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The resource decision | A question to investigate

Solvent recovery that earns its return

A solvent leaving a process can be an expense, a useful material or a difficult mixture. The investment question is whether recovering this particular stream creates dependable value after energy, testing, losses and quality controls. Resource Economics brings that question into focus before a recovery unit becomes a capital commitment.

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In the conversation.

NEUVIOR and our founder’s perspectives have appeared across science, business and technology publications.

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Reporting, commentary, letters and podcast appearances | Read each feature for its format and source.

The decision behind the tank

For an API plant manager, the attraction is less exposure to fresh-solvent purchasing and waste handling. For the quality team, the concern is what follows the recovered material back into production. Finance needs both perspectives. A proposed NEUVIOR study would examine one named solvent stream and its intended reuse, rather than begin with a site-wide recovery percentage that hides differences between processes. A cleaner segregated stream and a variable mixed stream should not share an assumed business case.

Draw the loop completely

Define the boundary from collection to recovered solvent released for its specified use. Include transfer losses, rejected fractions, still bottoms, storage, sampling, analysis, steam, cooling and any final waste treatment. Report fresh solvent displaced only when recovered material actually meets the agreed requirement and is used. A litre collected is not automatically a litre of procurement avoided. If material is sold externally, record its destination and commercial terms separately from internal reuse.

The trade-off worth testing

A higher recovery fraction may require more separation energy or leave a more troublesome residue. A low purchase price can make elaborate recovery unattractive even where the mass reduction looks strong. Conversely, volatile supply conditions may create a resilience reason that a simple payback misses. The study should compare continued disposal, an external recovery service and a suitable on-site option at the same production demand, with impurity carryover and operational flexibility considered explicitly.

Resource Economics | See the boundary

Where does the
improvement end?

A material can leave one ledger and enter another. Expand the view to see what a manufacturing decision still needs to account for.

A process and the resource flows around itFresh materials and water enter production. Used material may pass through recovery and return when suitable. Utilities support production and recovery; residues require treatment. Boundary selection changes which activities are included. This is a schematic without measured quantities.Fresh materialsWaterProductionSame product requirementAccepted productThe comparison unitRecoveryTest before reuseSuitable material returnedUsed material collectedUtilitiesHeat, power, coolingTreatmentA real destinationResidues and rejectsWider view: cleaning, shared services and relevant upstream or downstream activity
Schematic | Paths show relationships, not measured mass or energy. Select a boundary above.

What is needed to make the same accepted product?

A smaller input is only the beginning.

Included
Fresh materials, water, the transformation and accepted product output.
Still unresolved
Recovery energy, treatment, cleaning and upstream production are outside this first view.
The decision
Use this view to locate a material-intensive step. It cannot establish a whole-process environmental advantage.
Evidence to bring
Batch-linked charges, accepted output and a consistent product specification.

Boundary context: ACS (2014) and EMA (2026). Study framing is NEUVIOR’s proposed approach.

A bounded first study

Start with batch-linked stream composition, volumes or masses, purchase invoices, disposal charges, utility demand and existing specifications. The proposed output is a reconciled stream ledger, option comparison and a sampling plan agreed with qualified technical partners. Trial work would require suitable equipment, permissions and an approved protocol; this page is an invitation to scope that work, not a claim that a recovery line is installed. Each option should show its sensitivity to solvent purity, utilisation and rejection rate.

Count money and impact separately

The economic view should distinguish avoided purchases, recovery operating cost, laboratory time, storage and capital. The environmental view should report material flows, waste destinations and energy-related emissions with stated factors. Recovered mass is not a carbon saving by itself. Keep upstream solvent-production estimates visibly separate from measured on-site activity. Investors should be able to identify the throughput at which the option becomes attractive and how the conclusion changes when demand falls.

What would stop the proposal

Stop or redesign if recovered solvent cannot meet its intended specification, impurity accumulation cannot be controlled, volumes are too irregular, or an external provider cannot demonstrate the required custody. A negative comparison can prevent an expensive installation. The useful next step is a paid feasibility scope with a clear stream owner, evidence access and decision deadline. Only a subsequent authorised trial could establish performance for the selected process.

NEUVIOR Data Analysis

A source.
A question.
A clearer decision.

Useful intelligence keeps its evidence attached.

Our public analysis connects a defined question with named sources, reporting periods and methods. Each source below shows the work available today and the access still needed.

Published-data analysis, research hypotheses and evidence studies are distinct kinds of work. Their meaning should remain clear as the programme grows.

Department for Energy Security and Net Zero | Annual, with revision notices

Greenhouse-gas conversion factors 2026

Which dated factor and accounting boundary fit a measured resource activity?

Dataset retrieved

Official source

American Chemical Society | Green Chemistry Institute | Method reference; inspect dated guidance

Process Mass Intensity method

Which material inputs dominate a process, including water?

Method reference

Official source

European Medicines Agency | On guideline revision

Chemistry of active substances guideline

What process, recovered-material and impurity controls belong in a resource proposal?

Document retrieved

Official source

Explore NEUVIOR Data Analysis

The brief for the next investment decision

The proposed decision brief would show a recovery fraction that meets specification alongside the cost of producing it, then identify the minimum reliable stream volume needed by each option. The plant manager would own collection assumptions, quality would own intended-use requirements and finance would challenge the utilisation case. Before any trial, those owners would agree the acceptance threshold and the circumstances that invalidate the comparison. An external recovery quote should be reconciled with transport, rejected loads and custody obligations, so an attractive headline rate does not become a misleading purchasing decision.

Sources and scope

EMA | ICH Q7 Good Manufacturing Practice for APIs

EMA | Chemistry of active substances

DESNZ | Greenhouse gas reporting conversion factors 2026

These references inform the questions and boundaries. The study design above is a proposed NEUVIOR approach, not a published result or an installed service. Scope, specialist partners, access, responsibilities and fees would be agreed before any commissioned work.

Bring us the decision you need to make

A useful first discussion starts with one process, one accountable owner and the choice that needs evidence. Share the decision deadline, the information already available and what a credible result would allow your team to do next.

Another useful angle.

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