Paul Industries designs, installs and validates clean-in-place and steam-in-place systems across South Carolina. If your plant answers to a European parent as well as to the FDA, the cleaning validation question has already been settled in a way many American sites have not caught up with: since 1 June 2015 the European expectation has been a health-based limit calculated for the specific compound, not a convention like one thousandth of the minimum therapeutic dose. That changes what a CIP system has to be able to prove.
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A limit derived from toxicology, not from arithmetic
For decades cleaning limits in shared facilities were set by convention. The commonest were one thousandth of the minimum therapeutic dose of the previous product, a flat ten parts per million, and visually clean. These are easy to apply and they have an obvious weakness: none of them is derived from what the compound actually does to a person.
The EMA guideline on setting health-based exposure limits, effective 1 June 2015, replaced that logic for shared facilities. The limit becomes the permitted daily exposure, a figure derived from the toxicological data for the specific active ingredient. The guideline also provides a screening approach, so that products where existing conventional limits remain adequate can be identified rather than every compound requiring full derivation.
The reason this matters to engineering rather than only to quality is that it removes the ability to predict the answer. A compound with a benign toxicological profile may end up with a limit looser than the old convention. A potent or sensitizing compound may end up with one dramatically tighter. Nobody knows which until the derivation is done, and the system has to be capable of meeting whichever it turns out to be.
That has a specific design implication that is easy to state and expensive to retrofit: a CIP system designed against a convention is designed against a number that may not survive. Designing for demonstrated removal and reliable sampling, rather than for a particular residue figure, is what makes the system robust to a limit that changes.
What that means for the skid, the loop and the surfaces
Coverage has to be demonstrable, not assumed. Riboflavin coverage testing on vessels and spray devices, with the result recorded, is the difference between believing a tank is cleaned and being able to show it. Where a limit tightens, the first place residue survives is wherever coverage was marginal all along.
Sampling points have to exist and be reachable. Swab locations chosen for worst case rather than for convenience, rinse sampling points plumbed in rather than improvised, and the worst-case rationale written down. Retrofitting a sampling point into a validated system is a change control exercise nobody enjoys.
Analytical sensitivity becomes a design constraint. A tighter limit is only meaningful if the method can detect it with adequate margin. Conductivity and total organic carbon on the rinse are excellent for routine monitoring and are not necessarily sufficient for a compound-specific limit, which may require a specific method. Establishing what the method can see, before committing to the acceptance criterion, avoids a validated system that cannot demonstrate its own compliance.
Surfaces and dead legs decide the outcome. Cleaning chemistry and time can compensate for a great deal, but not for a pocket the solution never reaches at velocity. Drainable slopes, dead legs within ASME BPE limits, valve and instrument installations chosen for cleanability, and surface finish appropriate to the product.
| Basis | Derived from | Demands of the system |
|---|---|---|
| Visually clean | Inspection | Access and lighting; weakest as a sole criterion |
| 10 ppm | Convention | Routine analytics generally sufficient |
| 1/1000 minimum dose | Therapeutic dose arithmetic | Varies with the previous product |
| Permitted daily exposure | Toxicological data for the compound | Demonstrated coverage, real sampling, adequate method sensitivity |
| Heating load | Per cycle | Per 300 cycles |
|---|---|---|
| 60 kW | $12.31 | $3,693 |
| 120 kW | $24.62 | $7,387 |
| 240 kW | $49.25 | $14,774 |
South Carolina’s 6.84 cents per kilowatt-hour sits below the 8.13 cent national average, so the energy cost of a longer or hotter cycle is more absorbable here than in higher-tariff states. Where that helps is when a tightened limit makes a longer wash the cheapest available remedy, and the plant can afford to run it without the cycle time becoming a capacity problem.
Validation, and the sequence that avoids rework
The sequence that works is deliberately front-loaded. Establish the acceptance criterion first, in conversation with the toxicological assessment rather than after it. Confirm that an analytical method exists that can see that criterion with margin. Then design the system, with coverage and sampling as requirements rather than as things to be arranged later. Then demonstrate coverage. Then run validation.
Inverting that order is common and it is where cleaning validation projects fail. A system designed against an assumed limit, validated, and then confronted with a derived limit that is tighter leaves three options, all bad: modify a validated system, revalidate with extended cycles that eat capacity, or dedicate equipment that was purchased to be shared.
We build to ASME BPE, weld to AWS D18.1 with documentation retained, verify slope and drainability as built, and passivate to ASTM A967 after cleaning to ASTM A380. Where the plant is also subject to Annex 1 expectations, the cleaning and disinfection agents in use inform the material selection rather than the other way round.
Standards referenced: ASME BPE · EIA electricity price data · ASTM A967 · ASTM A380 · EU GMP Annex 1 (EudraLex Vol. 4)
Frequently asked questions
Do you build CIP and SIP systems in South Carolina?
Yes, across Greenville, Charleston, Columbia, Spartanburg and statewide: CIP skids, spray device selection and coverage testing, circuit design, SIP arrangements, instrumentation and the validation package. We work with sites answering to FDA alone and with sites whose European parent brings EMA expectations into scope.
What changed in 2015?
The EMA guideline on setting health-based exposure limits for shared facilities took effect on 1 June 2015. It replaced conventional cleaning limits with the permitted daily exposure, derived from toxicological data for the specific active ingredient, and provided a screening approach for identifying products where existing conventional limits remain adequate.
Does a health-based limit always make cleaning harder?
No, and that is the point. A compound with a benign toxicological profile may end up with a looser limit than the old convention gave it. A potent or sensitizing compound may end up with a dramatically tighter one. You cannot predict which until the derivation is done, which is why the system should be designed for demonstrated removal rather than a specific number.
What does that mean for design?
Design for demonstrable coverage and reliable sampling rather than for a particular residue figure. A system designed against a convention is designed against a number that may not survive the toxicological assessment, and the retrofit cost when it does not is far higher than the cost of designing robustly at the outset.
Why is coverage testing important?
Because it is the difference between believing a vessel is cleaned and being able to show it. Riboflavin coverage testing on vessels and spray devices, recorded, identifies the marginal areas. When a limit tightens, those marginal areas are exactly where residue survives, so knowing about them in advance is worth a great deal.
Can conductivity and TOC cover a compound-specific limit?
Not necessarily. They are excellent for routine rinse monitoring but a compound-specific limit may require a specific analytical method with adequate detection margin. Establish what the method can actually see before committing to an acceptance criterion, or you end up with a validated system that cannot demonstrate its own compliance.
Where should sampling points go?
At worst-case locations, chosen and justified on that basis rather than on accessibility, with the rationale written down and rinse sampling plumbed in rather than improvised. Retrofitting a sampling point into a validated system is a change control exercise that costs more than installing it would have.
What if the limit tightens after validation?
Three options, all unattractive: modify a validated system, revalidate with extended cycles that consume capacity, or dedicate equipment that was bought to be shared. This is the argument for establishing the acceptance criterion before designing rather than after, which is the sequence most projects get backwards.
Does South Carolina energy cost affect CIP decisions?
Helpfully, yes. At 6.84 cents per kilowatt-hour against a national average of 8.13 (EIA, 2024), a longer or hotter cycle is more absorbable here. That matters when a tightened limit makes extended washing the cheapest remedy, provided the extra cycle time does not turn into a capacity constraint.
How do I get a quote for a South Carolina CIP project?
Use the form on this page or call 201-450-8280. Useful inputs are the circuits and vessels involved, the products sharing the equipment, whether health-based exposure limits have been derived, what analytical methods are available, and whether EMA expectations apply alongside FDA.
What is a permitted daily exposure, and how does it set a cleaning limit?
A permitted daily exposure is a toxicologically derived dose of a compound that a patient can receive daily without harm, established from the compound's data. The cleaning limit for shared equipment is derived from it, the batch size and dose of the next product, and the equipment surface area.
Who calculates the health-based limit?
A qualified toxicologist prepares the assessment for each compound, and the plant's quality unit applies it to the cleaning limit calculation. The CIP contractor does not set the limit; the contractor designs the system to achieve and prove it.
Do health-based limits always apply to non-pharmaceutical products?
No. They apply to pharmaceutical products and their intermediates in shared facilities. Food, cosmetic and nutraceutical plants use different frameworks, though the principle of a defensible, product-specific limit is increasingly expected there too.
What is a cleaning validation matrix approach?
Grouping products by cleaning difficulty and toxicity so that the worst case in each group is validated and the others are covered by that result, which reduces the number of validation runs on a multi-product line. The grouping has to be justified scientifically and revisited whenever a product is added.
What is dedicated equipment justified by under the European approach?
Where the health-based limit is so low that cleaning cannot reliably achieve it, or where the compound is highly sensitising, the guidance expects dedicated facilities or equipment. The decision is documented from the toxicological assessment, not from convenience.
How does a European parent's quality system affect CIP documentation?
European sites expect cleaning validation aligned with EU GMP Annex 15 and the EMA guideline on health-based limits, with documentation formats and change control that the parent's quality system can review. The CIP records, protocols and reports are structured to satisfy both the parent and FDA.
What is a worst-case product in cleaning validation?
The product on shared equipment that is hardest to clean or has the lowest acceptable limit, used to bracket the validation. Under health-based limits the worst case may change as products are added, so the bracketing is reviewed with each new product.
How is a rinse sample related to a surface limit?
By a calculation that converts the surface limit to a concentration in the rinse volume, assuming the residue is fully recovered into the rinse. Rinse recovery has to be demonstrated, and swab sampling of hard-to-clean locations is normally required alongside.
How does a health-based limit affect SIP as well as CIP?
SIP does not remove residue and does not change the cleaning limit, but residue left before SIP can bake onto surfaces and become harder to remove. Cleaning validation under a tight limit therefore includes the sequence with SIP, not CIP alone.
What should be revalidated when a new product is introduced?
The new product's limit and cleanability are assessed against the existing bracket. If it becomes the new worst case, the cleaning validation is extended or repeated for it, and the CIP recipe may need changing.
Can a CIP system be designed for an unknown future limit?
Partly. Proven coverage, hot alkaline and acid capability, controllable time and temperature, and good sampling access give the plant room to tighten cycles later. What cannot be retrofitted cheaply is drainability and dead-leg elimination, so those are designed in from the start.
Does the aerospace and automotive base in South Carolina use these methods?
Industrial cleaning in those sectors follows different standards, but the German and European owners common in South Carolina often bring the same documentation expectations. Where a plant supplies pharmaceutical or medical customers, the cleaning validation approach applies directly.
How long does a cleaning validation under health-based limits take?
Longer than the conventional approach, mostly because the toxicological assessments and the specific analytical methods have to exist before the cleaning runs. Starting those early is what keeps a project on schedule.
What is the first step for a South Carolina plant moving to health-based limits?
Obtain the toxicological assessments for the products on shared equipment, recalculate the limits, and compare them with what the current cleaning has been proven to achieve. That comparison shows where the CIP system needs work before any redesign starts.
Do you work with the plant's toxicologist and quality unit?
Yes. The limit and the method come from them; the coverage, the cycle and the sampling access come from us, and the validation protocol is written together so that the system is designed to prove what the quality unit needs proven.
Cleaning validation for a South Carolina shared facility?
Tell us whether health-based exposure limits have been derived yet. If they have not, that is the conversation to have before the system is designed. Call 201-450-8280 or use the form below.
