As already mentioned, our main environmental objective is to further reduce emissions of dust, acidifying pollutants and CO2, but tackling these in an integrated way is a complex matter. Most reduction technologies have disadvantages as well as advantages in terms of efficiency, glass quality, yield, cross-media effects etc.
Under the terms of the European IPPC directive (2008/1/EC Integrated Pollution and Prevention Control) a Glass BAT (Best Available Techniques) reference document has been published. This describes the environmental techniques applicable to the glass industry together with their advantages and disadvantages. This document can be downloaded at http://eippcb.jrc.es/reference/.
To be proactive, AGC Glass Europe started the Air Pollution Control (APC) project six years ago. The project is led by a multi-disciplinary team (covering the environment, engineering, purchasing and technical coordination) in collaboration with the plants. The goal is to draw up the air environmental strategy for each plant, and to implement the strategies with real actions.
Within this project, AGC Glass Europe also participates actively in the process of developing new techniques.
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Fig. 9 SO2 and HCl specific emissions relative to 1980.

Fig. 10. Acid equivalent emissions (Hydrogen [H+] equivalent). Index 1998 = 100 on comparable basis

Fig. 11. Dust emissions. Index 1998 = 100 on comparable basis
Generally, in order to comply with the IPPC Directive and the local legislation derived from it, the main solution chosen is to install air pollution control (APC) units, together with a set of primary measures. These units are made up of a de-SOx system to abate the dust and acid components, and/or a de-NOx system to reduce the NOx depending on the level of reduction required.
At present, AGC Glass Europe has already installed eleven APCs, and the goal is to install five more in the next few years. The cost of one complete APC installation can be as much as € 5,000,000.
Fig. 9 shows the reduction in specific emissions of sulphur oxides and chlorides since 1980. This clear reduction has been achieved thanks to the early installation of de-SOx systems in our group, together with improvements in technology and more careful selection of our raw materials.
NOx, SOx, HCl and HF emissions cause acid rain; they are calculated as hydrogen ion [H+] equivalents or acid equivalents . Fig. 10 shows the total amount of acid equivalent emitted in the last few years. When we take into account the large growth in the Group’s production capacity over these years, this corresponds to a reduction of 40% in specific emissions since 1998!
The specific dust emissions are shown in Fig. 11. The decrease in production volumes mainly due to the economic crisis has a significant impact on specific dust. But these emissions have been reduced by more than 50% since 1998!
The de-SOx part of an APC not only reduces air emissions but also produces large quantities of by-products, mainly sulphates, resulting from desulphurisation of the flue gas. To avoid simply transferring the pollution from the air to landfill, AGC Glass Europe favours recycling these sulphates wherever possible as raw material for the production of glass.
In 2010, more than 2,180 tonnes of sulphates have been recycled as raw material, and nearly 15,000 tonnes since the start in 1999. (see Fig 12)
The de-NOx part is based on the Selective Catalytic Reduction (SCR) system. Ammonia is injected into the flue gases and in contact with the catalyst it reacts with the NOx to give N2 and H2O, both naturally present in air.
The aim of AGC Glass Europe was again to be proactive in this area, and so the Group has already installed six catalyst-based de-NOx systems; the first of these was the second catalyst de-NOx installed in Europe, and the second was the first catalyst de-NOx in the world to be installed on an oil-fired furnace.
These de-NOx systems help to prevent more than 3,500 tonnes of NOx emissions each year within AGC glass Europe.
1Hydrogen is used as the reference substance for potential acid deposition onto the soil and in water. The acid equivalent of a compound is calculated from the H+ ion equivalent of the acid form of NOx, SOx, HCl and HF emitted. The acidification potential equivalence factors are: sulphur oxides 0.031, nitrogen oxides 0.022, hydrogen fluoride 0.050 and hydrogen chloride 0.027.
Air pollution control and waste recycling
The Air Pollution Control units at AGC Glass Europe’s plants provide an example of an integrated approach to the environment. These units remove acids and particulates from furnace flues. They are based on a two step treatment. The first step is a gas scrubber where the acids in the flue gases react with a neutralising reagent injected into the reactor. The second step is an electrostatic precipitator that captures the dust from the flue gases as well as the products of the scrubbing reactions.

Fig. 12. Filter dust recycled. Up to now, around 15,000 tonnes of filter dust have been recycled.
The process is specific to glass production, as the acid scrubbing reagent in the scrubber is sodium carbonate (Na2CO3), which is a raw material used in glass production. This material was chosen because the reaction of the carbonate with the sulphur oxides in the flue gases produces sodium sulphate (Na2SO4), which is also a raw material for glass.
Na2CO3 + SO2 + ½ O2 = Na2SO4 + CO2
Thus, the scrubbing system uses a raw material as a reagent and produces another raw material as result of the flue gas desulphurisation. So instead of being disposed of in a landfill, this raw material goes back to the furnace to be reused for glass production.
In other words we have a zero waste system, avoiding transfer of pollution from one medium (air) to another (ground).
AGC Glass Europe has received a Belgian environmental award for this system.
Moustier Line 2 Air Pollution Control unit.
The desulphurisation products are returned to the batch house as new raw material.