Total organic carbon (TOC) is the amount of carbon found in an organic compound and is often used as a non-specific indicator of water quality or cleanliness of pharmaceutical manufacturing equipment. TOC may also refer to the amount of organic carbon in soil, or in a geological formation, particularly the source rock for a petroleum play; 2% is a rough minimum.For marine surface sediments, average TOC content is 0.5% in the deep ocean, and 2% along the eastern margins.
understand the analysis process better, some key basic terminologies should be understood and their relationships to one another
Total Carbon (TC) – all the carbon in the sample, including both inorganic and organic carbon
Total Inorganic Carbon (TIC) – often referred to as inorganic carbon (IC), carbonate, bicarbonate, and dissolved carbon dioxide (CO2).
Total Organic Carbon (TOC) – material derived from decaying vegetation, bacterial growth, and metabolic activities of living organisms or chemicals.
Elemental Carbon (EC) – charcoal, coal, and soot. Resistant to analytical digestion and extraction, EC can be a fraction of either TIC or TOC depending on analytical approach.[8]
Non-Purgeable Organic Carbon (NPOC) – commonly referred to as TOC; organic carbon remaining in an acidified sample after purging the sample with gas.
Purgeable (volatile) Organic Compound (VOC) – organic carbon that has been removed from a neutral, or acidified sample by purging with an inert gas. These are the same compounds referred to as Volatile Organic Compounds (VOC) and usually determined by Purge and Trap Gas Chromatography.
Dissolved Organic Carbon (DOC) – organic carbon remaining in a sample after filtering the sample, typically using a 0.45 micrometer filter.
Suspended Organic Carbon – also called particulate organic carbon (POC); the carbon in particulate form that is too large to pass through a filter.Total organic carbon (TOC) is the amount of carbon found in an organic compound and is often used as a non-specific indicator of water quality or cleanliness of pharmaceutical manufacturing equipment. TOC may also refer to the amount of organic carbon in soil, or in a geological formation, particularly the source rock for a petroleum play; 2% is a rough minimum.For marine surface sediments, average TOC content is 0.5% in the deep ocean, and 2% along the eastern margins.
understand the analysis process better, some key basic terminologies should be understood and their relationships to one another
Total Carbon (TC) – all the carbon in the sample, including both inorganic and organic carbon
Total Inorganic Carbon (TIC) – often referred to as inorganic carbon (IC), carbonate, bicarbonate, and dissolved carbon dioxide (CO2).
Total Organic Carbon (TOC) – material derived from decaying vegetation, bacterial growth, and metabolic activities of living organisms or chemicals.
Elemental Carbon (EC) – charcoal, coal, and soot. Resistant to analytical digestion and extraction, EC can be a fraction of either TIC or TOC depending on analytical approach.[8]
Non-Purgeable Organic Carbon (NPOC) – commonly referred to as TOC; organic carbon remaining in an acidified sample after purging the sample with gas.
Purgeable (volatile) Organic Compound (VOC) – organic carbon that has been removed from a neutral, or acidified sample by purging with an inert gas. These are the same compounds referred to as Volatile Organic Compounds (VOC) and usually determined by Purge and Trap Gas Chromatography.
Dissolved Organic Carbon (DOC) – organic carbon remaining in a sample after filtering the sample, typically using a 0.45 micrometer filter.
Suspended Organic Carbon – also called particulate organic carbon (POC); the carbon in particulate form that is too large to pass through a filter.

 

Total Organic Carbon (TOC) Analyzers Information

Image Credit: GE Analytical Instruments, Shimadzu Scientific Instruments, Teledyne Instruments

Carbon content is one of the most important parameters measured in various types of solutions, from commercial drinking water to industrial wastewater. Total organic carbon¹ (TOC) analyzers are devices used to analyze the organic carbon content in these water or liquid solutions. They provide highly sensitive, non-specific readouts of all TOC through two-stage processes involving oxidation and detection. These devices are necessary to account for chemical solvents and bacteria that contaminate water solutions. This is important because of the harmful effects that TOCs may have on health and the environment.

Type of Water	TOC (mg/L)
High purity water	<0.01
Water for injection	<0.50
Ground water	<1
Seawater	<1
Drinking water	<4
Surface water	<10
Wastewater	>10

Table 1 – Examples of water sample types and their average TOC levels. Table Credit: Tekmar-Dohrmann

In analyzing a material that contains carbon, one must first understand the different types of carbon that may be present. Figure 1 shows a hierarchy of carbon types.
In order to analyze a sample, TOC analyzers employ either differential or direct methods of measurement.
In the differential method (also known as TC-IC), both total carbon (TC) and total inorganic carbon² (TIC) may be determined by separate measurement and TOC may be calculated by subtracting TIC from TC. This method is suitable for samples in which TIC is less than or of similar size to TOC.

In the direct method, TIC is removed from a sample by purging³ the acidified sample with a purified gas. TOC is then determined by oxidation. This method is also known as NPOC (non-purgeable organic carbon) due to the fact that POC (purgeable organic carbon) such as benzene, toluene, cyclohexane, and chloroform may be partly removed from a sample by gas stripping. The direct method is suitable for surface water, ground water, and drinking water because of (in most cases) less TOC than IC and a negligible amount of POC in these samples.

Selection

When selecting a TOC analyzer, industrial buyers should focus on the analysis methods and performance specifications of the device.

Methods of Analysis

TOC analyzers can employ a number of different techniques for oxidation and detection of TOC. These methods generally have a specific analytical range and many have been officially standardized. The table below provides an overview of this information.

Oxidation	Detection Technique	Analytical Range	Official Methods
UV/persulfate4	NDIR5	0.002 to 10,000 mg/L	EPA 415.1, 9060A Standard Methods 5310C ASTM D2579, ISO (Draft) 8245, AOAC 973.47, USP 643
Heated persulfate	NDIR	0.002 to 1,000 mg/L	EPA 415.1, 9060A Standard Methods 5310C ASTM D2579, ISO (Draft) 8245, AOAC 973.47, USP 643
Combustion	NDIR	0.004 to 25,000 mg/L	EPA 415.1, 9060A Standard Methods 5310B ASTM D2579, ISO (Draft) 8245, AOAC 973.47, USP 643
UV/persulfate	Membrane/conductivity	0.0005 to 50 mg/L	Standard Methods 5310C, USP 643
UV	Conductivity or NDIR	0.0005 to 0.5 mg/L	USP 643

Table 2 – Overview of different types of analyzers based on oxidation and detection methods. Table Credit: Tekmar-Dohrmann

Oxidation

All TOC analyzers offered today employ either combustion or low-temperature oxidation techniques. The purpose of the oxidation step is to convert the organics to carbon dioxide which can be measured by a detector to provide TOC values.

• Low-temperature oxidation is chemical oxidation aided by 100°C heat and either persulfate, UV irradiation and persulfate, or only UV irradiation. The low-temperature techniques have the advantage of allowing a large volume of sample to be analyzed, thereby improving the low limit of detection. Also, the blank value is very low as long as the reagents are pure, which makes the analysis more accurate.
  1. Ultraviolet irradiation uses ultra-violet light to oxidize the carbon present in the sample to produce carbon dioxide. UV oxidation is the most reliable, low maintenance method for TOC analysis of ultra-pure waters.
  2. Thermo-chemical (persulfate) oxidation, also called “heated persulfate”, uses the same free radical formation method as UV/persulfate oxidation, but also uses heat to magnify the oxidation power of persulfate. Unlike UV/persulfate, this method is not susceptible to lower recoveries resulting from turbidity in samples. TOC analyzers which incorporate thermo-chemical oxidation are useful in wastewater, drinking water, and pharmaceutical water analysis. When used with sensitive non-dispersive infrared (NDIR) cell detectors, these analyzers can readily measure TOC up to hundreds of ppm depending on samples volumes.
  3. UV/persulfate irradiation uses UV light for oxidation magnified by a chemical oxidizer (usually persulfate). TOC analyzers that use this oxidation method can measure levels of organic carbon as low as 200 parts per billion (ppb).
• High temperature combustion uses heat (680°C or higher) in a stream of air or pure oxygen and usually in the presence of a catalyst. The catalysts used are generally cupric oxide, cobalt oxide, or platinum on an alumina support. In the process, the oxygen-rich atmosphere converts all carbon to carbon dioxide to be measured. Most modern analyzers use NDIR to detect the carbon dioxide produced from combustion.

Application	TOC Analysis Method	Comments
High purity water	UV or UV/persulfate	Samples with less than 50 ppb TOC. UV or UV/persulfate provides the most trouble free operation and the ease of detecting very low level TOC.
Water for injection	UV or UV/persulfate	Samples with less than 500 ppb TOC. Combustion technology can measure in this range, but UV or UV/persulfate is still the easier method.
Drinking or source water	UV/persulfate or combustion	For meeting precision and accuracy requirements, UV/persulfate is the better technology. Combustion should be used if capturing the particulated organic carbon as part of the TOC value is important.
Salty water	Combustion	Combustion technology is not affected by chlorides present in seawater and other salty matrixes.
Industrial waste effluent	Combustion	Combustion technology was designed to handle particulates, chlorides, and tough to oxidize compounds typical of industrial waste.

Table 3 – TOC analysis method for different water samples. Table Credit: Tekmar-Dohrmann

Detection

Out of all components of a TOC analyzer, accurate detection and quantification are considered the most vital. Detection techniques include conductivity cells and non-dispersive infrared cells.

• Conductivity cells rely on aqueous CO₂ to raise acidity levels, causing the conductivity of the solution to increase. TOC analyzers that use a conductometric method can be used for the measurement of carbon dioxide in the liquid phase. Unlike NDIR detection, this method displays an extremely stable calibration and is not susceptible to considerable drift over time. This means that the TOC analyzer can be calibrated less frequently without compromising on analytical performance. Direct conductivity and membrane conductivity are the two types of conductivity detectors.
  1. Direct conductivity detectors provide simple and inexpensive CO₂ measurement, using no carrier gas. They suffer from an analytical range limited to parts per billion measurement, and are also susceptible to interference from ionic contamination, halogenated organic material, acids, and bases.
  2. Membrane conductivity detectors are more robust than direct devices, with a wide analytical range for both deionized and ionized water samples. In membrane conductivity, the membrane forms a protective barrier to interfering ions, enabling the exclusive analysis of carbon dioxide. This method suffers from a slow analysis time and is also prone to ‘false negatives’ due to the membrane acting as a site for secondary chemical reactions.