Reuse of Drinking Water in the Cities: Types of Conflict, Legitimacy and Governance
Abstract
1. Introduction
2. Methodological Approach
- First Layer (Structural Coding): Each justification, acceptance, and urgency factor is structurally coded as sufficient or insufficient, according to its analytical function and the available evidence.
- Second Layer (Dispute Coding): A complementary coding layer is applied to determine whether the same factor manifests as uncontested, interpretively disputed, substantively disputed, or strategically instrumentalized within the conflict.
3. Results
3.1. Conflicts over Potable Water Reuse (DPR/IPR)
3.1.1. Justification
3.1.2. Urgency
3.1.3. Acceptance
3.1.4. Legitimacy
3.2. Conflict Configuration
3.2.1. Demands
- Demand orientations in the D × R matrix
- Demand Issues
3.2.2. Repertoires of Action
- Political opposition involves party competition, electoral framing, municipal council interventions, referenda, or veto coalitions that politicize, delay, redirect, or block the project [8].
- Institutional resistance is associated with utilities, operators, administrative agencies, or implementing bodies that delay, resist, or fail to cooperate with project execution [17].
- Regulatory blockage, by contrast, refers to permit constraints, restrictive standards, legal uncertainty, enforcement challenges, or administrative barriers [16].
3.2.3. Conflict Dynamics
4. Discussion
4.1. Operational Logic of the Three-Matrix Framework
4.2. Justification × Acceptance
- Consolidated legitimacy (sufficient justification + sufficient acceptance): Projects such as Orange County, which has managed to align technical success with a complete “legitimacy portfolio” [31];
- Apparent legitimacy (insufficient justification + sufficient acceptance): Projects with a high risk of reputational collapse as it is based on induced conformity or majority follow-up without real processing of technical information [25];
4.2.1. Consolidated Legitimacy
| Quadrant | Definition | Examples/Cases |
|---|---|---|
| B1 Sufficient justification + Sufficient acceptance. | Consolidated legitimacy Technical and social coherence. | -Windhoek (Namibia): DPR since 1968, legitimized by extreme necessity and transparency [4,43]. Orange County (California, USA): GWRS, intensive education campaigns aimed at building high acceptance [21]. Singapore (NEWater): national pride, positive framing [7,71]. Perth (Australia): Beenyup aquifer recharge project (2010). Justified by a 50-year strategic plan and legitimized after an open data pilot that generated institutional trust [17]. El Paso (Texas): Desert city with a culture of scarcity where 84% of the community supports direct potable reuse due to transparent and diversified resource management [16] |
| B2 Sufficient justification + Insufficient acceptance. | Contested legitimacy Rejection despite technical soundness. | Toowoomba (Australia): Rejected in a 2006 referendum despite severe drought [8]. San Diego (USA, 1990s): projects blocked by “toilet-to-tap” framing [47]. East Valley, Los Angeles (USA): Technically viable 38,000 m3/d IPR project with infrastructure built in the late 1990s. It was blocked politically in 2000 due to criticism of lack of transparency, forcing the water to be redirected to non-potable uses [17]. Canberra, Australia. IPR plan proposed during the Millennium Drought. It was rejected in public consultation, showing that the provision of official scientific information failed to reverse polarization or perceptions of risk among sceptical groups [17]. |
| B3 Insufficient justification + Sufficient acceptance (superficial or induced). | Apparent legitimacy Acceptance induced by urgency. Stability is fragile, collapsing in the face of incidents. | Wichita Falls: Emergency DPR was accepted under extreme drought, but discontinued once reservoirs recovered. Cape Town/FNWS: Potable reuse gained plausibility during “Day Zero”, but became more disputed after the emergency context shifted. Brownwood: DPR moved from emergency-driven acceptance toward contested legitimacy. |
| B4 Insufficient justification + Insufficient acceptance | Double legitimacy deficit Projects blocked from the outset. Design flaws, high costs, or lack of urgency, or water scarcity that would make them necessary. | Cloudcroft: DPR proposal moved from disputed legitimacy toward double deficit; the system was not stabilized as operating DPR. Western Corridor: IPR scheme shifted from emergency-driven legitimacy toward double deficit after the drought rationale weakened. Wichita Falls: Also illustrates a B4 trajectory once the emergency rationale disappeared and DPR lost practical necessity. |
4.2.2. Legitimacy in Dispute
4.2.3. Apparent Legitimacy
4.2.4. Double Legitimacy Deficit
4.3. Justification × Urgency
4.3.1. Trajectories Under Different Urgency Conditions
4.3.2. Political and Affective Mechanisms of Urgency
4.4. Demands and Repertoires
4.4.1. Resistance
4.4.2. Subordination
4.4.3. Negotiation
- Conditional Acceptance and Conflict as Institutional Adjustment
- Varieties, Boundaries, and Reversibility of Negotiation.
4.4.4. Dependency
- Legitimacy delegated
- Passive and Active Dependency
4.5. DPR and IPR as Distinct Conflict Modalities
4.6. Practical Implications
4.6.1. Implications for Potable Reuse Projects
4.6.2. Policy Implications for Water Governance
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Appendix A. Cases of DPR/IPR Used in the Analysis
| Case/Project | City/Region | Country | Type of Reuse | References | J × A—Quadrant | J × U—Quadrant | D × R—Quadrant |
|---|---|---|---|---|---|---|---|
| San Diego (1990s) | California | USA | IPR | [23,47] | B2 (Disputed Legitimacy) | A3 (Strategic Security) | Resistance |
| San Diego (Pure Water) | San Diego, CA | USA | IPR → DPR | [9,23,47] | B2 → B1 (Disputed Legitimacy → Consolidated Legitimacy) | A3 (Strategic Security) → A1 (Justification/High Urgency) | Resistance → Negotiation |
| Toowoomba | Queensland | Australia | IPR | [8] | B2 (Disputed Legitimacy) | A1 (Sufficient Justification/ High Urgency) | Resistance |
| Windhoek (Goreangab) | Windhoek | Namibia | DPR | [4,81] | B1 (Consolidated Legitimacy) | A1 (Sufficient Justification/High Urgency) | Subordination |
| Orange County (GWRS) | California | USA | IPR | [10,31,41] | B1 (Consolidated Legitimacy) | A1 (Sufficient Justification/High Urgency) | Negotiation |
| Singapore (NEWater) | Singapore | Singapore | IPR/DPR | [7,74] | B1 (Consolidated Legitimacy) | A3 (Strategic Security) | Subordination → Dependency |
| Wichita Falls (Emergency) | Texas | USA | DPR → IPR | [13,43,67] | B3 → B4 (Apparent Legitimacy → Double Deficit) | A2 (Emergency Exceptionality → A4 (Structural Blockage) | Dependency |
| Perth (Beenyup) | Western Australia | Australia | IPR | [17] | B1 (Consolidated Legitimacy) | A1 (Sufficient Justification/High Urgency) | Negotiation |
| Cape Town (FNWS) | Cape Town | South Africa | IPR/DPR | [19,27] | B3 → B2 (Apparent legitimacy → Disputed Legitimacy) | A2 (Emergency exceptionalism → A4 (Structural deadlock) | Dependence → Resistance |
| George | Western Cape | South Africa | IPR | [13,81] | B1 (Consolidated Legitimacy) | A2 (Emergency exceptionalism → A3 Strategic Security | Negotiation → Dependence |
| Aurora | Colorado | USA | IPR | [77] | B1 (Consolidated legitimacy) | A1 (Sufficient Justification/High Urgency) | Negotiation → Dependency |
| Big Spring | Texas | USA | DPR | [16,43] | B3 → B1(Apparent Legitimacy → Consolidated Legitimacy) | A1 (Sufficient Justification/High Urgency) | Subordination → Dependency |
| Cloudcroft | New Mexico | USA | DPR | [16,22,43] | B2 → B4 (Disputed Legitimacy→ Double Deficit) | A1 (Sufficient Justification/High Urgency) | Resistance |
| East Valley (L.A.) | Los Angeles | USA | IPR | [10,17,22] | B2 (Disputed Legitimacy) | A3 (Strategic Security) | Resistance |
| Canberra | Canberra | Australia | IPR | [1,17] | B2 (Disputed Legitimacy) | A1 (Sufficient Justification/High Urgency) | Resistance |
| Tampa | Florida | USA | IPR | [17] | B2 (Disputed Legitimacy) | A3 (Strategic Security) | Resistance |
| Torelle (Wulpen) | Flanders | Belgium | IPR | [24] | B1 (Consolidated legitimacy) | A3 (Strategic Security) | Dependency |
| Upper Occoquan | Virginia | USA | IPR | [60] | B1 (Consolidated Legitimacy) | A3 (Strategic Security) | Negotiation → Dependence |
| Beaufort West | Western Cape | South Africa | DPR | [43] | B1 (Consolidated legitimacy) | A1 (Sufficient Justification/High Urgency) | Dependency |
| Brownwood | Texas | USA | DPR | [16] | B3 → B2 (Apparent Legitimacy → Disputed Legitimacy) | A2 (Emergency Exceptionalism) → A3 (Strategic Security) | Resistance |
| Monterrey (IHSAP V) | Monterrey | Mexico | DPR/IPR | B3 (Apparent Legitimacy | A1 (Sufficient Justification/High Urgency) | Dependency | |
| El Paso | Texas | USA | DPR | [16] | B1 (Consolidated Legitimacy) | A3 (Strategic Security) | Negotiation |
| Dublin San Ramon | California | USA | IPR | [48] | B2 (Disputed Legitimacy) | A3 (Strategic Security) | Resistance |
| Western Corridor | Queensland | Australia | IPR | [13,17,39] | B3 → B4 (Apparent Legitimacy → Double Deficit) | A1 (Sufficient Justification/High Urgency) | Resistance |
| eThekwini | Durban | South Africa | DPR | [43,51,81] | B2 (Disputed Legitimacy) | A3 (Strategic Security | Resistance |
| Pure Water Monterey | Monterey County, California | USA | IPR | [48] | B1 (Consolidated legitimacy) | A3 (Strategic security) | Negotiation |
Appendix B. Typological Coding Framework
Appendix B.1. Coding Protocol Structure
- Justification assesses whether a DPR/IPR project can be substantively defended as necessary, viable, reasonable, and proportional in relation to available evidence and alternatives.
- Acceptance assesses whether the project has a meaningful social basis of support, tolerance, trust, endorsement, or conditional acceptance among relevant publics, users, and affected groups.
- Urgency assesses whether material or perceived water-related pressure meaningfully shapes the project’s necessity claims, timing, decision thresholds, implementation, contestation, or trajectory.
- Demands identify the dominant orientation of actor claims toward the project, distinguishing cancellation-oriented demands from conditional or coexistence-oriented demands.
- Repertoires of action identify how actors seek to influence the project trajectory, distinguishing disruptive repertoires from contained repertoires.
- The coding process follows four steps. First, Justification, Acceptance, and Urgency are assessed according to their analytical functions. Second, complementary dispute coding is used to clarify whether relevant factors are uncontested, interpretively disputed, substantively disputed, or strategically mobilized. Third, Demands and Repertoires are coded through their classificatory elements: demand orientation and repertoire mode. Fourth, these dimensions are combined into the three typological matrices.
- The protocol does not require every case to display the same type or amount of evidence. Clear and uncontested evidence may be classified directly according to the relevant coding threshold. Ambiguous, contradictory, incomplete, or contested evidence is interpreted through the integrated coding rules below.
| Dimension | Main Coding Threshold | Analytical Function | Used in |
|---|---|---|---|
| Justification | Sufficient/Insufficient | Assesses whether the project can be defended as necessary, viable, reasonable, and proportional. | J × A; J × U |
| Acceptance | Sufficient/Insufficient | Assesses whether there is a meaningful social basis of support, tolerance, trust, or conditional acceptance. | J × A |
| Urgency | High/Low | Assesses whether water-related pressure meaningfully shapes the decision context. | J × U |
| Demands | Cancellation-oriented/ Conditional-coexistence-oriented | Identifies what actors seek regarding the project. | D × R |
| Repertoires | Disruptive/Contained | Identifies how actors act to influence the project trajectory. | D × R |
Appendix B.2. Complementary Dispute Coding
- Dispute coding is applied as a complementary interpretive step. It does not constitute an additional score and does not automatically modify the structural classification of a factor. Its function is to clarify whether a factor remains a background condition, becomes contested in meaning, reveals substantive weaknesses, or is strategically mobilized by actors.
- Interpretive or strategic disputes do not automatically reduce Justification, Acceptance, or Urgency. They affect coding only when they reveal substantive gaps, unresolved contradictions, weak evidence, exclusion, unstable support, or other weaknesses that compromise the analytical function of the factor. This distinction is central to the original codebook, which separates structural assessment from the conflictive status of each factor.
| Dispute Status | Meaning | Methodological Use |
|---|---|---|
| Not disputed | The factor does not appear as a relevant object of dispute in the available evidence. | Records the absence of visible dispute over the factor. |
| Interpretively disputed | Actors disagree over the meaning, relevance, implications, or legitimacy of the factor. | Records disagreement over interpretation. It does not automatically change the structural coding. |
| Substantively disputed | The controversy reveals evidentiary gaps, omissions, contradictions, unaddressed impacts, unevaluated alternatives, or unevenly distributed burdens. | May affect the coding of the factor when the dispute undermines its analytical function. |
| Strategically mobilized/instrumentalized | The factor, or the dispute around it, is used by actors to legitimize, accelerate, block, redesign, or discredit the project. | Functions as an analytical qualifier linking the factor to narratives, repertoires, actor strategies, and conflict trajectories. |
Appendix B.3. Justification Coding Protocol
- Justification is coded as sufficient or insufficient. It is treated as a composite but non-additive dimension. Final coding does not depend on the number of favourable indicators, but on whether the available evidence allows the project to be defended as necessary, viable, reasonable, and proportional.
- Justification is assessed through six structural factors:
| Factor | Analytical Function | Observable Evidence | Coding |
|---|---|---|---|
| 1. Techno- sanitary | Assesses the physical and technical robustness of the system. | Treatment and disinfection barriers; system performance; monitoring of water quality and emerging contaminants. | Sufficient: clear evidence of robust sanitary control. Insufficient: there is not enough evidence on safety, monitoring, or incident control, or there are relevant technical gaps that prevent sanitary control from being sustained. |
| 2. Regulatory-legal | Assesses legal and regulatory certainty. | Applicable regulations; water quality standards; permits and authorizations obtained; clarity of competences; compatibility with water, health, and environmental plans. | Sufficient: clear regulatory framework and authorizations. Insufficient: regulatory gap or absence of a clear framework, uncertain permits, or relevant competence conflict. |
| 3. Economic- financial | Assesses the economic and financial viability of the project. | Capital and operating costs; sources of financing; tariff model; affordability for the user; long-term sustainability. | Sufficient: economically sustainable financing and operation. Insufficient: unviable, uncertain, or undemonstrated costs, financing, or economic burdens. |
| 4. Operational-institutional | Assesses management and response capacity. | Operational, technical, and institutional resources; maintenance and operational continuity; contingency management; oversight and inter-institutional coordination. | Sufficient: operators and institutions with demonstrable capacity. Insufficient: absence of demonstrable operational, institutional, or contingency capacity, or dependence on uncertain conditions that compromise the safe management of the system. |
| 5. Reasonableness-proportionality | Assesses the logic of the decision in relation to alternatives. | Pre-feasibility or feasibility studies; comparison with alternatives; cost–benefit analysis; risk assessment; demonstration of public or social utility. | Sufficient: documented necessity, suitability, proportionality, and comparison with alternatives. Insufficient: necessity, suitability, or proportionality in relation to available alternatives is not demonstrated, or there are relevant gaps regarding alternatives, costs, risks, or benefits. |
| 6. Socio-environmental-territorial | Assesses impacts and the distribution of burdens and benefits. | Assessment of environmental and social impacts; identification of affected stakeholders and territories; distribution of burdens, risks, and benefits; mitigation, compensation, or redistribution measures. | Sufficient: territorial impacts and the distribution of risks, burdens, and benefits are reasonably identified and managed. Insufficient: relevant impacts, territorial effects, vulnerabilities, or distributive inequalities are omitted, or there are assessment, mitigation, or distribution gaps that compromise the function of the factor. |
- A single critical or limiting factor may lead to insufficient justification when it undermines the project’s defensibility, even if other factors are strong. For example, technical robustness may coexist with financial weakness, legal feasibility with institutional fragility, or cost-effectiveness with unresolved distributive concerns.
| Coding | Coded When |
|---|---|
| Sufficient Justification | The available evidence allows the project to be defended as necessary, viable, reasonable, and proportional. Existing gaps are minor or manageable; no critical limiting factor is identified; and controversies do not reveal substantive omissions that compromise this defence. |
| Insufficient Justification | The available evidence does not allow the project to be defended as necessary, viable, reasonable, and proportional because of a critical limiting factor, strong contradictions between factors, substantive gaps, or disputes revealing relevant omissions in safety, legality, financing, operation, alternatives, impacts, or distribution. |
Appendix B.4. Acceptance Coding
- Acceptance is coded as sufficient or insufficient. It refers to the observable expression of support, tolerance, trust, endorsement, or conditional acceptance by relevant publics, users, and affected groups. It is not equivalent to the absence of protest, nor is it reduced to survey support.
- Acceptance is assessed through relational and processual factors:
| Factor | Analytical Function | Indicative Evidence | Coding Threshold |
|---|---|---|---|
| Public Orientation | Assesses declared support, rejection, tolerance, or willingness to use. | Surveys, public statements, electoral behaviour, willingness to drink/use, endorsement or rejection. | Sufficient: sustained support, tolerance, or willingness to use. Insufficient: dominant rejection, fear, stigma, or weak/superficial support. |
| Trust-related Credibility | Assesses whether institutions, operators, regulators, and experts are perceived as credible. | Acceptance of monitoring, belief in safety claims, credibility of regulators/operators, response to incidents. | Sufficient: institutions and safety claims are publicly regarded as reliable. Insufficient: authorities, monitoring, or safety claims are distrusted. |
| Participatory Incidence | Assesses whether affected actors had meaningful opportunities to access information, express concerns, influence safeguards, monitor, or contest decisions. | Hearings, consultations, advisory committees, citizen monitoring, deliberative forums, design changes, monitoring agreements. | Sufficient: participation is timely, inclusive, and has observable influence. Insufficient: participation is absent, late, symbolic, exclusionary, inaccessible, or non-responsive. |
| Narrative Framing and Stigma | Assesses how the project is socially named, imagined, morally evaluated, and emotionally framed. | “Toilet-to-tap” narratives, health-risk framing, scarcity narratives, media framing, symbolic contamination, resilience narratives. | Sufficient: narratives make the project understandable as safe, necessary, acceptable, or conditionally legitimate. Insufficient: stigmatizing, fear-based, or delegitimizing narratives dominate. |
| Conflict-repertoire Trajectory | Assesses whether opposition escalates, declines, stabilizes, or becomes conditional. | Protest, litigation, referenda, media campaigns, petitions, public hearings, shifts toward redesign or monitoring demands. | Sufficient: opposition is absent, limited, declining, institutionally channelled, or transformed into conditional acceptance. Insufficient: opposition persists or escalates through veto coalitions, cancellation demands, litigation, referenda, or disruptive campaigns. |
| Affected-group Inclusion | Assesses whether relevant affected groups are included in the social basis of acceptance. | Positions of users, local communities, vulnerable groups, territorial actors, civil society, directly exposed or burdened groups. | Sufficient: affected groups are included or their concerns are credibly addressed. Insufficient: support comes mainly from non-affected or institutional actors while affected groups remain excluded, opposed, distrustful, or subordinated. |
| Temporal Stability | Assesses whether acceptance persists beyond crisis, novelty, emergency, political pressure, or temporary scarcity. | Support before/during/after drought, post-incident responses, long-term normalization, sustained willingness to use. | Sufficient: acceptance persists or consolidates over time. Insufficient: acceptance is temporary, crisis-induced, reversible, or dependent on exceptional conditions. |
- A single critical or limiting factor may lead to insufficient acceptance when it undermines the project’s meaningful social basis, even if other acceptance factors appear favourable. For example, public tolerance may coexist with institutional mistrust, formal participation with perceived exclusion, or willingness to use with persistent stigma or crisis-induced compliance.
- Sufficient acceptance does not require consensus. It may coexist with disagreement, residual opposition, interpretive disputes, or conditional support. Conversely, insufficient acceptance does not require total rejection. It may occur when some support exists but affected groups are excluded, trust is structurally weak, stigma dominates public debate, participation is symbolic, or acceptance is unstable and crisis-induced.
- Passive compliance, silence, or low mobilization are not coded as sufficient acceptance by themselves. They support sufficient acceptance only when triangulated with evidence of meaningful tolerance, credible opportunities to contest, institutional trust, inclusion of affected groups, and absence of coercive or dependency-based conditions.
| Coding | Coded When |
|---|---|
| Sufficient Acceptance | The available evidence reasonably supports that the project has meaningful support, tolerance, endorsement, trust, or conditional acceptance among relevant publics, users, and affected groups. Existing controversies are minor, localized, manageable, or institutionally channelled; directly affected groups are not systematically excluded or subordinated; and low mobilization is not primarily explained by fear, dependence, fatigue, crisis-induced compliance, or lack of effective capacity to oppose. |
| Insufficient Acceptance | The available evidence does not reasonably support a meaningful social basis of support, tolerance, endorsement, trust, or conditional acceptance. This may result from persistent rejection, dominant veto coalitions, structural distrust, symbolic or exclusionary participation, dominant stigma, exclusion or subordination of affected groups, unresolved distributive concerns, crisis-induced compliance, or non-mobilization explained by subordination rather than trust. |
Appendix B.5. Urgency Coding Protocol
- Urgency is coded as high or low. It refers to the degree to which material or perceived water-related pressure shapes the project’s necessity claims, timing, decision thresholds, implementation, contestation, or trajectory.
- Urgency is broader than scarcity. It may arise from drought, supply risk, water-quality deterioration, contamination, salinity intrusion, groundwater depletion, demand–supply imbalance, climate-related stress, or crisis narratives.
| Factor | Analytical Function |
|---|---|
| Material urgency | Assesses whether documented water-related pressure makes potable reuse relevant to the decision context. |
| Perceived urgency | Assesses whether relevant actors understand the condition as pressing, severe, time-sensitive, or requiring action. |
- Urgency does not substitute for Justification or Acceptance. A project may be urgent but poorly justified, or structurally justified without being urgent. Likewise, stakeholders may recognize water-related urgency while rejecting the proposed DPR/IPR project. When urgency changes over time, cases should be coded by phase rather than averaged across the whole trajectory.
| Coding | Coded When |
|---|---|
| High Urgency | The available evidence shows that material water-related pressure and/or perceived urgency meaningfully shape the project’s necessity claims, timing, decision thresholds, implementation, contestation, or conflict trajectory. |
| Low Urgency | Material or perceived urgency is absent, weak, speculative, long-term, without clear decision relevance, peripheral, or not meaningfully connected to the project’s necessity claims, decision process, public debate, implementation, contestation, or conflict trajectory. |
Appendix B.6. Demands Coding Protocol
- Demands are coded according to their dominant orientation. The protocol distinguishes between the classificatory role of demand orientation and the interpretive role of substantive content and framing.
- Only demand orientation determines the position of the case within the D × R matrix. Substantive demand content and demand framing explain why the demand emerges, but do not create additional demand categories.
- When cancellation-oriented and conditional/coexistence-oriented claims coexist, coding follows the dominant orientation among the most relevant actors or conflict phases. Cancellation-oriented demands are prioritized when they have significant capacity to block, suspend, delegitimize, or redirect the project trajectory. Where no dominant orientation can be established, coding should be disaggregated by actor group or conflict phase.
| Demand Orientation | Coded When |
|---|---|
| Cancellation-oriented | Actors seek to cancel, suspend, block, reject, or delegitimize the project as unacceptable. |
| Conditional/ Coexistence-oriented | Actors do not reject potable reuse per se, but demand safeguards, redesign, transparency, monitoring, affordability, compensation, redistribution of risks and benefits, or stronger institutional guarantees. |
| Substantive Content | Observable Evidence |
|---|---|
| Health/sanitary | Concerns about drinking-water safety, pathogens, contaminants, exposure, or treatment reliability. |
| Ecological | Concerns about rivers, aquifers, reservoirs, ecosystems, water quality, or environmental degradation. |
| Distributive/justice | Claims about unequal distribution of risks, benefits, burdens, costs, or compensation. |
| Procedural | Claims about participation, transparency, consultation, information access, or accountability. |
| Institutional/regulatory | Concerns about regulatory gaps, permits, enforcement, audits, operator capacity, or institutional trust. |
| Economic/affordability | Claims about tariffs, costs, affordability, subsidies, financial sustainability, or burden-sharing. |
| Territorial/hydro-social | Concerns about water rights, territorial control, local uses, flow reconfiguration, or dispossession. |
| Cultural/symbolic | Claims involving disgust, purity, moral discomfort, symbolic contamination, or water imaginaries. |
| Technical-operational | Concerns about treatment performance, infrastructure reliability, operational failures, or contingency capacity. |
| Framing/Mechanism | Observable Evidence |
|---|---|
| Risk | Claims frame the project as creating health, environmental, technological, or social risks. |
| Scientific/regulatory uncertainty | Claims emphasize unknowns, incomplete evidence, monitoring gaps, emerging contaminants, or insufficient standards. |
| Institutional distrust | Claims question the credibility, independence, competence, or honesty of operators, regulators, or authorities. |
| Injustice/inequity | Claims emphasize unfair distribution of risks, costs, burdens, or benefits. |
| Transparency deficit | Claims point to secrecy, poor communication, insufficient information, or lack of access to data. |
| Precaution | Claims argue that the project should not proceed, or should proceed only under strict safeguards. |
| Moral discomfort/yuck factor | Claims invoke disgust, purity, symbolic contamination, or discomfort with wastewater-to-drinking-water transitions. |
| Rights-based | Claims invoke water, territorial, environmental, human, or community rights. |
| Affordability | Claims frame the project as creating excessive costs, tariff burdens, or water poverty risks. |
| Safeguard/governance | Claims demand stronger controls, audits, monitoring, public oversight, or institutional guarantees. |
| Alternatives | Claims argue that other supply options are preferable, cheaper, less risky, or more legitimate. |
| Proximity/bodily exposure | Claims focus on direct consumption, household exposure, or “not in my tap/body” concerns. |
Appendix B.7. Repertoires Coding Protocol
- Repertoires of action are coded according to their dominant mode. The protocol does not reduce repertoires to opposition or resistance. Repertoires include the recognizable ways through which actors seek to challenge, condition, redirect, legitimize, stabilize, support, or oppose a project.
- Only repertoire mode determines the position of the case within the D × R matrix. Arenas of action and strategic functions support interpretation but do not determine the classification.
- The same action may be disruptive or contained depending on its scale, visibility, persistence, confrontational character, institutional effects, and capacity to affect the project trajectory. Litigation, technical review, participation, public campaigns, monitoring, or administrative engagement may operate differently depending on context.
- Disruptive repertoires do not necessarily imply cancellation, and contained repertoires do not necessarily imply support. Demand orientation defines the substantive position, while repertoire mode captures the degree of pressure, visibility, disruption, and trajectory effect.
| Repertoire Mode | Coded When |
|---|---|
| Disruptive repertoire | Actors use visible, confrontational, legally contentious, politically salient, publicly mobilizing, or institutionally consequential actions capable of generating significant political, legal, technical, social, or reputational pressure and reshaping the project trajectory. |
| Contained repertoire | Actors use institutional, participatory, technical, monitoring, oversight-oriented, cooperative, or administratively mediated actions to influence, contest, improve, support, oversee, or stabilize the project without substantially disrupting routines, raising major decision costs, or redirecting the process. |
Appendix B.8. Justification × Acceptance (J × A) Coding
| Configuration | Label | Mechanism | Typical Trajectory |
|---|---|---|---|
| Sufficient J/ Sufficient A | Consolidated Legitimacy | Structural robustness and social-relational acceptance mutually reinforce each other. | Normalization, stabilization, durable legitimacy. |
| Sufficient J/ Insufficient A | Disputed Legitimacy | Structural justification fails to translate into sufficient acceptance because of mistrust, stigma, exclusion, weak participation, or veto coalitions. | Delay, blockage, escalation, redesign, or stabilization if acceptance deficits are addressed. |
| Insufficient J/ Sufficient A | Apparent Legitimacy | Social support or tolerance coexists with insufficient structural justification. | Fragile stabilization, reputational reversal, or collapse of support if weaknesses become visible. |
| Insufficient J/ Insufficient A | Double Deficit | Structural weakness and insufficient acceptance mutually reinforce delegitimation. | Blockage, abandonment, forced redesign, or escalation. |
Appendix B.9. Justification × Urgency (J × U) Coding
| Configuration | Label | Mechanism | Typical Trajectory |
|---|---|---|---|
| Sufficient J/ High U | Convergent Necessity | Structural justification and urgency reinforce each other. | Prioritization, accelerated implementation, or consolidation, depending on acceptance and governance capacity. |
| Sufficient J/ Low U | Strategic Water Security | The project is justified as long-term resilience or preventive planning rather than emergency response. | Gradual implementation, contestation over necessity, postponement, or stabilization. |
| Insufficient J/ High U | Emergency Exceptionality | Urgency pressures decision thresholds despite insufficient structural justification. | Temporary tolerance, compressed deliberation, boomerang effect, redesign, legal challenge, or loss of support once urgency declines. |
| Insufficient J/ Low U | Structural Blockage | Neither justification nor urgency provides a sufficient basis for advancement. | Paralysis, abandonment, postponement, redesign, or rejection. |
Appendix B.10. Demands × Repertoires (D × R) Agency Dynamics
| Configuration | Label | Mechanism | Typical Trajectory |
|---|---|---|---|
| Cancellation D/ Disruptive R | Resistance | Cancellation-oriented demands are pursued through disruptive repertoires capable of generating political, legal, media, technical, or social pressure. | Blockage, suspension, cancellation, escalation, judicialization, or forced redesign. |
| Conditional- Coexistence D/ Disruptive R | Negotiation | Actors do not reject reuse per se, but use high-pressure repertoires to force safeguards, redesign, monitoring, transparency, affordability, compensation, redistribution, or stronger guarantees. | Adaptive redesign, negotiated safeguards, institutional reform, delayed implementation, or escalation if conditions are ignored. |
| Cancellation D/ Contained R | Subordination | Actors seek cancellation or rejection, but opposition is expressed through low-pressure, fragmented, or institutionally constrained repertoires. | Hidden delegitimation, accumulated grievance, or sudden escalation if actor capacity increases. |
| Conditional- Coexistence D/ Contained R | Dependence | Actors accept or tolerate coexistence through contained repertoires, often relying on delegated trust, technical authority, institutional mediation, necessity, or limited capacity to contest. | Fragile stability, institutionalized coexistence, gradual normalization, or transition to negotiation/resistance if trust erodes. |
Appendix C. Search Protocol
(“potable water reuse” OR “potable reuse” OR “direct potable reuse” OR “indirect potable reuse” OR DPR OR IPR OR “purified recycled water” OR “water recycling”) AND (conflict OR controversy OR opposition OR mobilization OR mobilization OR acceptance OR “public perception” OR trust OR legitimacy OR governance)
(“[PROJECT_NAME]” OR “[LOCAL_PROGRAM_NAME]”) AND (“[CITY]” OR “[REGION]”)AND (“potable reuse” OR “direct potable reuse” OR “indirect potable reuse” OR DPR OR IPR OR “purified recycled water” OR “water recycling” OR “groundwater replenishment” OR “reservoir augmentation”) AND (“[CODING_FACTOR_TERMS]”)
| Dimension | Indicative Search Terms Used in [CODING_FACTOR_TERMS] |
|---|---|
| Justification | Technical safety, regulation, permits, approval, costs, funding, feasibility, alternatives, operator capacity, environmental impacts, risk assessment. |
| Acceptance | Public perception, trust, opposition, support, consultation, participation, transparency, stigma, yuck factor, “toilet-to-tap” narratives. |
| Urgency | Drought, water scarcity, emergency, water security, reservoir depletion, groundwater depletion, climate change, imported water dependency. |
| Demands | Safety, health, transparency, monitoring, safeguards, equity, environmental justice, tariffs, affordability, compensation, alternatives, redesign. |
| Repertoires | Protest, referendum, litigation, petitions, media campaigns, public hearings, council votes, administrative appeals, stakeholder coalitions, citizen monitoring, technical review. |
References
- Smith, H.M.; Brouwer, S.; Jeffrey, P.; Frijns, J. Public Responses to Water Reuse—Understanding the Evidence. J. Environ. Manag. 2018, 207, 43–50. [Google Scholar] [CrossRef] [PubMed]
- Al-Saidi, M. From Acceptance Snapshots to the Social Acceptability Process: Structuring Knowledge on Attitudes Towards Water Reuse. Front. Environ. Sci. 2021, 9, 633841. [Google Scholar] [CrossRef]
- National Research Council. Water Reuse: Potential for Expanding the Nation’s Water Supply Through Reuse of Municipal Wastewater; National Academies Press: Washington, DC, USA, 2012. [Google Scholar]
- du Pisani, P.L. Direct Reclamation of Potable Water at Windhoek’s Goreangab Reclamation Plant. Desalination 2006, 188, 79–88. [Google Scholar] [CrossRef]
- Nkhoma, P.R.; Alsharif, K.; Ananga, E.; Eduful, M.; Acheampong, M. Recycled Water Reuse: What Factors Affect Public Acceptance? Environ. Conserv. 2021, 48, 278–286. [Google Scholar] [CrossRef]
- Rosenberg Goldstein, R.E.; Gerdes, M.E.; Fix, S.; Vivino, A.; Rainey, K.; Bernat, E. Evaluating the Impact of Water Reuse Educational Videos on Water Reuse Perceptions Using EEG/Event Related Potential. J. Environ. Manag. 2024, 349, 119560. [Google Scholar] [CrossRef] [PubMed]
- Lefebvre, O. Beyond NEWater: An Insight into Singapore’s Water Reuse Prospects. Curr. Opin. Environ. Sci. Health 2018, 2, 26–31. [Google Scholar] [CrossRef]
- Hurlimann, A.; Dolnicar, S. When Public Opposition Defeats Alternative Water Projects—The Case of Toowoomba Australia. Water Res. 2010, 44, 287–297. [Google Scholar] [CrossRef]
- Mann, A. Public Involvement in Technology Integration: Understanding San Diego’s Successes and Failures with Potable Reuse. Bachelor’s Thesis, University of Virginia, Charlottesville, VA, USA, 2021. [Google Scholar]
- Markus, M.R.; Torres, E. How to Overcome Public Perception Issues on Potable Reuse Projects; Orange County Water District: Fountain Valley, CA, USA, 2020. [Google Scholar]
- Tortajada, C.; Nambiar, S. Communications on Technological Innovations: Potable Water Reuse. Water 2019, 11, 251. [Google Scholar] [CrossRef]
- Stefan, E.; Scapulatempo, C.V. Water Availability and Water Reuse: A New Approach for Water Resources Management. In Water Reuse Within a Circular Economy Context Series II. Global Water Security Issues (GWSI); UNESCO Publishing: Paris, France, 2020. [Google Scholar]
- Jeffrey, P.; Yang, Z.; Judd, S.J. The Status of Potable Water Reuse Implementation. Water Res. 2022, 214, 118198. [Google Scholar] [CrossRef]
- Akpan, V.E.; Omole, D.O.; Bassey, D.E. Assessing the Public Perceptions of Treated Wastewater Reuse: Opportunities and Implications for Urban Communities in Developing Countries. Heliyon 2020, 6, e05246. [Google Scholar] [CrossRef]
- Herman, J.G.; Scruggs, C.E.; Thomson, B.M. The Costs of Direct and Indirect Potable Water Reuse in a Medium-Sized Arid Inland Community. J. Water Process Eng. 2017, 19, 239–247. [Google Scholar] [CrossRef]
- Scruggs, C.E.; Thomson, B.M. Opportunities and Challenges for Direct Potable Water Reuse in Arid Inland Communities. J. Water Resour. Plan. Manag. 2017, 143, 04017064. [Google Scholar] [CrossRef]
- Mukherjee, M.; Jensen, O. Making Water Reuse Safe: A Comparative Analysis of the Development of Regulation and Technology Uptake in the US and Australia. Saf. Sci. 2020, 121, 5–14. [Google Scholar] [CrossRef]
- Rodrigues, P.M.; Pinto, F.S.; Marques, R.C. A Framework for Enabling Conditions for Wastewater Reuse. Sustain. Prod. Consum. 2024, 46, 355–366. [Google Scholar] [CrossRef]
- Warner, J.F.; Meissner, R. Cape Town’s “Day Zero” Water Crisis: A Manufactured Media Event? Int. J. Disaster Risk Reduct. 2021, 64, 102481. [Google Scholar] [CrossRef]
- Moesker, K.; Pesch, U.; Doorn, N. Public Acceptance in Direct Potable Water Reuse: A Call for Incorporating Responsible Research and Innovation. J. Responsible Innov. 2024, 11, 2304382. [Google Scholar] [CrossRef]
- Ormerod, K.J.; Redman, S.; Kelley, S. Public Perceptions of Potable Water Reuse, Regional Growth, and Water Resources Management in the Reno-Sparks Area of Northern Nevada, USA. City Environ. Interact. 2019, 2, 100015. [Google Scholar] [CrossRef]
- Sardana, P.; Javernick-Will, A.; Cook, S.M. Facilitators and Barriers of Global Water Reuse: A Systematic Literature Review. ACS ES T Water 2025, 5, 3–19. [Google Scholar] [CrossRef]
- Kenney, S. Purifying Water: Responding to Public Opposition to the Implementation of Direct Potable Reuse in California. UCLA J. Environ. Law Policy 2019, 37, 85. [Google Scholar] [CrossRef]
- Frijns, J.; Smith, H.M.; Brouwer, S.; Garnett, K.; Elelman, R.; Jeffrey, P. How Governance Regimes Shape the Implementation of Water Reuse Schemes. Water 2016, 8, 605. [Google Scholar] [CrossRef]
- Leong, C.; Lebel, L. Can Conformity Overcome the Yuck Factor? Explaining the Choice for Recycled Drinking Water. J. Clean. Prod. 2020, 242, 118196. [Google Scholar] [CrossRef]
- Rozin, P.; Haddad, B.; Nemerof, C.; Slovic, P. Psychological Aspects of the Rejection of Recycled Water: Contamination, Purification and Disgust. Judgm. Decis. Mak. 2015, 10, 50–63. [Google Scholar] [CrossRef]
- Ziervogel, G.; Franklin, B.; Thorson, J. Unpacking the Cape Town Drought: Lessons Learned; African Centre for Cities: Cape Town, South Africa, 2019. [Google Scholar]
- McAdam, D.; Tarrow, S.; Tilly, C. Dynamics of Contention. Soc. Mov. Stud. 2003, 2, 99–102. [Google Scholar] [CrossRef]
- Suchman, M.C. Managing Legitimacy: Strategic and Institutional Approaches. Acad. Manag. Rev. 1995, 20, 571. [Google Scholar] [CrossRef]
- Binz, C.; Harris-Lovett, S.; Kiparsky, M.; Sedlak, D.L.; Truffer, B. The Thorny Road to Technology Legitimation—Institutional Work for Potable Water Reuse in California. Technol. Forecast. Soc. Change 2016, 103, 249–263. [Google Scholar] [CrossRef]
- Harris-Lovett, S.R.; Binz, C.; Sedlak, D.L.; Kiparsky, M.; Truffer, B. Beyond User Acceptance: A Legitimacy Framework for Potable Water Reuse in California. Environ. Sci. Technol. 2015, 49, 7552–7561. [Google Scholar] [CrossRef]
- Paredes, M. One Industry, Different Conflicts: A Typology of Mining Mobilization. Extr. Ind. Soc. 2022, 9, 101052. [Google Scholar] [CrossRef]
- Sgroi, M.; Vagliasindi, F.G.A.; Roccaro, P. Feasibility, Sustainability and Circular Economy Concepts in Water Reuse. Curr. Opin. Environ. Sci. Health 2018, 2, 20–25. [Google Scholar] [CrossRef]
- Dingemans, M.M.L.; Smeets, P.W.M.H.; Medema, G.; Frijns, J.; Raat, K.J.; van Wezel, A.P.; Bartholomeus, R.P. Responsible Water Reuse Needs an Interdisciplinary Approach to Balance Risks and Benefits. Water 2020, 12, 1264. [Google Scholar] [CrossRef]
- Collier, D.; LaPorte, J.; Seawright, J. Putting Typologies to Work: Concept Formation, Measurement, and Analytic Rigor. Polit. Res. Q. 2012, 65, 217–232. [Google Scholar] [CrossRef]
- Nilsson, D.; Baxter, G.; Butler, J.R.A.; McAlpine, C.A. How Do Community-Based Conservation Programs in Developing Countries Change Human Behaviour? A Realist Synthesis. Biol. Conserv. 2016, 200, 93–103. [Google Scholar] [CrossRef]
- Flyvbjerg, B. Five Misunderstandings about Case-Study Research. Qual. Inq. 2006, 12, 219–245. [Google Scholar] [CrossRef]
- Jaakkola, E. Designing Conceptual Articles: Four Approaches. AMS Rev. 2020, 10, 18–26. [Google Scholar] [CrossRef]
- Duckett, D.; Troldborg, M.; Hendry, S.; Cousin, H. Making Waves: Promoting Municipal Water Reuse without a Prevailing Scarcity Driver. Water Res. 2024, 249, 120965. [Google Scholar] [CrossRef]
- Nemeroff, C.; Rozin, P.; Haddad, B.; Slovic, P. Psychological Barriers to Urban Recycled Water Acceptance: A Review of Relevant Principles in Decision Psychology. Int. J. Water Resour. Dev. 2020, 36, 956–971. [Google Scholar] [CrossRef]
- Ormerod, K.J. Illuminating Elimination: Public Perception and the Production of Potable Water Reuse. Wiley Interdiscip. Rev. Water 2016, 3, 537–547. [Google Scholar] [CrossRef]
- Ross, V.L.; Fielding, K.S.; Louis, W.R. Social Trust, Risk Perceptions and Public Acceptance of Recycled Water: Testing a Social-Psychological Model. J. Environ. Manag. 2014, 137, 61–68. [Google Scholar] [CrossRef]
- Aleksić, N.; Šušteršič, V. Future of Water Recycling: A Review of the Direct Potable Water Reuse. Reciklaza i Odrzivi Razvoj 2022, 15, 27–39. [Google Scholar] [CrossRef]
- Diodosio, K.; Ripberger, J.; Foltz, M.; Mangalgiri, K.; Gupta, K.; Carlson, N. Is It Still the Yuck Factor? Public Support and Willingness to Pay for Municipal Wastewater Reuse in Oklahoma. Sci. Total Environ. 2025, 986, 179749. [Google Scholar] [CrossRef]
- Wester, J.; Timpano, K.R.; Çek, D.; Broad, K. The Psychology of Recycled Water: Factors Predicting Disgust and Willingness to Use. Water Resour. Res. 2016, 52, 3212–3226. [Google Scholar] [CrossRef]
- Rodriguez, D.; Van Buynder, P.; Lugg, R.; Blair, P.; Devine, B.; Cook, A.; Weinstein, P. Indirect Potable Reuse: A Sustainable Water Supply Alternative. Int. J. Environ. Res. Public Health 2009, 6, 1174–1209. [Google Scholar] [CrossRef] [PubMed]
- Hartley, T.W. Public Perception and Participation in Water Reuse. Desalination 2006, 187, 115–126. [Google Scholar] [CrossRef]
- Marks, J.S. Taking the Public Seriously: The Case of Potable and Non Potable Reuse. Desalination 2006, 187, 137–147. [Google Scholar] [CrossRef]
- March, H.; Gorostiza, S.; Saurí, D. Redrawing the Hydrosocial Cycle Through Treated Wastewater Reuse in the Metropolitan Area of Barcelona. Water Altern. 2023, 16, 463–479. [Google Scholar]
- Ormerod, K.; Scott, C. Drinking Wastewater: Public Trust in Potable Reuse. Sci. Technol. Hum. Values 2013, 38, 351–373. [Google Scholar] [CrossRef]
- Kaiser, F.A.C.; Ribeiro, A.R.; Montagner, C.C. Environmental and Socioeconomic Aspects Related to the Acceptance of Direct Potable Reuse in a Metropolitan City in Brazil. J. Clean. Prod. 2024, 466, 142897. [Google Scholar] [CrossRef]
- Matland, R.E. Synthesizing the Implementation Literature: The Ambiguity-Conflict Model of Policy Implementation; Public Management Research Association: Lawrence, KS, USA, 1995; Volume 5. [Google Scholar]
- Tzanakakis, V.A.; Capodaglio, A.G.; Angelakis, A.N. Insights into Global Water Reuse Opportunities. Sustainability 2023, 15, 13007. [Google Scholar] [CrossRef]
- Villacorta-Ranera, C.; Eckstein, G.; Blanco-Gutiérrez, I. Challenges and Prospects of Reclaimed Water Reuse in Spanish Agriculture. Water Int. 2025, 50, 514–534. [Google Scholar] [CrossRef]
- Florides, F.; Giannakoudi, M.; Ioannou, G.; Lazaridou, D.; Lamprinidou, E.; Loukoutos, N.; Spyridou, M.; Tosounidis, E.; Xanthopoulou, M.; Katsoyiannis, I.A. Water Reuse: A Comprehensive Review. Environments 2024, 11, 81. [Google Scholar] [CrossRef]
- Diniz, V.; Rohwedder, J.J.R.; Rath, S. Direct Potable Reuse: A Prioritization of Emerging Contaminants for Monitoring Strategies and Pilot-Scale Advanced Treatment. In Emerging Pollutants: Protecting Water Quality for the Health of People and the Environment; Springer Nature: Cham, Switzerland, 2025; pp. 425–445. [Google Scholar]
- Dolnicar, S.; Hurlimann, A.; Nghiem, L.D. The Effect of Information on Public Acceptance—The Case of Water from Alternative Sources. J. Environ. Manag. 2010, 91, 1288–1293. [Google Scholar] [CrossRef]
- Fakhreddine, S.; Prommer, H.; Scanlon, B.R.; Ying, S.C.; Nicot, J.P. Mobilization of Arsenic and Other Naturally Occurring Contaminants during Managed Aquifer Recharge: A Critical Review. Environ. Sci. Technol. 2021, 55, 2208–2223. [Google Scholar] [CrossRef]
- Ore, A.; Sigmund, G.; Specker, J.; Helmus, R.; Aguilar-Alarcón, P.; Schriks, M.; van Wezel, A.P.; Sutton, N.B. Removal, Transport, and Transformation of Organic Micropollutants in Managed Aquifer Recharge: Insights from Target and Non-Target Analyses. Water Res. 2025, 287, 124409. [Google Scholar] [CrossRef]
- Abbaszadegan, M.; Alum, A.; Kitajima, M.; Fujioka, T.; Matsui, Y.; Sano, D.; Katayama, H. Water Reuse—Retrospective Study on Sustainable Future Prospects. Water 2025, 17, 789. [Google Scholar] [CrossRef]
- Specker, J.C.; Praetorius, A.; de Baat, M.L.; Sutton, N.B.; van Wezel, A.P. Risk Characterisation of Chemicals of Emerging Concern in Real-Life Water Reuse Applications. Environ. Int. 2025, 195, 109226. [Google Scholar] [CrossRef]
- Bub, S.; Petschick, L.L.; Stehle, S.; Wolfram, J.; Schulz, R. Limitations of Chemical Monitoring Hinder Aquatic Risk Evaluations on the Macroscale. Science 2025, 388, 1301–1305. [Google Scholar] [CrossRef] [PubMed]
- LaVanchy, G.T.; Winter, K.J. Water Reuse for Cape Town: Investing in Resilience to Avoid Another “Day Zero”. Wiley Interdiscip. Rev. Water 2025, 12, e70032. [Google Scholar] [CrossRef]
- Ubisse, H.; Naval, L.P. Perception and Acceptability of Reusing Treated Wastewater: Determining Factors and Public Engagement Strategies. Water Environ. J. 2025, 39, 387–401. [Google Scholar] [CrossRef]
- Mateo-Sagasta, J.; Al-Hamdi, M.; AbuZeid, K. (Eds.) Water Reuse in the Middle East and North Africa; A Sourcebook; International Water Management Institute (IWMI): Colombo, Sri Lanka, 2022; 292p. [Google Scholar] [CrossRef]
- Franco-Quintero, J.; Rizo-Maestre, C. When AI Intensifies Conflict: Algorithmic Governance and Socio-Environmental Conflicts in EIA. SSRN 2025. Preprint. [Google Scholar] [CrossRef]
- Benjamin, J.A.; Southard, M.; Adams, H.; MacNevin, D.; Zornes, G.; Nix, D.; Ikehata, K. The Emergency DPR Experience: Water Quality Lessons from Wichita Falls, TX. Water Reuse 2026, 16, 122–142. [Google Scholar] [CrossRef]
- Moya-Fernández, P.J.; López-Ruiz, S.; Guardiola, J.; González-Gómez, F. Determinants of the Acceptance of Domestic Use of Recycled Water by Use Type. Sustain. Prod. Consum. 2021, 27, 575–586. [Google Scholar] [CrossRef]
- van Rensburg, P. Overcoming Global Water Reuse Barriers: The Windhoek Experience. Int. J. Water Resour. Dev. 2016, 32, 622–636. [Google Scholar] [CrossRef]
- Moesker, K.; Wiarda, M. Value-Sensitive Design of Potable Water Reuse: Aligning Academic Research with Societal Concerns. Sci. Eng. Ethics 2025, 31, 18. [Google Scholar] [CrossRef]
- Tortajada, C.; Bindal, I. Water Reuse in Singapore: The New Frontier in a Framework of a Circular Economy? In Water Reuse Within a Circular Economy Context; Water Research Commission: Pretoria, South Africa, 2020. [Google Scholar]
- Scruggs, C.E.; Pratesi, C.B.; Fleck, J.R. Direct Potable Water Reuse in Five Arid Inland Communities: An Analysis of Factors Influencing Public Acceptance. J. Environ. Plan. Manag. 2020, 63, 1470–1500. [Google Scholar] [CrossRef]
- Leong, C. The Role of Emotions in Drinking Recycled Water. Water 2016, 8, 548. [Google Scholar] [CrossRef]
- Lee, H.; Tan, T.P. Singapore’s Experience with Reclaimed Water: NEWater. Int. J. Water Resour. Dev. 2016, 32, 611–621. [Google Scholar] [CrossRef]
- Wester, J.; Broad, K. Direct Potable Water Recycling in Texas: Case Studies and Policy Implications. J. Environ. Policy Plan. 2020, 23, 66–83. [Google Scholar] [CrossRef]
- Barnes, J.L.; Krishen, A.S.; Hu, H. Public Tap Water Perceptions and Potable Reuse Acceptance: A Cognitive Dissonance Theoretical Understanding. J. Clean. Prod. 2023, 429, 139587. [Google Scholar] [CrossRef]
- Rice, J.; Wutich, A.; White, D.D.; Westerhoff, P. Comparing Actual de Facto Wastewater Reuse and Its Public Acceptability: A Three City Case Study. Sustain. Cities Soc. 2016, 27, 467–474. [Google Scholar] [CrossRef]
- Alexander, K.S.; Price, J.C.; Browne, A.L.; Leviston, Z.; Bishop, B.J.; Nancarrow, B.E. Community Perceptions of Risk, Trust and Fairness in Relation to the Indirect Potable Use of Purified Recycled Water in South East Queensland: A Scoping Report. In Urban Water Security Research Alliance, Technical Report No 2; Urban Water Security Research Alliance: City East, QLD, Australia, 2008. [Google Scholar]
- Villacorta-Ranera, C.; Blanco-Gutiérrez, I.; Novo, P. Disentangling Social Perspectives on the Use of Reclaimed Water in Agriculture Using Q Methodology. J. Environ. Manag. 2025, 381, 125264. [Google Scholar] [CrossRef]
- Hernández-Chover, V.; Castellet-Viciano, L.; Hernández-Sancho, F. A Tariff Model for Reclaimed Water in Industrial Sectors: An Opportunity from the Circular Economy. Water 2022, 14, 3912. [Google Scholar] [CrossRef]
- Swartz, C.D. Direct Reclamation of Municipal Wastewater for Drinking Purposes. In Volume 1, Guidance on Monitoring, Management and Communication of Water Quality: Report to the Water Research Commission; Water Research Commission: Pretoria, South Africa, 2015. [Google Scholar]



| Quadrant | Definition | Examples |
|---|---|---|
| A1. Sufficient justification + High urgency | Sufficient justification and urgency Projects perceived as indispensable: solid technical basis and evident water crisis. | Windhoek (DPR): du Pisani (2006) [4]; van Rensburg (2016) [69]; Aleksić & Šušteršič (2022) [43]; Orange County: Ormerod et al. [21]; Markus and Torres (2020) [10]; |
| A2. Insufficient Justification + High urgency | Emergency exceptionality Urgency enables hasty solutions: deliberation and safeguards are cut short. Acceptance is pragmatic but volatile; if the crisis subsides or there is an incident, the “boomerang effect” may occur. | Wichita Falls (DPR 2014): Jeffrey et al. (2022) [13]; Mukherjee & Jensen (2020) [17]. Cape Town: Warner & Meissner (2021) [19]; Ziervogel (2019) [27] |
| A3. Sufficient Justification + Low Urgency | Strategic Security Solidity without immediate scarcity. Anticipatory projects for water security and long-term resilience. Legitimacy is built without the coercion of immediate scarcity, often as state policy | Singapore (Netzer): Lefebvre (2018) [7]; Lee & Tan (2016) [74]; Tortajada & Bindal (2020) [71] Los Angeles (Operation NEXT): Binz et al. (2016) [30]; Ormerod et al. (2019) [21] |
| A4. Insufficient Justification + Low Urgency | Structural Blockage Projects without urgency or sufficient technical basis, exposed to rejection or abandonment. Scenario where counter-narratives (toilet-to-tap stigma) and perceptions of environmental injustice thrive due to insufficient justification to society | San Diego (1990s): Hartley (2006) [47]; Mann (2021) [9]; Smith (2018) [1] |
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content. |
© 2026 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license.
Share and Cite
Franco-Quintero, J.; Rizo-Maestre, C.; Andújar-Montoya, M.D. Reuse of Drinking Water in the Cities: Types of Conflict, Legitimacy and Governance. Water 2026, 18, 1399. https://doi.org/10.3390/w18121399
Franco-Quintero J, Rizo-Maestre C, Andújar-Montoya MD. Reuse of Drinking Water in the Cities: Types of Conflict, Legitimacy and Governance. Water. 2026; 18(12):1399. https://doi.org/10.3390/w18121399
Chicago/Turabian StyleFranco-Quintero, Juan, Carlos Rizo-Maestre, and María Dolores Andújar-Montoya. 2026. "Reuse of Drinking Water in the Cities: Types of Conflict, Legitimacy and Governance" Water 18, no. 12: 1399. https://doi.org/10.3390/w18121399
APA StyleFranco-Quintero, J., Rizo-Maestre, C., & Andújar-Montoya, M. D. (2026). Reuse of Drinking Water in the Cities: Types of Conflict, Legitimacy and Governance. Water, 18(12), 1399. https://doi.org/10.3390/w18121399

