(BAT) Reference Document for the Production of Chlor-alkali ...
(BAT) Reference Document for the Production of Chlor-alkali ... (BAT) Reference Document for the Production of Chlor-alkali ...
Chapter 2 2.6 Chlorine processing production, storage and handling 2.6.1 General description Generally, before the chlorine can be used, it goes through a series of processes for cooling, cleaning, drying, compression and liquefaction. In some applications, it can be used as a dry gas without the need for liquefaction. Very occasionally it can be used directly from the electrolysers. A general flow of chlorine from the electrolysers to storage is presented in Figure 2.1 Figure 2.14. The chlorine process usually takes hot, wet cell gas and converts it to a cold, dry gas. Chlorine gas leaving the electrolysers has a temperature of is at approximately 80 – 90 ºC and is saturated with water vapour. It also contains brine mist, impurities such as N2, H2, O2, CO2 and traces of chlorinated hydrocarbons. Electrolysers are operated at essentially atmospheric pressure with only a few mbar milli-atmospheres differential pressure between the anolyte and the catholyte. Figure 2.14: The flow of chlorine from the electrolysers to storage [Euro Chlor report, 1997] {The figure was removed because the information is contained in Figure 2.1.} 2.6.2 Materials The strong oxidising nature of chlorine requires a careful choice of construction materials at all stages of processing, depending on the operating conditions (temperature, pressure, state of matter, moisture content). Most metals are resistant to dry chlorine at temperatures below 100 °C. Above a specific temperature for each metal, depending also on the particle size of the metal, spontaneous ignition takes place (150 – 250 °C for iron). Carbon steel is the material most used for dry chlorine gas (water content below 20 ppmw). Wet chlorine gas rapidly attacks most common metallic materials with the exception of tantalum and titanium, the latter being the preferred choice in chlor-alkali installations. However, if the system does not remain sufficiently wet, titanium ignites spontaneously (ignition temperature ~ 20 °C). Other construction materials such as alloys, graphite, glass, porcelain and polymers are used depending on the conditions. Oils or greases generally react with chlorine upon contact unless they are fully halogenated [ 1, Ullmann's 2006 ], [ 3, Euro Chlor 2011 ]. 2.6.3 Cooling In the primary cooling process, the total volume of gas to be handled is reduced and a large amount of moisture is condensed. Cooling is accomplished in either one stage with chilled water or in two stages, with chilled water only used in the second stage. Care is taken to avoid excessive cooling because, at around 10 ºC, chlorine can combine with water to form a solid material known as chlorine hydrate (Cl2 · n H2O; n = 7 – 8). Maintaining temperatures above 15 °C 10 ºC prevents blockages in process equipment [ 1, Ullmann's 2006 ], [ 54, Euro Chlor 2010 ]. WORKING DRAFT IN PROGRESS Two methods are most frequently used to cool chlorine gas [ 38, O'Brien and White 1995 ]. One method is indirect cooling through a titanium surface (usually in a single-pass vertical shell-and-tube heat exchanger). The resultant condensate is either fed back into the brine system of the mercury or membrane cell technique process or is dechlorinated by evaporation in the case of the diaphragm cell technique process. This method causes less chlorine to be condensed or absorbed and generates less chlorine-saturated water for disposal. [Brien-White, 1995] Another method is direct contact with water. The chlorine gas is cooled by passing it directly into the bottom of a tower. in which the packing is divided into two sections, for 2stage cooling. Water is sprayed from into the top and flows countercurrent to the chlorine. 48 December 2011 TB/EIPPCB/CAK_Draft_1
Chapter 2 The cooling water is generally should be free of traces of ammonium salts to avoid the formation of nitrogen trichloride. This method has the advantage of better mass-transfer characteristics and higher thermal efficienciesy. Closed-circuit direct cooling of chlorine combines the advantages of the two methods. The chlorine-laden water from the cooling tower is cooled in titanium plate coolers and is recycled. The surplus condensate is treated exactly like the condensate from indirect cooling [ 1, Ullmann's 2006 ]. 2.6.4 Cleaning of wet chlorine Following primary cooling, chlorine gas is demisted of water droplets and impurities such as brine mist impurities. Impurities are removed mechanically by using special filters with glass wool fillings or porous quartz granules, or by means of an electrostatic precipitator. Chlorine is then passed to the drying towers [ 1, Ullmann's 2006 ]. 2.6.5 Drying Chlorine from the cooling system is more or less saturated with water vapour. The water content is typically 1 – 3 vol-%. This must be reduced in order to avoid downstream corrosion and minimise the formation of hydrates [ 38, O'Brien and White 1995 ] [Brien-White, 1995]. The drying of chlorine is carried out almost exclusively with concentrated sulphuric acid (96 – 98 wt-%) [Ullmann’s, 1996]. Drying is accomplished in countercurrent sulphuric acid contact towers in two to six stages, which reduce the moisture content to less than 20 mg/m 3 ppm [ 54, Euro Chlor 2010 ]. [Stenhammar] The remaining moisture content depends on the temperature and concentration of the sulphuric acid in the last drying stage. For lowtemperature liquefaction (see Section 2.6.8), a lower moisture content is required, which can be achieved by adding more equilibrium stages to the drying towers or by using molecular sieves to levels of 3 – 9 mg/m 3 [ 3, Euro Chlor 2011 ], [ 54, Euro Chlor 2010 ]. The number of stages is usually increased to lower the final strength of the spent sulphuric acid. For example, three stages are needed to reach a spent acid concentration of 50 – 65 wt-% while six stages are needed for a final concentration of 30 – 40 wt-%. The columns contain plastic packing resistant to chlorine and sulphuric acid to improve fluids distribution, increase efficiency and lower pressure drops, and thus reduce energy consumption. The heat liberated during dilution of the circulating acid is removed by titanium heat exchangers, and the spent acid is dechlorinated chemically or by stripping. The concentration of the spent acid depends on the number of drying stages and the further potential use or method of disposal. In some cases, the acid is reconcentrated to 96 wt-% by heating it under vacuum and is subsequently recirculated. Sometimes the acid is sold or used in waste water treatment, otherwise it becomes waste [ 3, Euro Chlor 2011 ], [ 54, Euro Chlor 2010 ]. Dry chlorine leaving the top of the drying tower passes through high efficiency demisters to prevent the entrainment of sulphuric acid droplets. The spent acid usually becomes a waste product or requires reprocessing if it is reused. For example, it has to be dechlorinated by air blowing and may be reconcentrated before being sold or used for effluent treatment. WORKING DRAFT IN PROGRESS 2.6.6 Cleaning of dry chlorine When leaving the top of the drying tower, dry chlorine passes through high efficiency demisters or a packed bed to prevent the entrainment of sulphuric acid droplets. TB/EIPPCB/CAK_Draft_1 December 2011 49
- Page 13 and 14: List of Figures Figure 1.1: Share p
- Page 15 and 16: SCOPE WORKING DRAFT IN PROGRESS Sco
- Page 17 and 18: 1 GENERAL INFORMATION 1.1 Industria
- Page 19 and 20: Chlorine production in Mt/yr 12 11
- Page 21 and 22: Chapter 1 Figure 1.4 shows the annu
- Page 23 and 24: Share of total capacity in % 70 70%
- Page 25 and 26: 1.4 Chlor-alkali products and their
- Page 27 and 28: Total consumption: 9 801 kt Miscell
- Page 29 and 30: 1.4.5 Consumption of hydrogen Chapt
- Page 31 and 32: Chapter 1 and hazardous waste incin
- Page 33 and 34: 2 APPLIED PROCESSES AND TECHNIQUES
- Page 35 and 36: Chapter 2 WORKING DRAFT IN PROGRESS
- Page 37 and 38: Chapter 2 The main characteristics
- Page 39 and 40: 2.2 The mercury cell technique proc
- Page 41 and 42: Chapter 2 Characteristics of the ca
- Page 43 and 44: 2.3 The diaphragm cell technique pr
- Page 45 and 46: Source: [ 2, Le Chlore 2002 ] [USEP
- Page 47 and 48: 2.4 The membrane cell technique pro
- Page 49 and 50: Chapter 2 (carcinogenic) [ 76, Regu
- Page 51 and 52: Chapter 2 The membranes used in the
- Page 53 and 54: Table 2.2: Typical configurations o
- Page 55 and 56: 2.5 Brine supply 2.5.1 Sources, qua
- Page 57 and 58: Chapter 2 centrifuges before dispos
- Page 59 and 60: Source: [ 29, Asahi Glass 1998 ] (p
- Page 61 and 62: Impurity Source Upper limit of brin
- Page 63: Chapter 2 No such dechlorination tr
- Page 67 and 68: Chapter 2 composition of the chlori
- Page 69 and 70: 2.6.11 Dealing with impurities 2.6.
- Page 71 and 72: Chapter 2 amount of chlorine, and t
- Page 73 and 74: 2.6.12.2 Chemical reactions Chapter
- Page 75 and 76: 2.7 Caustic processing production,
- Page 77 and 78: Chapter 2 2.8 Hydrogen processing p
- Page 79 and 80: 3 CURRENT PRESENT EMISSION AND CONS
- Page 81 and 82: Chapter 3 Table 3.1: Overview of em
- Page 83 and 84: 3.3 Consumption levels of all cell
- Page 85 and 86: 3.3.3 Ancillary materials Ancillary
- Page 87 and 88: Further materials and/or further us
- Page 89 and 90: Chapter 3 current) and the efficien
- Page 91 and 92: Chapter 3 distance means a higher f
- Page 93 and 94: 3.3.4.3.6 Production of caustic pot
- Page 95 and 96: Chapter 3 hydrogen at low pressure
- Page 97 and 98: 28 kg of hydrogen is produced {Thes
- Page 99 and 100: Chapter 3 depleted brine is recircu
- Page 101 and 102: Chapter 3 Table 3.10: Emissions of
- Page 103 and 104: Chapter 3 When measuring chlorine i
- Page 105 and 106: Chapter 3 Table 3.13: Emissions of
- Page 107 and 108: Chapter 3 Table 3.15: Emissions of
- Page 109 and 110: Chapter 3 concentrations of organic
- Page 111 and 112: Chapter 3 3.4.3 Emissions and waste
- Page 113 and 114: Chapter 3 {Please TWG provide infor
Chapter 2<br />
The cooling water is generally should be free <strong>of</strong> traces <strong>of</strong> ammonium salts to avoid <strong>the</strong><br />
<strong>for</strong>mation <strong>of</strong> nitrogen trichloride. This method has <strong>the</strong> advantage <strong>of</strong> better mass-transfer<br />
characteristics and higher <strong>the</strong>rmal efficienciesy.<br />
Closed-circuit direct cooling <strong>of</strong> chlorine combines <strong>the</strong> advantages <strong>of</strong> <strong>the</strong> two methods. The<br />
chlorine-laden water from <strong>the</strong> cooling tower is cooled in titanium plate coolers and is recycled.<br />
The surplus condensate is treated exactly like <strong>the</strong> condensate from indirect cooling<br />
[ 1, Ullmann's 2006 ].<br />
2.6.4 Cleaning <strong>of</strong> wet chlorine<br />
Following primary cooling, chlorine gas is demisted <strong>of</strong> water droplets and impurities such as<br />
brine mist impurities. Impurities are removed mechanically by using special filters with glass<br />
wool fillings or porous quartz granules, or by means <strong>of</strong> an electrostatic precipitator. <strong>Chlor</strong>ine is<br />
<strong>the</strong>n passed to <strong>the</strong> drying towers [ 1, Ullmann's 2006 ].<br />
2.6.5 Drying<br />
<strong>Chlor</strong>ine from <strong>the</strong> cooling system is more or less saturated with water vapour. The water content<br />
is typically 1 – 3 vol-%. This must be reduced in order to avoid downstream corrosion and<br />
minimise <strong>the</strong> <strong>for</strong>mation <strong>of</strong> hydrates [ 38, O'Brien and White 1995 ] [Brien-White, 1995].<br />
The drying <strong>of</strong> chlorine is carried out almost exclusively with concentrated sulphuric acid<br />
(96 – 98 wt-%) [Ullmann’s, 1996]. Drying is accomplished in countercurrent sulphuric acid<br />
contact towers in two to six stages, which reduce <strong>the</strong> moisture content to less than<br />
20 mg/m 3 ppm [ 54, Euro <strong>Chlor</strong> 2010 ]. [Stenhammar] The remaining moisture content depends<br />
on <strong>the</strong> temperature and concentration <strong>of</strong> <strong>the</strong> sulphuric acid in <strong>the</strong> last drying stage. For lowtemperature<br />
liquefaction (see Section 2.6.8), a lower moisture content is required, which can be<br />
achieved by adding more equilibrium stages to <strong>the</strong> drying towers or by using molecular sieves<br />
to levels <strong>of</strong> 3 – 9 mg/m 3 [ 3, Euro <strong>Chlor</strong> 2011 ], [ 54, Euro <strong>Chlor</strong> 2010 ].<br />
The number <strong>of</strong> stages is usually increased to lower <strong>the</strong> final strength <strong>of</strong> <strong>the</strong> spent sulphuric acid.<br />
For example, three stages are needed to reach a spent acid concentration <strong>of</strong> 50 – 65 wt-% while<br />
six stages are needed <strong>for</strong> a final concentration <strong>of</strong> 30 – 40 wt-%. The columns contain plastic<br />
packing resistant to chlorine and sulphuric acid to improve fluids distribution, increase<br />
efficiency and lower pressure drops, and thus reduce energy consumption. The heat liberated<br />
during dilution <strong>of</strong> <strong>the</strong> circulating acid is removed by titanium heat exchangers, and <strong>the</strong> spent<br />
acid is dechlorinated chemically or by stripping. The concentration <strong>of</strong> <strong>the</strong> spent acid depends on<br />
<strong>the</strong> number <strong>of</strong> drying stages and <strong>the</strong> fur<strong>the</strong>r potential use or method <strong>of</strong> disposal. In some cases,<br />
<strong>the</strong> acid is reconcentrated to 96 wt-% by heating it under vacuum and is subsequently<br />
recirculated. Sometimes <strong>the</strong> acid is sold or used in waste water treatment, o<strong>the</strong>rwise it becomes<br />
waste [ 3, Euro <strong>Chlor</strong> 2011 ], [ 54, Euro <strong>Chlor</strong> 2010 ].<br />
Dry chlorine leaving <strong>the</strong> top <strong>of</strong> <strong>the</strong> drying tower passes through high efficiency demisters to<br />
prevent <strong>the</strong> entrainment <strong>of</strong> sulphuric acid droplets. The spent acid usually becomes a waste<br />
product or requires reprocessing if it is reused. For example, it has to be dechlorinated by air<br />
blowing and may be reconcentrated be<strong>for</strong>e being sold or used <strong>for</strong> effluent treatment.<br />
WORKING DRAFT IN PROGRESS<br />
2.6.6 Cleaning <strong>of</strong> dry chlorine<br />
When leaving <strong>the</strong> top <strong>of</strong> <strong>the</strong> drying tower, dry chlorine passes through high efficiency demisters<br />
or a packed bed to prevent <strong>the</strong> entrainment <strong>of</strong> sulphuric acid droplets.<br />
TB/EIPPCB/CAK_Draft_1 December 2011 49