From White Rust to Long-Term Protection Mechanisms:
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19 November 2025
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Key Factors, Passivation Strategies and Field Applications for Galvanized Cooling Towers
Foreword:
Strategic decisions on passivation must be made based on site-specific factors, which this article does not cover in detail.
1. Introduction to Galvanized Steel
Galvanized steel is widely used in the construction of industrial cooling towers (CTs) due to its relatively low cost and its intrinsic corrosion resistance, provided by a sacrificial layer of metallic zinc. However, this protection is not passive: it requires a controlled oxidation phase to develop a durable, adherent film capable of shielding the zinc substrate from further corrosion. This passivation process is critical during the first days following system start-up.
Two distinct passivation pathways exist, each with different chemical origins and long-term implications:
Natural passivation leads to the formation of penta-zinc hydroxycarbonate (PZHC), a thermodynamically stable compound that forms spontaneously in mildly alkaline and aerated water, without chemical additives. The formation of PZHC is highly sensitive to water chemistry and system parameters and tends to be self-limiting once a coherent layer is established.
In contrast, induced passivation by phosphoric passivation results in the formation of hopeite (Zn₃(PO₄)₂·4H₂O), a zinc phosphate compound precipitated deliberately through the addition of phosphate species. This approach, while potentially effective, shifts the corrosion control mechanism and must be carefully dosed to avoid destabilizing the surface layer or triggering undesirable interactions with other water treatment agents.
The confusion between these two mechanisms has led to widespread operational errors, particularly during commissioning, when the introduction of corrosion inhibitors containing phosphonates or orthophosphates can interfere with the natural development of the PZHC layer. As a result, many CT systems suffer from premature formation of white rust—a loosely adherent, porous corrosion product that signals a failed passivation and significantly reduces the durability of the galvanized surface.
Operational confusion between these two mechanisms—natural versus induced passivation—has led to commissioning errors. The early introduction of phosphonates or orthophosphates during startup can disrupt PZHC formation, triggering white rust: a loosely adherent, porous zinc corrosion product indicative of failed passivation and reduced service life.
The objective of this article is clearly defined:
• Discuss exclusively natural passivation, based solely on mineral elements naturally present in the process water, excluding
any phosphate or additive-based intervention.
• Clarify the mechanism of PZHC formation
• Present a robust, field-validated commissioning strategy to promote enduring PZHC-driven protection of galvanized CT
components.
• Propose corrective measures strictly rooted in natural passivation principles.
2.Formation of the Protective Oxide Layer on Galvanized Steel
The natural passivation of galvanized steel relies on the progressive transformation of metallic zinc into a coherent, protective layer of penta-zinc hydroxycarbonate (PZHC). This process is governed by electrochemical reactions occurring at the metal–water interface, where oxygen availability, water chemistry, and thermodynamic stability collectively define the layer’s quality and durability.
2.1. Electrochemical Pathway to PZHC Formation
The oxidation of zinc begins at the anode:
Zn → Zn²⁺ + 2e⁻
These products combine to form an initial, metastable precipitate:
Zn²⁺ + 2OH⁻ → Zn(OH)₂
Protection is provided by PZHC, defined by the formula: Zn₅(CO₃)₂₋ₓ(OH)₆₊₂ₓ·H₂O, where x depends on the presence of inorganic carbon (given by the P-Alk and M-Alk measurements). The most thermodynamically stable structure is obtained for x = 0
Under the influence of dissolved inorganic carbon—primarily in the form of bicarbonate (HCO₃⁻)—this hydroxide is gradually transformed into PZHC, following the reaction:
5Zn(OH)₂ + 2HCO₃⁻ → Zn₅(CO₃)₂(OH)₆ + 2H₂O + 2OH⁻
The resulting PZHC layer is dense, adherent, and chemically stable under mildly alkaline conditions. It limits further zinc oxidation by acting as a semi-permeable barrier, allowing for long-term corrosion control without external chemical intervention [3,4,5,6,7,8,9]
Screenshot 2025 11 20 at 09.00.03 ODYSSEE Environnement
An infrared analysis makes it possible to assess the quality of the PZHC layer formed, based on the following criteria:
• Hydration: Peak at 3400 cm⁻¹ / Peak at 1390 cm⁻¹ (second peak)
The higher the value, the lower the quality of the PZHC.
• Crystallinity: Calculation = (Peak at 1507 cm⁻¹ + Peak at 1390 cm⁻¹) / Trough between the two peaks at 1446 cm⁻¹
The higher the value, the better the quality of the PZHC. [11]
2.2. Role of Water Chemistry Parameters
The formation and stability of the PZHC layer depend critically on a narrow envelope of water quality parameters during the initial exposure period (typically the first 4 to 12 weeks). Depending on the parameter, manufacturer recommendations may vary. The values presented here reflect a combination of OEM guidance, laboratory research, and field observations. Any passivation strategy must be adapted to the equipment and the specific operating conditions.
PARAMETER
RECOMMENDED RANGE
pH
7.4 – 8.5
CONDUCTIVITY
250 – 2’400 µS/cm
M-ALKALINITY
100 – 500 ppm (CaCO₃)
TOTAL HARDNESS (TH)
50 ppm (Ca²⁺/Mg²⁺)
DISSOLVED OXYGEN
Saturated (>6 ppm at 20 °C)
TEMPERATURE
< 60 °C (140 °F)
CHLORIDES / SULFATES
< 250 ppm
These parameters must be monitored and maintained in real time during the passivation phase. Any deviation—such as high pH from caustic leaks or insufficient buffering from low alkalinity—can result in non-adherent Zn(OH)₂ or amorphous carbonates, both precursors to white rust
2.3. Factors to Avoid During Natural Passivation
To ensure the PZHC layer forms slowly and uniformly, the following must be strictly avoided:
Either prevents layer formation or induces non-coherent precipitates
Note: The PZHC layer must not form too quickly to be protective, nor too slowly. The use of effective corrosion inhibitors during the layer formation phase should therefore be avoided.
3. White Rust: Misconceptions, Identification and Consequences
White rust is one form of natural surface oxidation, it refers to a white, powdery corrosion product that forms on freshly exposed galvanized steel in humid or aqueous environments. It is primarily composed of zinc hydroxides, carbonates, and oxides, typically in non-crystalline or poorly adherent forms. While often perceived as a superficial or aesthetic issue, its presence is a strong indicator of failed natural passivation
The presence of ‘white rust’ can indicate:
• A non-homogeneous protective PZHC layer due to initial surface condition (hard and adherent deposit),
• A non-protective PZHC layer (less hard and non-adherent deposit).
3.1. Misconceptions and Common Errors
Despite its visual impact, white rust is frequently misunderstood in both field operations and OEM guidance. The following misconceptions are widespread and dangerous:
• “White rust is only cosmetic”: In reality, it reveals localized corrosion and depletion of the protective zinc layer, particularly in areas of low oxygen or unstable pH.
• “Adding corrosion inhibitors will stop it”: If introduced too early, inhibitors (especially phosphates and molybdates) divert the electrochemical pathway, preventing coherent PZHC formation and favoring weak, mixed oxide layers.
• “It can be safely cleaned with acid”: Acid washing may remove the layer, but also dissolves partially formed passivation, leading to uncontrolled re-corrosion and deeper substrate attack.
This confusion is compounded by overlapping surface appearances between protective PZHC and non-protective white corrosion products, making infrared or SEM/EDX analysis essential in determining the layer’s nature and structure. [12,13]
3.2. Mechanisms Leading to White Rust
White rust results from an imbalance or disruption in the early passivation reactions. The most common causes are:
• Low conductivity (< 250 µS/cm) or lack of carbonate alkalinity: Prevents full conversion to PZHC.
• Presence of oxidizing agents (e.g., chlorine): Creates unstable oxides or porous films.
• Water stagnation or non-aerated conditions: Leads to differential aeration corrosion.
• Surface contamination prior to startup: Dust, oils or atmospheric corrosion products inhibit uniform passivation.
These conditions often arise during construction, delayed commissioning, or when bypassing proper pre-commissioning cleaning and conditioning protocols. [14,15]
3.3. Practical Identification and Field Implications
Visual signs of white rust include chalky or fluffy white spots, often localized on flat surfaces, welds, or areas with water retention. However, IRM or SEM analysis is necessary to distinguish it from adherent PZHC layers that may have a similar hue but very different protective behaviors (Figure 2).
Screenshot 2025 11 20 at 09.23.18 ODYSSEE Environnement
Operational consequences include:
• Reduced lifespan of galvanized surfaces (accelerated zinc loss)
• Premature loss of hydrophobicity and surface uniformity
• Local under-deposit corrosion risks
• Difficulties in post-facto treatment and irreversible aesthetic degradation
In severe cases, white rust development within the first month of startup can lead to complete failure of the protective coating within 12–18 months, particularly in high-temperature, low-hardness systems [3,16]
4. Field-Based Passivation Strategies: Protocol and Operational Execution
Successful natural passivation of galvanized cooling systems requires more than chemical control: it is a structured, field-driven protocol that ensures favorable electrochemical conditions are maintained long enough for the formation of a dense, adherent PZHC layer. Below is a stepwise breakdown of best practices implemented during the passivation window.
4.1. Initial Assessment and System Baseline
Full system review and documentation must be conducted prior to startup. This includes a historical assessment of water treatment performance, previous corrosion issues, and manufacturer specifications.
Photographic documentation of the tower structure, new coils, and tube bundles is recommended to serve as a baseline reference for future visual assessments.
4.2. Deployment of Monitoring Coupons
Corrosion coupons should be installed in representative areas of the system to allow direct measurement of corrosion rates and layer morphology.
If available, OEM reference coupons from the CT manufacturer can be used for comparative evaluation against standard protocols.
4.3. Water Chemistry Control and Concentration Ratio Adjustment
The concentration ratio must be adjusted during the passivation phase to maintain the parameters of 2.2.
Avoid active pH regulation systems, which often destabilize M-alkalinity and introduce variability detrimental to PZHC layer formation.
4.4. Real-Time Monitoring and Instrumentation
Ensure continuous online monitoring and data logging for the following critical parameters:
• pH
• Conductivity
• Redox potential
• Flow rate
• Temperature
These data serve both as a real-time control tool and a traceable record for validation and audit purposes.
4.5. Controlled Chemical Dosing
The formation of a durable and protective PZHC layer on galvanized surfaces depends not only on water chemistry but also on the compatibility of additives used during the passivation window. This section summarizes experimental evidence showing how different chemical agents influence the structure and quality of the passivation layer.
As a reminder, the formation of a PZHC passive layer is the primary objective during the first month of operation of a cooling tower.
Galvanized steel test coupons were immersed for 35 days (from 06/30/2016 to 08/04/2016) in 250 mL of solution (sealed bottles). At the end of the test period, surface deposits were collected and analyzed using infrared absorption spectrometry to verify whether or not an PZHC layer had properly formed.
Screenshot 2025 11 20 at 09.27.49 ODYSSEE Environnement
Note regarding the photos: The surfaces were deliberately scraped to collect the deposit material, which explains their lack of uniform coverage. For visual comparison, a new (unused) coupon was placed on the right in each photo.
City Water Reference: BD817 This sample contains PZHC as well as calcium carbonate in the form of aragonite (peaks labeled A). Due to spectral interference from the aragonite carbonate peak at 1481 cm⁻¹, it would be inadvisable to assign a crystallinity index value. However, the hydration index suggests the presence of a high-quality PZHC layer.
City Water Concentrated 1.2× Reference: BD824 The spectral peaks clearly correspond to PZHC. The crystallinity is moderate. Traces of calcium carbonate in the form of aragonite cannot be ruled out, due to the small peak observed at 856 cm⁻¹.
Screenshot 2025 11 20 at 09.30.39 ODYSSEE Environnement
City Water Concentrated 2× Reference: BD825 PZHC is also present in this sample, but its quality is lower than that obtained with non- concentrated city water. All indices confirm this observation: the crystallinity index drops, and the hydration index is high.
Screenshot 2025 11 20 at 09.31.35 ODYSSEE Environnement
Softened Water Reference: BD837
The spectrum reveals the presence of high- quality PZHC. The hydration index and the crystallinity index indicate that the resulting corrosion product is effectively protective.
Screenshot 2025 11 20 at 09.32.30 ODYSSEE Environnement
Demineralized Water Reference: BD838
The spectrum clearly indicates the presence of poorly crystallized zinc oxide (ZnO) and the absence of PZHC.
Screenshot 2025 11 20 at 09.35.18 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Co-Passivating Agents [17, 18,19] Reference: BD822
All spectral peaks correspond to PZHC, except for a few organic contamination signals around 2927 cm⁻¹. Here too, the quality appears good. It is comparable to that obtained with softened water, with similar crystallinity and hydration index values.
Screenshot 2025 11 20 at 09.36.50 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Co-Passivating Agents / Corrosion Inhibitor Reference: BD819
The sample reveals a complex mixture in which PZHC is present (peaks at 1506, 1398, 1043, and especially 825 cm⁻¹), but with poor crystallinity that could not be quantitatively assessed.
Screenshot 2025 11 20 at 09.38.02 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Co-Passivating Agents / Isothiazolone Reference: BD820
In this sample, the spectrum shows that all major peaks can be attributed to PZHC, with the exception of signals related to organic matter. Index calculations indicate that the PZHC layer has relatively low crystallinity.
Screenshot 2025 11 20 at 09.40.07 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Co-Passivating Agents / Isothiazolone + 20 ppm Biodispersant Reference: BD826
The deposit formed consists primarily of calcium carbonate in the form of calcite (peaks labeled C) and shows significant organic contamination. No evidence of PZHC could be identified. The two broad signals centered around 1045 and 482 cm⁻¹ strongly suggest the presence of amorphous deposits.
Screenshot 2025 11 20 at 09.41.02 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Phosphonates / Corrosion Inhibitor / Quats Reference: BD818
The peaks at 1632, 1063, and 592 cm⁻¹ do not exactly match those of standard PZHC. The spectrum suggests a complex mixture containing PZHC. Its complexity points to the presence of a phosphate-based matrix—or possibly silicates, if the additive identity were unknown. In any case, given the hydration index, the PZHC present appears to be quasi-amorphous or very poorly crystallized.
Screenshot 2025 11 20 at 09.41.49 ODYSSEE Environnement
City Water + 10 ppm Phosphonates Reference: BD823
The spectrum of this sample closely resembles that of the previous one. The overall structure appears to be amorphous or only very weakly crystallized.
Screenshot 2025 11 20 at 09.42.35 ODYSSEE Environnement
City Water + 100 ppm Proprietary Blend of Phosphonates Reference: BD821
The spectrum of this sample closely resembles the previous two. The overall deposit also appears to be amorphous or only very weakly crystallized.
Screenshot 2025 11 20 at 09.43.24 ODYSSEE Environnement
Untested Coupon (Blank) Reference: BD844
The near absence of any deposit makes analysis difficult, resulting in a spectrum of average quality. However, no PZHC was detected.
Screenshot 2025 11 20 at 09.44.32 ODYSSEE Environnement
4.5.1. Influence of Water Quality Alone
Test conditions showed that water without additives can still lead to PZHC formation, particularly in:
• Raw tap water (city water), even at 1.0× and 1.2× concentration: moderate to good layer quality
• Softened water: resulted in a high-quality PZHC layer
• Demineralized water: failed to form PZHC; instead, zinc oxide (ZnO) was detected, indicating the absence of protective passivation
This confirms that minimal mineral content (alkalinity, hardness) is essential for PZHC development.
4.5.2. Effects of Co-Passivating Agents
The addition of Co-Passivating Agents during passivation showed a positive impact on PZHC formation, when used alone and at controlled concentrations.
Proprietary Blend of Co-Passivating Agents in city water produced a highly crystalline PZHC layer, comparable to that formed in softened water.
These results suggest that the Blend of Co-Passivating Agents, when free from corrosion inhibition functions, is compatible with natural passivation and may even enhance PZHC structural development, provided they do not contain interfering agents.
4.5.3. Impact of Additive Interferences
The formation of PZHC was disrupted or inhibited in the presence of:
• Phosphonate corrosion inhibitors: yielded poorly crystalline or amorphous deposits
• Biodispersants: led to layers rich in calcium carbonate (calcite) with no identifiable PZHC
• Certain phosphate-based blends: resulted in amorphous or mixed deposits with poor PZHC signature
This confirms that phosphorus-based inhibitors, multifunctional dispersants and biodispersants must be avoided during natural passivation, as they can block or distort the electrochemical formation of the PZHC structure.
4.5.4. Optimal Observed Conditions
The best results were obtained:
• In terms of surface appearance: with city water + 100 ppm of the proprietary Blend of Co-Passivating Agent
• In terms of spectral analysis: with softened water and city water + 100 ppm of the proprietary Blend of Co-Passivating Agents. City water alone ranked third.
4.6. Routine Field Inspection
Weekly on-site inspections are strongly recommended throughout the 4–12-weeks passivation window. These should include:
• On-site water sampling and analysis
• Visual inspection of CT surfaces, coil exteriors, basin bottom
• Integrity checks of dosing and monitoring systems. The importance of continuous monitoring lies in the fact that even brief or isolated deviations can significantly impact the effectiveness of the passivation process.
4.7. End-of-Phase Validation
After 4 to 12 weeks, corrosion coupons must be retrieved and subjected to:
• Gravimetric weight loss analysis (per ASTM G1 or equivalent)
• Surface morphology evaluation using optical or infrared methods
• Optional SEM/EDX for composition and PZHC structure verification by experts
4.8. Documentation and Certification
A comprehensive passivation report must be drafted, including:
• Time-series data of monitored parameters
• Photographic records
• Laboratory and field analyses
• Interpretation of coupon results
• Visual assessment of galvanized surfaces
Upon successful review, issue a Passivation Certificate confirming the quality and durability of the PZHC layer. This document should include:
• Coupon analysis results
• Layer validation outcomes
• Compliance with expected parameters
• Approval from technical field supervisor
4.9. Corrective Actions in Case of White Rust
Despite strict adherence to best practices, field conditions may deviate, and white rust can occasionally develop during or after the passivation period. When early signs of localized corrosion or surface whitening appear, rapid and proportionate corrective action is required to prevent irreversible damage to the galvanized surface.
The type and extent of remediation must be guided by the severity and distribution of the observed corrosion.
4.9.1. Case 1: Slight White Rust (Localized, Powdery, Non-Adherent Spots)
Characterized by scattered, soft, superficial corrosion products, typically due to marginal deviations
Recommended action: Initiate a re-passivation cycle, including:
• Restabilization of water chemistry (see 2.2)
• Re-deployment of corrosion coupons for confirmation
No surface cleaning is necessary unless biofilm or debris is also present.
4.9.2. Case 2: Significant White Rust (Widespread, Adherent, or Crystalline Growth)
Usually observed when passivation has failed entirely
The corrosion layer is dense, layered, and may be slightly adherent but non-protective.
Recommended action:
Perform acid cleaning: o This step must be validated case by case depending on the surface condition, galvanizing thickness, and environmental constraints. o Excessive cleaning may remove zinc coating entirely if poorly controlled.
Immediately follow with a full natural passivation cycle, under strict monitoring conditions, with renewed water chemistry stabilization and coupon tracking.
Note: Acid cleaning is a last-resort solution, not part of a standard commissioning protocol. Any such intervention should be documented and justified through photographic evidence and SEM/IR layer analysis.
After corrective actions, a full restart of the validation process is required:
• New coupon set deployment
• Analytical validation of surface integrity
• Issuance of a revised passivation certificate, with incident traceability included in the report.
5.Discussion and Perspectives
The implementation of natural passivation protocols for galvanized cooling systems presents both technical opportunities and operational challenges. Based on field evidence and scientific principles, the approach proves effective when conditions are strictly controlled—but its reproducibility and scalability remain subject to external variability and human factors.
5.1. Strengths of the Natural Passivation Approach
• Environmentally aligned: No phosphorus, halogens, or heavy metals involved. Meets sustainable water management objectives and avoids regulatory risks.
• Surface integrity: PZHC layers formed under controlled conditions show strong adhesion, structural coherence, and long-term resistance to corrosion.
• No chemical residuals: Unlike phosphate-based passivation, no risk of persistent chemical by-products or interactions with downstream treatments.
• Cost control: Lower chemical consumption and simplified startup protocols reduce commissioning overheads.
5.2. Identified Limitations and Risk Factors
• Narrow operational window: Natural passivation is highly sensitive to pH, alkalinity, conductivity, and oxygenation; even short deviations may compromise success.
• Human dependency: Execution relies on operator expertise, proper interpretation of data, and strict discipline in field practices.
• Incompatibility with fast-track projects: Construction delays or exposure to weather frequently lead to early corrosion that precludes natural layer formation.
• Lack of international standardization: No unified guidelines exist across OEMs, consultants, and operators for natural passivation workflows.
References
Quantin, D. (2006). Galvanisations à chaud. In Techniques de l’ingénieur, Traité Corrosion Vieillissement (Cor 1534), pp. 2–8.
Hamlaoui, Y., Pedraza, F., & Tifouti, L. (2010). On the corrosion resistance of porous electroplated zinc coatings in different corrosive media. Electrochimica Acta, xx(x), xx‑xx. https://arxiv.org/abs/1005.5554
Association of Water Technologies (AWT). (2012). White Rust Prevention: An Industry Update and Guide. Presented at the AWT Annual Conference, Baltimore.
Kalendová, A., Veselý, D., & Štěpánek, M. (2019). Study of white rust layer structures under dispersant-modified water chemistry. Surface and Coatings Technology, 374, Article 125133. https://doi.org/10.1016/j.surfcoat.2019.125133
ASTM International. (2017). ASTM G1-03(2017): Standard Practice for Preparing, Cleaning, and Evaluating Corrosion Test Specimens. West Conshohocken, PA.
Ahmad, Z. (2006). Principles of Corrosion Engineering and Corrosion Control. Oxford: Butterworth-Heinemann.
Maurice, V., & Marcus, P. (2018). Current developments of nanoscale insight into corrosion protection by passive oxide films. Corrosion Science, xx(x), xx‑xx. https://arxiv.org/abs/1807.10689
Zhang, X. G. (2013). Corrosion and Electrochemistry of Zinc. New York: Springer.
Collazo, A., Díaz, B., Figueroa, R. F., et al. (2024). Corrosion resistance of a water‑borne resin doped with graphene derivatives applied on galvanized steel. Materials Research Express, xx(xx), xx‑xx. https://arxiv.org/abs/2401.15410
Chaussec, F. (2024). Note Flash n°7 – Acier galvanisé et formation de couche passive d’HCPZ. Internal R&D Report, Requeil, France.
J. LEDION, P. LEROY, J.-P. LABBE, Détermination du caractère incrustant d’une eau par un essai d’entartrage accéléré, Tech. Sci. Munic. (1971) (1985) 323–328.
SPX Cooling Technologies. (2016). White Rust: Identification and Prevention in Galvanized Cooling Towers. Technical Report TR-009A.
Baltimore Aircoil Company. (1992). White Rust on Galvanized Steel Cooling Towers. Baltimore, MD: Baltimore Aircoil Company
Evapco, Inc. (2009). White Rust on Galvanized Steel, Engineering Bulletin No. 036A. Tonawanda, NY: Evapco.
Evapco, Inc. (2016). Beyond Laboratory Research on White Rust and Passivation. Evapco Technical White Paper
Cooling Tower Institute. (1994). Guidelines for Treatment of Galvanized Cooling Towers to Prevent White Rust.
Printz, B. ; Chaussec, F. (2018). Vers un traitement naturel ou bio-sourcé de l’entartrage des réseaux industriels (Towards a natural or bio-sourced treatment of scaling in industrial networks), in Poitiers.
A. Buvignier, H. Cheap-charpentier, G. Chaussec, F. Chaussec, L’entartrage et son inhibition dans les réseaux d’eaux industrielles, Téchniques de l’ingénieur (2022).
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