De Dietrich Process Systems is experienced in designing waste treatment systems that qualitatively meet process requirements for:
- PolyAluminum Chloride (PAC)
- Recovery of high boiling organics from waste water
- Recovery of acetic acid from aqueous waste streams
PolyAluminum Chloride (PAC)
Effective technology for water purification
PolyAluminum Chloride production is one of the most exigent processes for glass-lined equipment due to its high corrosive and abrasive effect. The glass-lined reactor is a critical component of the PAC process.
The PAC synthesis occurs under high pressure and high temperature. PolyAluminium Chloride is the product of the batch reaction between solid Aluminium Hydroxide [AL(OH)3] and liquid Hydrochloric acid (HCI).
DDPS has supplied hundreds of glass-lined reactors for PAC production over the past 30 years, acquiring a thorough understanding of PAC process requirements and characteristics. We have developed specific solutions for the PAC reactor to handle the highly corrosive and abrasive process:
- De Dietrich enamel 3009 HA - Visual signal with a great resistance against acid environment (HCI)
- Visual detection of the corrosion through different colors of enamel layers
- Adapted impeller agitator with a special geometry
Recovery of High Boiling Organics from Waste Water
Destroy or recover?
Industrial waste water often contains high boiling solvents, such as phenol or dichlorobenzene, preventing it from being discharged into a sewage treatment plant without reprocessing and cleaning. Since destruction through burning is a bad alternative for ecological and cost reasons, the preferred way is phenol recovery with simultaneous cleaning of the waste water. Phenol is the example used to describe the method preferred by DDPS. The phenol content, which depends on the process, is normally 2-12%. The low phenol concentrations eliminate separation by distillation, in which the water is evaporated out, due to the high energy requirements. Here, extraction offers the decisive advantage. Methylisobutylketone (MIBK), an extracting agent, removes phenol from the waste water in the extraction column K1. The charged extracting agent is cleaned again in the distillation column K2 and returned to the bottom of the extraction. The phenol accumulates in the bottom of the subsequent rectification (column K2) and can be used again in production.
While the waste water flowing out of the extraction K1 may be free of phenol, it carries along traces of the extracting agent, which are recovered in the stripper K3. The MIBK/water azeotrope accumulates at the head of the column, where it is separated in the separator B1 into the light MIBK phase and the heavy water phase. Since the distillation column K2 is operated without water, indirect heating is planned here, while direct steam can be introduced into the stripper.
Fig. 1: Sieve plate extraction column and distillation column 18 in. diameter column
Fig. 2: Phenol recovery flow sheet
Advantages of this system concept
The planned heat recovery in the waste water stream and the use of dephlegmators make the overall process energetically favorable and appropriate for the ecological requirements applicable today. With phenol content in the waste water of less than 5 ppm, the water can be discharged into the biological sewage treatment plant. The extracting agent circulates and is not consumed to a noticeable extent. The recovered phenol can be used again in the process.
Fig. 3: Head vessel of extraction column
Who needs phenol recovery?
Phenol waste water accumulates in many areas of plastic and resin production and in the production of alkylated phenols. The waste water volumes to be processed range from 0.5 m³/h up to 10 m³/h, whereby the chosen extraction unit depends on the waste water volume and the attendant material. With greater volume streams, extraction is performed continuously in serially connected mixer-settlers, since the technical effort is then more favorable than with the pulsed sieve plate column.
Example of a built system
The system shown in the illustrations processes waste water stream of 4 m³/h. In this case, we have chosen a pulsated sieve plate 16 in. diameter column with 105 plates for the extraction. The 20 in./18 in. diameter distillation column with ordered packing works at a pressure of 0.3 bar abs. The waste water with the phenol removed, lightly overheated via a flash tank, and enters the 18 in. diameter stripper. The scope of supply contained the system with measurement and control devices, vacuum generator, vessels and receivers and the performance run with original product. The special difficulty with every waste water cleaning lies in the attendant materials, whose effects on the main process can be critical. The feed can contain suspended matter, cresols, acetone, formaldehyde or methanol. In the system shown, suspended matter collects in the extraction head and must be continuously fed out. Cresols crystallize at low temperatures so that, when auxiliary heating is lacking and the pipeline layout is unsuitable, a blockage of the system through solids must be feared. The lightly volatile solvent acetone, methanol and formaldehyde, which the waste water also contains, could be removed by means of a preceding stripper. Experience with the built systems has shown that it is precisely the investigation of secondary materials in our test facility that contributes to an optimal system concept.
Recovery of Acetic Acid from Aqueous Waste Streams
Fig. 2: Liquid/vapor equilibrium
Selection of the extraction agent
Fig. 3: Equilibrium diagram of the MTBE/acetic-acid/water system
(information in wt% at 20°C).
Fig. 4: Equilibrium diagram of the ethyl-acetate/acetic-acid/water system
(information in wt% at 20°C).
Table 1: Extraction agents for the separation of acetic acid from effluent
Fig. 5: Flow chart of the classical process
Fig. 6: Flow chart of the QVF process
- approx. 280 kW per 100 kg/h of acetic acid with an acetic-acid concentration of 10 wt%, and
- approx. 260 kW per 100 kg/h of acetic acid with an acetic-acid concentration of 35 wt%.
The following values have been calculated for the QVF process:
- approx. 260 kW per 100 kg/h of acetic acid with an
- acetic-acid concentration of 10 wt%, and
- approx. 180 kW per 100 kg/h of acetic acid with an
- acetic-acid concentration of 35 wt%.
Drawing off accompanying components
Fig. 7: Stripper with the additional draw off for accompanying components