NPower Innovative Barriers Survey

Name

First NameLast Name

Email

example@example.com

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Organization

Which Regional Cluster do you belong to?

Which sector(s) best represent your activity?

Which type of organisation do you represent?

General Barriers

Beliefs and perception barriers

Rows	0	1	2	3	4	5	n/a
1. Preference for familiar and proven practices can slow the adoption of alternative nutrient-management approaches
2. Low trust between sectors, institutions or stakeholder groups can hinder cooperation and joint action
3. Nutrient policies may be perceived mainly as restrictions rather than as opportunities for improvement
4. Costs and benefits of nutrient-management measures may be perceived as unfairly distributed between stakeholders
5. Uncertainty about technical, economic or environmental outcomes can reduce willingness to adopt new solutions

Incentives and economic barriers

Rows	0	1	2	3	4	5	n/a
1. Economic incentives can favour conventional or nutrient-intensive practices over more efficient or circular alternatives
2. Administrative, monitoring, reporting and compliance requirements can create excessive costs or workload
3. High upfront costs and competing investment priorities can delay or prevent adoption of innovative solutions
4. Existing infrastructure, supply chains and business models can make transition to alternative solutions difficult
5. Environmental costs of nutrient losses are not sufficiently reflected in prices, charges or incentives

Information and knowledge gaps barriers

Rows	0	1	2	3	4	5	n/a
1. Scientific and technical evidence is not sufficiently translated into practical policy or management decisions
2. Stakeholders may lack accessible information, nutrient data, expertise or advisory support for informed decisions
3. Nutrient monitoring is fragmented or incomplete across sources, sectors and environmental compartments
4. Nutrient data are fragmented across institutions and do not provide an integrated regional N/P picture
5. The benefits of some nutrient-management measures take time or are difficult to demonstrate reliably

Institutional capacity and governance barriers

Rows	0	1	2	3	4	5	n/a
1. Responsibilities for nutrient management are fragmented across authorities, sectors and policy areas
2. Coordination is weak between sectors and between actors addressing diffuse and point-source nutrient pollution
3. Stakeholder participation and influence in nutrient-management decisions are uneven across affected groups
4. EU and national policy frameworks can be difficult to translate into measures suited to regional realities
5. Institutional inertia and short political cycles can hinder long-term nutrient-management transitions
6. Public authorities may lack sufficient funding, staff or technical capacity to implement nutrient-management measures

Regulatory barriers

Rows	0	1	2	3	4	5	n/a
1. Complex or overlapping nutrient-related regulations can be difficult to interpret and apply consistently
2. Regulatory pathways for approving and implementing innovative nutrient-management solutions are unclear or difficult to navigate
3. Waste, by-product and product status of recovered nutrient materials can create uncertainty for reuse and market uptake
4. Nutrient-related rules may be implemented or enforced inconsistently across authorities, regions or actors
5. Rigid or poorly aligned rules can constrain circular, innovative or outcome-based nutrient-management approaches.

Sectorial barriers

Agriculture

Rows	0	1	2	3	4	5	n/a
1. Concerns about the safety, quality or agronomic performance of recovered fertilisers can limit their use
2. Practices promoted by peers or advisers can reinforce conventional choices and slow the uptake of alternatives
3. Agricultural support and agri-environment schemes may not sufficiently reward measures according to their actual nutrient-reduction performance
4. Concentrated livestock and manure production can create local nutrient surpluses that are difficult or costly to redistribute
5. Phosphorus accumulated in soils can continue causing nutrient losses even after current fertiliser inputs are reduced
6. Lack of harmonised quality, safety or end-use standards can limit the uptake of recovered nutrient products
7. Transport distances, storage requirements and logistics costs can limit the redistribution and reuse of nutrient-rich materials

Other primary sectors

Rows	0	1	2	3	4	5	n/a
1. Sector-specific regulatory requirements can complicate the recovery and reuse of nutrients or biomass from residues and effluents
2. Practices promoted by peers or advisers can reinforce conventional choices and slow the uptake of alternatives
3. Strongly site-specific ecological or hydrological conditions can limit the transferability of nutrient-management practices
4. Integrating nutrient-recovery or mitigation measures into existing production systems can be technically difficult or costly
5. Some nutrient-recovery solutions are not sufficiently mature or scalable for reliable deployment at the required scale
6. Weak market demand or uncertain buyers can reduce the economic viability of recovered nutrients or biomass
7. Transport distances, storage requirements and logistics costs can limit the redistribution and reuse of nutrient-rich materials

Water and waste management

Rows	0	1	2	3	4	5	n/a
1. Quality, safety and end-use requirements can limit the reuse or market uptake of nutrients recovered from wastewater, sludge or biowaste
2. Transport distances, storage requirements and logistics costs can limit the redistribution and reuse of recovered nutrient materials
3. Existing treatment infrastructure can be difficult or costly to retrofit for nutrient recovery and circular use
4. High energy use, operating costs or process complexity can limit advanced nutrient-recovery technologies
5. Some nutrient-recovery solutions are not sufficiently mature or scalable for reliable deployment at the required scale
6. Weak market demand or uncertain buyers can reduce the economic viability of recovered nutrient products
7. Siting, permitting or local acceptance issues can delay nutrient-recovery or treatment infrastructure

Energy and Transport

Rows	0	1	2	3	4	5	n/a
1. Quality, safety or end-use requirements can limit the use of digestate, recovered phosphorus or other nutrient-rich outputs
2. Transport distances, storage requirements and logistics costs can limit movement of feedstocks and recovered nutrient products
3. Some nutrient-recovery solutions are not sufficiently mature or scalable for reliable deployment at the required scale
4. Weak market demand or uncertain buyers can reduce the economic viability of recovered nutrient products
5. Siting, permitting or local acceptance issues can delay anaerobic digestion or nutrient-recovery infrastructure
6. Energy-recovery objectives can compete with nutrient-recovery objectives when deciding how residual streams are used
7. Poor coordination between feedstock sources, treatment plants and nutrient end-users can limit circular value chains

Industry

Rows	0	1	2	3	4	5	n/a
1. Quality, safety or end-use requirements can limit the valorisation of recovered nutrients and nutrient-rich industrial by-products
2. Transport distances, storage requirements and logistics costs can limit redistribution or reuse of nutrient-rich industrial streams
3. High energy use, operating costs or additional treatment requirements can limit industrial nutrient recovery
4. Some nutrient-recovery solutions are not sufficiently mature or scalable for reliable industrial deployment
5. Weak market demand or uncertain buyers can reduce the economic viability of recovered nutrient products
6. Siting, permitting or local acceptance issues can delay new nutrient-recovery or treatment infrastructure
7. Variable composition or contamination of industrial nutrient streams can complicate recovery, standardisation and reuse

Regional Cluster

Murcia, Spain

Rows	0	1	2	3	4	5	n/a
1. Water scarcity can limit the feasibility of some nutrient-management and nutrient-recovery options
2. Strong use of reclaimed water links water reuse decisions directly with nutrient management
3. Torrential rainfall can rapidly mobilise nutrients and sediments, reducing the effectiveness of preventive measures
4. Historical nutrient loads in soils, aquifers and sediments can delay environmental recovery
5. The ecological sensitivity of the Mar Menor requires particularly stringent nutrient-management measures
6. Spatial zoning creates different nutrient-management requirements across the Mar Menor catchment
7. Groundwater and surface runoff connect inland nutrient sources with the Mar Menor

Flanders, Belgium

Rows	0	1	2	3	4	5	n/a
1. High livestock density and limited land availability increase pressure to redistribute manure and nutrients
2. Area-specific fertilisation requirements create different nutrient-management conditions across Flanders
3. Manure movements are subject to extensive traceability, registration and reporting requirements
4. Nitrogen-deposition constraints can affect permitting of livestock and other nutrient-related activities
5. Federal product rules and Flemish manure and environmental rules interact in the use of recovered nutrients
6. Intensive water-quality monitoring can lead to increasingly targeted requirements for farms and high-risk areas
7. Rules linking livestock production capacity and nutrient emissions affect how agricultural activities can develop

Finland

Rows	0	1	2	3	4	5	n/a
1. Long winters and a short growing season constrain the timing of nutrient-management measures
2. Freeze-thaw cycles and snowmelt can affect the effectiveness of nutrient-loss mitigation measures
3. Nutrient loading from drained peatland forestry can persist or change over long periods
4. Drained peatlands can increase humus and organic-matter loads entering the Bothnian Bay
5. Peatland hydrology makes the effectiveness of mitigation measures strongly site-specific
6. Long distances between nutrient sources and users increase the cost of nutrient redistribution
7. Dispersed nutrient sources can reduce economies of scale for collection, treatment and recovery

Ireland

Rows	0	1	2	3	4	5	n/a
1. High rainfall can increase runoff and the risk of nutrient losses to water
2. Differences in soil drainage affect whether nitrogen leaches or phosphorus is lost through runoff
3. Fragmented farm structures can complicate efficient distribution and use of organic nutrients
4. Agriculture and urban wastewater create simultaneous nutrient pressures that require coordinated action
5. High nitrate pressures in the south-east require strongly targeted nutrient-management measures
6. Expansion of anaerobic digestion and biomethane creates new feedstock, transport and digestate-management needs
7. New nutrient-balance, storage and nutrient-movement requirements are reshaping farm nutrient management

MISSING BARRIERS: Are there any important governance, regulatory, institutional, economic, behavioural, knowledge-related or technical barriers affecting nutrient management in your sector or region that have not been covered above? Please briefly describe them

CONCRETE EXPERIENCE: Can you provide a concrete example of how one of the barriers above affects implementation in your context? If possible, please also indicate what change, incentive or enabling condition could help overcome it or support adoption.

NPower Innovative Barriers Survey

Introduction

Barrier relevance assessment