Blog

Chapter 9: Chemical Analysis in Water Treatment 

masthead-graphics

Introduction to Chemical Analysis in Water Treatment 

Source water sampling is vital to the design phase of industrial plants. Samples are ideally collected over a period of several months or longer to capture seasonal chemistry variations. This is particularly important when surface water is the makeup source. The data provides critical information that plant personnel and the water treatment chemical supplier use to develop the most effective treatment programs for the various plant systems. Additionally, this data is crucial for selecting makeup treatment equipment and determining the appropriate materials for heat exchangers and other water system components. Design engineers often select materials without considering water chemistry, only to learn later that some of the selected metals are ill-suited. For existing facilities, periodic makeup, cooling, and wastewater analyses are necessary to evaluate process conditions and discover if treatment programs are effective or in need of modifications.

This chapter highlights laboratory capabilities and provides examples of how data is utilized to solve customer issues at ChemTreat’s state-of-the-art Technology and Innovation Center; however, water is not the only constituent of importance. Addressing scaling or microbiological fouling issues requires performing deposit analyses, while metallurgical analyses are often needed for corrosion investigations, as will be explored in this chapter. When troubleshooting water system issues, it is also critical to consider operational parameters, equipment manuals, and manufacturer’s guidelines.

Figure 9.1 ChemTreat Technology and Innovation Center

 Interpreting a Water Analysis

The document below demonstrates the analyses ChemTreat lab personnel perform on a standard sample, and it features water chemistry data from an industrial facility. Additional analyses are available upon client request or as necessitated by specific circumstances.

Figure 9.2. An analysis of makeup and cooling water chemistry at an industrial plant.

The first item to note is that this plant has two possible makeup sources, groundwater and municipal wastewater treatment plant effluent (designated in this report as WTP). WTP is the primary source at this facility. The WTP sample contains a high concentration of dissolved solids, which can affect makeup pre-treatment equipment selection and influence the potential for corrosion, scaling, and microbiological fouling in the cooling systems. One may ask, “Why would the plant accept WTP effluent as raw makeup instead of well water?” There are a few potential possibilities.

  • The groundwater capacity may be limited and unable to supply the full needs of the plant.
  • The WTP effluent may be much cheaper.
  • In some places, like California, regulations require plants to take wastewater plant effluent for makeup. In other cases, plant management makes that choice as support for sustainable technology.

Now we will examine other constituents in the WTP stream that have significant impact on plant operations or on treatment programs and materials selection. It is important to note that Figure 9.2 is only a snapshot analysis. Conditions can fluctuate significantly within short periods of time or seasonally.

  • Higher calcium, magnesium, alkalinity, and phosphate concentrations increase the potential for scale formation in cooling systems, particularly in heat exchangers where temperatures are higher. At this facility, sulfuric acid is injected to the cooling makeup to remove most alkalinity, minimizing the potential for calcium carbonate scale formation. This treatment method is reflected by the high sulfate concentration in the cooling water sample. As previously outlined, monitoring of calcium sulfate scaling potential becomes important in systems that utilize acid feed to reduce alkalinity.
  • The relatively high WTP dissolved solids concentration appears to limit the cooling tower to roughly three cycles of concentration (COC). The blowdown rate would be considerably lower if the COC could be adjusted upwards, potentially to five, six, or seven.
    • The data clearly illustrates why on-line specific conductivity measurement is common for cooling tower COC and blowdown control. The difference in conductivity between the WTP effluent and cooling water is nearly threefold, reflecting the presence of hard-to-measure constituents like chloride and magnesium 
  • The total organic carbon (TOC) concentration in the sample is 6.1 mg/L. This value is relatively high, and likely fluctuates significantly. TOC can impact operation in several ways.
    • Organics provide food for microbes that foul water systems.
    • Large organic compounds can foul the reverse osmosis membranes and ion exchange resins of high-purity makeup systems.
    • TOC reduction may require installation of tertiary treatment equipment at the industrial plant. Membrane bioreactors (MBR) and moving-bed bioreactors (MBBR) are two examples of emerging technologies. Installation of either adds cost and complexity to plant operations.
    • TOC can consume oxidizing biocides in cooling water systems, requiring elevated feed rates.
    • TOC can lead to trihalomethane compounds when oxidized using sodium hypochlorite or chlorine gas.
  • The ammonia, nitrate, and phosphate concentrations are all much higher than typically seen in freshwater or groundwater supplies. These species are primary nutrients for microorganisms and can promote rapid microbiological growth in cooling water systems.
  • The relatively high chloride concentration in the WTP effluent cycles up in the cooling tower. Chloride is a primary pitting agent of stainless steel, particularly the 300 series. Yet, on numerous occasions, ChemTreat personnel have seen new project specifications that call for 304 or 316 stainless steel steam surface condenser tubes without any consideration given to water quality, including chloride content. As outlined in Chapter 7, Introduction to Corrosion, Scale, and Biofouling Control in Cooling Systems, 304 SS can suffer pitting at chloride concentrations as low as 200 ppm, particularly if suspended solids or microbes have deposited on the tubes. The recommended limit for 316 SS is 400 ppm. Thus, these materials would be inadequate for this application.
  • The elevation in sulfate concentration per acid feed could require a higher grade of concrete for the cooling tower basin. Standard concrete is susceptible to sulfate degradation, which is an additional issue that the design engineers may not typically consider.

We will examine other constituents of a water sample that are significant in many plant operations, but it is first necessary to discuss the fundamental concept of balancing the major cations and anions. 

Balancing the Major Cations and Anions

When first evaluating a water report, it is essential to balance the major cations and anions. This allows you to initially confirm the laboratory report’s reliability. For example, the primary chemistry data from a snapshot analysis of a Midwestern lake that supplies a 1,500 MW power plant is included below.

Table 9-1. Analysis of a Midwestern Lake Water Sample

Parameter mg/L as Ion mg/L as CaCO3

Calcium (Ca2+)

46.4

116*

Magnesium (Mg2+)

9.2

37.7*

Potassium (K+)

5.1*

6.5

Sodium (Na+)

14.9*

32.5

Major Cations Subtotal   192.7
M-Alkalinity (HCO3) 144 117*
Chloride (Cl) 14.4* 20.3
Nitrate (NO3) 1.0* 0.8
Sulfate (SO42-) 49.0* 51.0
Major Anions Subtotal   189.1

* Indicates the units in which the constituent was reported.

Calcium carbonate equivalents involve a crucial accounting method used in raw water analysis. Consider the nature of the aqueous ions. Potassium and sodium are monovalent (+1 charge), while calcium and magnesium are divalent (+2). Likewise, bicarbonate alkalinity, chloride, and nitrate are monovalent, while sulfate is divalent. Thus, sodium will associate with one chloride, but calcium will associate with two. Similarly, two sodium ions will associate with sulfate, while only one calcium ion does. These valence variations, coupled with the different molecular weights of the ions, signify that an analysis with the constituents reported “as ion” or “as species” will not indicate whether the ions are in balance. Various techniques can be used to balance the constituents, such as converting ions to moles per liter or, more frequently in the water industry, to equivalents per liter. The most common method, however, is to convert the ions to their calcium carbonate equivalent. With a molecular weight close to 100, the calculation is simplified. The following table outlines the conversion factors for the ions shown above.

Table 9-2. Ion to CaCO3 Conversion Factors

Ion

Conversion Factor to CaCO3 Equivalent

Calcium

2.50

Magnesium

4.12

Potassium

1.28

Sodium

2.18

‘M’ alkalinity

0.81

Chloride

1.41

Nitrate

0.81

Sulfate

1.04

Many labs, including ChemTreat’s, report hardness ions and alkalinity as CaCO3, while other ions are recorded as species. Common guidelines suggest that the sums of the major cations and the major anions (as CaCO3) should balance within 10 percent to indicate acceptable lab accuracy. The two subtotals in Table 9-1 are within 1.9 percent, which is well within this threshold. Silica, as it is only weakly ionized in water, is not included in the balancing calculations.

Other Applications

The preceding sections highlighted important analyses for cooling water and makeup water systems. The following section will address additional applications.

Condensate Return

At many industrial facilities, a percentage (often large) of the steam utilized for process heating is recovered as condensate and returned to the boilers. Depending on the plant unit operations, or those facilities to which steam might be exported, condensate return may contain a wide variety of impurities ranging from corrosion products to chemicals leaking in at heat exchangers. Space limitations prevent a review of the many contaminants that could be present, but at refineries, petrochemical plants, and similar facilities, TOC is a critical measurement. Reliable on-line TOC analyzers are now available and can provide immediate notification of upset conditions.

Iron is another critical parameter to monitor in condensate samples, primarily because most of the condensate system is fabricated with carbon steel components. It is essential to measure total iron, because under the operating conditions of a well-functioning condensate system, most iron in the sample will be insoluble and require acid digestion for measurement.

Wastewater Trace Metal Analyses

Trace metal analyses can be particularly important for monitoring plant discharge streams, including those into and out of the facility’s wastewater treatment plant. The following table outlines harmful metals and metalloids that may appear in industrial wastewater for which regular analyses may be required.

Table 9-3. Toxic Trace Elements That May Be in Industrial Wastewaters

Table Adapted from Reference 1

Element

Sources

Arsenic

Mining wastewater, pesticides, chemical wastes

Beryllium

Coal leachate, industrial processes

Cadmium

Mining and metal industry wastewaters

Chromium (hexavalent species)

Metal plating

Copper

Metal plating, mining wastewater, heat exchanger corrosion

Lead

Industrial and mining wastewaters

Mercury

Industrial, coal, and mining wastewaters

Selenium

Coal combustion wastewaters

Silver

Electroplating processes

Zinc

Industrial and cooling tower wastewaters, metal plating

For these analyses, ChemTreat personnel utilize a variety of modern analytical equipment, including gas, ion, and liquid chromatography, inductively coupled plasma (ICP), ICP coupled with mass spectrometry, and TOC instrumentation.

Chapter-9-ChemTreat_Laboratory_042-2

Monitoring Industrial Plant Discharge Metals and TOC

Read Article

Deposit Analysis

Analyses of solids deposits and density are valuable in determining the factors behind scale formation or other deposition. The figure below shows a typical qualitative analysis of a boiler tube deposit.

Figure 9.3. Deposit analysis from the mud drum of an industrial steam generator.

This report illustrates a common problem in steam generators, buildup of iron oxides on boiler tubes and internals. The iron oxides are often corrosion products generated in condensate return or feedwater systems. When the particulates reach the boiler, the high temperatures induce deposition. Heavy deposits restrict heat transfer and can cause tube overheating. More critical is the potential for under-deposit corrosion by either acidic or alkaline species. The data shown in Figure 9.3 suggests that investigation is needed into sources of carbon steel corrosion within the steam generating network. Water sample iron analyses would assist in the investigation, potentially through grab-sampling methods and on-line techniques like nephelometry. 

Presence of other constituents in a deposit analysis suggest additional issues. For example:

  • Noticeable concentrations of calcium, magnesium, and silica indicate cooling water ingress from leaking steam surface condensers or heat exchanger tubes. Such ingress also allows additional contaminants to enter, most notably chloride and sulfate. In high-pressure boilers, these compounds can cause significant under-deposit corrosion, leading to premature tube failure.
  • The presence of hardness deposits may also indicate makeup water system upsets. Many industrial plants have low- to medium-pressure steam generators, where the primary makeup treatment method is sodium zeolite softening. Frequently, when ChemTreat representatives visit a plant for the first time, the plant staff mentions boiler tube failures. A review of plant records often shows softening system upsets, which may allow hardness-laden makeup to enter the boilers.
  • Copper in the deposit typically suggests corrosion of copper-alloy heat exchangers. Copper deposition will considerably increase the difficulty of chemically cleaning the equipment.
  • Loss on Ignition (LOI). Similar to TOC for water samples, LOI in solids samples typically suggests the infiltration of organic compounds into the system. As noted, organic ingress to condensate return is common at refineries and organic chemical plants. The organic compounds may bake onto boiler tubes and reduce heat transfer. Organics can also cause foaming in steam drums, which in turn induces solids carryover into steam. Rapid superheater tube failures are a well-known outcome of this phenomenon.  

Analytical techniques for deposit chemistry include:

  • Loss on Ignition (LOI)
  • X-ray Diffraction (XRD)
  • X-ray Fluorescence (XRF)
  • Scanning Electron Microscopy (SEM)
  • Thermogravimetric Analysis (TGA)

Figure 9.4. A scanning electron microscope in use at ChemTreat’s analytical lab.

Chapter-9-ChemTreat_Laboratory_042-2-1024x767-1

Optimizing an Alumina Plant’s Interstage Cooling Operation Campaign with FlexPro® Technology

View Case Study

Metallographic Analyses

Metallurgical analyses are often critical for evaluating failure mechanisms, and ChemTreat works closely with metallurgical experts to precisely determine the causes of corrosion and failures. A common corrosion example is shown in Figure 9.5 below, where an analysis revealed under-deposit acid corrosion of rifled boiler tubes caused by ingress of chloride from condenser tube leaks.

Figure 9.5. Under-deposit acid corrosion of a rifled boiler tube.

Other instances where metallurgical analyses provide crucial insights include, but are not limited to:

  • Boiler tube failures from overheat conditions. Short-term overheat differs from long-term overheat. The distinction between the two can be determined through close examination, providing clues about the operating conditions that led to the failures.
  • The mechanism responsible for an under-deposit corrosion failure. While Figure 9.5 illustrates corrosion caused by acid concentration under deposits, concentrated caustic can also lead to corrosion through a different pathway. In boilers on phosphate chemistry programs, attack may occur through acid-phosphate corrosion. The latter often resembles caustic attack, but the corrosion process is much different.
  • The mechanisms behind failures at weld seams. Improper welding procedures can alter the material composition at the heat affected zone (HAZ), rendering the metal in that region susceptible to corrosion. A metallurgical analysis can identify the change in metal composition at the HAZ.

Metallurgical analyses are often a guide for evaluation of chemistry treatment programs. For many years, coordinated and congruent phosphate chemistry were the recommended practices for high-pressure boilers. Researchers later found that this chemistry caused acid-phosphate corrosion in many units. Today, alternative phosphate programs are the standard.

In some cases, following failures, metallurgical examination has revealed that the tube or piping material is not what was specified in the original design. For example, the substitution of 304 SS for more robust materials in cooling water applications.

Corrosion Coupon Analysis 

Corrosion coupons are discussed in detail in Chapter 7. After field evaluation of extracted coupons, they require further lab analysis. It is very important, for example, to differentiate general corrosion from pitting.

Figure 9.6. A corrosion coupon that clearly illustrates pitting.

Figure 9.6 illustrates the benefit of having pictures of the coupon included before and after cleaning in the report. The images provide insights into the type of corrosion present, assisting in the recommendation of methods to mitigate corrosion in the system.

Similarly, analysis of scale on deposit coupons can reveal issues related to deposit-control chemistry.

Chapter-9-ChemTreat_Laboratory_042-2-1024x767-1

Industrial Manufacturer Saves $250,000 per Year with ChemTreat Service Water Corrosion Treatment Program


View Case Study

Microbiological Deposits

Chapter 7 discusses microbiological fouling of cooling waters and the tests that can identify the organisms responsible. If biofouling is observed during equipment inspection, inspectors should have the appropriate tools ready, including a small spatula, sample collection bottles or bags, and writing tools to document the sample time, date, and location, for further lab analysis. The analyses will provide valuable information about the microbes that have flourished in the system and offer guidance for future control. 

Figure 9.7. A microbiological analysis.

The microorganism species and the number of colony-forming units (cfu) are examples of the important criteria included in this report. This data enables the evaluation of the biocide program’s performance and potential modifications, and it highlights areas where treatment may be lacking, even if the rest of the system is in good condition.

Conclusion

Earlier chapters outlined the importance of on-line instrumentation for continuous monitoring of makeup, process, and cooling water chemistry. However, laboratory analyses are still vital for evaluating system conditions and revealing pathways for the selection or enhancement of chemical treatment programs. For new projects, pre-design raw water analyses are important for materials selection and preparation of chemical treatment programs. Always remember to consult with a team of experts when developing a treatment program.

References

  1. Manahan, S.E., Fundamentals of Environmental Chemistry, CRC Press LLC,
    Boca Raton, FL, 1993.
  2. Buecker, B., Kuruc, K., and F. Murphy, “Iron Monitoring in Industrial Steam Generating Systems”; Water Technology, Jan/Feb 2021.

About the Authors

Joel Phillips

Director, Analytical Lab

As the Director of ChemTreat’s Analytical Laboratory, Joel Phillips oversees a diverse team of scientists and researchers. Joel earned his B.S. in Chemistry from Virginia Tech, followed by a post-bac degree in Computer Science and an M.B.A. from Virginia Commonwealth University. Joel was instrumental in the construction and development of ChemTreat’s new, state-of-the-art Innovation Center in Ashland, Virginia, where new technologies and solutions are developed by ChemTreat’s experts. 

 

Mark McIntyre 

Senior Technical Support Consultant

Mark McIntyre has a B.S. in Mechanical Engineering Technology from LeTourneau University in Longview, Texas. He has worked in industrial water treatment since 1988 focusing primarily on heavy industry accounts. As part of ChemTreat’s internal consulting group, Mark provides technical oversight to our heavy industry customers, focusing primarily on boiler and cooling applications. 

Acknowledgements

The ChemTreat Water Essentials Handbook would not have been possible without the contributions of many people. See the full list of contributors.

cta-banner

Our Team has an Average of 15 Years Field Sales Experience

Talk to Your Local Representative

Contact Us

Table of Contents Back to Top