Sensors create a stir in WWT sector
19 Mar 2013
Issues around the maintenance of dissolved oxygen (DO) sensors and the accuracy of measurements provided by these devices are causing significant concern in the UK water and wastewater industries.
In this sector, galvanic DO sensors were the device of choice up to about 10 years ago, until the arrival of optical DO probes, which removed the need for frequent recalibration and maintenance.
Optical DO sensors employ a technique that measures the rate at which oxygen absorbs an optical signal generated within a membrane impregnated with a fluorescent dye.
Galvanic oxygen sensors measure the current produced in an electrochemical reaction cell. A membrane serves as a barrier to allow molecular oxygen to diffuse into the reaction cell where it is reduced at the working electrode. This reaction produces a small current, which is proportional to oxygen concentration.
Galvanic dissolved oxygen sensors are inherently more precise when measuring low levels of dissolved oxygen, experts say. At zero oxygen concentration there is no current. At low concentrations there is little quenching of fluorescence, the processor has to reliably measure the small difference between two large numbers.
Galvanic sensors, however, consume oxygen and need a flowing or moving sample, whereas optical sensors work in stagnant water.
Both types of sensor have a membrane. The membrane on a galvanic sensor controls the rate of diffusion into the electrochemical reaction cell; on an optical sensor its primary role is to prevent ambient light affecting the measurement. The cleanliness of the membrane is vital to both types of sensor.
Although most water companies use optical sensors due to the guidance of their frameworks, there is often uncertainty about using these sensors and the measurements they provide. This, in turn, leads to costly over-treatment of wastewater to meet regulatory requirements.
The energy required for an activated sludge plant represents about two thirds of a wastewater treatment plant’s total costs, so controlling it is extremely important, notes Graham Meller, a specialist in this subject as environmental writer at Buttonwood Marketing.
“Water companies are also under pressure to reduce their carbon footprint, whilst complying with tighter EU discharge permits,” he said.
Over-aeration is often there to cope with any surge in influent load, but this results in wasted energy/cost.
Real-time controls are an obvious solution to the problem, Meller noted that many plants around Europe have been able to make energy savings of 20% or more with such systems.
A recent roundtable discussion on DO sensors brought together industry and regulatory experts, including: Alan Henson of Yorkshire Water; Andy Morse, Richard Bragg and Khaled Gajam, United Utilities; Jorgen Jonsson of The Water Research Centre and Robin Lennox, South West Water.
Their consensus was that many water companies are running their treatment plants at dissolved oxygen levels higher than strictly necessary to optimise the process, and so comply with environmental regulations.
Lack of confidence
A key factor behind these issues was an historic lack of confidence in the ability of monitors to reliably measure low dissolved oxygen levels, found the panel, which was chaired by Michael Strahand, general manager of Analytical Technology Europe – the manufacturer of electrochemical-sensor devices which hosted the discussion.
This overaeration was blamed for large energy costs built up by water treatment plants. Producing high dissolved oxygen concentrations requires large amounts of energy, particularly if dissolved oxygen levels become too high, the speakers noted.
Water companies, however, prefer to remain on the safe side by over-aerating sewage in order to over-treat it. Incurring large electricity bills, it seems, is a greater evil than being hit by penalties for breaching consents with the Environment Agency.
There was a consensus among the panel about the most pressing problem with dissolved oxygen sensors: the difficulty of cleaning both optical and galvanic sensors, due to the build up of sludge which affects the accuracy of both instrument types.
Problems with cleaning dissolved oxygen sensors also encompassed issues of “damaged trust” between manufacturers of sensors and water companies, as previously some manufacturers had sold sensors as “maintenance free”.
Experts at the meeting went on to complain that large amounts of time and resources were being spent each year on cleaning sensors. The panel members also asked suppliers of dissolved oxygen sensors – some present at the meeting – to provide more information and guidance on the cleaning of these instruments.
Indeed, one of the most important points to emerge from the discussion was that instrument maintenance was more important to users than the actual technology: the instrument must be properly maintained and regularly cleaned in order to measure dissolved oxygen accurately.
Manufacturers were also urged to offer maintenance warranties, and to work to develop technologies such as auto-cleaning functions for dissolved oxygen sensors, as well as capabilities to detect and alert end users when a device needs cleaning.
The overall conclusion of the roundtable discussion, though, was that electrochemical and optical sensor are both capable of delivering the accuracy and reliability required by water companies if they are kept clean and well maintained.
The rise and rise of optical sensors
Graham Meller details how the technology has quickly become established throughout the wastewater industry over recent years
The energy required by an activated sludge plant represents about two thirds of a wastewater treatment plant’s total costs so it is extremely significant – not least because water companies are also under pressure to reduce their carbon footprint, whilst complying with tighter EU discharge permits.
Over-aeration is possible when plants are set to cope with any surge in influent load. However, this results in wasted energy and higher costs, so the answer is real-time control (RTC) or process optimisation that monitors influent ‘strength’ and adjusts the aeration process accordingly.
Many plants around Europe have been able to make energy savings of 20% or more with RTC systems. For example, a wastewater treatment plant at Holdenhurst near Bournemouth has reduced power consumption by 25% following the introduction of a real-time control system.
Under this system, the ammonia load is measured by sensors, which are installed at the beginning and the end of each set of aeration lanes, and dissolved oxygen (DO) probes are located in each of the zones within every lane.
The RTC system determines the most efficient aeration level and continuously feeds DO set points to the PLC which controls the blowers. This means, when the plant is under RTC control, DO set points are no longer ‘fixed’, instead they ‘float’ according to the load.
A reliable DO sensor is obviously very important and the development of optical DO sensors has revolutionised this sector.
Galvanic DO sensors predominated until the early 2000’s. They employ membranes, anodes, cathodes, and electrolyte solutions that generally require a high degree of maintenance. These sensors can also suffer from drift – gradual loss of accuracy – and so have to be recalibrated frequently. In addition, the sensor’s anode is consumed over time and will require replacement. It can also need replacement if it, or the electrolyte, becomes poisoned by gases such as hydrogen sulphide.
Other factors that can affect the accuracy of these traditional sensors, include variations in pH or the presence of chemicals that induce voltage, such as iron and aluminium salts, and polymers.
Optical DO sensors do not consume oxygen as part of the measurement process, and do not suffer from drift.
Back in 2003, I interviewed engineers from seven of the UK’s major water companies about their experiences with a new optical DO sensor. The feedback was unanimously positive, not least because it was no longer necessary to repeatedly remove and recalibrate a sensor that spent most of its life in sewage.
The sensor which I reported on in 2003 was developed by Hach Lange. Known as the LDO, this sensor is coated with a luminescent material, called luminophore, which is excited by blue light from an internal LED. As the luminescent material relaxes it emits red light, and this luminescence is proportional to the dissolved oxygen present.
The luminescence is measured both in terms of its maximum intensity and its decay time. An internal red LED provides a reference measurement before every reading to ensure that the sensor’s accuracy is maintained.
Since the launch of this sensor, a number of other manufacturers also introduced optical sensors and this technology is now commonplace in both municipal and industrial wastewater applications.
Graham Meller is environmental writer at Buttonwood Marketing