search.noResults

search.searching

saml.title
dataCollection.invalidEmail
note.createNoteMessage

search.noResults

search.searching

orderForm.title

orderForm.productCode
orderForm.description
orderForm.quantity
orderForm.itemPrice
orderForm.price
orderForm.totalPrice
orderForm.deliveryDetails.billingAddress
orderForm.deliveryDetails.deliveryAddress
orderForm.noItems
Monitoring & metering


FID: THE VOC EMISSIONS MONITORING REFERENCE METHOD - FOR OVER 50 YEARS!


The Flame Ionisation Detection (FID) method was first developed in the 1950s for the laboratory analysis of organic chemicals. Later, when environmental regulations began to limit the emissions of volatile organic chemicals (VOCs) in the 1970’s and 1980’s, the FID method was adapted for emissions monitoring. Signal Group was one of the first companies in the world to develop VOC emissions analysers, and in the following article the company’s managing director, James Clements, will explain why FID became the reference method, and why it lasted the test of time.


O


rganic chemicals have always been widely used in industrial processes, but awareness of the harmful effects of VOCs on health and the environment did not become significant until the 1970s. At that time, President Richard Nixon presented proposals on environmental protection which included the establishment of a federal Environmental Protection Agency (EPA). This led to the development of maximum allowable concentrations for pollutants, many of which were subsequently adopted around the world. VOCs are common constituents in the emissions of processes that involve petrochemicals, paints, coatings, adhesives, waxes, disinfectants and cleaning chemicals. In many of these processes, solvents play a major role and the release of VOCs represents a risk to health and the environment. Similarly, combustion processes give rise to VOC emissions, particularly where combustion involves the use of an organic fuel. This includes fossil fuels such as petrol, diesel and oil, as well as wastes and biofuels.


By monitoring total organic carbon (TOC) concentration in emissions, process operators can demonstrate compliance with relevant legislation. However, such measurements also provide insights for process optimisation, because, for example, the presence of organic compounds may be an indicator of incomplete combustion. In addition, TOC is frequently measured post-abatement in order to measure abatement efficiency.


WHY WAS FID CHOSEN AS THE REFERENCE METHOD FOR VOC EMISSIONS MONITORING? It is normal practice for regulators to specify a standard reference method for monitoring pollutants, so that compliance measurements are accurate and directly comparable with the limits, and with measurements from other process operators. FID has been widely acknowledged as the reference method for VOCs for over 50 years, and there are many reasons for this:


60


1. Already proven: initially developed as a detection method for laboratory Gas Chromatographs, FID was already well- established as a reliable technology for the detection of hydrocarbons. Adaptation for measuring VOC emissions was therefore relatively straightforward. As a consequence, Signal Group has been developing and supplying thousands of FID analysers all over the world for almost as long as FID has been the reference method.


2. Cost: in comparison with methods such as mass spectrometry (MS) or Fourier transform infrared spectroscopy (FTIR), FID is relatively simple and therefore less costly to manufacture. This is important because, globally, the number of processes that generate VOC emissions is enormous, so it is important that reference method technology is affordable for the organisations, large and small, that are required to monitor their hydrocarbon emissions, or that need to monitor for other purposes such as process control or abatement management.


3. Specificity: the FID detection method is specifically designed to detect carbon-hydrogen (C-H) bonds, making it highly selective for organic compounds. Unlike some other detection methods, FID does not respond significantly to inorganic gases which helps to minimise interference from non-VOCs, providing more accurate and reliable emissions measurements.


4. High sensitivity: the FID method is highly sensitive to hydrocarbons, which makes it ideal for even low-level measurements, particularly as environmental regulations become more stringent. Signal Group’s latest FIDs, for example, offer measurement resolution down to 0.01ppm. It is also important to note that FID sensitivity is much less variable than other techniques. Photoionisation detection (PID) for example exhibits widely varying response factors for individual hydrocarbons, rendering it inappropriate for the measurement of hydrocarbon mixtures. In contrast, FID is ideal for the measurement of total hydrocarbon content, whether the hydrocarbon is an individual compound or a mixture of species.


5. Wide range: in addition to their high sensitivity, FIDs are also able to make measurements at significantly higher ranges. The S4 Solar FID for example, has a number of user- selectable ranges, all the way from 0 to 1ppm with a resolution of 0.01ppm, up to 0 to 300,000 ppm with a resolution of 1ppm.


6. Fast response: FID analysers provide an almost immediate response to a sample gas, which is extremely important for regulatory compliance, particularly with processes emissions that can vary significantly from one minute to the next. The typical response time for Signal’s latest FIDs can be less than 1 second. This is also important for process control and engine emissions testing.


7. Stability and reproducibility: decades of experience in a wide variety of applications have shown FID’s ability to produce stable measurements in the long-term. Similarly, when identical FID units measure the same sample gas, the same results are given. This is an extremely important feature of standard reference methods because it provides confidence in measurements – for both the user and the regulator.


April 2025 Instrumentation Monthly


Page 1  |  Page 2  |  Page 3  |  Page 4  |  Page 5  |  Page 6  |  Page 7  |  Page 8  |  Page 9  |  Page 10  |  Page 11  |  Page 12  |  Page 13  |  Page 14  |  Page 15  |  Page 16  |  Page 17  |  Page 18  |  Page 19  |  Page 20  |  Page 21  |  Page 22  |  Page 23  |  Page 24  |  Page 25  |  Page 26  |  Page 27  |  Page 28  |  Page 29  |  Page 30  |  Page 31  |  Page 32  |  Page 33  |  Page 34  |  Page 35  |  Page 36  |  Page 37  |  Page 38  |  Page 39  |  Page 40  |  Page 41  |  Page 42  |  Page 43  |  Page 44  |  Page 45  |  Page 46  |  Page 47  |  Page 48  |  Page 49  |  Page 50  |  Page 51  |  Page 52  |  Page 53  |  Page 54  |  Page 55  |  Page 56  |  Page 57  |  Page 58  |  Page 59  |  Page 60  |  Page 61  |  Page 62  |  Page 63  |  Page 64  |  Page 65  |  Page 66  |  Page 67  |  Page 68  |  Page 69  |  Page 70  |  Page 71  |  Page 72  |  Page 73  |  Page 74  |  Page 75  |  Page 76  |  Page 77  |  Page 78  |  Page 79  |  Page 80