The present disclosure relates to a process and to a plant of treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution containing at least 5% by weight of dissolved ammonia and at most 20% by weight of dissolved carbon dioxide and a purified wastewater stream containing at most 1,000 ppm dissolved ammonia.
Ammonia and carbon dioxide containing wastewater streams are generated during a plurality of industrial processes, such as the production of biogas, for instance by anaerobic digestion of agricultural and municipal waste. Such processes gain more and more importance, since biogas is obtainable as valuable product and simultaneously agricultural and municipal waste is reduced at least partially. From anaerobic digestion, large volumes of wastewater are generated containing both ammonia and carbon dioxide. An example of such a wastewater including ammonia and carbon dioxide is filtered fermentation broth or anaerobically digested cattle manure effluent. These wastewater streams need to be appropriately treated, which is, however, challenging, since the respective known processes are energy intensive and require expensive plants. Moreover, the valuable ammonia is not recovered.
For example, it is common practice to treat such wastewater streams by stripping in one step with a dosage of caustic. It is desired that in the initial carbon dioxide stripping step, the lowest amount possible of the ammonia contained in the wastewater stream is lost, i.e. removed from it together with the carbon dioxide. In addition, enough carbon dioxide must be removed in the initial carbon dioxide stripping step in order to reliably avoid precipitation of salts during the later treatment steps, such as the precipitation of ammonium carbonate. In addition, it is desired that the obtained purified water contains the lowest possible concentration of ammonia. The known processes for treating an ammonia and a carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution and a purified wastewater stream, reliably avoiding a salt precipitation during the process and in the produced concentrated aqueous ammonia solution during usual storage temperature, have the drawback of being very energy intensive and requiring complex plants.
In view of this, the object underlying the present disclosure is to provide a plant and a process for treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution and a purified wastewater stream, which reliably avoids a salt precipitation during the process and in the produced concentrated aqueous ammonia solution at usual storage temperature, and which is in particular very energy and capital efficient, i.e. which requires a plant of low complexity and which is characterized by a low operational energy demand.
In accordance with the present disclosure this object is satisfied by providing a process of treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution containing at least 5% by weight of dissolved ammonia and at most 20% by weight of dissolved carbon dioxide and a purified wastewater stream containing at most 1,000 ppm dissolved ammonia, the process comprising:
This solution is based on the surprising finding that performing, before the carbon dioxide removal from the ammonia and carbon dioxide containing wastewater feed stream, a feed split into a first portion of feed being fed into the carbon dioxide degasser column at a position being above at least one bed of one or more random packings, at least one bed of one or more structured packings or at least one tray and into a second portion of feed (optionally admixed with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column) having a higher temperature than the first portion of feed being fed into the carbon dioxide degasser column at a position being below at least one bed of one or more random packings, at least one bed of one or more structured packings or at least one tray into the carbon dioxide degasser column and being separated from the position, at which the first portion of feed is introduced into the carbon dioxide degasser column by at least one bed of one or more random packings, at least one bed of one or more structured packings or at least one tray, wherein the mass flow ratio of the first portion of the wastewater stream to the total wastewater stream fed into the carbon dioxide degasser column is 0.01 to 0.6, allows one to separate in a carbon dioxide degasser column a required amount of carbon dioxide with a very low energy demand and with minimal ammonia loss of less than 1%. The present disclosure is further based on the finding that it is not required to remove all or essentially all of the carbon dioxide during the step of feeding the wastewater stream into the carbon dioxide degasser column, which would be associated with a high loss of ammonia. Instead, it is only necessary to remove a minimum amount of carbon dioxide, which is sufficient to avoid a salt precipitation during the further process steps and in the concentrated aqueous ammonia solution at the desired storage temperature. In other words, the present disclosure allows one to remove in comparably low amounts of carbon dioxide in the step of feeding the wastewater stream into the carbon dioxide degasser column, further decreasing the operational costs of the process in comparison to a complete removal of carbon dioxide. In particular, this is achieved without any need of using inert gas during the carbon dioxide stripping step and/or the ammonia stripping step, which would be connected with a complex plant and increased operational costs, and also without any need of recycling large volumes of process streams from downstream steps to upstream steps, as required in most of the conventional processes. The process in accordance with the present disclosure allows one to efficiently remove ammonia from the ammonia and carbon dioxide containing wastewater stream without the need to adjust any base before or during the ammonia stripping step, thus avoiding a complex pH value control as well as handling and dosage of caustic. Accordingly, the addition of acid and/or base to the feed and/or to the liquid carbon dioxide depleted stream is not at all necessary, which facilitates the process as well as the plant in which the process is performed. This is due to the fact that the liquid carbon dioxide depleted stream being withdrawn from the carbon dioxide degasser column as bottom fraction and being fed into the ammonia stripper column has a pH value of 9.0 or higher, thus having a pH value assuring that all or at least most of the ammonia is present in the liquid carbon dioxide depleted stream in non-dissociated from allowing to get stripped in the ammonia stripper column. As described in further detail below, the present disclosure further allows one to efficiently use heat of process streams generated during the process by heat integration. All in all, the present disclosure provides a plant and a process for treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution and a purified wastewater stream, which reliably avoids a salt precipitation during the process and in the produced concentrated aqueous ammonia solution during usual storage temperature, and which is in particular very energy and capital efficient. i.e. which requires a quite simple plant and which is characterized by a low operational energy demand. Even if the present disclosure allows the removal of comparably low amounts of carbon dioxide when feeding the wastewater stream into the carbon dioxide degasser column, the present disclosure also allows removal of all of the carbon dioxide contained in the wastewater stream and the production of a very pure ammonium hydroxide solution.
The term “dissolved” as used herein means a physical dissolution of a compound as well as a chemical dissolution of a compound. Thus, the term “ammonia being dissolved in aqueous ammonia solution” comprises ammonia molecules being physically dissolved in water as well as ammonium ions and hydroxide ions resulting from the chemical dissolution of ammonia in water. Likewise, the term “carbon dioxide being dissolved in aqueous ammonia solution” comprises carbon dioxide molecules being physically dissolved in water as well as aqueous carbonic acid, i.e. a mixture of carbonate ions, bicarbonate ions, carbamate ions, ammonium ions and hydronium ions resulting from the chemical dissolution of carbon dioxide in water.
In accordance with the present disclosure, a liquid carbon dioxide depleted stream having a pH value of 9.0 or higher is withdrawn as bottom fraction from the carbon dioxide degasser column. This means that in the carbon dioxide degasser column, so much carbon dioxide is removed from the wastewater stream that the resulting liquid carbon dioxide depleted stream has a pH value of 9.0 or higher. For instance, the conditions necessary therefore can be calculated with the statistical model described further below. Thus, even if, as set out above, in the process in accordance with the present disclosure not all or essentially all of the carbon dioxide is removed when feeding the wastewater stream into the carbon dioxide degasser column, but only a minimal amount of carbon dioxide is removed, the removed minimal amount is high enough so as to assure a pH value of 9.0 or higher in the resulting liquid carbon dioxide depleted stream. Preferably, the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column has a pH value of 10.0 or higher. Moreover, it is preferred that the liquid carbon dioxide depleted stream being withdrawn as the bottom fraction from the carbon dioxide degasser column has a pH value of 13.0 or lower, preferably of 12.0 or lower and more preferably of 11.0 or lower. Good results are in particular obtained, when the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column has a pH value of 9.0 to 11.0 and most preferably of 10.0 to 11.0.
As set out above, the present patent application allows one to remove only a minimum of the carbon dioxide from the concentrated aqueous ammonia solution, thus minimizing the energy required for the process and minimizing the requires separation equipment for the plant. Thus, the concentrated aqueous ammonia solution can comprise carbon dioxide to a certain extent. However, it is preferred that the carbon dioxide content of the concentrated aqueous ammonia solution is limited so that the produced concentrated aqueous ammonia solution does not form any precipitate and in particular no ammonium carbonate precipitate, when stored for at least 1 day at a temperature of 10° C.
In accordance with the present disclosure, a liquid carbon dioxide depleted stream having a pH value of 9.0 or higher is withdrawn as bottom fraction from the carbon dioxide degasser column, and the liquid carbon dioxide depleted stream is fed into an ammonia stripper column. This means that the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is fed directly into the ammonia stripper column, i.e. without any further process step between the withdrawal of the liquid carbon dioxide depleted stream as bottom fraction from the carbon dioxide degasser column and the introduction of this liquid carbon dioxide depleted stream into the ammonia stripper column. In particular, no mixing and no phase separation is performed between the withdrawal of the liquid carbon dioxide depleted stream as bottom fraction from the carbon dioxide degasser column and its introduction into the ammonia stripper column.
According to a further particular preferred embodiment of the present disclosure, no inert gas is fed in addition to the gaseous ammonia rich stream and the water into the quencher column. Even more preferably, in the whole process no inert gas is fed into any of the columns, i.e., the carbon dioxide degasser column, the ammonia stripper column and the quencher column. This further reduces the required plant investment costs as well as the operational costs. Inert gas means in this context any gas which does not react with ammonia, such as for instance nitrogen, argon, helium, oxygen, air or coke oven gas.
In a further development of the idea of the present disclosure, it is suggested that no base and/or no acid is added to the wastewater stream or feed, respectively, before or during it is fed into the carbon dioxide degasser column, to the mixture contained in the carbon dioxide degasser column, to the liquid carbon dioxide depleted stream before or during it is fed into the ammonia stripper column or to the mixture contained in the ammonia stripper column. More preferably, in the whole process no base and/or no acid is added to any of the process streams. It is a further surprising finding of the present disclosure that—contrary to the conventional ammonia stripping processes—an adjustment of the pH value of the liquid stream entering the ammonia stripper column and of the mixture contained in the ammonia stripper column is not necessary. This not only facilitates the process, but further reduces the operational costs.
Furthermore, it is preferred that the purified wastewater stream withdrawn from the ammonia stripper column in accordance with the present disclosure is neither completely nor partially recycled to the carbon dioxide degasser column.
In addition, it is preferred that no further stream is fed to the carbon dioxide degasser column in addition to i) the first portion of the wastewater stream and ii) the second portion of the wastewater stream and/or mixture of a second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser.
The present disclosure is not particularly limited concerning the kind of ammonia and carbon dioxide containing wastewater stream. For example, the wastewater stream can be filtered or centrifuged fermentation broth, an anaerobically digested cattle manure effluent or any effluent from a fermenter or from the production of biogas by anaerobic digestion of agricultural or municipal waste. Good results are in particular obtained, when the wastewater stream fed into the carbon dioxide degasser column comprises more than 0.05 to 0.65% by weight of dissolved ammonia, 0.10 to 0.79% by weight of dissolved carbon dioxide and 0 to 1% by weight of organic solids. For instance, the content of organic solids can be more than 0 to 1% by weight, such as 0.10 to 1.00% by weight, 0.20 to 1.00% by weight or 0.50 to 1.00% by weight. The organic solids can be sugar, protein, cell debris, decomposition molecules, biomass or the like. Further optional components of the wastewater can be methanol, ethanol, ethylacetate, acetic acid and salts being different from ammonia or carbonate salts.
In accordance with the present disclosure, i) a first portion of the wastewater stream is fed at a position above the at least one bed of one or more random packings, above the at least one bed of one or more structured packings or above the at least one tray and ii) a second portion of the wastewater stream having a higher temperature than the first portion and/or a mixture of a second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column having a higher temperature than the first portion is fed at a position below at least one bed of one or more random packings, below at least one bed of one or more structured packings or below at least one tray into the carbon dioxide degasser column, wherein the bed of one or more random packings, the bed of one or more structured packings or the tray above which the first portion of the wastewater stream is fed is the same as or located above the bed of one or more random packings, above the bed of one or more structured packings or above the tray below which the second portion of the wastewater stream and/or the mixture of a second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream is fed. This means that the position at which the first portion of the wastewater stream is fed and the position at which the second portion of the wastewater stream is fed into the carbon dioxide degasser column are separated by at least on bed of one or more random packings, one bed of one or more structured packings or one tray. For instance, if the carbon dioxide degasser column comprises five beds of one or more random packings, five beds of one or more structured packings or five trays, the first portion of the wastewater stream can be fed into the carbon dioxide degasser column above any of the first to fourth beds of one or more random packings, first to fourth beds of one or more structured packings or first to fourth trays seen from the top to the bottom of the carbon dioxide degasser column, whereas the second portion of the wastewater stream can be fed at a position being at least one bed of one or more random packings, at least one bed of one or more structured packings or at least one tray below that of the first portion of the wastewater stream.
The present disclosure is not particularly restricted concerning the number of beds comprising one or more random packings, the number of beds comprising one or more structured packings or the number of trays included in the carbon dioxide degasser column. For instance, the carbon dioxide degasser column can comprise one bed of one or more random packings, one bed of one or more structured packings or one tray, wherein the first portion of the wastewater stream is fed above and the second portion of the wastewater stream and/or mixture of the second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream is fed below the bed of one or more random packings, below the bed of one or more structured packings or below the tray into the carbon dioxide degasser column. Suitable examples for structured packings are cross-channel structured packings.
In accordance with an alternative embodiment of the present disclosure, the carbon dioxide degasser column comprises two beds of one or more random packings, two beds of one or more structured packings or two trays on top of each other, wherein the first portion of the wastewater stream is fed at a position above the uppermost and the second portion of the wastewater stream is fed at a position below the lowermost bed of one or more random packings, below the lowermost bed of one or more random packings structured packings or below the lowermost tray into the carbon dioxide degasser column.
In order to further reduce the operational costs of the process of the present disclosure, it is suggested in a further development of the idea of the present disclosure that the second portion of the wastewater stream and/or the mixture of the second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is heated, before being introduced into the carbon dioxide degasser column. As heating medium, one or more of a water rich condensate stream obtained from the gaseous ammonia rich stream withdrawn from the ammonia stripper column by partial condensation, of the purified wastewater stream withdrawn from the ammonia stripper column and of the liquid carbon dioxide depleted stream or a portion of the liquid carbon dioxide depleted stream withdrawn from the carbon dioxide degasser column can be used in the heat exchanger(s). If necessary, external heating medium can be used in addition to or instead of the aforementioned internal process streams. The external heating medium can be for instance steam, hot oil or compressed hot water. For example, i) the second portion of the wastewater stream can be heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein a water rich condensate stream obtained from the gaseous ammonia rich stream withdrawn in step d) by partial condensation is used in the heat exchanger as heating medium, and/or ii) the second portion of the wastewater stream can be heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein the purified wastewater stream withdrawn in step d) is used in the heat exchanger as heating medium, and/or iii) the second portion of the wastewater stream can be heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein the liquid carbon dioxide depleted stream or a portion of the liquid carbon dioxide depleted stream withdrawn in step b) is used in the heat exchanger as heating medium. The heat exchanger(s) can be for instance shell tube heat exchangers or plate and frame heat exchangers.
In accordance with a particular preferred embodiment of the present disclosure, i) the second portion of the wastewater stream is heated in a (first) heat exchanger, before being fed into the carbon dioxide degasser column, wherein a water rich condensate stream obtained from the gaseous ammonia rich stream withdrawn in step d) by partial condensation is used in the (first) heat exchanger as heating medium, and thereafter ii) the second portion of the wastewater stream is heated in a (second) heat exchanger, before being fed into the carbon dioxide degasser column, wherein the purified wastewater stream withdrawn in step d) is used in the (second) heat exchanger as heating medium. Good results are in particular obtained, when in this embodiment downstream of the (second) heat exchanger iii) the second portion of the wastewater stream and/or a mixture of the second portion of the wastewater stream with a portion of the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is heated in a (third) heat exchanger, before being fed into the carbon dioxide degasser column, wherein the liquid carbon dioxide depleted stream or a portion of the liquid carbon dioxide depleted stream withdrawn in step b) is used in the heat exchanger as heating medium. Again, the heat exchanger(s) can be for instance shell tube heat exchangers or plate and frame heat exchangers.
In particular, if more than the internal energy is necessary to heat/evaporate the second portion of the wastewater stream, the second portion of the wastewater stream or a mixture of the second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column can be heated/evaporated, after optionally having been heated in one or more heat exchangers, such as the aforementioned heat exchangers, in an evaporator with an external heating medium, before the heated/evaporated second portion of the wastewater stream or mixture of the second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is fed into the carbon dioxide degasser column. The incorporation of an evaporated stream of the second portion of the wastewater stream or of a mixture of the second portion of the wastewater stream and with a portion of a liquid carbon dioxide depleted stream into the carbon dioxide degasser column has the advantage that the vapor fraction of this stream does not mix with the liquid and thus does not dilute the (liquid) bottom fraction of the carbon dioxide degasser column, but rises as vapor in the carbon dioxide degasser column upwards.
As an alternative, instead of evaporating the second portion of the wastewater stream and/or the mixture of the second portion of the wastewater stream with a portion of a liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column in a heat exchanger, this stream can be supplied as liquid to the sump of the carbon dioxide degasser column and additionally, low pressure stripping steam is supplied to the sump of the same column.
As set out above, the second portion of the wastewater stream can be fed directly, i.e. without addition of any substance, into the carbon dioxide degasser column.
As set out above, however, in a further development of the idea of the present disclosure it is suggested that a portion of the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is mixed with the second portion of the wastewater stream, before the so obtained mixture is fed into the carbon dioxide degasser column. Thereby, due to the additional heat of the admixed liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column, the second portion of the wastewater stream is efficiently heated/evaporated, before being introduced into the liquid carbon dioxide depleted stream.
Good results are in particular obtained, when the first portion of the wastewater stream being fed into the carbon dioxide degasser column has a temperature of 10 to 50° C. and preferably of 30 to 40° C., whereas preferably the second portion of the wastewater stream being fed into the carbon dioxide degasser column has a temperature of 70 to 160° C. and more preferably of 100 to 130° C. at the inlet of the carbon dioxide degasser column.
As set out above, the mass flow ratio of the first portion of the wastewater stream to the total wastewater stream fed into the carbon dioxide degasser column is 0.01 to 0.6. The sum of the first portion of the wastewater stream and of the second portion of the wastewater stream is the total wastewater stream. For instance, the mass flow ratio of the first portion of the wastewater stream to the total wastewater stream fed into the carbon dioxide degasser column is more than 0.1 to 0.6, such as more than 0.1 to 0.5, more than 0.1 to 0.4, more than 0.1 to 0.3 or more than 0.1 to 0.2.
Good results are in particular obtained, when the pressure within the carbon dioxide degasser column during step a) is at least essentially atmospheric, such as between 0.095 and 0.1013 MPa, or atmospheric, i.e. 0.1013 MPa. However, it has been found in the present disclosure that the ammonia loss is minimized in the carbon dioxide degasser column, if the pressure in the carbon dioxide degasser column is above atmospheric pressure. Therefore, it is more preferred that the pressure within the carbon dioxide degasser column during step a) is more than 0.1013 to 0.6 MPa, still more preferably more than 0.1013 to 0.4 MPa, yet more preferably 0.15 to 0.3 MPa and most preferably 0.15 to 0.25 MPa.
The carbon dioxide depletion ratio obtained in the carbon dioxide degasser column during feeding of the wastewater stream into the carbon dioxide degasser column, i.e. the ratio of the carbon dioxide amount removed with the gaseous carbon dioxide rich stream divided by the carbon dioxide amount contained in the ammonia and carbon dioxide containing wastewater stream, is preferably adjusted to be at least 20%, more preferably at least 50% and most preferably at least 70%. Moreover, it is preferred that the ammonia loss in the carbon dioxide degasser column during feeding of the wastewater stream into the carbon dioxide degasser column, i.e. the ratio of the ammonia amount removed with the gaseous carbon dioxide rich stream divided by the ammonia amount contained in the ammonia and carbon dioxide containing wastewater stream, is preferably adjusted to be at most 5% and most preferably at least 1%.
Preferably, the gaseous carbon dioxide rich stream being withdrawn from the carbon dioxide degasser column contains less than 5% by weight, more preferably less than 1% by weight and most preferably less than 0.1% by weight of the ammonia contained in the wastewater stream.
The liquid carbon dioxide depleted stream being withdrawn from the carbon dioxide degasser column preferably contains less than 0.5% by weight of dissolved carbon dioxide and 0 to 2% by weight of dissolved ammonia and has a temperature of 100 to 130° C. It has been found in the present disclosure that the sump temperature of the carbon dioxide degasser column should not exceed 150° C.
In accordance with a further preferred embodiment of the present disclosure, during the feeding of the liquid carbon dioxide depleted stream into the ammonia stripper column, the pressure is adjusted within the ammonia stripper column to be 0.09 to 0.13 MPa and the temperature is adjusted within the ammonia stripper column to be 90 to 120° C.
In accordance with a further preferred embodiment of the present disclosure, the operational parameters in the carbon dioxide degasser column) during feeding of the wastewater stream into the carbon dioxide degasser column can be optimized by the following statistical model. The statistical model allows one to calculate the optimal value of the operation parameters column pressure and feed split ratio related to the CO2-degasser column. The statistical model is in particular reliable for an ammonia and carbon dioxide containing wastewater stream fed into step a) comprising more than 0.05 to 0.65% by weight of dissolved ammonia and 0.10 to 0.79% by weight of dissolved carbon dioxide, wherein the intended storage temperature of the obtained concentrated aqueous ammonia solution is 5 to 30° C., wherein during the storage no precipitate shall form in the concentrated aqueous ammonia solution.
To select the optimal process configuration, decision variables are defined, wherein the decision variables are defined as follows:
wherein the parameters pij, qik and rk are given in the following tables:
and wherein the variables are defined as follows:
The decision for the optimal process configuration is based on the calculation results.
If fb,A≤0, then the optimal process comprises three of the aforementioned heat exchange steps i) to iii), i.e. i) the second portion of the wastewater stream is heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein a water rich condensate stream obtained from the gaseous ammonia rich stream withdrawn in step d) by partial condensation is used in the (first) heat exchanger as heating medium, ii) the second portion of the wastewater stream is heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein the purified wastewater stream withdrawn in step d) is used in the heat exchanger as heating medium and iii) the second portion of the wastewater stream and/or a mixture of the second portion of the wastewater stream with a portion of the liquid carbon dioxide depleted stream being withdrawn as bottom fraction from the carbon dioxide degasser column is heated in a heat exchanger, before being fed into the carbon dioxide degasser column, wherein the liquid carbon dioxide depleted stream or a portion of the liquid carbon dioxide depleted stream withdrawn in step b) is used in the heat exchanger as heating medium. In this case, the feed split ratio and the column pressure have to be calculated with the below equations 2 and 3.
If fb,A>0, then the optimal process comprises two of the aforementioned heat exchange steps i) to iii). In this case, the feed split ratio has to be calculated with the below equation 2 and the column pressure is 101,000 Pa.
The optimal feed split ratio and the optimal column pressure are calculated according to the following equations 2 and 3:
wherein fCS=ff and pcol=fp and the model parameters aijk and bijk are given in the following table:
and wherein the variables are defined as follows:
In order to obtain a high separation efficiency, it is suggested in a further development of the idea of the present disclosure that the ammonia stripper column comprises one or more beds being constituted by one or more random packings, one or more beds being constituted by one or more structured packings or by one or more trays. Particularly good results are obtained, when the ammonia stripper column comprises at least two beds comprising one or more random packings, at least two beds comprising one or more structured packings or at least two trays, wherein the at least two beds or trays are arranged on top of each other, wherein the liquid carbon dioxide depleted stream is fed into the ammonia stripper column at a position between two adjacent beds of one or more random packings, between two adjacent beds of one or more structured packings or between two adjacent trays, and wherein the evaporated liquid purified wastewater stream withdrawn from the ammonia stripper column is fed back into the ammonia stripper column below the at least two beds of one or more random packings, below the at least two beds of one or more structured packings or below the at least two trays. For instance, the ammonia stripper column comprises in the aforementioned embodiment exactly two such beds or trays being arranged on top of each other. As set out further above, it is preferred that no inert gas stream is fed into the ammonia stripper column.
It is preferred that the purified wastewater stream being withdrawn from the ammonia stripper column contains at most 1,000 ppm, more preferably at most 500 ppm, even more preferably at most 250 ppm, yet more preferably at most 150 ppm, still more preferably less than 50 ppm and most preferably less than 10 ppm of dissolved ammonia.
Moreover, it is preferred that the portion of the evaporated purified wastewater stream, which is fed back into the ammonia stripper column, has a temperature of 100 to 120° C.
In accordance with a further particular preferred embodiment of the present disclosure, the gaseous ammonia rich stream, which is withdrawn from the ammonia stripper column, is led through a compressor, which is preferably a multi-stage turbofan compressor, so as to compress and heat the gaseous ammonia rich stream to a temperature of 110 to 130° C., wherein the compressed and heated gaseous ammonia rich stream is then led through a heat exchanger, in which it heats and evaporates the liquid purified wastewater stream to be evaporated when the purified wastewater stream is withdrawn from the ammonia stripper column, whereupon the compressed and heated gaseous ammonia rich stream partially condenses, wherein the condensed portion thereof is separated and led optionally via a heat exchanger back into the ammonia stripper column, whereas the non-condensed portion thereof is fed as gaseous ammonia rich stream into the quencher column. The condensed portion of the heated gaseous ammonia rich stream can be led through a head exchanger for heating the second portion of the of the wastewater stream as described above.
In the aforementioned preferred embodiment, according to which the ammonia stripper column comprises at least two beds comprising one or more random packings, at least two beds comprising one or more structured packings or at least two trays, it is particularly preferred that the condensed portion of the compressed and heated gaseous ammonia rich stream is led back into the ammonia stripper column at a position above the at least two beds of one or more random packings, at least two beds of one or more structured packings or at least two trays.
In view of a good separation efficiency, it is further preferred that the quencher column comprises at least two beds comprising one or more random packings, at least two beds comprising one or more structured packings or at least trays, wherein the at least two beds or trays are arranged on top of each other, wherein the water is fed into the quencher column at a position above the uppermost of the at least two beds of one or more random packings, uppermost of the at least two beds of one or more structured packings or uppermost of the tray and the gaseous ammonia rich stream is fed into the quencher column at a position below the lowermost of the at least two beds of one or more random packings, lowermost of the at least two beds of one or more structured packings or lowermost of the at least two trays.
In a further development of the idea of the present disclosure, it is proposed that a portion of the concentrated aqueous ammonia solution being withdrawn from the bottom of the quencher column is led back into the quencher column and preferably at a position between two adjacent beds of one or more random packings, two adjacent beds of one or more random structured packings or two adjacent trays.
Preferably, the concentrated aqueous ammonia solution being withdrawn from the quencher column contains at least 10% by weight, more preferably at least 15% by weight, still more preferably at least 20% by weight and most preferably at least 25% by weight of dissolved ammonia. The vent gas stream being withdrawn as overhead fraction from the quencher column contains less than 10 ppm ammonia.
In accordance with another aspect, the present disclosure relates to a plant for treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution containing at least 5% by weight of dissolved ammonia and at most 20% by weight of dissolved carbon dioxide and a purified wastewater stream containing at most 1,000 ppm dissolved ammonia, the plant comprising:
“Ammonia stripper column comprising an inlet line directly connected with the bottom outlet line of the carbon dioxide degasser column” means that between the bottom outlet line and the inlet line to the ammonia stripper column, no further device is arranged, such as in particular no mixer and/or no phase separator or settler, respectively. Moreover, no base and/or acid dosing line is combined with any of the bottom outlet line and the inlet line to the ammonia stripper column.
The plant can comprise a (central) feed line, which splits into the first feed inlet line and into the second inlet line for feed or a mixture of feed and a liquid carbon dioxide depleted stream. Alternatively, the (central) feed line splits into the first feed inlet line and into a second feed line, wherein the second feed line leads into the second inlet line for feed or a mixture of feed. In the last mentioned alternative, the second feed line preferably combines with a recycle line for liquid carbon dioxide depleted stream, thus forming the second inlet line for a mixture of feed, wherein the recycle line splits off from the bottom outlet line for liquid carbon dioxide depleted stream of the carbon dioxide degasser column.
The present disclosure is not particularly restricted concerning the number of beds comprising one or more random packings, the number of beds comprising one or more structured packings or the number of trays included in the carbon dioxide degasser column. For instance, the carbon dioxide degasser column can comprise one bed of one or more random packings, one bed of one or more structured packings or one tray, wherein the first portion of the wastewater stream is fed above and the second portion of the wastewater stream is fed below the bed of one or more random packings, the bed of one or more structured packings or the tray into the carbon dioxide degasser column. Suitable examples for structured packings are cross-channel structured packings.
In accordance with an alternative embodiment of the present disclosure, the carbon dioxide degasser column comprises two beds of one or more random packings, two beds of one or more structured packings or two trays on top of each other, wherein the first feed inlet line enters the carbon dioxide degasser column at a position above the upper bed of one or more random packings, above the upper bed of one or more structured packings or above the upper tray and the second inlet line for feed or a mixture of feed and a liquid carbon dioxide depleted stream enters the carbon dioxide degasser column at a position below the lower bed of one or more random packings, below the lower bed of one or more structured packings or below the lower trav.
In a further development of the idea of the present disclosure, it is suggested that the plant further comprises i) a heat exchanger, through which a) the second feed line or second inlet line and b) a condensate line being connected with the overhead outlet line for gaseous ammonia rich stream are led, and/or ii) a heat exchanger, through which c) the second feed line or the second inlet line and d) the bottom outlet line for the purified wastewater stream of the ammonia stripper column are led and/or iii) a heat exchanger, through which e) the second feed line or the second inlet line and f) the bottom outlet line for the liquid carbon dioxide depleted stream of the carbon dioxide degasser column are led.
Preferably, the plant comprises i) a heat exchanger, through which the second feed line and a condensate line being connected with the overhead outlet line for gaseous ammonia rich stream are led, and downstream thereof ii) a heat exchanger, through which the second feed line and the bottom outlet line for the purified wastewater stream of the ammonia stripper column are led.
Good results are in particular obtained, if the plant further comprises downstream of the heat exchanger ii) a iii) heat exchanger, through which the second feed line and the bottom outlet line for the liquid carbon dioxide depleted stream of the carbon dioxide degasser column are led.
The plant can further comprise, optionally downstream of one or more of the aforementioned heat exchangers, an evaporator comprising an inlet and outlet line for external heating medium as well as an inlet and outlet for the second inlet line for feed or a mixture of feed and a liquid carbon dioxide depleted stream.
In accordance with a further particularly preferred embodiment of the present disclosure, the ammonia stripper column comprises at least two beds of one or more random packings, at least two beds of one or more structured packings or at least two trays arranged on top of each other, wherein the inlet line connected with the bottom outlet line of the carbon dioxide degasser column enters the ammonia stripper column at a position between two adjacent beds of one or more random packings, between two adjacent beds of one or more structured packings or between two adjacent trays, and wherein a return line enters the ammonia stripper column at a position below the at least two beds of one or more random packings, below the at least two beds of one or more structured packings or below the at least two trays and optionally another return line enters the ammonia stripper column at a position above the at least two beds of either random packing, structured packing or trays.
The plant can further comprise a compressor, which is preferably a multi-stage turbofan compressor, that is connected with the overhead outlet line for the gaseous ammonia rich stream of the ammonia stripper column and with an outlet line. Downstream of the compressor preferably a heat exchanger is arranged, to which the outlet line of the compressor and the bottom outlet line for a purified wastewater stream of the ammonia stripper column are led, wherein the evaporator is connected with the inlet line of the quencher column.
In a further development of the idea of the present disclosure, it is proposed that the aforementioned evaporator is also connected with a second line, which is preferably the return line to the ammonia stripper column. Preferably, the second line or return line, respectively, is connected with the ammonia stripper column at a position above the at least two beds of random packing and/or structured packing.
In accordance with yet a further particularly preferred embodiment of the present disclosure, the quencher column of the plant comprises at least two beds of one or more random packings, at least two beds of one or more structured packings or at least two trays arranged on top of each other, wherein the inlet line for water enters the quencher column at a position above the uppermost of the at least two beds of one or more random packings, of the at least two beds of one or more structured packings or of the at least two trays and the vapor inlet line being directly or indirectly connected with the overhead outlet line of the ammonia stripper column enters the quencher column at a position below the lowermost of the at least two beds of one or more random packings, of the at least two beds of one or more structured packings or of the at least two trays.
Preferably, the plant further comprises a return line, which is connected with the outlet line for concentrated aqueous ammonia solution of the quencher column and which leads back into the quencher column.
It is further preferred that the return line enters the quencher column at a position between two adjacent beds of one or more random packings, two adjacent beds of one or more structured packings or two adjacent trays.
The disclosure will be explained in more detail hereinafter with reference to the drawings.
The plant 10 for treating an ammonia and carbon dioxide containing wastewater stream to produce a concentrated aqueous ammonia solution containing at least 5% by weight of dissolved ammonia and at most 20% by weight of dissolved carbon dioxide and a purified wastewater stream containing at most 1,000 ppm dissolved ammonia shown in
The ammonia stripper column 14 comprises two beds 38, 38′ of structured packing arranged on top of each other, wherein the inlet line 36 being connected with the bottom outlet line 34 of the carbon dioxide degasser column 12 enters the ammonia stripper column 14 at a position between the two adjacent beds 38, 38′ of structured packing. The ammonia stripper column 14 further comprises an overhead outlet line 40 for gaseous ammonia rich stream, a bottom outlet line 42 for purified wastewater stream and a return line 44 being connected with the bottom outlet line 42 for withdrawing a portion of the purified wastewater stream and returning it into the ammonia stripper column 14. The return line 44 splits from the bottom outlet line 42 and leads through an evaporator (reboiler) 46 and then enters the ammonia stripper column 14 at a position below the lower bed 38′ of structured packing. The bottom outlet line 42 leads through the heat exchanger 28 and then out of the plant 10. The plant 10 further comprises a compressor 48, which is preferably a multi-stage turbofan compressor, which is connected with the overhead outlet line 40 for the gaseous ammonia rich stream of the ammonia stripper column 14 and further with a line 50, which connects the compressor 48 with the evaporator (reboiler) 46. The evaporator (reboiler) 46 has two outlets, one of which being connected to a vapor inlet line 54 of the quencher column 16 and the other one being connected to a condensate return line 56 to the ammonia stripper column 14, which leads through the heat exchanger 26 and which enters the ammonia stripper column 14 at a position above the upper bed 38 of structured packing.
Also, the quencher column 16 comprises two beds 58, 58′ of structured packing arranged on top of each other. Furthermore, the quencher column 16 comprises an inlet line 60 for water, which enters the quencher column 16 at a position above the uppermost of the two beds 58 of structured packing, whereas the inlet line 54 being indirectly connected with the overhead outlet line 40 of the ammonia stripper column 14 enters the quencher column 16 at a position below the lowermost of the two beds 58′ of structured packing. In addition, the quencher column 16 comprises an outlet line 62 for concentrated aqueous ammonia solution leading through heat exchanger 66. Downstream of the heat exchanger 66, line 62 splits into leading back into the quencher column 16 at a position between the two adjacent beds 58, 58′ of structured packing and a line to outside battery limits, in which the product ammonia solution is obtained. Finally, the quencher column 16 comprises an outlet line 68 for withdrawing vent gas from the quencher column 16.
The plant 10 for treating an ammonia and carbon dioxide containing wastewater stream shown in
During the operation of the plants 10 shown in
The second portion of the wastewater stream is fed via the second feed line 25 through heat exchangers 26, 28 in the embodiment of
The liquid carbon dioxide depleted stream is led in the embodiment of
Number | Date | Country | Kind |
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21194125.7 | Aug 2021 | EP | regional |
This application is a U.S. National Stage application of International Application No. PCT/EP2022/073608, filed Aug. 24, 2022, which claims priority to European Application No. 21194125.7, filed Aug. 31, 2021, the contents of which are hereby incorporated by reference.
Filing Document | Filing Date | Country | Kind |
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PCT/EP2022/073608 | 8/24/2022 | WO |