Process & Systems › Reuse Planning
Each reuse decision carries its own risk profile, its own assurance obligation, and its own set of constraints. We apply targeted diagnostics to confirm what is driving risk, what must be measured, and what the performance and verification basis has to be - so the scope you take to vendors is built from confirmed findings, not assumptions.
Overview
Planning a reuse scheme means working through a sequence of decisions before design begins, combining feasibility assessment with risk identification at each step. Is the water quality suitable for the intended end-use, and what health and operational risks does that application carry? Is the Class A biosolids route viable, and what pathogen or metals risks influence that route? Does the industrial feed support the ZLD scope, and what hazardous loads need to be managed? These four categories organise that planning work. Each is supported by diagnostic tools that test viability, identify the controls needed, and define the performance checks before the project moves ahead.
Each of the four diagnostic categories - reuse and water planning, biosolids, industrial and ZLD, and septicity and hazard - follows the same three-stage path: confirm what the risk profile actually is, map the treatment response to a sequenced set of FlowPlan modules, then translate the findings into a vendor-ready scope with performance verification defined before anyone quotes.
Select a planning category to see the diagnostic tools used to confirm viability, define the treatment route, and set performance and verification requirements at each decision point.
Reuse & Water Planning
Sludge & Biosolids
Industrial & ZLD Diagnostics
Septicity, Odor & Hazard DiagnosticsScreens solids degradability and energy yield to confirm whether digestion or co-digestion adds value.
Each diagnostic tool is used at a specific planning decision point - confirming whether a route is viable, what it requires, and how the findings connect to FlowPlan module selection, scope definition, and performance verification.
Reuse & Water PlanningThese diagnostics work through the planning decisions that precede design - combining feasibility assessment with reuse risk evaluation. Which end-use is viable given actual effluent quality? What health and operational risks does that application carry, and what assurance class governs it? Which treatment barriers are needed to hold that class reliably, and what monitoring and verification requirements follow from the risk profile? The answers define the planning basis and the scope before any vendor is engaged.
Checks whether the intended end use can be supported by the treated water available, covering exposure risk, demand pattern, storage, and the treatment and monitoring level needed before reuse is committed.
Links to: → Clari+, Micra+, OxiClear+
Builds a design usable picture of the water, covering key parameters, variability, and data gaps so early reuse or treatment decisions are not based on partial sampling.
Links to: → MBBR+, MicraRO+, ROCore+
Clarifies the health and operating risks tied to the intended reuse application, so barrier needs, monitoring, and the required level of control are set before the route is carried forward.
Links to: → OxiClear+, Clari+
Turns the intended reuse application into a practical treatment route, linking reuse class, health protection needs, polishing steps, storage, and monitoring so the route can be scoped with confidence.
Links to: → Clari+, Micra+, OxiClear+, ROCore+
Clarifies the approval route, operating limits, submission requirements, and performance checks that need to be in place before the reuse or discharge route is taken forward.
Links to: → Micra+, OxiClear+, ROCore+, Clari+
Builds a usable picture of inlet quality, variability, and flow behaviour, so treatment choices respond to plant conditions rather than one-off samples.
Links to: → Batch+, Micra+
Sludge & BiosolidsBefore dewatering and drying assets are committed, the biosolids pathway has to be confirmed as both viable and safe. What do the stream characteristics actually support? Are pathogen concentrations and contaminant loads within the bounds that Class A and the intended end-use require? Do metals or toxics constrain the reuse or market option? These diagnostics address both the planning viability and the risk picture - so the pathway, QA regime, and handling route are defined on a confirmed basis before capital commitments are made.
Quantifies biosolids volumes, solids content, stabilisation status, and handling constraints, then maps the viable Class A route, including dewatering, drying, composting, or thermal steps, so footprint, logistics, QA points, and downstream scope are defined before equipment or off take commitments are made.
Links to: → Sludge+Dewater, Sludge+Dry
Tests whether the sludge is better routed to compost, biofertilizer, or organo-mineral product, and what processing, compliance, and buyer requirements each route brings.
Links to: → Sludge+Fert, Sludge+Bio
Checks whether pathogen and contaminant levels support the intended Class A route, and what processing and QA controls are needed before material can move off site.
Links to: → Sludge+Compost, Sludge+Dry
Shows whether metals or toxic compounds narrow land application and product routes, call for tighter source control and batch checks, or push the material away from reuse toward a thermal route.
Links to: → Sludge+Dewater, Incineration+
Tests whether the sludge has enough degradable organic content to justify digestion or co digestion, using VS, sludge origin, and heat energy balance to show whether recovery adds value or whether the route is mainly about stabilisation.
Links to: → Sludge+Dewater, Thermo+, Incineration+
Assesses whether phosphorus concentration and mass balance justify recovery, and which route fits the stream, direct biosolids use, liquid phase recovery, or ash based recovery after incineration, with contaminant limits, product quality, and market fit checked at the same time.
Links to: → Sludge+Fert, Sludge+Bio, Incineration+
Industrial & ZLD DiagnosticsIndustrial and ZLD planning begins with confirming whether the intended route is feasible given the actual feed, and what hazardous load and scaling risks have to be managed along the way. Batch discharges, CIP cycles, and peak loads define the practical treatment range. Hazardous compounds, scaling ions, and toxicity levels determine whether the route is safe to operate and what protection the downstream stages need. These diagnostics establish both the feasibility basis and the risk controls before membranes, thermal equipment, or brine handling assets are specified.
Builds the industrial feed picture across shifts, batches, and cleaning cycles so pretreatment, ZLD readiness, and membrane duty are set on plant behaviour, not averages.
Links to: → Batch+, MBBR+, ROCore+
Tests whether the feed can be prepared for concentration without fouling or scaling the system, and what pretreatment and recovery approach makes the ZLD route workable.
Links to: → ZLD+Prep+, ROCore+, Batch+
Works through how reject brine and resulting solids are concentrated, separated, and handled, so evaporator choice, crystallizer need, and solids management are thought through together.
Links to: → ZLD+Prep+
Identifies hazardous chemical loads that change treatment selection, containment needs, operator protection, and the reuse or discharge route that can realistically be taken forward.
Links to: → Batch+, ZLD+Prep+, ROCore+
Checks whether the upstream chemistry is fit to protect UF, RO, or thermal stages, and where extra conditioning is needed to avoid scaling, fouling, or unstable operation.
Links to: → Batch+, MBBR+, ROCore+
Defines the pretreatment steps, monitoring points, and paperwork needed to keep trade effluent discharge within permit limits and reduce compliance risk.
Links to: → Batch+, MBBR+, Clari+
Septicity, Odor & Hazard DiagnosticsA reuse scheme designed against assumed feed quality carries planning gaps and risk gaps simultaneously. Upstream contamination, septic rising mains, H₂S loads, and first-flush events affect both what the scheme needs to handle and what risks it exposes operators and downstream processes to. These diagnostics confirm what is actually entering the system - so the pretreatment scope, risk controls, and monitoring requirements are built into the design from the start, not discovered after the first operational problem.
Tracks where upstream contamination is entering the catchment so the reuse scheme is not sized around assumptions and the right control points are dealt with first.
Links to: → Batch+, MBBR+, ROCore+
Builds a clearer view of runoff quality and first-flush behaviour so storage, pretreatment, and reuse expectations reflect what arrives during wet-weather events.
Links to: → Batch+, MBBR+, Clari+
Identifies where septicity and H₂S are likely to develop, what that means for feed quality and safety, and whether source control, dosing, capture, or polishing need to be built into scope early.
Links to: → Odor+Capture, Odor+Dose, Odor+Polish
Shows how centrate, filtrate, backwash, and other return streams alter the inlet load, and where recycle, sidestream treatment, or separate handling would improve recovery.
Links to: → Batch+, MBBR+, Clari+
Share your planning stage, the decisions you need to make, and the constraints affecting implementation. We will identify the most relevant diagnostic path, clarify what needs to be checked, and turn the findings into a practical scope with coordination points, monitoring needs, and performance checks clearly set out.
Select the area most relevant to your current stage and we will respond with the appropriate planning approach.
