Classifications

• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/30—Aerobic and anaerobic processes
  • C02F3/302—Nitrification and denitrification treatment
  • C02F3/307—Nitrification and denitrification treatment characterised by direct conversion of nitrite to molecular nitrogen, e.g. by using the Anammox process
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/02—Aerobic processes
  • C02F3/10—Packings; Fillings; Grids
  • C02F3/104—Granular carriers
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
  • C02F3/341—Consortia of bacteria
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F2209/00—Controlling or monitoring parameters in water treatment
  • C02F2209/001—Upstream control, i.e. monitoring for predictive control
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F2209/00—Controlling or monitoring parameters in water treatment
  • C02F2209/003—Downstream control, i.e. outlet monitoring, e.g. to check the treating agents, such as halogens or ozone, leaving the process
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F2209/00—Controlling or monitoring parameters in water treatment
  • C02F2209/14—NH3-N
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F2209/00—Controlling or monitoring parameters in water treatment
  • C02F2209/16—Total nitrogen (tkN-N)
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F2301/00—General aspects of water treatment
  • C02F2301/04—Flow arrangements
  • C02F2301/043—Treatment of partial or bypass streams
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/006—Regulation methods for biological treatment
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/02—Aerobic processes
  • C02F3/06—Aerobic processes using submerged filters
• • C—CHEMISTRY; METALLURGY
  • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
  • C02F3/00—Biological treatment of water, waste water, or sewage
  • C02F3/02—Aerobic processes
  • C02F3/08—Aerobic processes using moving contact bodies
  • C02F3/085—Fluidized beds
  • C02F3/087—Floating beds with contact bodies having a lower density than water
• • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
  • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
  • Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
  • Y02W10/00—Technologies for wastewater treatment
  • Y02W10/10—Biological treatment of water, waste water, or sewage

Definitions

• TITLE Aerated biological filtration process for water treatment in order to reduce the nitrogen content (NGL) with reduction of carbon source and aeration needs
• the present invention belongs to the technical field of the biological treatment of water, in particular waste water, in particular municipal and industrial waste water. More particularly, the present invention relates to a process for the biological treatment of nitrogen-laden water in which part of the water to be treated is used to adjust the stoichiometry of the Anammox reaction, before it enters the reactor in which this reaction takes place.
• Biological wastewater treatment processes are commonly implemented in order to reduce the nitrogen pollution content.
• the nitrification-denitrification process is based on the implementation of an aerated phase and an anoxic phase, either within the same reactor, or each carried out in a separate reactor.
• the supply of oxygen during the aerated phase promotes the development of an autotrophic nitrifying bacterial biomass, composed of AOB bacteria (“ammonia oxidizing bacteria”) capable of transforming ammoniacal nitrogen (NhV) into nitrites (NO 2 ) and bacteria of the NOB type (“nitrite oxidizing bacteria”) capable of transforming nitrites into nitrates (NO 3 ).
• AOB bacteria ammonia oxidizing bacteria
• NO 2 nitrite oxidizing bacteria
• the anoxic phase in the absence of aeration, favors the development of a denitrifying biomass capable of reducing nitrates to nitrites, then to molecular gaseous nitrogen (dinitrogen, N 2 ), thanks to the organic carbon contained in wastewater or coming from an external source of organic carbon such as methanol.
• N 2 molecular gaseous nitrogen
• nitritation process also called “nitrate shunt”, in which the operating conditions are modulated in such a way as to favor the development of the AOB biomass to the detriment of the NOB bacteria.
• This process makes it possible to reduce the oxygen consumption compared to the nitrification-denitrification process.
• Anammox for ANaerobic AMMonia OXidation
• Anammox bacteria are autotrophic, and able to transform nitrites and ammoniacal nitrogen into gaseous nitrogen (N2) and a small amount of nitrates (about 11%), without the need to add an organic carbon source. in the reactor. This process therefore makes it possible to reduce the contribution of organic carbon and consequently the costs of water treatment.
• US2018257966A1 discloses a waste water treatment which includes a biological filtration tank, a nitritation tank and an anammox tank.
• the Biological Filtration Tank performs biological filtration as a pre-treatment process to incoming wastewater and removes solids and organics.
• the nitritation tank performs a nitritation process with respect to the wastewater from the biological filtration tank and provides an electron acceptor needed to remove organic matter in the biological filtration tank by returning part of the wastewater to the biological filtration tank.
• the anammox tank carries out an anaerobic process of ammonium oxidation of the filtered waste water, coming from the biological filtration tank and the nitritation tank. Under real conditions, however, the nitritation tank cannot only produce nitrites and also produces nitrates. Since these nitrates are not treated in the following stages, the water will still contain nitrates at the end of the treatment process.
• Electron donors in particular exogenous carbon sources, are added to a reactor containing heterotrophic biomass and Anammox bacteria, dedicated to the deammonification.
• the quantities of electron donor supplied are modulated according to the quantity of oxidized nitrogen measured at the outlet of this reactor.
• An object of the invention is to provide a process for treating nitrogen-laden water by virtue of which the consumption of oxygen and/or carbon source is further reduced compared with the solutions known in the state of the art.
• Another objective is to propose a method for treating nitrogen-laden water in which the optimization of the deammonification conditions is carried out without delay.
• the object of the invention is therefore to propose a method for treating nitrogen-laden water which is more economical and at least as effective as the methods known from the state of the art.
• the invention proposes a process for the biological filtration of water loaded with nitrogenous pollutants with a view to reducing the overall nitrogen content (NGL) which requires little or no supply of an exogenous carbon source.
• NNL overall nitrogen content
• the method according to the invention allows to optimize the deammonification processes independently of the ammoniacal or oxidized nitrogen values measured at the end of the process according to the invention.
• the process according to the invention comprises a first stage of nitritation and filtration, and a second stage of deammonification, denitrification and filtration.
• the first stage of nitritation and filtration consists in passing water to be treated through a first aerated biological reactor having a bed of filtering support and containing an autotrophic biomass mainly composed of AOB bacteria, thanks to which part of the nitrogen ammoniacal (NhV) contained in said water to be treated is transformed into nitrites (NO 2 ).
• This first stage makes it possible to obtain filtered water rich in nitrites and low in nitrates (NO 3 ) at the outlet of the first reactor.
• the second stage of deammonification, denitrification and filtration consists in passing, according to an upward flow, the water rich in nitrites and poor in nitrates coming from the first reactor into a second non-aerated biological reactor.
• This non-aerated biological reactor has a first stage containing mobile supports receiving a bacterial biomass composed mainly of Anammox bacteria and heterotrophic bacteria, and a second stage containing a bed of a filtering support.
• the nitrites coming from the first reactor and the nitrites produced by the heterotrophic bacteria are transformed mainly into molecular nitrogen and a small quantity of nitrates by the Anammox bacteria (deammonification) .
• the nitrates coming from the first reactor and the small quantity of nitrates produced by the Anammox bacteria are transformed into nitrites by the heterotrophic bacteria (denitrification).
• the water coming from the first stage is again filtered in the second stage.
• the method according to the invention also comprises a step consisting in evaluating the ratio of the nitrite content to the ammoniacal nitrogen content of the water as it leaves said first reactor.
• the method according to the invention further comprises, when the ratio of the nitrite content to the ammoniacal nitrogen content of the water leaving said first reactor is greater than a predetermined stoichiometry value, a step of adding water to be treated to the water coming from the first reactor so as to obtain, at the inlet of the second reactor, a mixture having a ratio of its nitrite and ammoniacal nitrogen contents approximating the stoichiometric ratio of the Anammox reaction.
• the process according to the invention is implemented with a reduced or even zero exogenous supply of carbon source.
• the method according to the invention makes it possible to create conditions favorable to heterotrophic bacterial activity without requiring an exogenous supply of carbon, or by requiring only a reduced supply as much as possible.
• the method according to the invention is therefore more economical and at least as effective as the methods known from the state of the art.
• the predetermined stoichiometry value is between 1 and 2.5, preferably between 1.1 and 2, more preferably between 1.2 and 1.5.
• the supply of ammoniacal nitrogen from the water to be treated is operated as soon as the stoichiometric value deviates from the stoichiometric ratio of the Anammox reaction due to an imbalance in favor of the nitrites.
• the predetermined stoichiometry value makes it possible to tolerate a variation in the ammoniacal nitrogen content which would remain acceptable for the good activity of the Anammox bacteria, and would not harm the good performance of deammonification in the second reactor.
• the nitrite content of the water at its outlet from said first reactor is measured using a probe placed at the outlet of the first reactor.
• the ammoniacal nitrogen content of the water at its outlet from said first reactor is measured using a probe placed at the outlet of the first reactor.
• These probes being placed at the outlet of the first reactor, they allow a rapid evaluation of the contents of nitrogenous products in the water intended to enter the second reactor.
• the information that these probes provide will allow you to quickly, that is to say almost instantaneously, make the decision to add water to be treated to rebalance the nitrite content on the ammoniacal nitrogen content in the water. which will enter the second reactor.
• the method according to the invention further comprises measuring the ammoniacal nitrogen content of the water to be treated, using a probe located upstream of the first reactor.
• Such a probe also allows rapid reading of the ammonia nitrogen contents in the water to be treated and makes it possible to better adjust the quantity of water to be treated to be added to the water coming from the first reactor.
• the autotrophic biomass from the first reactor is attached to the filter medium.
• the first reactor comprises a first stage containing movable supports and a second stage containing a bed of a filter medium.
• nitrification mainly takes place in the first stage.
• autotrophic biomass will also grow on the filter media of the second stage and nitrification may continue in the second stage.
• the filter media of the second stage allow the filtration of the water in the first reactor, whether the bacterial biomass has developed on their surface or not. This This solution is advantageous because it further improves the efficiency of the nitrification and can be implemented easily in existing installations, which would comprise two reactors with two stages in series.
• the filter medium of the first reactor and/or of the second reactor is a fixed bed of particles with a particle size between 2 and 6 mm and a bulk density between 15 and 100 kg/m 3 .
• Such a particle size makes it possible to store the biomass and retain the particulate pollution. It is then possible to effectively filter the particles in suspension as well as the associated particulate organic matter present in the water to be treated during its passage through the first reactor, as well as in the water contained in the second reactor when water to be treated was added to the water from the first reactor.
• carrier particles fixed bed
• Such carrier particles have a lower density than water. Thus, by flotation, they position themselves spontaneously in the upper part of the reactors, which also allows them to be cleaned by gravity washing.
• the particles of the support are made of polystyrene.
• This material is advantageous because it is economical and resistant.
• the mobile supports of the second reactor and/or, where applicable, of the first reactor have a density of between 900 and 1200 kg/m 3 , preferably between 920 and 980 kg/m 3 , and comprise a surface protected from collision with the surface of other mobile supports.
• Such supports allow the biomass of Anammox bacteria and the biomass of heterotrophic bacteria to grow despite the movements caused by the upward flow of water rich in nitrites and poor in nitrates. Such movements can in fact cause collisions between the supports, which would detach part of the biomass located outside the surface protected from collisions.
• the water to be treated passes through a decanter, prior to the supply of this water to the first reactor.
• This embodiment makes it possible to remove some of the particles in suspension and of the associated particulate organic matter contained in the water to be treated, which may sediment in the bottom of the settling tank.
• the term “Anammox reaction” means the deammonification reaction according to which the nitrites are transformed by the Anammox bacteria, in the presence of ammoniacal nitrogen, into gaseous nitrogen and into a small quantity of nitrates. Based on material balances (Strous et al. 1999), the detailed stoichiometry of this reaction can be written as follows:
• the term "stoichiometric ratio of the Anammox reaction” means the molar ratio of the nitrite content to the ammoniacal nitrogen content which, in accordance with equation 1 above, is approximately 1.3. This ratio also corresponds to the mass ratio of nitrite nitrogen to ammoniacal nitrogen (1.3 mg N—N0 2 /1 mg N—NH4).
• the term "stoichiometry value”, unless explicitly mentioned, is the molar ratio of the nitrite content to the ammoniacal nitrogen content.
• the process according to the invention makes it possible to supply ammoniacal nitrogen to the water coming from the first reactor when the stoichiometry value reflects an imbalance in the stoichiometric numbers in favor of the nitrites.
• the “predetermined stoichiometry value” according to the invention corresponds to the highest acceptable stoichiometry value at the inlet of the second reactor. It follows from equation 1 above that the optimal stoichiometry value is about 1.3. Consequently, according to one embodiment, the predetermined stoichiometry value according to the invention is equal to 1.3.
• the predetermined stoichiometry value may however deviate from this value in order to cover acceptable variations in the contents of nitrites and/or ammoniacal nitrogen, without this significantly affecting the activity of the Anammox bacteria present in the second reactor.
• the predetermined stoichiometry value can be between 1 and 2.5, preferably between 1.1 and 2, more preferably between 1.2 and 1.5.
• the predetermined stoichiometry value can be approximately 1, approximately 1.1, approximately 1.2, approximately 1.3, approximately 1.4, approximately 1.5, approximately 1.6, approximately 1.7, approximately 1, 8, about 1.9, about 2.0, about 2.1, about 2.2, about 2.3, about 2.4 or about 2.5.
• exogenous carbon supply means an addition of organic compounds, such as methanol, which do not come directly from the water to be treated but which are generally added thereto to promote the activity of heterotrophic bacteria.
• nitrogenous pollutants means the nitrogen derivatives present in the waste water.
• FIG. 1 represents a diagram of an installation suitable for implementing the method according to the invention.
• FIG. 2 represents a diagram of another installation suitable for implementing the method according to the invention.
• FIG. 3 schematizes the method according to the invention.
• the inventors have demonstrated that it was possible to further improve the methods for treating water loaded with existing nitrogenous pollutants, in particular by making them more economical. Indeed, the inventors have shown, in a clever way, that it was possible to use water loaded with nitrogenous pollutants (water to be treated) to adjust the stoichiometry of nitrites and ammoniacal nitrogen of the Anammox reaction before entering in the reactor in which the Anammox reaction takes place.
• the water loaded with nitrogenous pollutants contains carbon sources which advantageously make it possible to promote the activity of the heterotrophic bacteria responsible for denitrification while limiting the exogenous supply of carbon sources, or even avoiding any exogenous supply of sources. of carbon.
• the oxygen consumption can be reduced by up to 55% and the consumption of an exogenous carbon source can be reduced by up to 100% compared to the methods currently implemented.
• the process according to the invention is a process for the biological filtration of water charged with nitrogenous pollutants with a view to reducing the overall nitrogen content (“NGL” for N GLobal).
• the process according to the invention comprises a first step of nitrification 101 and filtration 102 which takes place in a first aerated biological reactor 10 having a bed of a filter medium 12.
• a reactor can comprise known means for injecting oxygen, in particular air, such as a ramp located in the lower part of the first reactor.
• the water to be treated 100 is brought 100a through a pipe 1 to the inlet 13 of the first reactor 10.
• the water passes through the first reactor 10 according to an upward flow and passes through a filtration and nitrification zone containing an autotrophic biomass mainly composed of AOB bacteria fixed on a bed of a filter medium 12.
• nitrification 101 and filtration 102 take place at the same level in the reactor, and occur simultaneously.
• the water to be treated 100 is led 100a to the inlet of the first reactor 10, in which the stages of nitrification 101 and filtration 102 will be carried out simultaneously, and the pipe 101a from one stage to the another in the first reactor is not necessary.
• the water passes through the first reactor 10 according to an upward flow and passes through a first stage containing mobile supports 11, on which is fixed an autotrophic biomass mainly composed of bacteria AOB able to carry out the nitrification 101.
• the water is then led 101a into the second stage containing the bed of filter medium 12 to allow the filtration 102 of the water.
• Autotrophic biomass can also grow on the filter media bed in this second stage.
• the filtration 102 is accompanied by a nitrification activity.
• the first reactor 10 can contain other autotrophic bacteria such as NOB bacteria.
• the conditions inside the first reactor such as the pH, the aeration, the applied load and/or the temperature, are adapted so as to favor the majority development of the AOB bacteria within the autotrophic biomass, according to techniques known from the state of the art. Maintaining a low level of density of bacteria of the NOB type limits the transformation of nitrites into nitrates, according to the principle of the “nitrate shunt”. Thus, during the first stage, part of the ammoniacal nitrogen contained in the water to be treated is transformed mainly into nitrites by the AOB bacteria.
• the water obtained at the outlet 14 of the first reactor 10, at the end of the first stage is a water rich in nitrites and poor in nitrates.
• the first reactor 10 can also contain a heterotrophic bacterial biomass participating in the reduction of most of the dissolved organic carbon contained in the water to be treated (oxidation of the dissolved organic carbon to CO2).
• autotrophic and heterotrophic bacteria can grow, within the first reactor, on the bed of a filter medium 12 and, if necessary, on the mobile supports 11.
• the fixed bed of filtering particles 12 makes it possible to retain the organic matter and the particles in suspension present in the water during the first step of the method according to the invention.
• the water rich in nitrites and poor in nitrates reaches 102a at the outlet 14 of the first reactor 10.
• the ratio of the nitrite content to the ammoniacal nitrogen content of the water at its outlet 14 of the first reactor 10 is then evaluated at 103.
• the water is led 103a through a pipe 2 to the inlet 23 of the second non-aerated biological reactor 20.
• the second step of de-ammonification, denitrification and filtration of the process according to the invention occurs in the second reactor 20.
• the water at the inlet 23 of the second reactor 20 passes through the second reactor 20 according to an upward flow. It passes through a first stage 21 containing mobile supports accommodating a bacterial biomass composed of Anammox bacteria and heterotrophic bacteria. In this first stage 21, deammonification and denitrification occur together 104 due to the presence of a carbon source.
• the nitrites coming from the first reactor and the nitrites produced by the heterotrophic bacteria are converted mainly into molecular nitrogen and a small quantity of nitrates by the Anammox bacteria (deammonification).
• the nitrates coming from the first reactor and the small quantity of nitrates produced by the Anammox bacteria are transformed into nitrites by the heterotrophic bacteria (denitrification). These nitrites are then used by Anammox bacteria.
• the water leaving the first stage 21 thus mainly contains molecular nitrogen. It then passes 104a through the second stage 22, containing a bed of filter media, and there undergoes a filtration step 105. It should be noted that bacterial biomass can also grow on the filter bed of the second stage, allowing deammonification and denitrification to continue simultaneously with filtration in the second stage.
• the mobile supports of the first and/or of the second reactor have a density of between 900 and 1200 kg/m 3 , preferably between 920 and 980 kg/m 3 , and comprise a surface protected from collision with the surface. other mobile media.
• Such mobile supports are for example the mobile supports described in the patent application published under the number WO2012/136654.
• the filter medium of the first and/or of the second reactor consists of a fixed bed of particles with a particle size between 2 and 6 mm and a bulk density between 15 and 100 kg/m 3 .
• Such particles make it possible to retain particulate pollution.
• their density lower than that of water allows particles to be washed by gravity.
• these particles are made of polystyrene.
• these particles are made of expanded polystyrene.
• the water which leaves 105a the second reactor 20 is a treated water 106.
• This treated water is led from the outlet 24 of the second reactor 20 by a pipe 3.
• This treated water can be brought to a storage zone, a treatment zone additional or distribution area for use.
• the bypass 4 is a pipe which connects the pipe 1 for supplying the water to be treated 100 in the first reactor 10 to the pipe 2 for supplying the water from the first reactor 10 in the second reactor 20.
• the bypass 4 can be equipped with a valve (not shown) to control the entry of the water to be treated at the level of the pipe 1, and/or with a valve (not shown) to control the exit of the water to be treated at the level of the pipe 2.
• the water at the outlet 14 of the first reactor 10 may be different from the water at the inlet 23 of the second reactor 20.
• the conditions in the first reactor 10 are adjusted according to known means to allow the efficient transformation of the ammoniacal nitrogen mainly into nitrites by the biomass. These known means are, for example, aeration and the charge applied with ammoniacal nitrogen in the first reactor 10. Adjustment of the conditions in the first reactor 10 are necessary when the nitrite content of the water becomes too low compared to the ammoniacal nitrogen content, in particular when the ratio of the nitrite content to the ammoniacal nitrogen content becomes significantly lower than a predetermined stoichiometry value.
• the predetermined stoichiometry value can be between 1 and 2.5, preferably between 1.1 and 2, more preferably between 1.2 and 1.5.
• the predetermined stoichiometry value can be about 1, about 1.1, about 1.2, about 1.3, about 1.4, about 1.5, about 1.6, about 1.7, about 1.8, about 1.9, about 2.0, about 2.1, about 2.2, about 2.3, about 2.4 or about 2.5.
• the process according to the invention is implemented with an exogenous supply of carbon source reduced to the maximum or even zero.
• the carbon consumption is significantly reduced thanks to the method of the invention, compared to known methods.
• Another advantageous consequence of the process according to the invention is that the quantity of sludge formed by the exogenous supply of carbon sources is also reduced.
• it may be desirable to provide an exogenous carbon source for example when the water to be treated does not contain enough to allow satisfactory activity of the heterotrophic bacteria.
• the second reactor 20 can advantageously be equipped with a carbon source feed pipe at the level of the first stage 21.
• carbon source means easily biodegradable carbonaceous substrates, such as methanol.
• the evaluation 103 of the ratio of the nitrite content to the ammoniacal nitrogen content is carried out from measured values of the nitrite and nitrate contents.
• This evaluation can be carried out by means of a known calculation apparatus, such as for example a computer-implemented calculation tool.
• a computer can advantageously control the opening and closing of the valve(s) that can equip the bypass 4, when they are present.
• the measurement of the nitrite content can be carried out by any known means.
• the measurement of the nitrite content is carried out by a probe 31.
• the use of a probe 31 is advantageous because it makes it possible to take continuous measurements of the nitrite content in the water.
• Such probes are commercially available, such as for example the “OPUS” nitrite probe marketed by the company Trios.
• the measurement of the ammoniacal nitrogen content can be carried out by any known means.
• the measurement of the ammoniacal nitrogen content is carried out by a probe 32.
• the use of a probe is advantageous because it makes it possible to take continuous measurements of the ammoniacal nitrogen content in the water.
• An example of a probe suitable for measuring the ammoniacal nitrogen content according to the invention is the ammonium analyzer marketed under the brand AMTAX from the company Hach.
• the method according to the invention further comprises measuring the ammoniacal nitrogen content of the water to be treated 100. This measurement can be carried out by any known means. In a particular embodiment, this measurement is carried out using a probe SS located upstream of the first reactor 10, for example on the pipe 1.
• An example of a probe suitable for measuring the ammoniacal nitrogen content according to the invention is the ammonium analyzer marketed under the trademark AMTAX from the company Hach.
• the method according to the invention also comprises measuring the nitrate content in the water leaving the first reactor 10.
• This measurement can be carried out by any known means, in particular by a probe (not shown) placed at the outlet of the first reactor, for example on line 2. This measure allows rapid detection of nitrates, and thus reduces the air supply in the first reactor in order to limit the development of bacterial biomass NOB type.
• the method according to the present invention may comprise a preliminary step consisting in passing the water to be treated through a decanter.
• a water treatment station is fitted out in order to implement the method according to the invention.
• a first aerated biological reactor followed by a second non-aerated biological reactor are installed, connected by a pipe fitted with probes for measuring the content of nitrites and ammoniacal nitrogen.
• the feed pipe for the water to be treated in the first reactor is modified so as to also communicate with a "bypass" pipe.
• the bypass pipe joins the pipe connecting the two reactors together upstream of the inlet to the second reactor.
• the first aerated biological reactor 10 contains an autotrophic biomass mainly composed of AOB bacteria fixed on a filter medium 12. It also contains a heterotrophic biomass to break down dissolved organic carbon.
• the second non-aerated biological reactor 20 has a first stage containing mobile supports 21 accommodating a bacterial biomass composed of Anammox bacteria and heterotrophic bacteria, and a second stage containing a bed of a filtering support 22, on which the bacterial biomass can also be fixed.
• a water loaded with nitrogenous pollutants 100 is brought 100a into the first reactor 10, in which the aeration and nitrogen loading conditions are set so as to promote the nitrification of the ammoniacal nitrogen.
• the water is rich in nitrites and poor in nitrates.
• the nitrite and ammoniacal nitrogen contents of the water leaving the first reactor are measured using probes 31, 32.
• the molar ratio of the nitrite content to the ammoniacal nitrogen content is measured and, when the value of this ratio is greater than 1.7, the water to be treated 100 is injected 103c into the bypass 4.
• the water to be treated is mixed with the water from the first reactor 10, upstream of the inlet 23 of the second reactor 20 , so that the mixture has a ratio of the nitrite content to the ammoniacal nitrogen content approaching the stoichiometric ratio of the Anammox reaction.
• the oxygen consumption and the carbon source consumption are measured, related to the quantity of nitrogen treated, and compared with the values obtained by conventional methods.

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• Engineering & Computer Science (AREA)
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• Biological Treatment Of Waste Water (AREA)

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• 2021
  • 2021-03-25 FR FR2103031A patent/FR3121137B1/fr active Active
• 2022
  • 2022-03-25 KR KR1020237032788A patent/KR20230160831A/ko unknown
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