• 专利附录
  • 专利说明
  • 权利要求
  • 类似技术
  • 同族专利
  • 引用文献
  • 法律状态
  • 优先权
    • 专利摘要:
    The invention provides a process and a treatment plant for HTF-contaminated waters, essentially biphenyl and diphenyl oxide, which allows obtaining an effluent with concentrations of both compounds below the discharge limits, said process being applicable on a semi-scale. industrial, this is with high treatment flows, of approximately 2 m3/day, by means of an essentially biological treatment and with a performance of elimination of pollutant in the effluent much lower than the performance of the processes already known, less than 0.10 μg/l. (Machine-translation by Google Translate, not legally binding)
    公开号:ES2766931A1
    申请号:ES201831210
    申请日:2018-12-14
    公开日:2020-06-15
    发明作者:Borst Norbert Nägele；Pollo Cynthia Alcantara；Perez Enrique Hernandez；Herrera Juan Pedro Cristian Romero
    申请人:KEPLER INGENIERIA Y ECOGESTION S L；
    IPC主号:
    专利说明:

    [0003] FIELD AND BACKGROUND OF THE INVENTION
    [0005] The invention is encompassed in the field of industry dedicated to the management of biphenyl and diphenyl oxide pollutants, for example the management of waste derived from the synthesis of plastics, foams and other waste materials from the textile, construction and electronics, as well as in the treatment of pollutants derived from the use of thermal oils in solar thermal power plants.
    [0007] The present invention relates to a process for the microbiological treatment of the biphenyl and diphenyl oxide contaminants that constitute the thermal oil, commonly called HTF (for its acronym in English Heat Transfer Fluid), as well as a treatment plant to carry out said process.
    [0009] Biphenyl and diphenyl oxide, like their polyhalogenated derivatives, are widely used today in many industrial applications, such as the synthesis of plastics, foams or other materials produced in the textile, construction and electronics industries (White -Moreno et al., Isolation of bacterial strains able to degrade biphenyl, diphenyl ether and the heat transfer fluid used in thermo-solar plants, Journal of New Biotechnology, 35 (2017) 35-41).
    [0011] The accumulation of these chemical pollutants can lead to serious health risks and damage to the environment. The eutectic mixture consisting of 26.5% biphenyl and 73.5% diphenyl ether (diphenyl oxide) is currently used as thermal oil or HTF in Solar Thermal Power Plants (CT) to transport the thermal energy accumulated by the solar panels to a heat exchanger, which will allow the energy transported by the thermal fluid to be transmitted to a steam turbine, which generates electrical energy (Vignarooban et al., Heat transfer fluids for concentrating solar power systems - A review, Journal of Applied Energy, 146 (2015) 383-396).
    [0013] This thermal oil or HTF is a pollutant with a low vapor pressure, moderately volatile according to the Henry's constant of both compounds, and has a clear hydrophobicity, with a very low solubility in water and a moderate to strong adsorption in the soil.
    [0015] Accidental spills of HTF, mainly due to leaks in pipes and valves, represent an alteration in the ecosystem that puts both human health and the biota of the soil and groundwater of the affected site at risk. When a discharge occurs in thermal power plants, a significant volume of contaminated water is generated, either by leaching HTF through the soil to the groundwater of an aquifer in the area, or by the water used to channel the discharge to the oil spill storage basin at the plant.
    [0017] Therefore, it is necessary to adequately manage the wastewater generated in thermal power plants that are likely to be contaminated by biphenyl and diphenyl oxide and their degradation products, guaranteeing compliance with the objective values required by the corresponding Hydrographic Confederation before its discharge to rivers or lakes.
    [0019] The present invention allows these contaminants to be eliminated by means of a microbiological treatment process on a semi-industrial scale, essentially based on the purification of these contaminated waters in a biological reactor inoculated with a bacterial consortium capable of degrading biphenyl and diphenyl oxide to concentrations by below the established discharge limit values.
    [0021] In this regard, the article by Raza et al. "Water Recovery in a Concentrated Solar Power Plant” (AIP Conference Proceedings. 1734 (2016) 160014.1-160014.8) describes a system for filtering water through a membrane. This membrane is made of a copper mesh with a micro inorganic nanostructure porous capable of retaining ultra small particles and traces of oil.
    [0022] From the Spanish patent application document P201430655 a process is known for the purification of water contaminated by thermal oil (eutectic mixture of biphenyl and diphenyl oxide) and its recovery, which comprises a cooling phase of the contaminated water to a temperature between freezing point of thermal oil and water, followed by recovery of the frozen thermal oil part by means of mechanical filtration, purifying the rest of the contaminated water in absorption filters and activated carbon adsorption filters.
    [0024] In this context, the authors have verified that the filtered water with the system described by Raza et al. it has amounts of HTF less than 70 ppm. For its part, the application of the process described in document P201430655 results in concentrations of diphenyl and biphenyl oxide (HTF) in the effluent <0.002 ppm, the most unfavorable result being <0.1 ppm. Although this process is more favorable than the one mentioned above, it is associated with high energy consumption.
    [0026] From another perspective, microbiological processes have also been developed for the treatment of waters contaminated with other types of oils.
    [0028] Thus, for example in patent application JP2001198594A, "Method for treating organic waste liquid", a method for treating mineral oil-containing wastewater is described whereby the waste mineral oil, such as the industrial oil contained in the wastewater industrial, it is decomposed in a first treatment tank that includes bacteria Bacillus sp and Pseudomonus genus, optionally Enterobacter and Shingomonas, diluted in water.The treated water thus obtained is then introduced into a second treatment tank similar to the first and, subsequently, the The water obtained is discharged to the exterior In this document no reference is made to the performance of the process regarding the level of removal of the contaminant.
    [0030] Patent application WO200690859 A1, "Method of recycling water-soluble processed liquid, apparatus for recycling water-soluble processed liquid, method of treating oil-containing wastewater and apparatus for treating oil-containing wastewater", describes a first stage of separation by adding a flocculant for the precipitation of mineral oil, which is removed, and a second filtering stage in an activated carbon filter impregnated with a consortium of GRAM negative bacteria (Pseudomonas, Achromobacter, Pasteurella and Bacillus). There are no references in this document to the concentration of the oil in the effluent or of the dissolved oil at the inlet of the activated carbon filter.
    [0032] Patent application JP2005199167A, "Oil-containing wastewater treatment method and apparatus", describes the treatment of wastewater containing oil, grease, kitchen wastewater or n-hexane including a biological contact aeration treatment step with an aerobic filter bed of urethane foam and sedimentation, using Bacillus and Pseudomonas bacteria.
    [0034] In patent application JP2001198594 A, "Method and device for treating waste water containing mineral oil", the bacterial decomposition of a mineral oil in wastewater using Bacillus subtilis and Epistylis bacteria is described.
    [0036] DESCRIPTION OF THE INVENTION
    [0038] The present invention is established and characterized in the independent claims, while the dependent claims describe other features thereof.
    [0040] An object of the invention is to provide a process for treating HTF-contaminated water, consisting of biphenyl and diphenyl oxide, which allows obtaining an effluent with concentrations of both compounds below the discharge limits (less than 0.10 ^ g / l), said process being applicable on a semi-industrial scale, that is, with high treatment flows, of approximately 2 m3 / day, through an essentially biological treatment and with a performance of pollutant removal in the effluent that is much higher than yields of the processes already known. Another object of the invention is a HTF-contaminated water treatment plant according to said process.
    [0042] In this regard, physical methods (cooling) require energy consumption Very high, direct filtration with activated carbon implies early saturation of the coal, therefore large amounts of contaminated activated carbon are generated that need to be managed as waste and centrifugation is not a profitable option because the density of HTF is very similar to that of water, which makes it difficult to remove the pollutant due to differences in densities.
    [0044] BRIEF DESCRIPTION OF THE FIGURES
    [0046] The present specification is complemented with a set of illustrative and non-limiting figures of the invention.
    [0048] Figure 1 graphically shows the bacterial diversity (OTU) in a grouping by taxonomic levels and their relative abundance according to Example 2.
    [0050] Figure 2 shows a schematic view of a HTF-contaminated water treatment plant according to an embodiment of the invention.
    [0052] Figure 3 shows a graph of the HTF removal performance in the biological reactor (gray) and in the filter unit (white) in two years according to example 3.
    [0054] Figure 4 shows a graph of the evolution of the microbiological activity (CFU per ml) in the biological reactor in two years according to Example 4.
    [0056] DETAILED STATEMENT OF THE INVENTION
    [0058] The process of microbiological treatment of biphenyl and diphenyl oxide contaminants from thermal oils or HTF, of the invention comprises the following steps:
    [0060] i) Feeding of HTF-contaminated water, for example from a spill storage basin of a solar thermal power plant, to at least a first storage tank, adding to this a source of nitrogen and phosphorous;
    [0061] ii) Aerobic microbiological treatment of biphenyl and diphenyl oxide degradation of HTF with a bacterial consortium supported by a high porosity floating material in a biological reactor, the bacterial consortium consisting of gram-negative bacteria where at least 50% of said bacteria they belong to the genus Sphingobium, continuously injecting air into the reactor in order to maintain the concentration of dissolved oxygen in water and keeping the temperature in a range between 19 ° C and 30 ° C;
    [0062] iii) Filtration of treated water using activated carbon filters to adsorb traces of contaminant that may remain in the water after its residence time in the biological reactor, as well as to retain possible particles in suspension; and
    [0063] iv) Collection of the treated effluent in cisterns for later discharge.
    [0065] As indicated in step i), the HTF-contaminated water is pumped into at least a first storage tank.
    [0067] In a preferred embodiment, the number of storage tanks is two to ensure a regular flow supply.
    [0069] Since subsequently, in the biological reactor, the microbiological degradation of the biphenyl and of the diphenyl oxide contained in the waters contaminated with HTF will take place through a bacterial consortium, as shown in formula 1, the presence of nutrients is necessary for the Microorganisms can incorporate organic carbon into their cellular material in the form of biphenyl and diphenyl oxide to be removed from the water.
    [0071] HTF + O 2 + Nutrients + Microorganisms ^ CO 2 + H 2 O Formula 1
    [0073] Therefore, a source of nitrogen and phosphate is added to the storage tank (s).
    [0075] Preferably, in the process of the invention a concentrated solution of urea and diammonium phosphate is used as a source of nitrogen and phosphorus in order to maintain a C / N / P ratio between 100/8 / 0.5 and 100/11/1 , 5, preferably 100/10/1.
    [0076] To maintain these C / N / P ratios, the dose of urea and diammonium phosphate (NH 4 ) 2 HPO 4 is added daily to the contaminated water storage unit in order for the elimination of HTF in the reactor via biological assimilation to take place. of the pollutant. In a preferred embodiment, the average concentration of urea and diammonium phosphate in the reactor is kept between 7.8 mg urea / l and 1.7 mg (NH4) 2HPO4 / l, and 3.9 mg urea / l and 0.9 mg ( NH4) 2HPO4 / l, preferably 3.9 mg urea / l and 0.9 mg (NH4) 2HPO4 / l as usual.
    [0078] Thus, in step ii), the bacterial consortium uses essentially biphenyl and diphenyl oxide as a carbon source. In this regard, bacteria of the genus Sphingobium stand out for including species with high potential and versatility to carry out metabolic pathways that include organic compounds of complex structures as carbon and energy sources, for example polycyclic aromatic hydrocarbons (Pinyakong et al., 2003 ; Balkwill et al., 2006; Zhao et al., 2017), hexachlorocyclohexane (Pal et al., 2005), lignin (Abdelaziz et al., 2016) or naphthalene, phenanthrene, biphenyl, diphenyl ether (Kim et al., 2007; Cai et al., 2017) or toluene, in whose initial reactions the enzyme dioxygenase intervenes (Zylstra and Kim, 1997; Pinyakong et al., 2003). The study carried out by Gibson, 1999 (Beijerinchia sp strain B1: a strain by any other name. Journal of Industrial Microbiology and Biotechnology. 23 (1999) 284-293.), Describes the existence of bacterial strains such as Sphingobium yanoikuyae with the ability to use biphenyl as the only carbon source.
    [0080] Preferably for the process of the invention a bacterial consortium from a soil culture contaminated with HTF is used, since in these soils the bacterial strains of Sphingobium (S. herbicidovoran, S. chungtnckensis, S. chlorophenolica or S. chlorophenolicium) are they are found indigenously and in relatively high population densities thanks to the metabolic versatility that allows their survival in such specific and unfavorable conditions.
    [0082] During the process of biological degradation by the bacterial consortium of both biphenyl and diphenyl ether, the following reactions and intermediates involved in the metabolic pathways of both compounds are identified:
    [0084] Aerobic biological degradation of biphenyl
    [0085] In the presence of oxygen, biphenyl is biologically mineralized to CO 2 and water. 2,3-Dihydroxybiphenyl, benzoate and catechol appear as degradation intermediates in the metabolic pathway, according to the following reaction schemes:
    [0089] cr x em o . - enoa or
    [0093] Aerobic biological degradation of diphenyl ether
    [0101] The bacteria involved in the degradation process of biphenyl and diphenyl ether need oxygen to mineralize the contaminants, so in this stage air is continuously injected into the reactor in order to maintain the concentration of dissolved oxygen in water.
    [0102] In a preferred embodiment, the average concentration of dissolved oxygen in the water is maintained between 8.0 and 8.5, preferably 8.3 mg / l, by continuously injecting an air flow of 40 m3 / h into the reactor.
    [0104] In order to increase the specific contact surface between the microorganisms and the contaminant, a high porosity material is incorporated into the reactor as a support on which the biofilm of microorganisms grows. In this way, the bacterial consortium is prevented from leaving the reactor together with the effluent, therefore increasing its residence time in the reactor.
    [0106] In a preferred embodiment, this high porosity floating material is made of granulated polyethylene.
    [0108] Also, in a second aspect, the invention relates to a HTF-contaminated water treatment plant for carrying out the process described above, including the plant:
    [0110] - A storage unit for HTF-contaminated water (1) consisting of at least one storage tank, preferably two storage tanks (2, 3), in each case associated with a feed pump (4) to a biological reactor (5);
    [0111] - A biological reactor (5) containing a high porosity floating material that supports a bacterial consortium of gram-negative bacteria where at least 50% of said bacteria belong to the Sphingobium genus, the reactor including a thermo-resistance (6) and being said reactor (5) associated with an air blower (7) and a corresponding discharge pump (8) from the reactor to a filtration unit (9);
    [0112] - A filter unit (9) consisting of two activated carbon filter elements (10, 11) installed in series and
    [0113] - A collection unit (12) of the treated effluent made up of flexible tanks (13), preferably three flexible tanks of 50 m3, with a total storage capacity of 150 m3.
    [0114] As mentioned previously in relation to the process of the invention, the operating range of the thermo-resistance (6) is between 19 and 30 ° C, preferably it maintains a constant temperature inside the reactor of between 19 ° C and 20 ° C.
    [0116] In this context, biological processes are characterized by being sensitive to changes in the operating conditions to which they are subjected, hence the importance of being able to ensure a steady regime in the reactor to avoid drops in purification performance. If changes are required (for example, variations in flow rate or contaminant load), it should be done gradually.
    [0118] Thus, a fundamental part of the development of the described plant is the control and adjustment of the operating conditions in the biological reactor based on the bacterial populations that carry out the water purification (adjustment of the temperature range, mg of O 2 / l provided by the blower, dosage of nutrients, control of pH variations due to changes in the composition of the inlet water, etc.)
    [0120] The most robust parameters are pH, conductivity and dissolved oxygen, that is, significant changes in the composition of water are necessary to modify the average value maintained during the HTF degradation process, on the contrary, temperature is a more sensitive parameter to changes, so it is necessary to maintain a more exhaustive control of it. To keep the temperature in the reactor constant (especially in winter, when the water entering the storage unit is around 5 ° C), the thermo-resistance (6) is turned on when the temperature of the water fed to the reactor drops by below a reference temperature of 19 ° C. Also, the plant stops automatically if the temperature in the reactor exceeds 30 ° C, at which time cold water is fed into the reactor.
    [0122] In a preferred embodiment, the air blower (7) maintains an average concentration of dissolved oxygen in water in the reactor (5) of 8-8.5 mg / l, preferably 8.3 mg / l, by injection into continuous air flow of 40 m3 / h.
    [0123] Examples
    [0125] Example 1
    [0127] A process and a corresponding treatment plant were designed for the treatment of HTF-contaminated waters as described above and the removal performance of the contaminant was evaluated in comparison with two already known processes, the one described in patent P201430655 and the one developed by Raza et al. "Water Recovery in a Concentrated Solar Power Plant” (AIP Conference Proceedings. 1734 (2016) 160014.1-160014.8) with a membrane filtration system (see above ). The results are shown in Table 1 below:
    [0128] Table 1
    [0129] HTF concentration in the treated effluent in each of the techniques
    [0134] As can be seen from these data, the process of the invention has the highest removal performance of HTF from water, obtaining a concentration of pollutant in the effluent 20 times lower than the technology by cooling the P201430655 and 700,000 times lower than the technology published by Raza et al.
    [0136] Example 2
    [0138] Both the contaminated water fed to the reactor and the water leaving the reactor to the filter unit were periodically analyzed to check that the concentration of the nutrients present in the wastewater itself is sufficient to allow the degradation of HTF via biotic assimilation of the contaminant .
    [0140] In this context, the microorganisms mainly need nitrogen and phosphorus to be able to incorporate the contaminant into their cellular material as a carbon source to form new cells.
    [0141] To avoid changes in the ambient temperature that could affect the microbiological degradation performance of the contaminant, the culture was kept at an average temperature of 22.0 ± 3.0 ° C.
    [0143] During two years of treatment, in order to maximize the removal performance in the biological reactor, the operating conditions and the specificity of the microbiological culture were adjusted.
    [0145] Table 2 below shows the average values maintained during the two years of operation that allow obtaining a concentration of HTF (biphenyl plus diphenyl oxide) in the treated water below the established discharge limits (biphenyl <10 ^ g / l; diphenyl oxide <10 ^ g / l).
    [0147] Table 2
    [0152] As part of the development of microbiological treatment of HTF-contaminated water, a bacterial consortium was initially grown on a laboratory scale obtained from a sample of HTF-contaminated soil. This native inoculum was maintained in the laboratory in a mineral medium enriched with nutrients and repeatedly fed with HTF. Thus, a consortium with a high avidity for the pollutant was obtained. As the cell density of the culture increased, it was transferred to a larger reactor until finally 3 m3 of inoculum were cultivated, with which the biological reactor was initially started in the treatment plant.
    [0154] Likewise, the bacterial diversity in the biological reactor was analyzed using the DNA metabarcoding technique, with the aim of identifying those dominant genera that offer greater resistance to changes in operating conditions and, therefore, contribute to a greater degree to offer higher HTF removal performance in the reactor.
    [0155] This technique is based on the identification of the families, genera and / or bacterial species present in the biological reactor through the sequencing of the 16S rRNA gene using new generation massive sequencing techniques. DNA metabarcoding analysis of the water sample generated a total of 17,644 sequences from the 16S genomic region. The identical 16S sequences (100% similarity) identified in the biological reactor water sample were grouped into Operational Taxonomic Units (OTU), obtaining a total of 63 OTUs belonging to 9 classes, 20 families and, at least, 24 genders different. These sequences were compared with the reference databases for their taxonomic allocation. In cases where it is not possible to reach the species level, the taxonomic allocation algorithm performs the allocation to a higher taxonomic level (genus or family). For most OTUs the species or even the genus could not be identified as they do not belong to formally described bacteria. In these cases, the assigned taxonomic information was "non-cultivable bacteria" or "metagenome". Figure 1 graphically depicts OTU diversity, grouped by taxonomic levels, and their relative abundance in the sample using the Krona package (Ondov 2011, Bioinformatics 12: 385).
    [0157] The results confirm that the dominant genus in the bacterial consortium used to carry out the degradation of HTF in the biological reactor according to the process of the invention is that of the Sphingobium bacterium, with an abundance of 55%.
    [0159] Example 3
    [0161] With the objective of evaluating the purification performance of the treatment plant of the invention, from its start-up an analytical monitoring was carried out biweekly for 24 months of operation to characterize the composition of the contaminated water in the following points of the process:
    [0162] • Sample taken in the storage tanks of the water contaminated with HTF;
    [0163] • Sample taken at the exit of the biological reactor;
    [0164] • Sample taken at the exit of the filtration unit;
    [0165] • Sample taken from the collection unit.
    [0167] HTF concentration in contaminated water
    [0169] During two years of operation, the average concentration of HTF in the contaminated water charged in the storage unit was 20,012 ± 14,947 Mg / l.
    [0171] The analysis data of the effluent collected in the 3 tanks (13) of 50 m3 capacity arranged in parallel (CF1, CF2, CF3) throughout two years of operation are shown in the following table 3. In bold the values below the laboratory quantification limit. In the specific case of 1 HTF, these values are 100 times lower than the admissible concentration for discharge set by the competent Administration.
    [0173] Table 3
    [0178] In view of the purification yields shown in figure 3, the process / plant of the invention results in an average elimination of HTF of 99.50 ± 0.56% in the biological reactor since January 2017, highlighting the potential of this biotechnology in the purification of waters contaminated with thermal oil.
    [0180] Thus, the average contribution of the biological reactor in the elimination of HTF during two years of operation has been 84.4 ± 22.1%, corresponding therefore to an average percentage of HTF eliminated in the filtration units of only 15 , 6 ± 22.1% (Figure 3).
    [0182] This means that, during 25 months of operation, it has been possible to eliminate 99.98 ± 0.09% of the biphenyl and biphenyl oxide present in the initially contaminated water.
    [0184] Example 4
    [0186] Monitoring of microbiological activity in the biological reactor was also carried out to detect possible inhibitions on the bacterial population during the development of the process. The results obtained are shown in Figure 4. As can be seen from said data, the potential microbiological activity reached a steady state from the first quarter of operation, presenting stable microbiological activity as of January 2017 (when it was maximized operating performance in the reactor).
    [0188] Therefore, the results obtained during two years of operation demonstrate the success of the process and of the treatment plant of the invention to eliminate the presence of biphenyl and diphenyl oxide from HTF-contaminated waters.
    权利要求:
    Claims (7)
    [1]
    1. -Process of microbiological treatment of biphenyl and diphenyl oxide contaminants from thermal oils, which includes the following stages: i) Feeding of contaminated water with thermal oil to at least a first storage tank (2,3), adding to this one a nitrogen and phosphorous source;
    ii) Aerobic microbiological treatment of degradation of biphenyl and diphenyl oxide of thermal oil with a bacterial consortium supported by a high-porosity floating material in a biological reactor (5), the bacterial consortium consisting of gram-negative bacteria where at least 50 % of said bacteria belong to the genus Sphingobium, continuously injecting air into the reactor in order to maintain the concentration of dissolved oxygen in water and keeping the temperature in a range between 19 ° C and 30 ° C;
    iii) Filtration through activated carbon filters (10,11) to adsorb traces of contaminant that may remain in the water after its residence time in the biological reactor (5), as well as to retain possible particles in suspension; and
    iv) Collection of the treated effluent in cisterns (13) for subsequent discharge.
    [2]
    2. - Process of microbiological treatment of biphenyl and diphenyl oxide contaminants according to claim 1, where, as a source of nitrogen and phosphorus, a concentrated solution of urea and diammonium phosphate is used.
    [3]
    3.-Process of microbiological treatment of biphenyl and diphenyl oxide pollutants according to claim 1, where the average concentration of dissolved oxygen in the water is maintained between 8.0 and 8.5 mg / l by continuous injection of a flow rate of air of 40 m3 / h in the reactor.
    [4]
    4. -Process of microbiological treatment of biphenyl and diphenyl oxide pollutants according to claim 3, where the average concentration of dissolved oxygen in the water is kept at 8.3 mg / l.
    [5]
    5.-HTF-contaminated water treatment plant for carrying out the process according to the preceding claims, including the plant:
    • A storage unit for HTF-contaminated water (1) consisting of at least one storage tank, preferably two storage tanks (2, 3), in each case associated with a feed pump (4) to a biological reactor (5);
    • A biological reactor (5) containing a high porosity floating material that supports a bacterial consortium of gram-negative bacteria where at least 50% of said bacteria belong to the Sphingobium genus, the reactor including a thermo-resistance (6) and being said reactor (5) associated with an air blower (7) and a corresponding discharge pump (8) from the reactor to a filtration unit (9);
    • A filter unit (9) consisting of two activated carbon filter elements (10, 11) installed in series and
    • A collection unit (12) of the treated effluent consisting of flexible tanks (13).
    [6]
    6.-HTF-contaminated water treatment plant according to claim 5, where the thermo-resistance (6) has an operating range between 19 and 30 ° C, preferably it maintains a constant temperature within the reactor of between 19 ° C and 20 ° C.
    [7]
    7.-HTF-contaminated water treatment plant according to claim 5, where the air blower (7) maintains an average concentration of oxygen dissolved in water in the reactor (5) of 8-8.5 mg / l, preferably 8.3 mg / l, by continuously injecting an air flow of 40 m3 / h.
    类似技术:
    公开号 | 公开日 | 专利标题
    Haugen et al.2002|A novel in situ technology for the treatment of nitrate contaminated groundwater
    Wang et al.2009|Denitrification of nitrate contaminated groundwater with a fiber-based biofilm reactor
    Zhang et al.2009|Autohydrogenotrophic denitrification of drinking water using a polyvinyl chloride hollow fiber membrane biofilm reactor
    TWI594957B|2017-08-11|Method of removing recalcitrant organic pollutants
    US20120145628A1|2012-06-14|Phytoremediation for desalinated water post-processing
    Wirasnita et al.2018|Effect of activated carbon on removal of four phenolic endocrine-disrupting compounds, bisphenol A, bisphenol F, bisphenol S, and 4-tert-butylphenol in constructed wetlands
    Zhang et al.2015|Nitrogen removal processes in deep subsurface wastewater infiltration systems
    Liu et al.2014|Advanced treatment of refractory organic pollutants in petrochemical industrial wastewater by bioactive enhanced ponds and wetland system
    Ha et al.2016|Degradation of the long-resistant pharmaceutical compounds carbamazepine and diatrizoate using mixed microbial culture
    Jiang et al.2019|Using nano-attapulgite clay compounded hydrophilic urethane foams | as biofilm support enhances oil-refinery wastewater treatment in a biofilm membrane bioreactor
    Xie et al.2017|The water treatment and recycling in 105-day bioregenerative life support experiment in the Lunar Palace 1
    Zhou et al.2016|Enhanced stable long-term operation of biotrickling filters treating VOCs by low-dose ozonation and its affecting mechanism on biofilm
    Kwon et al.2016|Simultaneous biodegradation of carbon tetrachloride and trichloroethylene in a coupled anaerobic/aerobic biobarrier
    Al-Baldawi2018|Removal of 1, 2-Dichloroethane from real industrial wastewater using a sub-surface batch system with Typha angustifolia L
    JP4288198B2|2009-07-01|Purification method for contaminated soil
    Liang et al.2021|Application of a heavy metal-resistant Achromobacter sp. for the simultaneous immobilization of cadmium and degradation of sulfamethoxazole from wastewater
    ES2766931B2|2021-05-28|PROCESS AND PLANT OF MICROBIOLOGICAL TREATMENT OF BIPHENYL AND DIPHENYL OXIDE POLLUTANTS FROM THERMAL OILS
    JP2004130184A|2004-04-30|Method and apparatus for decontaminating soil
    Mehdizadeh et al.2011|Biological treatment of toluene contaminated wastewater by Alcaligenese faecalis in an extractive membrane bioreactor; experiments and modeling
    KR20040106910A|2004-12-20|Remediation method of contaminated soil and groundwater by the sequentially combined treatment of hydrogen peroxide, ultraviolet ray and biological treatment
    US7311743B2|2007-12-25|Biofiltration apparatus and method for reducing methyl bromide concentration in a volume of gas
    Gupta et al.2019|Treatment and recycling of wastewater from pharmaceutical industry
    Yu et al.2006|Removal of dichloromethane from waste gases by a biotrickling filter
    Rezaee et al.2012|Denitrification of high salinity, high nitrate wastewater using clinoptilite in a packed bed bioreactor
    KR100661815B1|2006-12-27|The sewage treatment system
    同族专利:
    公开号 | 公开日
    ES2766931B2|2021-05-28|
    引用文献:
    公开号 | 申请日 | 公开日 | 申请人 | 专利标题
    US4755296A|1985-03-21|1988-07-05|Occidental Chemical Corporation|Integrated biological-adsorption process for treating waste water|
    WO1991011396A1|1990-01-23|1991-08-08|Kaldnes Miljøteknologi A/S|Method and reactor for purification of water|
    WO2014036732A1|2012-09-10|2014-03-13|General Electric Company|Method of reducing residual recalcitrant organic pollutants|
    ES2550396A1|2014-05-06|2015-11-06|Pgma, S.L.P.|Process and equipment for water treatment contaminated by thermal oil and recovery thereof |
    法律状态:
    2020-06-15| BA2A| Patent application published|Ref document number: 2766931 Country of ref document: ES Kind code of ref document: A1 Effective date: 20200615 |
    2021-05-28| FG2A| Definitive protection|Ref document number: 2766931 Country of ref document: ES Kind code of ref document: B2 Effective date: 20210528 |
    优先权:
    申请号 | 申请日 | 专利标题
    ES201831210A|ES2766931B2|2018-12-14|2018-12-14|PROCESS AND PLANT OF MICROBIOLOGICAL TREATMENT OF BIPHENYL AND DIPHENYL OXIDE POLLUTANTS FROM THERMAL OILS|ES201831210A| ES2766931B2|2018-12-14|2018-12-14|PROCESS AND PLANT OF MICROBIOLOGICAL TREATMENT OF BIPHENYL AND DIPHENYL OXIDE POLLUTANTS FROM THERMAL OILS|
    [返回顶部]