined to look at the environment or at soil quality, soil biology, etc. In Spain, where consultants are often inﬂuenced by their employers, one respondent suggested that there is no intention to damage soil; however, they may not be aware of the externalities of their advice: I don’t think there is one main advisory service that has either a positive or negative impact. Normally advisers have the objective of increasing overall production. The adviser does Land 2022, 11, 599 15 of 26 not go against soil sustainability or soil quality, but [ . . . ] the use of these technologies continuously without other guidelines in the end leads to an overall degradation of the system, mainly of the soil. ES2 Environmental Shift The Green Deal and the demands from supply chain companies and retailers to meet food and farming standards and gain a market advantage were considered by many respondents to be driving advisers towards SHM advice. However, there is some cynicism in Poland that advisers and input-sellers are using slogans related to environmental and soil protection issues but, fundamentally, are still largely dependent on the producers of chemical agents for their income. In England and Germany, there has been a shift in commercial adviser activities to- wards supplying environmental advice (supporting agri-environment scheme applications, as well as practices for good soil management), and for agronomists linked to input sales to sell cover crop and, pollinator seeds and biosolutions. A German respondent described the growing demand: In recent years companies have emerged that strive towards sustainability, selling crop fortiﬁers, soil additives and so on. Active local consultants and some farms use these products in their cultivation. This is of course due to the fact that, in the last few years, little has been done in terms of soil fertility and sustainability on many farms. They are now reaching their limits in terms of plant cultivation, they have problems with diseases, with the soil, etc., and companies, which offer the appropriate products, have been in greater demand in recent years. GR1 This situation is replicated in Poland where more companies are entering the market with ‘natural products’ aiming to meet farmer demands. Heterogeneity One common factor across all case studies was the heterogeneity in the quality of advisers with respect to soil advice, with a spectrum of very good to very bad commonly being described. In Spain, a range from very good agricultural technicians to others who do not have the necessary knowledge was linked to the number of untrained advisers emerging to meet the increasing demand for sustainability and ecological advice. Similarly, in England, a respondent (UK1) referring to agronomists said, “I think the good are very good, but I don’t think we’ve got many very good ones, I think a lot of us are in the category of willing triers”. However, he acknowledged that there are excellent pockets of SHM advice amongst independent advisers and non-commercial initiatives. This range is echoed in another comment by a respondent from England who described the value of long-term experience: Some of them are extremely knowledgeable and interested [about soil] and have been in their post for quite a long time. Some of them are on short term contracts. And some of them who are less good than others, in terms of their understanding of the technicalities of what they’re talking about, and what they’re being asked to do. UK2 The same sentiment was expressed by respondents in other case studies, where advisers develop a very good reputation because they have been in the profession for many years. A range of abilities and interests was also described in Germany, where the ease of substituting SHM principles with agrochemicals was blamed on a lack of attention to soil by some advisers: There are consultation services, or even individual consultants on the part of the industry, who attach importance to the topic [soil]. But there are also people who have never bothered with the subject, because it is still possible to achieve good yields with the use of mineral fertilizers or chemical-synthetic pesticides. GR1 The distinction between the role of the advisers as generalists or experts was widely discussed. There are very few agricultural advisers across the case studies who focus Land 2022, 11, 599 16 of 26 speciﬁcally on the soil or get the opportunity to become experts. Some take the view that soil experts can be consulted when necessary, but that wider skills are needed at farm level, as this respondent explained: Rather than being experts on that particular aspect, we reﬂect the farming community, in the sense that we are people with a wide range of skills, but an expert in nothing. An expert—he’s talking purely about the soil, and the health of the soil, we will be talking about it on the proﬁtability of the rotation, the control of various injurious weeds, diseases and pests, and then looking at a rotation that is sustainable, which then comes back to the soil. However, we know where to go to get expert [soil] advice. UK1 Differing perspectives on the value of experts versus generalists were picked up in the Spanish interviews. One respondent agreed that a historical focus on supporting production has led to fragmentation where an agricultural technician may know a lot about tillage or agricultural equipment but does not have a general vision of sustainable soil management. The other two respondents in Spain, however, argued that advice to farmers on soil management is too general and the level of expertise low; one (ES4) identiﬁed “A strong need for the participation of people who are soil specialists—soil scientists, biotechnologists with application to soil microbiology”. 4.3.3. Advisers’ Training for Delivering SHM Advice There are a number of opportunities through multiple talks and events for all advisers to expand and update their SHM knowledge, mentioned for all case studies. In Flanders and England, for example, large numbers of advisers reportedly attend dissemination events and demonstration days, and for many, this is important for networking. In addition, there is now comprehensive information about soil topics on the internet and social media and opportunities for peer-to-peer learning and exchange. However, as noted already, poor attention by advisers to SHM has been attributed to the absence of good training. Time and resources for soil training are a concern for some. As one respondent (N2) in Norway noted, “unfortunately we have to prioritise covering our hourly rate as employees, so that can affect how much time we have to educate ourselves, go to conferences, seminars”, illustrating the fact that advisers (from all organisations) are often under ﬁnancial targets and pressures to the detriment of their training and upskilling in SHM. This imperative steers organisations’ decisions about training as well. In Flanders, for example, obtaining a certiﬁcate (Flemish Land Agency certiﬁcation or other quality control procedures) is costly both in terms of time and money, and as a consequence, certiﬁcation is proﬁtable for only a few advisory institutes/services. There are a large number of options for in-service training in Poland with ODRs taking on a key role for farmers and advisers. Advisers within the commercial sector in Poland are also considered well trained but only within the sphere of their operations and products: It seems to me that every commercial business tries to train its advisers so that they do at least have this information as regards their own products, how they affect the soil and therefore they must have prior knowledge or learn about the soil, its quality, the processes that take place in the soil environment. PL3 In Spain, the nature of skills and training depends on the type of agricultural tech- nicians (cooperative, input company or independent). Most respondents agreed that the level of SHM training of technical advisers in Spain is low overall, as one remarked (ES2): “Advisers do not have sufﬁcient skills and experience to give advice on sustainable soil manage- ment [, . . . ] because they have not had sufﬁcient training during their studies”. As such, these agricultural technicians need to seek out further training to enable them to meet chang- ing demands. These points were reiterated for Poland, where the notion of continuing education was raised: Every adviser needs to participate in continuing education, as the knowledge gained when graduating from college is not enough [ . . . .]. It is necessary to educate, educate and Land 2022, 11, 599 17 of 26 again educate advisers and farmers, and to provide this new knowledge about sustainable soil management, which is completely different from the information provided before. PL1 Another respondent from Poland (PL3) supported this, remarking that studies are only the basis and a good adviser has to train for the ‘rest of their life’, otherwise, they quickly lose touch with reality. In Spain, respondents noted that there is no uniﬁed certiﬁcation validating the agricultural technicians’ knowledge. In Germany, large differences in the range of training courses were described, with more being offered in recent years. In England, there is an established continuing professional development (CPD) scheme for advisers (FACTS, BASIS) which offers courses on soil and water management. While acknowledged to be outstanding compared to other European countries, a respondent pointed to the inadequacy of these courses in terms of SHM: In terms of sustainability, I think they’re both useless. They’ve evolved out of a commercial requirement. So it wasn’t evolved to deliver good, independent, impartial information [ . . . ] they do provide a level of professionalism. UK1 Another respondent from England thought that a FACTS-qualiﬁed adviser would understand about nutrient management but argued that BASIS is too technical and aca- demic and that the modular training does not prepare advisers to deliver integrated advice, considering soils, nutrients, water management together, nor help them understand the underlying principles of SHM: So as far as, is the training ﬁt for purpose for the next generation of advisors? One of the problems that we and the whole industry has got to know that there’s plenty of advisers who are qualiﬁed, but not necessarily have a good understanding of the principles[ . . . ] you need to be able to understand what you’re doing. And why are you doing it. UK2 There was also agreement that capabilities need to be expanded to beyond a focus on production objectives and soil fertility and crop nutrition advice, to meet new demands, reinforcing the points made earlier. This respondent from Spain noted that this was a key limitation for SHM advice: From my point of view, there is enough organisation to provide advice on sustainable soil management and there are enough people capable of providing basic guidelines for sustainable soil management but there is a lack of general training on what is the true nature of soil quality beyond nutrient fertility. ES3 The extent of informal learning through adviser networking was mentioned by some respondents but did not emerge as a particularly strong aspect in the interviews. 4.3.4. Attitudes and Motivations of Different Advisers and AAS Positive adviser attitudes towards the soil were described by a number of respondents, however, there is still a range of attitudes linked to economic motivations. Fundamental differences in motivations between advisers were identiﬁed in Spain and this aligned to their organisations’ objectives: An adviser who belongs to a trade union or a regional agricultural ofﬁce has a different vocation than an adviser who belongs to a commercial company or to a research centre; their motivations are very different, which means that their inclinations are also very different. ES1 This can have implications for advisers’ reputation and credibility. According to respondents, for example, in the horticulture sector in Almeria, agricultural technicians do not always have high social value and may even start to have a bad reputation. This is echoed in Poland, where the balance between commercial advantage and gaining farmers’ respect was seen to be important: “There is no doubt that an advisor’s motivation is inﬂuenced both by economics and by the desire to be respected by farmers, it really depends on the person” (PL1). Many agreed that farmers are able to quickly discern any ‘shortermism’ and the commitment and motivation of advisers. Land 2022, 11, 599 18 of 26 For many respondents the different motivations and attitudes of the individual adviser were regarded as more important than the type of organisation they belong to. The high level of personal commitment required by some advisers to pursue their interests in, and deliver, SHM advice was mentioned by respondents. Consultants in Spain, for example, are often limited by speciﬁc short-term projects or task forces. When these are ﬁnished, if they want to continue with the topic, this has to be done in their own time. Similarly, in Germany, personal effort is linked to quality advice: Yes, well, there are advisers who are just all-around good advisers who really give their best and try to constantly educate themselves in order to be able to provide the best possible consultation to the farmers . . . I think most of the vocational counsellors actually—and yes, I think that of the ones that I know, most really put their full effort into it. GR2 5. Discussion 5.1. Governance Structures This analysis conﬁrms the picture painted by previous researchers of considerable AAS diversity between, and pluralism within, European countries . This translates into a diverse landscape for SHM advice with different governance, funding and delivery mech- anisms and no evidence of any integrated advisory frameworks for delivering advice for soil management. The analysis shows that institutional options available for ﬁnancing and the level of coordination are limited with respect to delivering advice for soil management, as observed elsewhere for AAS more generally [50,56]. A reduced central organisational role of government agencies in AAS and an emerging ‘knowledge market’  has led to a continued decline in the public sector ’s role in delivering on-farm soil advice for all case studies, with the diversion of their resources and staff towards compliance regulation and scheme/grant administration. Conversely, the prominent role of the private sector, independent organisations, FBOs and NGOs is apparent in ﬁlling the gap in delivering on-farm advice that inﬂuences and impacts soil management, either through contracts (projects) to fulﬁl government objectives (e.g., FAS, grants) or commercially in a more market-led environment, as described in other AAS studies . When state and private advisors are incentivised to administer regulations and grant applications, this narrows down choices and limits broader understanding of ‘know-why’ soil processes [14,72]. New services are also emerging, and overall, the number of advisers with commercial links to economic actors (input suppliers, consultants) is increasing . Fragmentation means competition for clients and project funding, and soil advice at farm level can be compromised by conﬂicting delivery or duplicating advice in multi- partner approaches, as reported by others . However, many hybrid and dynamic arrangements for partnering and funding for delivering SHM advice are notable. These ‘creative alliances’ provide opportunities for the effective integration of delivery of soil advice at programme level. This ability of pluralistic advisory services to overcome con- straints (shortages in funding, stafﬁng, etc.) through increased cooperation, collaboration and partnerships has been observed elsewhere [29,71,74,75]. Individual relationships of both competition and cooperation, described by Compagnone and Simon , were not shown in this analysis. 5.2. Advisory Services Capacity These governance arrangements provide a backdrop to understanding different or- ganisational arrangements and capacity to provide SHM. 5.2.1. Management and Organisation Capacities for SHM Advice The analysis identiﬁed organisational constraints in resources, funding and stafﬁng, notably in the public services, which are not always able to meet demands, and this impacts the capacity to deliver SHM advice. There are inherent frustrations concerning reliance on short-term project funding for developing and continuing with advice streams, as previously described for environmental advice [31,76]. This often means only committed Land 2022, 11, 599 19 of 26 advisers continue with the SHM advice when the project ends. Poor staff retention , with the loss of advisers’ knowledgeable about SHM to the private sector, reduces farmer access to SHM advice. Although farmers might look outside of formal advice in such circumstances , their options for beneﬁting from high-quality soil advice are diminished. Other commentators have noted that commercialisation threatens the extension capacity of government agencies , however, technical expertise has not been considered. Investment in staff capacity for SHM advice (training and ﬁeld days) is restricted in both public and private sector organisations by limited time and resources and the competitive business environment. Small ﬁrms also struggle to meet new environmental requirements, corresponding with previous observations [34,42]. Furthermore, in some commercial organisations, economic drivers can lead to an organisational culture that values input sales over expertise in SHM. These organisational capacities affect individual advisers’ capacity to operate effec- tively, their objectives and motivations, their professional culture and the support they are offered to deliver SHM. As observed by Klerkx and Jansen , this wider set of in- stitutional conditions, and the relationship with the ‘back-ofﬁces’ which supports them professionally, is critical for enabling advisers to develop and deliver specialist and pro- fessional advice. Furthermore, maintaining a stable or increasing workforce as well as diversifying the expertise and increasing the competence of staff are seen to be critical for AAS . 5.2.2. Individual Capacities for SHM Advice Individual capacity results from a combination of attributes: quality of advice; training; and motivations in relation to SHM. Firstly, regarding advice quality, heterogeneity in levels of advisers’ soil knowledge was observed across all cases and across all AAS types, with few advisers considered to be delivering all-round high-quality advice to support SHM. This adds to the emerging body of evidence showing that advice on soil management is suboptimal. What constitutes ‘good quality advice’ with respect to soil management was understood differently due to advisers’ varying goals and their clients’ needs. It was generally characterised by, not only extensive on-farm practical experience and a good level of subject-matter knowledge or expertise , but also critically by an understanding of soil chemical, biological and physical processes and principles . Private advisers (commercial consultants, technicians and agronomists), while being credible with respect to providing high-quality technical advice, are limited in scope to soil fertility and crop nutrition. This observation is supported by studies showing the predominance of advice based on nutrient testing and interpretation to support farmers’ short-term production decisions, e.g., . This limits opportunities to incorporate soil health perspectives into advice, which are critical to understanding the capacity of soil to function as a vital living system [16,17]. Only very few advisers are taking a holistic approach, accounting for non-linear mechanistic relationships between various physical, chemical and biological soil properties considered important for soil health . The signiﬁcance attributed to practical experience, however, should not be overlooked. This allows advisers to provide localised advice and meet the ﬁne resolution of soil infor- mation and data that farmers require . This highlights the value of experiential learning (and co-learning with farmers), which has a particular signiﬁcance for soil management due to the in-ﬁeld observations and sensory experiences required [79,80] and is highly appreciated by peers and the practitioner community . Equally, whilst expertise in soil science and management (demonstrated by some individual advisers) is valued, the role for the generalist agronomic adviser who takes a whole farm perspective is seen as important. Interestingly, advisers have been shown to be capable systems thinkers  and positioning SHM within the wider farm business and environment is in itself an important skill. Further specialisation, in, for example, soil microbiology was called for by some respondents, in line with emerging farmer interest in soil health, but how such specialists would position themselves in the AAS Land 2022, 11, 599 20 of 26 landscape was not elaborated. Landini  suggested that not all individual advisers can hold the same knowledge and capabilities but instead can act in groups to enrich their work. This professional distribution of advisers’ SHM roles, skills and specialisms and the way they interact, complement and learn from each other, is an interesting area for future research [24,79]. Furthermore, the changing role of the technical ‘expert’ needs consideration . Secondly, with respect to training, poor investment in training and particularly in continuing education in SHM in both private and public spheres was seen to be a key reason for the limited scope of advisers’ expertise. Training and professional development courses on soil topics, whilst considered to be at a high standard in certain countries, do not always provide an understanding of the principles and processes of SHM. A number of studies have shown that advisers are increasingly relying on each other for sharing soil expertise through professional networking ; however, this was not identiﬁed in this analysis as an alternative to training. These ﬁndings are inconsistent with previous studies , although the focus was not SHM. Thirdly, regarding motivations, personal intrinsic interest in soil was a further facet demonstrated by a few public and independent advisers. The economic motivations of private sector advisers’ (linked to input sales) observed here are widely reported in studies that concern soil [10,36,83]. The image of advisers as ‘locked into’ supporting intensive agriculture pathways has been also described for high-input production systems [26,84], as has the power of supply chain actors . However, analysis here suggests a more nuanced picture, with many private advisers balancing economic motivations with the need to retain respect, social value and trust in the farming community. This loyalty dilemma between private good (what the farmer demands and pays for) and public good (issues of broader importance for society as a whole) , may need to be re-examined in a future context when incentives for providing SHM become available (e.g., carbon farming, Environmental Land Management Schemes in England). Organisations are already responding to the market and offering a range of environmental services, and supporting sales of ‘natural’ biological products. However, the depth of understanding and commitment that accompanies these was queried, and there were calls for a more fundamental shift in advisers’ mindsets. Professional culture is closely connected to individual advisers’ motivations and mind- sets, accepted norms and values, how they perceive and execute their tasks , and their performance rationale and economic strategies . However, adviser roles are not set: Nettle, Crawford and Brightling  describe the ﬂuid nature of adviser professional iden- tities and opportunities for evaluating their roles through reﬂective practice [41,85], which, if organisations were more ﬂexible, could lead to reorientation of soil management advice. 5.2.3. Narrowing Down Although it was not the intention here to assess the performance characteristic of the framework, some observations can be made. The needs and opportunities, which characterise performance  that have been steering advice in relation to soil are: policy (cross-compliance regulation and grant administration support) and markets (farmer de- mands for crop production advice). As a result, there has been a narrowing down of soil advice, both with respect to content and access, as depicted in Figure 2. However, the increasing interest in soil health from both farmers, in part due to the recognition of soil degradation [18,86], and policy makers, will provide the new drive and opportunities to widen the scope of advice to cover physical and biological, as well as chemical, processes. To achieve this, AAS organisations will need to invest in adviser training and capacity building and aim to shift professional cultures and mindsets at or- ganisation and individual level. This will require incentivisation, and Dhiab, Labarthe and Laurent  identiﬁed a need for public policy intervention to support this. This could be through, for example, strengthening national FAS with requirements for member states to provide standardised and certiﬁed adviser training and continuing professional development in SHM. Ultimately, however, AAS are shaped by the framing conditions, Land 2022, 11, 599 21 of 26 the priorities within the agricultural sector strategies (high-value commodities or environ- mental sustainability) which are beyond the direct inﬂuence of policy makers and advisory services managers . In turn, these determine the governance structures and the relative capacities of public, private or NGO AAS and the services offered. As Knierim, Labarthe, Laurent, Prager, Kania, Madureira and Ndah  point out, the historically grown, path- dependent institutions and institutional constellations in each EU member state play an important role in AAS. Figure 2. This ﬁgure shows how the collection of capacities act to narrow down the nature and extent of advice for soil. Changing needs and opportunities will open up the scope of advice for delivering SHM. There have been calls for capacity building in knowledge systems at individual, organisational and AKIS levels . This encompasses adviser training and professional development and more back-ofﬁce support [28,85] as well as the need to understand the varying roles of professional advisers . However, the focus has often been on process skills, the (new) intermediary, advisory styles and facilitatory skills that advisers should master to support and empower farmers in networks of interactive learning . Adviser technical or specialist roles have received less attention, notably for soil, despite the growing demands placed on them for understanding and supporting land managers in the management of complex soil functions. 6. Conclusions The framework employed allows the collective capacities (governance structures; organisational and individual capacities) of AAS for SHM advice to be revealed. It shows that advisers’ competences and skills should not be seen in isolation. As such, the rec- ommendations for expanding the scope of content and access to SHM advice include addressing deﬁciencies in training and capacity building, shifting professional culture as well as addressing more deep-seated institutional conditions and governance structures. Incentivising such changes will require changes in both policy and market drivers. These insights show that AAS can play a central role in the transformation of food systems more widely . The method based on in-depth interviews (18 experts) provides insights for a cross- section of European countries offering a range of perspectives, as well as common themes with respect to capacities which affect the nature and extent of SHM advice. However, the results can only be indicative for Europe as a whole and further qualitative and quantitative research will be needed to provide a more comprehensive picture. In particular the results Land 2022, 11, 599 22 of 26 show how different advisory services that inﬂuence and impact soil evolve in speciﬁc country contexts. This suggests that the model of identifying systems that best ﬁt context- speciﬁc conditions is suitable for future support of national AAS with respect to SHM. Critically, the methodology did not explore the complexities of the relationship between advisers and farmers/land managers, nor capacities in terms of the soft skills required for co-producing technical soil knowledge or the changing mature of the ‘expert’ role of advisers. With the accelerated move towards the integration of soil health issues in a number of European Commission strategies and the actions and ambitious targets set for soil health within the Soil Mission ‘A Soil Deal for Europe’, the requirements for building capacities and a knowledge base for soil health enhancing practices in agriculture will increase . This will require member states to signiﬁcantly enhance their AAS capacities to achieve this desired transition, with implications for both European and national level policies. Supplementary Materials: The following supporting information can be downloaded at: https: //www.mdpi.com/article/10.3390/land11050599/s1, SoilCare advice review Interview schedule. Author Contributions: Conceptualization, J.I., J.M. and C.-A.C.; formal analysis, J.I. and C.-A.C.; investigation, J.M., J.E.B., C.-A.C., J.A.A.-S., A.E., M.F., B.L.-F., P.M.-G., K.S. and J.S.; methodology, J.I. and J.M.; project administration, J.M.; resources, J.M.; supervision, J.M.; writing—original draft, J.I.; writing—review and editing, J.I., J.M., J.E.B., C.-A.C., J.A.A.-S., A.E., M.F., B.L.-F., P.M.-G., K.S., J.S. and M.T. All authors have read and agreed to the published version of the manuscript. Funding: This work was part of SoilCare (Soil care for proﬁtable and sustainable crop production in Europe). Grant Agreement 677407 funded by the European Union’s Horizon 2020 research and innovation programme. www.Soilcare-project.eu (accessed on 20 September 2021). 2016–2021. This funder had no role to play in the design, data collection, analysis or interpretation of results presented here. Informed Consent Statement: Ethical standards and guidelines have been applied to the collection, processing and storage of data about persons, in accordance with the agreed project ethical statement. All subjects gave their informed consent for inclusion before they participated in the study. Data Availability Statement: Data are conﬁdential and not available. Acknowledgments: We acknowledge the support given by other partners and stakeholders in the SoilCare project and in particular the interview respondents. Conﬂicts of Interest: The authors declare no conﬂict of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, or in the decision to publish the results. Abbreviations AAS Agricultural Advisory Service AKIS Agricultural Knowledge and Innovation System FAS Farm Advisory System FBO Farmer based organisation NGO Non-governmental organisation EU European Union GAEC Good Agricultural and Environmental Condition PROAKIS Prospects for Farmers’ Support: Advisory Services in European AKIS NRL Norwegian Advisory Service (Norsk landbruksrådgiving) SHM Soil Health Management SSM Sustainable Soil Management CVBB Coordination centre for education and guidance to sustainable fertilisation, Belgium B3W Coaching service for a better soil and water quality, Belgium OPAs Professional farmer ’s organisations and Agri Food cooperatives, Spain ODRs Agricultural Advice Centres, Poland NIBIO Norwegian Institute of Bioeconomy Research Land 2022, 11, 599 23 of 26 UK United Kingdom CPD Continuing Professional Development References 1. European Commission. Communication From the Commission to the Council, the European Parliament, the European Economic and Social Committee and the Committee of the Regions—Thematic Strategy for Soil Protection (COM(2006) 231 Final); European Commission: Brussels, Belgium, 2006. 2. Stolte, J.; Tesfai, M.; Øygarden, L.; Kværnø, S.; Keizer, J.; Verheijen, F.; Panagos, P.; Ballabio, C.; Hessel, R. Soil Threats in Europe; Publications Ofﬁce Luxembourg: Luxembourg City, Luxembourg, 2015. 3. Montanarella, L.; Panagos, P. The relevance of sustainable soil management within the European Green Deal. Land Use Policy 2021, 100, 104950. [CrossRef] 4. European Commission. The European Green Deal; European Commission: Brussels, Belgium, 2019. 5. Juerges, N.; Hansjürgens, B. Soil governance in the transition towards a sustainable bioeconomy–A review. J. Clean. Prod. 2018, 170, 1628–1639. [CrossRef] 6. Prager, K.; McKee, A. Co-production of knowledge in soils governance. Int. J. Reg. Rural. Remote Law Policy 2015, 1, 81–97. [CrossRef] 7. Vrebos, D.; Bampa, F.; Creamer, R.E.; Gardi, C.; Ghaley, B.B.; Jones, A.; Rutgers, M.; Sandén, T.; Staes, J.; Meire, P. The Impact of Policy Instruments on Soil Multifunctionality in the European Union. Sustainability 2017, 9, 407. [CrossRef] 8. FAO. Voluntary Guidelines for Sustainable Soil Management Food and Agriculture Organization of the United Nations Rome, Italy; FAO: Rome, Italy, 2017. 9. Campbell, G.A.; Lilly, A.; Corstanje, R.; Mayr, T.R.; Black, H. Are existing soils data meeting the needs of stakeholders in Europe? An analysis of practical use from policy to ﬁeld. Land Use Policy 2017, 69, 211–223. [CrossRef] 10. McNeill, A.; Bradley, H.; Muro, M.; Merriman, N.; Pederson, R.; Tugran, T.; Lukacova, Z. Inventory of opportunities and bottlenecks in policy to facilitate the adoption of soil-improving techniques. SoilCare, Scientiﬁc Report Milieu, 2 March 2018. Available online: https://www.soilcare-project.eu/resources/deliverables(accessed on 20 September 2021). 11. Lobry de Bruyn, L.; Ingram, J. Soil information sharing and knowledge building for sustainable soil use and management: Insights and implications for the 21st Century. Soil Use Manag. 2019, 35, 1–5. [CrossRef] 12. Aznar-Sánchez, J.A.; Velasco-Muñoz, J.F.; López-Felices, B.; del Moral-Torres, F. Barriers and Facilitators for Adopting Sustainable Soil Management Practices in Mediterranean Olive Groves. Agronomy 2020, 10, 506. [CrossRef] 13. European Commission. A Soil Deal for Europe Implementation Plan; European Commission: Brussels, Belgium, 2022. 14. Ingram, J. Are farmers in England equipped to meet the knowledge challenge of sustainable soil management? An analysis of farmer and advisor views. J. Environ. Manag. 2008, 86, 214–228. [CrossRef] 15. Baumgart-Getz, A.; Prokopy, L.S.; Floress, K. Why farmers adopt best management practice in the United States: A meta-analysis of the adoption literature. J. Environ. Manag. 2012, 96, 17–25. [CrossRef] 16. Doran, J.W.; Zeiss, M.R. Soil health and sustainability: Managing the biotic component of soil quality. Appl. Soil Ecol. 2000, 15, 3–11. [CrossRef] 17. Lehmann, J.; Bossio, D.A.; Kögel-Knabner, I.; Rillig, M.C. The concept and future prospects of soil health. Nat. Rev. Earth Environ. 2020, 1, 544–553. [CrossRef] [PubMed] 18. Mattila, T.J.; Hagelberg, E.; Söderlund, S.; Joona, J. How farmers approach soil carbon sequestration? Lessons learned from 105 carbon-farming plans. Soil Tillage Res. 2022, 215, 105204. [CrossRef] 19. Hou, D.; Bolan, N.S.; Tsang, D.C.; Kirkham, M.B.; O’Connor, D. Sustainable soil use and management: An interdisciplinary and systematic approach. Sci. Total Environ. 2020, 729, 138961. [CrossRef] [PubMed] 20. Karlen, D.L.; Veum, K.S.; Sudduth, K.A.; Obrycki, J.F.; Nunes, M.R. Soil health assessment: Past accomplishments, current activities, and future opportunities. Soil Tillage Res. 2019, 195, 104365. [CrossRef] 21. Rinot, O.; Levy, G.J.; Steinberger, Y.; Svoray, T.; Eshel, G. Soil health assessment: A critical review of current methodologies and a proposed new approach. Sci. Total Environ. 2019, 648, 1484–1491. [CrossRef] [PubMed] 22. Briggs, S.; Eclair-Heath, G. Helping UK farmers to choose, use, and interpret soil test results to inform soil management decisions for soil health. Asp. Appl. Biol. Crop Prod. South. Br. 2017, 134, 161–168. 23. Knierim, A.; Labarthe, P.; Laurent, C.; Prager, K.; Kania, J.; Madureira, L.; Ndah, T.H. Pluralism of agricultural advisory service providers–Facts and insights from Europe. J. Rural. Stud. 2017, 55, 45–58. [CrossRef] 24. Compagnone, C.; Simon, B. Cooperation and competition among agricultural advisory service providers. The case of pesticides use. J. Rural. Stud. 2018, 59, 10–20. [CrossRef] 25. Kania, J.; Vinohradnik, K.; Knierim, A. WP3—AKIS in the EU: The Inventory Final Report Volume I—Summary Findings; Krakow, Poland, 2014. Available online: https://proakis.webarchive.hutton.ac.uk/sites/proakis.hutton.ac.uk/ﬁles/FINAL_REPORT_ 08_07_2014_VOL_I.pdf (accessed on 20 September 2021). 26. Dhiab, H.; Labarthe, P.; Laurent, C. How the performance rationales of organisations providing farm advice explain persistent difﬁculties in addressing societal goals in agriculture. Food Policy 2020, 95, 101914. [CrossRef] 27. Laurent, C.; Nguyen, G.; Triboulet, P.; Ansaloni, M.; Bechtet, N.; Labarthe, P. Institutional continuity and hidden changes in farm advisory services provision: Evidence from farmers’ microAKIS observations in France. J. Agric. Educ. Ext. 2021, 1–24. [CrossRef] Land 2022, 11, 599 24 of 26 28. Klerkx, L.; Proctor, A. Beyond fragmentation and disconnect: Networks for knowledge exchange in the English land management advisory system. Land Use Policy 2013, 30, 13–24. [CrossRef] 29. Garforth, C.; Angell, B.; Archer, J.; Green, K. Fragmentation or creative diversity? Options in the provision of land management advisory services. Land Use Policy 2003, 20, 323–333. [CrossRef] 30. Prager, K.; Creaney, R.; Lorenzo-Arribas, A. Criteria for a system level evaluation of farm advisory services. Land Use Policy 2017, 61, 86–98. [CrossRef] 31. Klerkx, L.; De Grip, K.; Leeuwis, C. Hands off but strings attached: The contradictions of policy-induced demand-driven agricultural extension. Agric. Hum. Values 2006, 23, 189–204. [CrossRef] 32. Prager, K.; Labarthe, P.; Caggiano, M.; Lorenzo-Arribas, A. How does commercialisation impact on the provision of farm advisory services? Evidence from Belgium, Italy, Ireland and the UK. Land Use Policy 2016, 52, 329–344. [CrossRef] 33. Labarthe, P.; Laurent, C. Privatization of agricultural extension services in the EU: Towards a lack of adequate knowledge for small-scale farms? Food Policy 2013, 38, 240–252. [CrossRef] 34. Klerkx, L.; Jansen, J. Building knowledge systems for sustainable agriculture: Supporting private advisors to adequately address sustainable farm management in regular service contacts. Int. J. Agric. Sustain. 2010, 8, 148–163. [CrossRef] 35. Pedersen, A.B.; Nielsen, H.Ø.; Christensen, T.; Ørum, J.E.; Martinsen, L. Are independent agricultural advisors more oriented towards recommending reduced pesticide use than supplier-afﬁliated advisors? J. Environ. Manag. 2019, 242, 507–514. [CrossRef] 36. Kik, M.; Claassen, G.; Meuwissen, M.P.; Smit, A.; Saatkamp, H. Actor analysis for sustainable soil management–A case study from the Netherlands. Land Use Policy 2021, 107, 105491. [CrossRef] 37. Madureira, L.; Barros, A.B.; Fonseca, A.F. Deliverable D2. 5: Synthesis Report Innovation, Farm Advice, and Micro-AKIS in Europe; AgriLink: Castanet, France, 2021. 38. Louwagie, G.; Gay, S.H.; Sammeth, F.; Ratinger, T. The potential of European Union policies to address soil degradation in agriculture. Land Degrad. Dev. 2011, 22, 5–17. [CrossRef] 39. Ingram, J.; Mills, J. Are advisory services “ﬁt for purpose” to support sustainable soil management? An assessment of advice in Europe. Soil Use Manag. 2019, 35, 21–31. [CrossRef] 40. House of Commons. Environmental Audit Committee on Soil Health; House of Commons: London, UK, 2016. 41. Landini, F. How to be a good rural extensionist. Reﬂections and contributions of Argentine practitioners. J. Rural. Stud. 2016, 43, 193–202. [CrossRef] 42. Nettle, R.; Crawford, A.; Brightling, P. How private-sector farm advisors change their practices: An Australian case study. J. Rural. Stud. 2018, 58, 20–27. [CrossRef] 43. Mills, J.; Reed, M.; Skaalsveen, K.; Ingram, J. The use of Twitter for knowledge exchange on sustainable soil management. Soil Use Manag. 2019, 35, 195–203. [CrossRef] 44. Skaalsveen, K.; Ingram, J.; Urquhart, J. The role of farmers’ social networks in the implementation of no-till farming practices. Agric. Syst. 2020, 181, 102824. [CrossRef] 45. Daxini, A.; O’Donoghue, C.; Ryan, M.; Buckley, C.; Barnes, A.P.; Daly, K. Which factors inﬂuence farmers’ intentions to adopt nutrient management planning? J. Environ. Manag. 2018, 224, 350–360. [CrossRef] 46. Prager, K.; McKee, A. Use and awareness of soil data and information among local authorities, farmers and estate managers. James Hutton Inst. Intern. Rep. 2014. Available online: https://www.hutton.ac.uk/sites/default/ﬁles/ﬁles/Use%20of%20soil%20 information_ﬁnal%20report_14Jan2014.pdf (accessed on 20 September 2021). 47. Rhymes, J.M.; Wynne-Jones, S.; Williams, A.P.; Harris, I.M.; Rose, D.; Chadwick, D.R.; Jones, D.L. Identifying barriers to routine soil testing within beef and sheep farming systems. Geoderma 2021, 404, 115298. [CrossRef] 48. Poppe, K. 2. Agricultural Knowledge and Innovation Systems in transition: Findings of the SCAR Collaborative Working Group on AKIS. In Improving Agricultural Knowledge and Innovation Systems; OECD Publishing: Paris, France, 2012; p. 41. 49. Labarthe, P.; Caggiano, M.; Laurent, C.; Faure, G.; Cerf, M. Concepts and Theories Available to Describe the Functioning and Dynamics of Agricultural Advisory Services. Learning for the Inventory (PRO AKIS WP3): Deliverable WP2-1 (Pro AKIS: Prospect for Farmers’ Support: Advisory Services in European AKIS; WP2: Advisory Services within AKIS: International Debates); European Union: Brusssels, Belgium, 2013. 50. Birner, R.; Davis, K.; Pender, J.; Nkonya, E.; Anandajayasekeram, P.; Ekboir, J.; Mbabu, A.; Spielman, D.J.; Horna, D.; Benin, S. From best practice to best ﬁt: A framework for designing and analyzing pluralistic agricultural advisory services worldwide. J. Agric. Educ. Ext. 2009, 15, 341–355. [CrossRef] 51. Faure, G.; Desjeux, Y.; Gasselin, P. New challenges in agricultural advisory services from a research perspective: A literature review, synthesis and research agenda. J. Agric. Educ. Ext. 2012, 18, 461–492. [CrossRef] 52. Rietra, R.; Heinen, M.; Oenema, O. A Review of Crop Husbandry and Soil Management Practices Using Meta-Analysis Studies: Towards Soil-Improving Cropping Systems. Land 2022, 11, 255. [CrossRef] 53. Piccoli, I.; Seehusen, T.; Bussell, J.; Vizitu, O.; Calciu, I.; Berti, A.; Börjesson, G.; Kirchmann, H.; Kätterer, T.; Sartori, F.; et al. Opportunities for Mitigating Soil Compaction in Europe—Case Studies from the SoilCare Project Using Soil-Improving Cropping Systems. Land 2022, 11, 223. [CrossRef] 54. Jian, J.; Lester, B.J.; Du, X.; Reiter, M.S.; Stewart, R.D. A calculator to quantify cover crop effects on soil health and productivity. Soil Tillage Res. 2020, 199, 104575. [CrossRef] Land 2022, 11, 599 25 of 26 55. Nunes, M.R.; Karlen, D.L.; Veum, K.S.; Moorman, T.B.; Cambardella, C.A. Biological soil health indicators respond to tillage intensity: A US meta-analysis. Geoderma 2020, 369, 114335. [CrossRef] 56. Nettle, R.; Klerkx, L.; Faure, G.; Koutsouris, A. Governance dynamics and the quest for coordination in pluralistic agricultural advisory systems. J. Agric. Educ. Ext. 2017, 23, 189–195. [CrossRef] 57. Eisinger, P. Organizational Capacity and Organizational Effectiveness among Street-Level Food Assistance Programs. Nonproﬁt Volunt. Sect. Q. 2002, 31, 115–130. [CrossRef] 58. Labarthe, P.; Laurent, C. The Importance of the Back-ofﬁce for Farm Advisory Services. EuroChoices 2013, 12, 21–26. [CrossRef] 59. Davis, K. The new extensionist: Core competencies for individuals. GFRAS Brief 2015, 3. Available online: https://www.g-fras. org/en/gfras/652-the-new-extensionist-core-competencies-for-individuals.html (accessed on 20 September 2021). 60. Suvedi, M.; Ghimire, R.; Channa, T. Examination of core competencies of agricultural development professionals in Cambodia. Eval. Program Plan. 2018, 67, 89–96. [CrossRef] 61. Kilis, E.; Adamsone-Fiskovica, A.; Šumane, ¯ S.; Tisenkopfs, T. (Dis)continuity and advisory challenges in farmer-led retro- innovation: Biological pest control and direct marketing in Latvia. J. Agric. Educ. Ext. 2021, 1–18. Available online: https: //www.tandfonline.com/doi/full/10.1080/1389224X.2021.1997770 (accessed on 20 September 2021). [CrossRef] 62. Klerkx, L.; Van Mierlo, B.; Leeuwis, C. Evolution of systems approaches to agricultural innovation: Concepts, analysis and interventions. In Farming Systems Research into the 21st Century: The New Dynamic; Springer: Berlin/Heidelberg, Germany, 2012; pp. 457–483. 63. Herrera, B.; Gerster-Bentaya, M.; Tzouramani, I.; Knierim, A. Advisory services and farm-level sustainability proﬁles: An exploration in nine European countries. J. Agric. Educ. Ext. 2019, 25, 117–137. [CrossRef] 64. Eurostat. Key Figures on the European Food Chain; Publications Ofﬁce of the European Union: Luxembourg, 2021. 65. Metzger, M.J.; Bunce, R.G.H.; Jongman, R.H.; Mücher, C.A.; Watkins, J.W. A climatic stratiﬁcation of the environment of Europe. Glob. Ecol. Biogeogr. 2005, 14, 549–563. [CrossRef] 66. PROAKIS Project. Prospects for Farmers’ Support: Advisory Services in European AKIS (PRO AKIS). Available online: https: //proakis.hutton.ac.uk/ (accessed on 1 March 2020). 67. i2connect. i2onnect Project AKiS Country Reports. Available online: https://i2connect-h2020.eu/resources/akis-country-reports/ (accessed on 2 February 2021). 68. Knuth, U.; Knierim, A. Interaction with and governance of increasingly pluralistic AKIS: A changing role for advisory services. In Knowledge and Innovation Systems towards the Future; Publications Ofﬁce of the European Union: Luxembourg, 2016; p. 104. 69. Klerkx, L.; Petter Stræte, E.; Kvam, G.-T.; Ystad, E.; Butli Hårstad, R.M. Achieving best-ﬁt conﬁgurations through advisory subsystems in AKIS: Case studies of advisory service provisioning for diverse types of farmers in Norway. J. Agric. Educ. Ext. 2017, 23, 213–229. [CrossRef] 70. Vuylsteke, A.; De Schepper, S. Agricultural knowledge and innovation systems. In The Case of Flanders; Deparment of Agricul- ture and Fisheries, Division for Agricultural Policy Analysis and Institute for Agricultural and Fisheries Research: Brussels, Belgium, 2011. 71. Knierim, A.; Boenning, K.; Caggiano, M.; Cristóvão, A.; Dirimanova, V.; Koehnen, T.; Labarthe, P.; Prager, K. The AKIS concept and its relevance in selected EU member states. Outlook Agric. 2015, 44, 29–36. [CrossRef] 72. Sutherland, L.-A.; Madureira, L.; Dirimanova, V.; Bogusz, M.; Kania, J.; Vinohradnik, K.; Creaney, R.; Duckett, D.; Koehnen, T.; Knierim, A. New knowledge networks of small-scale farmers in Europe’s periphery. Land Use Policy 2017, 63, 428–439. [CrossRef] 73. Vrain, E.; Lovett, A. The roles of farm advisors in the uptake of measures for the mitigation of diffuse water pollution. Land Use Policy 2016, 54, 413–422. [CrossRef] 74. Ingram, J.; Chiswell, H.; Mills, J.; Debruyne, L.; Cooreman, H.; Koutsouris, A.; Alexopoulos, Y.; Pappa, E.; Marchand, F. Situating demonstrations within contemporary agricultural advisory contexts: Analysis of demonstration programmes in Europe. J. Agric. Educ. Ext. 2021, 27, 615–638. [CrossRef] 75. Creaney, R.; McKee, A.; Prager, K. Designing, implementing and maintaining (rural) innovation networks to enhance farmers’ ability to innovate in cooperation with other rural actors. Monitor Farms in Scotland, UK. Report for AKIS on the Ground: Focusing Knowledge Flow Systems (WP4) of the PRO AKIS Project; February 2015. Available online: www.proakis.eu/ publicationsandevents/pubs (accessed on 20 September 2021). 76. Knuth, U.; Knierim, A. Characteristics of and challenges for advisors within a privatized extension system. J. Agric. Educ. Ext. 2013, 19, 223–236. [CrossRef] 77. Marsh, S.P.; Pannell, D. Agricultural extension policy in Australia: The good, the bad and the misguided. Aust. J. Agric. Resour. Econ. 2000, 44, 605–627. [CrossRef] 78. Chivers, C.-A.; Collins, A.L. (Un)willingness to contribute ﬁnancially towards advice surrounding diffuse water pollution: The perspectives of farmers and advisors. J. Agric. Educ. Ext. 2022, 1–24. Available online: https://www.tandfonline.com/doi/abs/ 10.1080/1389224X.2022.2043917?journalCode=raee20 (accessed on 20 September 2021). [CrossRef] 79. Compagnone, C.; Hellec, F. Farmers’ Professional Dialogue Networks and Dynamics of Change: The Case of ICP and No-Tillage Adoption in Burgundy (France). Rural. Sociol. 2015, 80, 248–273. [CrossRef] 80. Ingram, J. Technical and social dimensions of farmer learning: An analysis of the emergence of reduced tillage systems in England. J. Sustain. Agric. 2010, 34, 183–201. [CrossRef] Land 2022, 11, 599 26 of 26 81. Krzywoszynska, A. Making knowledge and meaning in communities of practice: What role may science play? The case of sustainable soil management in England. Soil Use Manag. 2019, 35, 160–168. [CrossRef] 82. Phillipson, J.; Proctor, A.; Emery, S.B.; Lowe, P. Performing inter-professional expertise in rural advisory networks. Land Use Policy 2016, 54, 321–330. [CrossRef] 83. Rust, N.A.; Stankovics, P.; Jarvis, R.M.; Morris-Trainor, Z.; de Vries, J.R.; Ingram, J.; Mills, J.; Glikman, J.A.; Parkinson, J.; Toth, Z.; et al. Have farmers had enough of experts? Environ. Manag. 2022, 69, 31–44. [CrossRef] [PubMed] 84. Vanloqueren, G.; Baret, P.V. Why are ecological, low-input, multi-resistant wheat cultivars slow to develop commercially? A Belgian agricultural ‘lock-in’case study. Ecol. Econ. 2008, 66, 436–446. [CrossRef] 85. Gorman, M. Becoming an agricultural advisor—The rationale, the plan and the implementation of a model of reﬂective practice in extension higher education. J. Agric. Educ. Ext. 2019, 25, 179–191. [CrossRef] 86. Carlisle, L. Factors inﬂuencing farmer adoption of soil health practices in the United States: A narrative review. Agroecol. Sustain. Food Syst. 2016, 40, 583–613. [CrossRef] 87. Cerf, M.; Guillot, M.-N.; Olry, P. Acting as a change agent in supporting sustainable agriculture: How to cope with new professional situations? J. Agric. Educ. Ext. 2011, 17, 7–19. [CrossRef] 88. Schneider, F.; Fry, P.; Ledermann, T.; Rist, S. Social learning processes in Swiss soil protection—The ‘from farmer-to farmer ’project. Hum. Ecol. 2009, 37, 475–489. [CrossRef] 89. Klerkx, L. Advisory services and transformation, plurality and disruption of agriculture and food systems: Towards a new research agenda for agricultural education and extension studies. J. Agric. Educ. Ext. 2020, 26, 131–140. [CrossRef]
Land – Multidisciplinary Digital Publishing Institute
Published: Apr 19, 2022
Keywords: agricultural advisory services; soil health; governance; agricultural advisers; sustainable soil management; soil policy; advice
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