JP2020037098A - Czts adsorbent, czts-based alloy adsorbent, and/or effluent control system using carbon-based adsorbent, and method for use thereof - Google Patents

Abstract

To provide an effluent control system for a gas and a non-gas polluting effluent, which comprises fluidized bed equipment including a reactive adsorbent substance.SOLUTION: A reactive adsorbent substance may be CZTS, CZTS alloy, or carbon-based adsorbent substance. In fluidized bed equipment, one or more closed loop adsorbent recycling sub systems are configured. The adsorbent recycling sub systems separate adsorbents from each other, separate pollution substances from the adsorbent and dispose and/or recycle the pollution substances, and clean and/or reproduce the adsorbent and return the same to the fluidized bed equipment, dispose consumed and worn adsorbent, replace the consumed and worn adsorbent with a new adsorbent, and thus, can maintain consistent adsorbent function in the fluidized bed equipment. A monitoring sensor provides information useful in a method for establishing and maintaining consistent process parameter control.SELECTED DRAWING: None

Description

CROSS-REFERENCE TO RELATED APPLICATIONS This application claims priority to US Provisional Application No. 62 / 029,044 filed July 25, 2014 and US Provisional Application No. 62 / 133,791 filed March 16, 2015. It is a continuation-in-part of U.S. Patent Application No. 15 / 606,704 filed on May 26, 2017, which is a continuation-in-part of U.S. Patent Application No. 14 / 808,563 filed on July 24, 2017. The entire disclosure of the above application is incorporated herein by reference.

  The present disclosure relates generally to industrial emission control systems and methods, and the devices used in such systems, and methods for removing contaminants from gaseous and non-gaseous emissions.

  This section presents background information related to the present disclosure that is not necessarily prior art.

  Industries in many economic sectors emit more than one type of emissions. Such emissions can be divided into two basic groups, one gaseous and the other non-gaseous. Emissions in the gaseous group and those in the non-gaseous group often contain harmful pollutants. The emissions in the gas group may be exhaust gases generated by a coal burning plant or a natural gas burning facility. The effluent in the non-gaseous group may be a liquid, a sludge or a slurry. If the level of harmful contaminants in the effluent reaches and / or exceeds acceptable limits, neutralize, capture, collect, remove, discard, and / or dispose of the contaminants. It must be properly sealed by means.

  Many industries rely on burning fuel as a means to accomplish some aspect of each method. For example, as a first example, steel mills burn and / or melt metals during metal forming, extrusion and other metal casting processes. The methods used within the metal industry include releasing the powder as metal vapor and ionized metal. Harmful pollutants for the environment, plants, animals and / or humans are released into the air via metal vapor. To varying degrees, the harmful contaminants in the metal vapor and / or metal vapor compound must be collected and disposed of properly. As a second example, the mining industry for precious metals such as gold, silver and platinum also produces metals, including heavy metal contaminants, metal vapor emissions, and powders, which are captured, collected, and disposed of properly. If not, it is considered harmful. As a third example, the natural gas burning industry produces emissions that often contain high levels of pollutants, which are considered harmful if trapped, collected, and disposed of properly. As a fourth example, energy producers using coal as a combustible consumable that generates steam in a boiler that rotates a generator may be a metal vapor and metal compound that is considered dangerous to the environment, plants, animals and humans. Produces significant amounts of effluents, including Among other harmful pollutants, metal vapor emissions often contain mercury (Hg).

  Due to global jet flow patterns, airborne metal vapor emissions can be transported from one country and deposited in another. For example, much of the mercury emissions generated in China and / or India may actually deposit in the United States and / or seawater in between. Similarly, many of the United States-generated mercury-containing emissions can actually accumulate in Europe and / or the sea between them. In a manner that completes this cycle, mercury-containing emissions from Europe may actually deposit in China and / or India. Thus, mercury and other harmful pollutants in emissions from industrial processes are a global problem with global significance that requires a global solution.

  National and international regulations, rules, restrictions, fees, surveillance, and many revised and more stringent laws are proposed and / or implemented for those generating such emissions. For example, one of the most harmful and regulated pollutants in metal vapor emissions is mercury. Due to human industrial processes, mercury accumulation and / or mercury deposits are increasing far beyond naturally occurring levels. At a global level, the total amount of mercury released by human activity is estimated to be 1960 metric tons per year. This figure was calculated from data analyzed in 2010. Globally, the largest contributors to this particular type of emissions are coal burning (24%) and gold mining (37%) activities. In the United States, coal combustion accounts for a higher percentage of emissions than gold mining activities.

  A major problem with exposure to mercury for animals and humans is that mercury is a bioaccumulative substance. Thus, any amount of mercury ingested by fish or other animals will remain (ie, accumulate) in the animal and migrate to humans, or to the other animal if the former is ingested by the latter. . In addition, mercury is not excreted from the body of the ingested host. Largest predators in the food chain that feed on the longest lived and / or large amounts of other animals are at increased risk of consuming the most excess mercury accumulation. Humans that eat animals containing mercury, especially fish, are exposed to a wide range of well-known medical problems, including nervous system disorders and / or reproductive problems.

  There are three main types of mercury emissions: Anthropogenic release, re-release, and natural release. Anthropogenic releases are largely the result of industrial activity. Anthropogenic sources include industrial coal burning plants, natural gas burning facilities, cement production plants, petroleum refining facilities, chlor-alkali industries, vinyl chloride industries, mining and refining businesses. Re-emissions occur when mercury deposited on the soil is re-sprayed by floods or forest fires. Mercury absorbed into and / or deposited on soil is released back into the water by runoff and / or flooding by rainwater. Soil erosion contributes to this problem. Forest fires, whether spontaneous, arson, or deliberate deforestation fires, release mercury to air and / or water sources and deposit elsewhere. Natural emissions include volcanoes and geothermal vents. It is estimated that about half of the total mercury released to the atmosphere is from natural events such as volcanoes and geothermal vents.

  As mentioned above, coal-fired plants release large amounts of mercury and other pollutants into the environment each year. Accordingly, a number of efforts are currently being made to reduce the amount of harmful pollutants in flue gas emissions generated by coal combustion plants. Many coal burning plants in the United States are equipped with emission control systems that capture, seal and / or regenerate harmful elements such as mercury. In a coal burning plant, coal is boiled to boil water, convert water to steam, and drive a generator. The flue gas emissions from coal combustion are often passed through a conduit system to a fluid gas desulfurization unit and / or a spray dryer system where some of the emissions from the flue gas and sulfur dioxide (SO2 ) And hydrogen chloride (HCl). The flue gas stream is then sent to the wet / dry gas scrubber by a conventional conduit system, where more sulfur dioxide, hydrogen chloride and fly ash are removed. The flue gas stream passes through the baghouse, where particles are separated from the air stream in the flue gas, similar to a household vacuum bag. The flue gas passes through a filter sack having a porosity that is permeable to larger air particles, which passes through the air flow but travels in the air flow. By shaking and / or washing the surface of the filter bag, the collected particles are collected and made available for disposal. Generally, these deposits are themselves harmful emissions and must be disposed of. The remainder of the flue gas that passes through this type of emission control system passes through a high stack and is released to the atmosphere.

  The problem with this type of emission control system is that it is not practically effective in capturing and / or collecting heavy metals such as mercury in metal vapors and vaporous metal compounds. Because the coal combustion system burns coal at a relatively high 1500 ° F., mercury is converted to nano-sized particles and can pass through even the most effective filter systems. As a result, large amounts of mercury and other harmful pollutants carried by the air are released to the atmosphere.

  Several known systems have been developed to address this issue for capturing and collecting mercury from coal combustion systems and / or other sources. These fall into one of three categories.

  The first category is a group of methods and / or systems that capture mercury by injecting an adsorbent into the flue gas stream. In addition to noble metals, the most common adsorbent materials are activated carbon and / or biochar. Activated carbon is often halogenated by bromine. Biochar is charcoal rich in carbon. Injecting the adsorbent into the flue gas facilitates the capture of pollutants in one and / or a combination of the following conventional emission control devices. An electrostatic precipitator, a fluidized gas desulfurization system, a washer system, or a fiber filter system. There are several variations of these systems that require injection of activated carbon at various points in the emission control system after coal combustion. Some of the first category exemplary methods and / or systems are described in U.S. Patent Nos. 7,578,869, 7,575,629, 7,494,632, 7,306,774, 7,850,764; 7,704,920,7,141,091,6,905,534,6,712,878,6,695,894,6,558,454,6,451,094,6,136,072,7, 618,603, 7,494,632, 8,747,676, 8,241,398, 8,728,974, 8,728,217, 8,721,777, 8,685,351, and 8,029. , 600.

  The second category is a group of methods and / or systems for pretreating coal fuel prior to combustion to reduce mercury levels in the coal fuel. Some of the exemplary methods and / or systems in this second category are described in U.S. Patent Nos. 7,540,384, 7,275,644, 865,282, 8523963, 8579999, 8062410, and 7987613. All of the methods and / or systems described in these exemplary patents produce large amounts of unusable coal, which is also considered hazardous waste. As a result, the methods and / or systems of the second category of known solutions are inefficient and expensive to implement. Furthermore, coal pretreatment often requires large amounts of capital and physical space, making it impractical to modify many existing emission control systems that have the necessary equipment.

  The third category is a group of methods and / or systems for injecting catalyst into emission control facilities upstream of the activated carbon injection system. The catalyst in these methods and / or systems ionizes mercury to facilitate collecting and removing mercury from flue gases. However, the efficiency of such methods and / or systems is low and the operating costs are high, and the methods and / or systems of the third category of this known solution are not cost-effective. Examples of this third category are described in U.S. Patent Nos. 8480791, 8241398, 7753992, and 7731781. In addition to these examples, U.S. Pat. No. 7,214,254 discloses a method and apparatus for regenerating expensive adsorbent material using microwaves and a fluidized bed reactor. In this method, mercury is selectively evaporated from the adsorbent, at which point the mercury is captured by a special filter or concentrated and made available for collection. Due to the use of microwaves, this method is not practical for large scale commercial applications and is therefore only useful for regenerating expensive adsorbents. U.S. Patent Application No. 2006/0120935 discloses another method of removing mercury from flue gas using one of several substrate materials to impart affinity to the mercury as the flue gas passes through an emission control facility. Examples will be disclosed. This method is also not practical for large scale commercial applications. Accordingly, current emission control systems and methods generally operate by moving hazardous pollutants from gaseous emissions to non-gaseous emissions, thereby creating another emission management problem.

  Numerous laws and regulations focus on metal vapor emissions, while slurries and / or slurries, sludge and / or sludges, liquids and / or liquids, and other types of emissions Emissions containing other forms of harmful pollutants should not be overlooked. All types of emissions listed also require treatment to neutralize, capture, collect, remove, dispose of, and / or properly seal any harmful pollutants contained. there's a possibility that. Historically, the most cost-effective and most widely used hazardous pollutant removal processes have used activated carbon (in some form) through which emissions pass. Thus, the demand for activated carbon in the United States is expected to exceed one billion pounds annually and increase each year until 2017, resulting in costs to the industry of over $ 1-1.50 / lb. This equates to approximately $ 1 billion each year. Much of the projected increase in activated carbon demand is affected by the implementation of regulations issued by the EPA that require utilities and manufacturers to update coal-fired plants to comply with more stringent requirements.

  In addition to stricter gas emission regulations, the EPA has also added stricter regulations for non-gas emissions through the Water Pollution Control Act, which must be fully compliant by 2016. The enhanced combined regulation for all types of emissions covers multiple types of emissions produced by various different industries. Businesses that burn fuel to generate power, such as electric power companies, generate primary gas emissions containing harmful pollutants. In accordance with industry standards, these gaseous emissions are exposed to activated carbon in order to capture a sufficient amount of harmful pollutants to bring the gaseous emission pollutants below acceptable limits. This step of removing harmful pollutants from the gaseous emissions produced by burning the fuel produces secondary non-gaseous emissions that are liquid or slurry-like substances containing harmful pollutants. Hazardous contaminants in this secondary non-gaseous effluent must also be captured and / or properly sealed to prevent release of this harmful contaminant into the environment. Both primary and secondary non-gas emissions require means to properly capture and / or regenerate and / or seal sufficient hazardous pollutants to comply with environmental standards And The industrial costs of known methods that can remove harmful pollutants from secondary non-gas emissions are almost prohibitive, and some industries require equipment if costs cannot be added to consumers. Forced to close.

  According to some practices, non-gaseous emissions that are considered harmful because they contain high levels of contaminants are disposed of and stored in ponds, piles or dry beds for extended periods of time. Such practices, while sequestering harmful pollutants, can be costly and consume land without neutralizing the harmful pollutants themselves, which can lead to environmental problems in containment sites. There is. One example of a non-gaseous emission is fly ash, which is a natural product of burning coal. Fly ash is basically identical in composition to volcanic ash. Fly ash contains trace levels (i.e., traces) of various heavy metals and other known harmful and toxic contaminants such as mercury, beryllium, cadmium, barium, chromium, copper, lead, molybdenum, nickel, radium, selenium, thorium, Uranium, vanadium, zinc). According to one estimate, 10% of coal burned in the United States is made of non-combustible materials, which becomes ash. Thus, the concentration of harmful trace elements in coal ash is ten times higher than the concentration of these elements in the original coal.

  Fly ash is considered a pozzolanic material and, when mixed with calcium carbonate, forms a cement material that aggregates with water and other compounds to form a concrete mixture suitable for roads, airport runways and bridges. Has long been used in the manufacture of Fly ash produced in a coal combustion plant is a flue ash composed of ultrafine particles that rise with the flue gas. Ash that does not rise is often referred to as bottom ash. In early coal-fired plants, fly ash was simply released to the atmosphere. In recent years, due to environmental regulations, it has become necessary to install an emission control mechanism to prevent fly ash from being released into the atmosphere. Many plants use electrostatic precipitators to trap fly ash before it reaches the chimney and exits to atmosphere. Normally, bottom ash is mixed with the captured fly ash to form what is known as coal ash. Fly ash typically contains higher levels of harmful pollutants than bottom ash, which allows the mixing of bottom ash and fly ash to produce a proportionate level of harmful pollution that conforms to many standards for non-gas emissions. Material will result. However, future standards may redefine fly ash as a hazardous substance. If fly ash is redefined as a hazardous substance, it cannot be used for cement, asphalt production and other widely used applications. According to one study, the ban on the use of fly ash for concrete production could add to the cost of over $ 5 billion per year alone in the United States. This cost increase is a direct consequence of using more expensive alternative materials in place of fly ash. In addition, due to its inherent physical properties, there are no other known materials that are directly replaced by fly ash as an additive to cement.

  According to the report, more than 130 million tonnes of fly ash are produced annually in the United States at more than 450 coal-fired power plants. One report estimates that only 40% of fly ash is recycled, which means that 52 million tonnes / year of fly ash will be recycled, but 78 million tonnes / year will remain in slurry ponds and mountains. Indicates that it will be stored. Fly ash is typically stored in a wet slurry pond to reduce scattered particles from being transported to the air and contaminants from leaving bulk storage to the atmosphere or the surrounding environment. In addition to the bulk fly ash being transported to the air for release, the containment system required to contain the fly ash for extended periods of time may be damaged and / or broken. A notable example of a 2008 damage in Tennessee was the collapse of a wet storage fly ash pond embankment, flooding 5.4 million cubic yards of fly ash. The overflowing fly ash destroyed several homes and polluted nearby rivers. Cleaning costs are undetermined at the time of filing of the present application and can exceed $ 1.2 billion.

  As another example, non-gaseous emissions may be found as a by-product of the wastewater generation system of a conventional coal-fired facility. In a typical wastewater generation system, a large amount of water comes from the boiler and water cooling process. These large volumes of wastewater contain relatively low levels of pollutants and are used to dilute other wastewater streams containing higher levels of pollutants. The contaminated wastewater stream normally discharged from the scrubber is diluted by a large amount of wastewater from the boiler and / or cooling water process and then treated with lime in a large continuous mixing tank to form gypsum, It is pumped to the sedimentation basin. During this process, certain amounts of mercury and other heavy metals are incorporated into the gypsum and stabilized for use in wallboard and cement. This gypsum is generally considered non-leachable and not polluting. However, the water from the sedimentation basin is normally discharged to a drain. Current regulations allow for this ongoing emission, but upcoming regulations require certain pollutants and / or certain levels of these pollutants to be harmful. It is suggested that:

  Regarding the removal of mercury and heavy metals from non-gaseous industrial waste streams, carbonates, phosphates or sulfur are often used to reduce harmful pollutants to low residual levels. One known method for removing mercury and other harmful pollutants from industrial wastewater streams is the chemical precipitation reaction. Another known method uses ion exchange. One of the major problems with chemical precipitation reactions and ion exchange methods is that when the amount of contaminants is high (eg, when processing fly ash slurry effluents), these methods can be more demanding on non-gas emissions. Is not fully compliant with the EPA rules for

  Another source of contaminated non-gaseous emissions is the discharge of marine vessel wastewater and / or ballast water. Commercial vessels such as cargo ships and tankers discharge both wastewater and ballast water. Recreational cruising vessels also generate wastewater to be treated during berths at the port. In addition, military and defense vessels also generate significant amounts of wastewater.

  Another large amount of wastewater is generated by offshore drilling operations. Wastewater treatment in offshore rig facilities is much less expensive than transporting and treating wastewater on land. Therefore, efficient filtration of marine wastewater prior to discharge into the sea is necessary to maintain appropriate and acceptable ecology requirements. Virtually all polluting emissions differ in the type and / or concentration of pollutants in the effluent. Thus, for a suitable adsorbent optimized for all possible polluting emissions, a one-size-fits-all approach is not possible. One needs to consider an application-specific sorbent solution to optimize effective emission control based on the specific pollutants contained in the emissions. During use, it may also be necessary to be able to adjust the sorbent application used in response to changes in the level and / or type of contaminants contained in the effluent.

  There are also various known commercial emission control methods and systems sold under different trade names to treat secondary non-gas emissions. A treatment method known as Blue PRO is a reactive filtration method that removes mercury from secondary non-gas emissions using co-precipitation and adsorption. Another process, known as MERSORB-LW, uses a powdered coal-based adsorbent to remove mercury from secondary non-gas emissions by co-precipitation and adsorption. Another process, known as Chloralkali Electrolysis Wastewater, removes mercury from secondary non-gaseous effluents when electrolytically producing chlorine. In another treatment method, mercury is removed from secondary non-gas emissions using absorption kinetics and activated carbon from fertilizer wastewater. In another treatment method, mercury is removed from the secondary non-gas effluent using porous cellulose alone modified with polyethyleneimine as an adsorbent. Another treatment method uses microorganisms to remove mercury from secondary non-gas emissions during enzymatic reduction. Yet another treatment method, known as MerCURxE, uses a chemical precipitation reaction to treat the contaminated liquid non-gas emissions.

  A treatment method found in some emission control systems is to dilute contaminants instead of removing them from the emissions. As a result, if the PPM level of a contaminant in the effluent exceeds an acceptable level, additional non-contaminant is added to the effluent and tolerated, rather than removing this contaminant and reducing the level. The actual amount of contaminants remains unchanged, but lowers the PPM levels obtained to acceptable levels. It is desirable to overcome this dilution practice by providing effective emission control methods that not only reduce the PPM levels of pollutants, but also remove them from emissions.

  This section presents a general summary of the disclosures and does not exhaustively disclose the entire scope or all of the features.

  In one aspect of the present disclosure, an apparatus for removing contaminants from an effluent is disclosed. The device includes an inverted venturi-shaped housing. The housing has an inlet portion through which the discharged material flows at a predetermined inlet flow rate, an outlet portion discharging the discharged material at a predetermined outlet flow speed, and an outlet portion disposed between the inlet portion and the outlet portion of the housing. And an enlarged diameter portion for trapping contaminants. The inlet, outlet, and enlarged diameter portions of the housing are arranged to communicate with each other via a fluid. In addition, the inlet of the housing has an inlet cross-sectional area, the outlet of the housing has an outlet cross-sectional area, and the enlarged diameter portion of the housing has an enlarged diameter cross-sectional area. According to the inverted venturi shape of the housing, the cross-sectional area of the enlarged-diameter portion is larger than the cross-sectional area of the inlet portion and the cross-sectional area of the outlet portion. Due to the shape of the housing, the discharge flowing into the enlarged diameter portion of the housing is decelerated and passes through the enlarged diameter portion of the housing at a lower speed than the speed of passing through the inlet portion and the outlet portion of the housing. . Since the flow of the waste material is decelerated at the enlarged diameter portion of the housing, the residence time of the discharged material in the enlarged diameter portion of the housing increases.

  The device also includes a reactant mass that includes one or more adsorbents disposed within the enlarged portion of the housing. The reactant mass has an outer reaction surface that is arranged to contact the effluent. In addition, the reactant mass contains amalgam-forming metal on the outer reaction surface. The amalgam-forming metal in the reactant mass is chemically bonded to at least a portion of the contaminants in the effluent that reach the outer reaction surface of the reactant mass through the enlarged portion of the housing. One or more sorbent recycling subsystems are disposed in communication with the enclosure. In each of the adsorbent recycling subsystems, the adsorbent is taken in from the casing through the adsorbent discharge port, and the washed adsorbent is returned to the casing through the adsorbent return port. The adsorbent recycling subsystem includes a chemical reagent that separates contaminants from the adsorbent during the cleaning and regeneration steps before the washed adsorbent is returned to the fluidized bed housing.

  In another aspect of the present disclosure, an emission control method for removing contaminants from emissions is disclosed. The method includes sending the effluent to a processing system that includes an inverted Venturi fluidized bed apparatus that includes one or more adsorbents that chemically bind to contaminants contained in the effluent, and the effluent is passed through the reverse Venturi fluidized bed apparatus. And sending it in a direction away from it. According to this method, the adsorbent is selected from the group of materials including copper, zinc, tin, sulfur (CZTS) adsorbent, copper, zinc, tin, sulfur (CZTS) alloy adsorbent, and carbon-based adsorbent. You. The method further includes sending the sorbent through one or more sorbent recycling subsystems for chemical cleaning and regeneration.

  It is important to maintain optimal operating conditions of the adsorbent used to remove contaminated effluent from the reverse venturi fluidized bed apparatus. Thus, the sorbent is sent from the reverse venturi fluidized bed apparatus to the sorbent recycling subsystem. The adsorbent recycling subsystem is designed to optimally clean and / or regenerate the adsorbent before returning it to the reverse venturi fluidized bed apparatus. The sorbent recycling subsystem is also designed to separate depleted and worn sorbents from other washable and / or renewable sorbents and send them for disposal. The sorbent recycling subsystem is further designed to separate trapped contaminants from the sorbent for reuse in various industries or for proper disposal when there is no available recycling option. In addition, the sorbent recycling subsystem replenishes and / or replaces sorbent consumed during normal operations to remove separated sorbent and / or contaminants from contaminated effluents for disposal. Designed to be.

  According to another aspect of the present disclosure, the sorbent recycling subsystem includes one or more monitoring sensors that provide continuous in-line testing and monitoring feedback to maintain a constant and consistent optimal sorbent state. In an exemplary embodiment of the present disclosure, three sorbent recycling subsystems are installed and configured in at least three other locations. A first sorbent recycling subsystem is provided for the CZTS sorbent. A second sorbent recycling subsystem is provided for the CZTS alloy sorbent. A third sorbent recycling subsystem is provided for the carbon sorbent. Depending on the needs of a particular effluent, it may be determined which adsorbent recycling subsystem is specifically needed. Depending on the level of contamination in the reverse venturi fluidized bed apparatus, the reverse venturi fluidized bed apparatus may be configured to use all three adsorbent recycling subsystems and use any of the adsorbent recycling subsystems. Or the same adsorbent recycling subsystem may be located at multiple locations along the reverse venturi fluidized bed apparatus and used simultaneously.

  In addition to the significant labor savings benefits, the present apparatus and method is more effective at removing harmful pollutants from gaseous and non-gaseous emissions than known emission control systems and methods. These improvements are substantial enough to meet and / or exceed the expected regulatory requirements of the industry, but this is economically feasible with current technology It is impossible. Thus, the devices and methods of the present application have the ability to allow fly ash to continue to be used, even if fly ash is reclassified as a hazardous substance by regulation, thereby allowing construction, commercial power generation and other In the industry that produces non-gaseous ash by-products, significant cost increases can be prevented.

  Reverse venturi fluidized bed devices have a specific length / diameter ratio so that the effluent has an optimal constrained residence time as it passes through a special adsorbent contained within the device. It may be a specific size as described above. By trial and error, it has been found that the optimum length / diameter ratio of the enclosure of the fluidized bed apparatus is between 2.9: 1 and 9.8: 1, for example preferably 4.4: 1. ing. Thus, in an exemplary preferred embodiment. The diameter is 4.5 feet, the length is 19.8 feet, and the length / diameter ratio is 4.4: 1.

  Another feature of the exemplary reverse venturi fluidized bed apparatus is that it has a generally circular outwardly projecting convex end when viewed from both ends outside the enclosure. Testing an example of a system having a fluidized bed apparatus configured in this manner, the flow of the effluent was randomized back to its own side with minimal cavitation turbulence and close contact was observed. It has been demonstrated that the residence time (the time the effluent is in contact with the sorbent) is maximized because it is maximized. The generally circular outwardly projecting end provides a relatively smooth return flow at both ends of the fluidized bed apparatus and minimizes cavitation turbulence of the effluent. It is known that turbulence with cavitation through a filter impedes and / or disrupts flow. Prolonging the residence time in the fluidized bed apparatus is desirable to capture and remove contaminants from the effluent in an optimized manner. However, extension of the residence time is not optimized if the flow is turbulent with cavitation. Various baffles and / or flow-restricted obstacles corresponding to specific applications may be provided in the housing of the fluidized bed apparatus.

  In another aspect of the present disclosure, an exemplary contaminant removal system comprises a component consisting of reconfigurable segments. Each system component may be isolated, bypassed, integrated, and / or reconfigured according to application-specific requirements.

  According to another aspect of the present disclosure, an emissions control system includes a fluidized bed of a reactive adsorbent mass comprising copper, zinc, tin, sulfur (CZTS) adsorbent, CZTS alloy, and / or carbon-based adsorbent. Included in the device. The fluidized bed apparatus also includes additional ports for cleaning and / or replacing the sorbent material. The sorbent recycling subsystems disclosed herein provide methods for using CZTS sorbents, CZTS alloy sorbents, and / or carbon-based sorbents. The exemplary emissions control system may further include a pre-filter and / or post-filter that includes one or more reactive adsorbent masses. Depending on the specific needs of the application, a plurality of pre- and post-filters are connected in parallel or in series to the fluidized bed apparatus.

  Hg (mercury), As (arsenic), Ba (barium), Cd (cadmium), Cr (chromium), Cu (copper), Pb (lead), Sn (tin) include the pollutants emitted from industrial applications. , P (phosphorus), NO2 (nitrogen dioxide), NO3 (nitrate), and NH3 (ammonia). This long list of contaminants makes it impossible to provide a one-size-fits-all emissions control solution. Further, an emission control solution that works on one type of pollutant in gaseous emissions may not be effective on the same contaminant in non-gaseous emissions, and vice versa.

  International, federal, state, and local regulatory standards define various acceptable ppm levels for each contaminant in gaseous and / or non-gaseous emissions. Many of these regulatory standards set acceptable levels of different pollutants depending on whether the pollutants are in gaseous or non-gaseous emissions.

  Testing of contaminated emissions may involve sampling and / or using continuous in-line monitoring equipment to determine the type and level of contaminants contained in the effluent. Depending on the test results, a specific pre-filter and / or post-filter to which the contaminated effluent may be introduced may be selected. Each pre-filter and / or post-filter contains a specific reactive adsorbent mass intended for specific contaminants in the effluent as a wide range of treatment options.

  The type and / or level of contaminants contained in the effluent may change and / or fluctuate during the emission of the effluent. Frequent monitoring and / or continuous in-line monitoring of contaminants allows for specific pre-filters and / or best fit for specific contaminants contained in the effluent at any point in the effluent flow. The selection of the post filter can be adjusted.

  The present disclosure includes an extensive table that maps specific types of contaminants in gaseous and non-gaseous emissions to specific reactive adsorbents that are effective at capturing and removing corresponding contaminants. . This table maps whether a specific reactive adsorbent can be separated from specific trapped contaminants to recycle or dispose of contaminants, and whether the adsorbent can be reclaimed and reused in emissions control systems. Show.

  In addition to systems that are permanently installed for a particular application, the systems of the present application may be configured as transportable systems. Examples of transportable systems include, but are not limited to, truck-mounted systems, barge-mounted systems, trailer-mounted systems, and rail-mounted systems. The transportable system is useful for providing a bypass for temporary on-site systems by providing a bypass for temporary emissions, allowing the permanent on-site system to be repaired, serviced and / or repaired. It is. The transportable system is also useful to provide permanent field construction equipment with extra filtering capacity when the flow rate of contaminated effluents exceeds the capacity of the permanent field construction facility.

  There are numerous advantages to using the particular sorbents described herein with the disclosed devices and methods. In general, the ability of the effluent device disclosed by this sorbent to capture, contain and / or recycle mercury and other harmful substances has not previously been possible using known emission control systems and methods. Another important advantage of the adsorbent disclosed herein is that the adsorbent can be used to treat both gaseous and non-gaseous emissions, thereby providing a means for treating gaseous emissions. Many of the problems of known methods of treating contaminated non-gas emissions, such as secondary emissions resulting from the primary emissions control process used, can be overcome. In addition, the adsorbents described herein treat gaseous effluents efficiently enough to eliminate the need for secondary treatment of non-gaseous effluents produced as a by-product of the primary gaseous effluent treatment process. Ability is obtained. The adsorbents disclosed herein are also advantageous in that they can be reused. Through the regeneration process, it is possible to collect (ie, remove) harmful contaminants from the sorbent that chemically bind to the amalgam forming metal in the sorbent, thereby contaminating gaseous and / or non-gaseous emissions. Restores the sorbent's ability to remove material.

  Other areas of applicability will become apparent from the description provided herein. The descriptions and specific examples in this summary are for illustrative purposes only and are not intended to limit the scope of the present disclosure.

  The descriptions and specific examples in this summary are for illustrative purposes only and are not intended to limit the scope of the present disclosure.

  Other advantages of the present invention will be readily understood by referring to the following detailed description in conjunction with the accompanying drawings. These figures show:

The schematic diagram which shows the well-known structure of a coal-fired power plant. FIG. 2 is a schematic diagram illustrating a known configuration of an emission control system used to remove pollutants from emissions generated by a coal-fired power plant of the type illustrated in FIG. 1. FIG. 3 is a schematic diagram of the emissions control system shown in FIG. 2 and modified by adding an exemplary reverse venturi device configured in accordance with the present disclosure. FIG. 2 is a side cross-sectional view of an exemplary inverted Venturi device having a housing configured with an inlet, an enlarged diameter, and an outlet configured in accordance with the present disclosure. FIG. 4B is a front cross-sectional view of the inlet portion of the housing of the exemplary reverse Venturi device shown in FIG. 4A. FIG. 4B is a front cross-sectional view of the enlarged diameter portion of the housing of the exemplary inverted Venturi device shown in FIG. 4A. FIG. 4B is a front cross-sectional view of the outlet of the housing of the exemplary reverse Venturi device shown in FIG. 4A. FIG. 7 is a side cross-sectional view of another exemplary inverted Venturi device configured according to the present disclosure, wherein a series of interleaved baffles are disposed in an enlarged portion of the housing to form a serpentine flow path for effluent. FIG. 6 is a side cross-sectional view of another exemplary inverted Venturi device configured in accordance with the present disclosure, wherein a helical baffle is disposed in an enlarged portion of the housing to form a helical flow path for effluent. FIG. 6B is a front perspective view of the spiral baffle of the exemplary inverted Venturi device shown in FIG. 6A. FIG. 4 is a side cross-sectional view of another exemplary inverted venturi device configured with a plurality of spaced baffles disposed within an enlarged portion of a housing, configured in accordance with the present disclosure. FIG. 7B is a front cross-sectional view of the exemplary inverted Venturi device shown in FIG. 7A, taken along line AA, showing one orifice of the baffle. FIG. 4 is a side cross-sectional view of another exemplary inverted Venturi device configured in accordance with the present disclosure and having a plurality of debris disposed within an enlarged portion of a housing. FIG. 4 is a side cross-sectional view of another exemplary inverted venturi device configured according to the present disclosure, wherein a plurality of entangled threads are disposed in an enlarged portion of a housing to form a thread. FIG. 7 is a side cross-sectional view of another exemplary inverted Venturi device configured in accordance with the present disclosure and having a filter element disposed in an enlarged portion of a housing. FIG. 9 is a side cross-sectional view of another exemplary inverted Venturi device configured in accordance with the present disclosure, wherein the flared portion of the housing accommodates a plurality of baffles and a plurality of various sized debris disposed between adjacent baffles. FIG. 12 is an exemplary front view showing an example of a fragment sized to be accommodated in the enlarged-diameter portion of the housing of the exemplary reverse Venturi device shown in FIG. 11; FIG. 12 is a front view showing another example of the shards accommodated in the enlarged diameter portion of the housing of the exemplary reverse venturi apparatus shown in FIG. 11. FIG. 12 is a front view showing another example of the shards accommodated in the enlarged diameter portion of the housing of the exemplary reverse venturi apparatus shown in FIG. 11. FIG. 12 is a front view showing another example of the shards accommodated in the enlarged diameter portion of the housing of the exemplary reverse venturi apparatus shown in FIG. 11. FIG. 12 is a front view showing an example of a piece having an asterisk shape of free material that can be used in combination with other pieces to replace the debris shown in the exemplary reverse venturi device shown in FIGS. 8 and 11. FIG. 12 is a front view showing an example of crystal flakes that can be used in combination with other crystal flakes to replace the fragments shown in the exemplary reverse venturi apparatus shown in FIGS. 8 and 11. FIG. 12 is a front view showing an example of a wire coil that can be used in combination with other wire coils to replace the debris shown in the exemplary reverse venturi apparatus shown in FIGS. 8 and 11. FIG. 6 is a side cross-sectional view illustrating another exemplary inverted Venturi device having two separated diameter enlargements connected in series, constructed in accordance with the present disclosure. FIG. 4 is a side cross-sectional view illustrating another exemplary inverted Venturi device having two separated enlarged portions connected in parallel, constructed in accordance with the present disclosure. FIG. 4 is a side cross-sectional view illustrating another exemplary inverted Venturi device configured in accordance with the present disclosure. FIG. 3 is a block flow diagram illustrating a known method for removing contaminants from gaseous emissions. The method of removing contaminants from gaseous emissions shown in FIG. 17 is modified by adding a step of injecting the adsorbent into the gaseous emissions at the first point of introduction and then passing the gaseous emissions through a reverse venturi apparatus. FIG. The method of removing contaminants from gaseous emissions shown in FIG. 17 is modified by adding a step of injecting the adsorbent into the gaseous emissions at a second point of introduction and then passing the gaseous emissions through a reverse venturi apparatus. FIG. FIG. 1 is a block diagram illustrating a known method of removing contaminants from non-gas emissions, which requires the non-gas emissions to settle in a settling basin. FIG. 19 is a block diagram showing a method for removing contaminants from non-gas emissions shown in FIG. 19 by adding a step of treating a part of the non-gas emissions extracted from a sedimentation tank with an adsorbent; . 3 is a graph illustrating the percentage of contaminants removed from an effluent by known emission control systems and the percentage of contaminants removed from the effluent by the apparatus and method disclosed herein. FIG. 4 is a block flow diagram illustrating an exemplary method for removing contaminants from a gaseous effluent and cleaning the reactants that separate the contaminants from the gaseous effluent using a reverse venturi fluidized bed apparatus. FIG. 4 is a block flow diagram illustrating an exemplary method for removing contaminants from non-gaseous effluents and cleaning reactants that separate the contaminants from non-gaseous effluents using an inverted venturi fluidized bed apparatus. FIG. 4 is a flow diagram illustrating an extended non-turbulent effluent flow through an exemplary reverse venturi fluidized bed apparatus and exemplary method steps for cleaning and recycling the adsorbent that separates contaminants from the effluent. In an exemplary method using an inverted Venturi fluidized bed device having a tilting mechanism mounted on a transportable gantry deck, a housing of the inverted Venturi fluidized bed device is used to remove contaminants from gaseous emissions. FIG. 2 is a block flow diagram showing a device arranged in parallel with a deck. In an exemplary method using an inverted Venturi fluidized bed apparatus having a tilting mechanism mounted on a transportable gantry deck, the housing of the inverted Venturi fluidized bed apparatus is used to remove contaminants from non-gas emissions. FIG. 3 is a block flow diagram illustrating a traverse deck arranged in a direction transverse to the gantry deck. FIG. 3 is a table contrasting the specific types of contaminants and the effectiveness of the disclosed CZTS alloy adsorbent when compared to activated carbon and zeolite adsorbents for gaseous and non-gaseous emissions. FIG. 4 is a schematic diagram showing a specific CZTS alloy adsorbent compared to other specific types of adsorbents for gaseous and non-gaseous emissions. 1 is a table showing prior art adsorbents and their ability to separate and recycle pollutants in gaseous and non-gaseous emissions. 1 is a table showing the disclosed broad spectrum CZTS alloy adsorbents and their ability to separate and recycle pollutants in gaseous and non-gaseous emissions. FIG. 4 is a block diagram illustrating a method of passing contaminated gaseous emissions through different filters that include specific effective sorbents that match the type and / or level of contaminants contained in the gaseous emissions. FIG. 4 is a block diagram illustrating a method of passing contaminated non-gas emissions through different filters that include a specific effective sorbent that matches the type and / or level of contaminants contained in the non-gas emissions. Extended non-turbulent effluent flow through an exemplary reverse venturi fluidized bed apparatus and contaminants by a series of sorbent recycling subsystems for CZTS sorbents, CZTS alloy sorbents, and / or carbon-based sorbents FIG. 4 is a flow diagram illustrating exemplary method steps for cleaning and recycling an adsorbent that separates effluent from effluent.

  An apparatus and method for removing pollutants from industrial effluent will be described with reference to the drawings, wherein like reference numerals indicate corresponding elements throughout the drawings.

  Exemplary embodiments are described more fully with reference to the accompanying drawings. The illustrative embodiments are provided to complete the disclosure and to fully convey the scope to those skilled in the art. In order to provide a thorough understanding of embodiments of the present disclosure, numerous specific details are set forth, including specific examples of components, elements, and methods. It will be apparent to one skilled in the art that the specific details need not be used and that the example embodiments can be implemented in many different forms and should not be construed as limiting the present disclosure. In some exemplary embodiments, well-known methods, well-known device structures, and well-known technologies are not described in detail.

  The terms used in this specification are for the purpose of describing particular exemplary embodiments only, and are not intended to be limiting. As used herein, the singular is intended to include the plural unless specifically stated otherwise. The terms "comprising," "including," "including," and "having" are inclusive and identify the presence of the stated feature, integer, step, operation, element, and / or component. However, this does not preclude the existence or addition of one or more features, integers, steps, operations, elements, parts and / or groups. The method steps, processes, and operations described herein should not necessarily be construed as requiring execution in the particular order described or illustrated, unless otherwise specified. Of course, additional or alternative steps may be used.

  When an element or layer is described as "engaged with," "connected to," or "coupled to," it is "on" another element or layer, the element or layer is directly above the other element or layer. Or may be engaged, connected, or connected. Alternatively, there may be intervening elements or layers. On the other hand, if an element is described as "directly on", "directly connected to", "directly connected to" or "directly connected to" another element or layer, then no intervening element or layer is present. May be. Other terms used to describe the relationship between elements (eg, "between" and "directly between", "adjacent to" and "directly adjacent", etc.) are interpreted similarly It should be. As used herein, the term "and / or" includes any and all combinations of one or more associated listings.

  The terms first, second, third and the like are used herein to describe various elements, components, regions, layers and / or portions, but these elements, components, regions, layers and / or The cut surface is not limited by these terms. These terms may only be used to distinguish one element, component, region, layer and / or section from another region, layer or section. Terms such as "first," "second," and other numerical terms as used herein do not imply a sequence or order, unless context clearly indicates otherwise. Accordingly, a first element, component, region, layer and / or cut surface discussed below may be referred to as a second element, component, region, layer and / or cut surface without departing from the teachings of the embodiments. Is also possible.

  Spatial relative terms such as “inner”, “outer”, “below”, “below”, “below”, “above”, “above” etc. It may be used herein to facilitate describing the relationship between an element or feature and another element or feature. Spatial relative terms may encompass different orientations of the device in use or operation, in addition to the orientation shown. For example, if the apparatus in the figures is turned over, an element described as "below" or "directly below" another element or feature will be placed "above" the other element or feature. Thus, the exemplary term "down" can encompass both an upward and downward orientation. The device may be oriented in the other direction (90 degree rotation or other orientation) and the spatially relevant descriptions used herein are to be interpreted as such.

  The term "conduit" as used herein is intended to cover the description of liquids and / or liquid effluents and all pipes normally available for carrying gaseous and / or gaseous effluents It is. Regardless of the type of effluent, no priority is given or implied on the actual method of transport of the effluent. In addition, the terms "contaminant continue (s)" and "contaminant continue (s)" are used interchangeably in the present disclosure.

  Referring to FIG. 1, a schematic diagram of a typical coal-fired power plant 100 is shown. The coal-fired power plant 100 has a fluidized-bed reactor 1 which is an industrial facility that burns one or more types of coal fuel 2 and generates electric power 7. This power 7 may then be distributed to the power grid via electric wires 8. Combustion in the fluidized bed reactor 1 is performed by air 3, fire 4 and coal fuel 2. This combustion process is used to heat water to generate steam 5. This steam is then used to turn generator 6 to generate power 7. Gas emissions 10 from the combustion process are released into the environment through the chimney 9. If the coal-fired power plant 100 is not provided with any emission control system (FIG. 1), this emission 10 will include fly ash, mercury (Hg), metal vapor, sulfur dioxide (SO2), hydrogen chloride (HCl) and Contains many harmful pollutants such as other harmful gases.

  Referring to FIG. 2, a schematic diagram of an improved coal-fired power plant 200 having a conventional emissions control system 202 is shown. The emission control system 202 captures and collects some of the harmful pollutants in the gaseous emission 10. The emission control system 202 converts a gaseous effluent 10 from a fluidized bed reactor 1 in which a combustion reaction takes place into a wet / dry gas scrubber 11 for removing a portion of sulfur dioxide and fly ash contaminants from the gaseous effluent 10. Transport to Instead of, or in addition to, transporting the gaseous effluent 10 to a wet / dry gas scrubber 11, the effluent control system 202 can reduce the gaseous effluent 10 from sulfur dioxide, noxious gases and other contaminants. The section may be conveyed to the spray dryer 12 where it is captured and collected. This effluent may be passed through a fiber filter unit 13 (ie, a baghouse) that removes particles from the stream of gaseous effluent 10 using a filter bag. The system collects and removes many contaminants from the gaseous effluent 10 before the gaseous effluent 10 is released through the chimney 9 to the surrounding atmosphere (ie, the environment). The problem with the conventional emission control system 202 shown in FIG. 2 is that nano-sized contaminants, such as mercury, contained in the metal vapor effluent are discharged from the wet / dry gas cleaning device 11 of the emission control system 202 by spray drying. The machine 12 and the fiber filter unit 13 easily.

  Referring to FIG. 3, a schematic diagram of an improved coal-fired power plant 300 having an adsorbent injector 14 and a reverse venturi device 15 in addition to the emissions control system 202 shown in FIG. 2 is shown. The sorbent injector 14 operates to add sorbent to the gaseous effluent 10 and may be located upstream of the reverse venturi device 15. More specifically, in the example shown in FIG. 3, the adsorbent sprayer is disposed between the spray dryer 12 and the fiber filter unit 13. Although the reverse venturi device 15 can be located at a different position, in FIG. 3 the reverse venturi device is located between the fiber filter unit 13 and the chimney 9. One of the main advantages of this arrangement is that the reverse venturi device 15 can be installed in the existing equipment, and it is only necessary to apply for “Modification to Exchanging Permit” and a completely new emission control is required. It saves both time and money compared to applying for a system. In operation, gas exhaust 10 is sent from fiber filter unit 13 to reverse venturi device 15. As will be described in more detail below, the reverse venturi device 15 is provided with internal structures suitable for collecting and capturing significant amounts of mercury, heavy metals, nano-sized particles and other contaminants. Thus, the gaseous effluent 10 leaving the chimney 9 is substantially free of all harmful pollutants.

  As shown in FIGS. 4A-4D, the reverse venturi device 15 has a housing 16 that is in the shape of a reverse venturi. It should be noted that a venturi is generally described as a conduit that first contracts from a larger cross section to a smaller cross section, and then expands from a smaller cross section to a larger cross section. Thus, as used herein, the term "reverse venturi" means the opposite, i.e., a conduit that first expands from a smaller cross-section to a larger cross-section and then reduces in diameter from a larger cross-section to a smaller cross-section. . Specifically, the housing 16 of the disclosed inverted Venturi device 15 extends along a central axis 17 and has an inlet 18, an enlarged diameter 19, and an outlet 20. The inlet 18 of the housing 16 is sized so that the gaseous effluent 10 flows in at a predetermined inlet flow rate characterized by an inflow velocity V1 and a pressure P1. The outlet 20 of the housing 16 is sized so that the gaseous effluent 10 flows out at a predetermined outlet flow rate characterized by an outlet velocity V3 and a pressure P3. The enlarged diameter portion 19 is disposed between the inlet portion 18 and the outlet portion 20 of the housing 16 and forms an enlarged diameter chamber 21 for trapping contaminants in the gas discharge 10 therein. The enlarged diameter portion 19 of the housing 16 has an inner surface 68 substantially facing the central axis 17. The inlet 18, the enlarged diameter 19, and the outlet 20 of the housing 16 communicate with each other via the fluid along the central axis 17. Are arranged in order. That is, the inlet 18, the enlarged diameter 19, and the outlet 20 of the housing 16 together form a conduit extending along the central axis 17.

  The inlet 18 of the housing 16 has an inlet cross-sectional area A1 crossing the central axis 17, and the outlet 20 of the housing 16 has an outlet cross-sectional area A3 crossing the central axis 17. The inlet cross-sectional area A1 may be equal to (i.e., the same as) the outlet cross-sectional area A3 such that the predetermined inlet flow velocity is equal to (i.e., the same as) the predetermined outlet flow velocity. Alternatively, the inlet cross-sectional area A1 and the outlet cross-sectional area A3 are different (i.e., smaller or larger) such that the predetermined inlet flow velocity is different from (i.e., smaller or larger than) the predetermined outlet flow velocity. ) Is also good. The term "flow rate" as used herein refers to the volumetric flow rate of the effluent.

  The enlarged diameter portion 19 of the housing 16 traverses the central axis 17 and has an enlarged diameter sectional area A2 larger than the inlet sectional area A1 and the outlet sectional area A3. Therefore, the enlarged diameter portion 19 has a configuration in which the flow velocity V2 of the gas discharge 10 in the enlarged diameter portion 19 of the housing 16 is smaller than the flow velocity V1 of the gas discharge 10 in the inlet portion 18 of the housing 16, and It is sized to be smaller than the flow velocity V3 of the gas discharge 10 in the outlet 20 of the body 16. As the flow velocity decreases, the residence time of the gas discharge 10 in the enlarged diameter portion 19 of the housing 16 increases. Note that the term “residence time” used in the present specification means the average of the time required for the molecules in the gas discharge 10 to pass through the enlarged diameter portion 19 of the housing 16. That is, the “residence time” of the enlarged diameter portion 19 of the housing 16 is equal to the time required for all the discharges in the enlarged diameter chamber 21 to be updated. Further, the term “cross-sectional area” used in the present specification means an internal cross-sectional area (that is, a space inside the housing 16) that is the same regardless of a change in the thickness of the housing 16. Therefore, the enlarged-diameter portion cross-sectional area A2 reflects the size of the enlarged-diameter chamber 21 and is defined by the inner surface 68.

  Due to the shape of the housing 16, the internal pressure P 1 of the gas exhaust 10 passing through the inlet 18 of the housing 16 and the internal pressure P 3 of the gas exhaust 10 passing through the outlet 20 of the housing 16 are equal to each other. It is larger than the internal pressure P2 of the gas discharge 10 passing through the enlarged diameter portion 19. The flow velocity V2 of the gas discharge 10 in the enlarged diameter portion 19 of the housing 16 is smaller than the flow velocity V1 of the gas discharge 10 at the inlet 18 of the housing 16 and the gas discharge at the outlet 20 of the housing 16. Combined with the fact that the flow velocity is smaller than the flow velocity V3 of the object 10, this pressure difference causes the gas discharge 10 to stay in the enlarged diameter portion 19 of the housing 16. As a result of the pressure and velocity differences described above, and because the gas discharge 10 naturally expands and occupies the entire volume of the expanded chamber 21, the gas discharge 10 in the expanded portion 19 of the housing 16 Will be expanded. This fact, combined with the effects of laminar flow, pneumatic dynamics, and gas behavior physics, effectively increases the residence time created and effectively removes gas from the gas vent 10 of the reverse venturi apparatus 15. The ability to capture and thereby remove contaminants is improved.

  The housing 16 may have various different shapes and structures. As a non-limiting example, the inlet 18, the enlarged diameter 19, and the outlet 20 of the housing 16 shown in FIGS. 4A-4D all have circular cross-sectional areas A1, A2, A3. Alternatively, one or more cross-sectional areas A1, A2, A3 of the inlet portion 18, the enlarged diameter portion 19, and the outlet portion 20 of the housing 16 may be non-circular, and may have a circular or non-circular cross-section. Various combinations are possible and are considered to be within the scope of the present disclosure. In some constructions, the enlarged diameter portion 19 of the housing 16 may have a diverging end 22 and a converging end 23. According to these structures, the enlarged diameter portion 19 of the housing 16 is tapered outward from the cross-sectional area A1 of the entrance portion to the cross-sectional area A2 of the enlarged diameter portion at the diverging end portion 22. That is, the cross section of the enlarged diameter portion 19 of the housing 16 becomes larger at the diverging end portion 22 as it moves away from the entrance portion 18 of the housing 16. On the other hand, the enlarged diameter portion 19 of the housing 16 is gradually tapered inward at the converging end portion 23 from the enlarged diameter sectional area A2 to the outlet sectional area A3. That is, the cross section of the enlarged diameter portion 19 of the housing 16 becomes smaller at the converging end 23 as it moves in the direction toward the outlet 20 of the housing 16. Therefore, the gas discharge 10 in the enlarged diameter portion 19 of the housing 16 flows from the diverging end 22 to the converging end 23. In an embodiment in which the inlet section 18, the enlarged diameter section 19, and the outlet section 20 of the housing 16 all have circular cross-sectional areas A1, A2, A3, the diverging end and converging end 22, 23 of the housing 16 are approximately It may have a conical shape. Regardless of the above, the diverging and converging ends 22, 23 of the enlarged diameter portion 19 of the housing 16 may have another shape. By way of a non-limiting example, the diverging and converging ends 22, 23 can be made more manufacturable while not significantly affecting the flow of the gas exhaust 10 through the housing 16 of the reverse venturi device 15. May be a polygon. In another alternative configuration, the enlarged portion 19 of the housing 16 resembles sausage where a relatively rapid change occurs between the inlet 18 and the diverging end 22 and between the converging end 23 and the outlet 20. May have a different shape. It is presumed that the smooth change is preferable to the rapid change because the laminar flow behavior of the gas emission 10 is more preferable. However, slight disturbances to the laminar flow of the gaseous effluent 10 during abrupt changes are not considered to be absolute problems, but rather can provide better flow in areas where increased residence time is not required. There is also.

  With continued reference to FIGS. 4A-4D, and further FIGS. 5-11, a reactant mass 24 is disposed within the enlarged diameter portion 19 of the housing 16. This reactant mass 24 has an outer reaction surface 25 arranged to contact the gaseous effluent 10. In addition, the reactant mass 24 chemically bonds with at least a portion of the contaminants in the gaseous effluent 10 that reach the outer reaction surface 25 of the reactant mass 24 through the enlarged portion 19 of the housing 16. The amalgam-forming metal is contained on its outer reaction surface 25. In this manner, contaminants bound to the outer reaction surface 25 of the reactant mass 24 remain trapped in the enlarged portion 19 of the housing 16 and thus flow out of the enlarged portion 19 of the housing 16. Thus, the gas is discharged from the flow of the gas exhaust 10 flowing into the outlet 20 of the housing 16. As used herein, the term "amalgam-forming metal" means a material selected from the group of metals that can form compounds with one or more of the contaminants in the gaseous effluent 10. As a non-limiting example, the amalgam-forming metal is zinc and the contaminant in the gaseous effluent 10 may be mercury, whereby the gaseous effluent 10 contacts the outer reaction surface 25 of the reactant mass 24. At this time, an amalgam of zinc and mercury may be formed.

  The enlarged diameter portion 19 of the housing 16 has a predetermined inlet flow rate while ensuring a sufficiently long residence time for the amalgam forming metal in the reactant mass 24 to chemically combine with the contaminants in the gaseous effluent 10. Must be large enough to accommodate the gaseous exhaust 10 of the present invention. Thus, to achieve this balance, the expanded section cross-section A2 may be in the range of 3 square feet to 330 square feet to achieve a residence time in the range of 1 second to 2.5 seconds. This particular residence time is necessary to ensure that the contaminants in the gaseous effluent 10 have sufficient time to chemically bond with the amalgam-forming metal in the reactant mass 24. Thus, the range of the cross-sectional area A2 of the expanded portion was calculated to realize this residence time in the coal-fired power plant 100 having an output in the range of 1 megawatt (MW) to 6000 megawatts (MW). As is known in the chemical arts, the amalgam-forming metal can be a variety of different metals. As a non-limiting example, the amalgam-forming metal may be selected from the group consisting of zinc, iron and aluminum. The housing 16 is made of a material different from the reactant mass 24. By way of non-limiting example, housing 16 may be made of steel, plastic, or fiberglass.

  The reactant mass 24 may have a variety of different, non-limiting structures. In FIG. 4A, reactant mass 24 is shown as coating inner surface 68 of housing 16. Alternatively, as shown in FIGS. 5-11, the reactant mass 24 may form one or more obstruction elements 26a-26j disposed within the enlarged diameter portion 19 of the housing 16. These obstruction elements 26 a-26 j form, as such, a bent channel 27 of the gas exhaust 10 passing through the enlarged diameter portion 19 of the housing 16. Thus, the obstruction elements 26a-26j increase the residence time of the gas exhaust 10 passing through the enlarged diameter portion 19 of the housing 16. In some embodiments described below, since the flow of the gas exhaust 10 passing through the enlarged diameter portion 19 of the housing 16 is completely cut off, the bent flow path 27 formed is completely random, This will greatly increase the chance of a chemical reaction between the contaminants in the gaseous effluent 10 and the amalgam forming metal in the reactant mass 24.

  Each of the obstruction elements 26a-26j of the structure shown in FIGS. 5-11 has a large surface area, which increases the outer reaction surface 25 of the reactant mass 24. This is due to the chemical reaction between the amalgam forming metal in the outer reaction surface 25 of the reactant mass 24 and the contaminant in the gaseous effluent 10, whereby the contaminant is collected in the enlarged portion 19 of the housing 16 and captured. Advantageously, and / or as being collectable, contaminants are removed from the gaseous effluent 10. Therefore, the amount of contaminants that can be removed from the gas discharge 10 passing through the enlarged diameter chamber 21 by the enlarged diameter portion 19 of the housing 16 depends on the reaction outer surface of the reactant mass 24 in the enlarged diameter portion 19 of the housing 16. It is proportional to the size of 25. In addition, due to the complex topography and / or texture of the obstruction elements 26a-26j, contaminants can be trapped regardless of whether entrapment of the contaminants is the result of a chemical reaction between the contaminants and the amalgam forming metal. Additional surface area is obtained that facilitates physical capture.

  Referring again to FIG. 3, the sorbent added to the effluent by the sorbent injector 14 includes amalgam-forming metal. The amalgam-forming metal in the adsorbent chemically bonds with at least some contaminants in the gaseous effluent 10 before the gaseous effluent 10 flows into the enlarged portion 19 of the housing 16. Although the sorbent may have many different compositions, the sorbent may be, for example, zinc (Zn) powder or a copper-zinc-tin-sulfur (CZTS) compound. Since the adsorbent chemically bonds to at least some of the contaminants in the gas exhaust 10 before the gas exhaust 10 flows into the enlarged diameter portion 19 of the housing 16, the adsorbent causes the reactant mass 24 facilitates the removal of pollutants from the gaseous effluent 10.

  As shown in FIG. 5, the obstruction elements 26a-26j are provided as a series of alternating baffles 26a extending from the inner surface 68 of the enlarged diameter portion 19 of the housing 16. This series of alternately arranged baffles 26a traverses the central axis 17 and makes the bent channel 27 meandering. The meandering shape of this tortuous channel 27 increases the residence time of the gaseous discharge 10 in the enlarged diameter portion 19 of the housing 16, thereby causing the gaseous discharge by the reactant mass 24 to form a series of alternating baffles 26 a. Entrapment and removal of contaminants in 10 is facilitated. In one example, the series of interleaved baffles 26a comprises zinc. In another example, the series of interleaved baffles 26a comprises a material other than zinc coated with zinc. The arrangement of the interleaved baffles 26a need not be equally spaced or symmetric along the longitudinal direction of the central axis 17. This is because in some applications it is preferable to have more space between adjacent baffles 26a, and in other applications it is preferable to have more space between adjacent baffles 26a. The series of interleaved baffles 26a may be replaced and / or cleaned as needed if they become saturated during operation of the reverse venturi device 15.

  As shown in FIGS. 6A and 6B, at least one obstruction element 26a-26j may be a spiral baffle 26b. The spiral baffle 26b extends along the central axis 17 and spirals about the central axis 17 in the enlarged diameter portion 19 of the housing 16. Therefore, the spiral flow path 27 has a spiral shape by the spiral baffle 26b. Due to the spiral shape of the bent flow path 27, the residence time of the gas discharge 10 in the enlarged diameter portion 19 of the housing 16 is increased, whereby the gas discharge 10 due to the reactant mass 24 forming the spiral baffle 26b is formed. The capture and removal of contaminants is facilitated. In one example, the spiral baffle 26b comprises zinc. In another example, the spiral baffle 26b is made of a material other than zinc coated with zinc. In yet another example, the helical baffle 26b is mechanically driven to rotate about the central axis 17 within the enlarged portion 19 of the housing 16. By rotating the spiral baffle 26b, it is possible to artificially accelerate or decelerate the flow of the gas exhaust passing through the enlarged diameter portion 19 of the housing 16 according to the rotation direction of the spiral baffle. If the spiral baffle 26b becomes saturated during operation of the reverse venturi device 15, it may be replaced and / or cleaned as needed.

  As shown in FIGS. 7A and 7B, at least one obstruction element 26a-26j is a plurality of baffles 26c. Each baffle 26 c extends from the inner surface 68 of the enlarged diameter portion 19 of the housing 16 across the enlarged diameter portion 19 of the housing 16. The baffles 26c are spaced apart from each other along the central axis 17 and each baffle 26c has an orifice 28 that allows the flow of the gas exhaust 10 through the baffle 26c. Of course, any number of baffles 26c may be provided, including configurations having only a single baffle 26c. The size, shape, and number of orifices 28 in each baffle 26c can vary. For example, the baffle 26c may be screen-shaped and the orifices 28 may be provided between crosses of the screen. The orifice 28 in the baffle 26c restricts the flow of the gas exhaust 10 in the enlarged diameter portion 19 of the housing 16 and increases the residence time of the gas exhaust 10 in the enlarged diameter portion 19 of the housing 16. This facilitates the capture and removal of contaminants from gaseous effluent 10 by reactant mass 24 forming baffle 26c. In one example, the baffle 26c is made of zinc. In another example, the baffle 26c is made of a material other than zinc coated with zinc. If the baffle 26c becomes saturated during operation of the reverse venturi device 15, it may be replaced and / or cleaned as needed. In yet another example, the size of one orifice 28 of baffle 26c is different from the size of orifice 28 of adjacent baffle 26c. By using differently sized orifices 28 for different baffles 26c, the flow of the gas effluent 10 is accelerated and / or restricted, and the capture and removal of contaminants in the gas effluent 10 by the reactant mass in the baffle 26c. Promoted. Similarly, the baffles 26c need not be equally spaced within the enlarged chamber 21 and one orifice 28 of the baffle 26c is the same size, shape, or location as the orifice 28 of the adjacent baffle 26c. No need. By making the size, shape and position of these orifices 28 different from one baffle 26c to another baffle 26c and by making the interval between the baffles 26c different, the inside of the enlarged diameter portion 19 of the housing 16 can be improved. The residence time of the gaseous effluent 10 can be increased to facilitate increased physical and chemical capture along the reactant mass 24 and contact with the collection point.

  In the alternative configuration shown in FIGS. 8-11, at least one obstruction element 26a-26j may not be fixed to the housing 16 itself, but instead may be freely placed inside the enlarged portion 19 of the housing 16. It may be arranged. In such a configuration, at least one obstacle element 26a-26j may include various forms of obstacle media 26d-26j. As with the obstacle elements 26a-26c, the obstacle medium 26d-26j may be made of zinc or a material other than zinc coated with zinc. Zinc dissolves easily and complex shapes can be cast using conventional molding, waxing, centrifugation, and the like. Other forming methods include cutting, extrusion, sintering, stamping, hot forging and forming, laser cutting, and the like. Alternatively, a prototype may be made using steel and then coated or plated with zinc as a surface cover. The obstruction medium 26d-26j is used to completely fill the entire enlarged chamber 21, partially fill the enlarged chamber 21, or fill the space between the baffles 26c described above with reference to FIGS. 7A and 7B. It is possible.

  FIG. 8 shows a configuration in which at least one obstacle element 26 a-26 j is a plurality of pieces 26 d contained in the enlarged diameter portion 19 of the housing 16. According to this configuration, when the gas exhaust 10 moves along the enlarged diameter portion 19 of the housing 16 from the inlet 18 to the outlet 20 of the housing 16, the gas exhaust 10 is separated from the adjacent debris 26 d. Pass through the space between. For this purpose, the plurality of pieces 26 d may be irregular so that the pieces 26 d are loosely packed in the enlarged diameter portion 19 of the housing 16. As a non-limiting example, the plurality of pieces 26d may be made of mossy zinc. Modified zinc has a popcorn-shaped zinc structure and is manufactured by immersing molten zinc in a cooling liquid such as water. The resulting molten zinc droplets solidify into a relatively small, spherical structure with a very large surface area in volume ratio. In addition, the surface area of the resulting structure has a mossy surface texture. These structures can be manufactured to sizes for specific applications. By processing the steel, it is possible to produce a composite spherical structure of a steel plate similar to mozii zinc, which may be coated with zinc.

  By loosely filling the plurality of fragments 26 d in FIG. 8, the bent flow path 27 has a random shape, thereby increasing the residence time of the gas discharge 10 in the enlarged diameter portion 19 of the housing 16. Yes-. This facilitates the capture and removal of contaminants from the gaseous effluent 10 by the reactant mass 24 forming a plurality of debris 26d. If the plurality of fragments 26d in FIG. 8 become saturated during operation of the reverse venturi device 15, they may be replaced and / or cleaned as needed.

  In another configuration shown in FIG. 9, at least one obstruction element 26 a-26 j is a plurality of entangled threads 26 e housed in the enlarged diameter portion 19 of the housing 16. The plurality of entangled yarns 26 e form a thread-like body in the enlarged diameter portion 19 of the housing 16. In one possible configuration, the plurality of entangled threads 26e are folded and rolled like steel wool to form a mass having a very large surface area. The tangled yarn 26e itself may be of the same composition, thickness and length, or may be a combination of different compositions, thicknesses and / or lengths. In one example, the plurality of entangled yarns 26e comprise a zinc wire and are randomly entangled to form zinc wool. The zinc wool can be manufactured from various levels of wire density and / or size and can provide specific flow-limiting capabilities. In another example, the plurality of entangled threads 26e are made of steel wire and are randomly entangled to form steel wool. This steel wool may be coated with zinc. By loosely filling the plurality of entangled yarns 26 e in FIG. 9, the bent flow path 27 has a random shape, and thereby the residence time of the gas discharge 10 passing through the enlarged diameter portion 19 of the housing 16. Increase. This facilitates the capture and removal of contaminants in the gaseous effluent 10 by the reactant mass 24 forming the entangled yarn 26e. If the plurality of entangled yarns 26e become saturated during operation of the reverse venturi device 15, they may be replaced and / or cleaned as needed.

  Referring to FIG. 10, another configuration is shown in which at least one obstruction element 26a-26j is a filter element 26f. The filter element 26 f extends across the enlarged diameter portion 19 of the housing 16 with respect to the central axis 17. The filter element 26f is porous, and the holes in the filter element 26f allow the gas exhaust 10 to flow through the enlarged diameter portion 19 of the housing 16 from the inlet 18 to the outlet 20 of the housing 16. It can pass through the filter element 26f. This configuration of the filter element 26f, which may be made of sintered metal, causes the bent flow path 27 to have a random shape, thereby increasing the residence time of the gas exhaust 10 passing through the enlarged diameter portion 19 of the housing 16. This facilitates the capture and removal of contaminants in gaseous effluent 10 by reactant mass 24 forming filter element 26f. The sintered metal of the filter element 26f is preferably made of zinc or a non-zinc material coated with zinc. This filter element 26f may be replaced and / or cleaned as needed if it saturates during operation of the reverse venturi device 15.

  Referring to FIG. 11, as a combination of a plurality of baffles 26c shown in FIGS. 7A and 7B and a plurality of pieces 26g-26j having different sizes and similar to the plurality of pieces 26d shown in FIG. At least one obstacle element 26a-26j is shown. According to this other configuration, the plurality of baffles 26c and the plurality of pieces 26g-26j are arranged in the enlarged diameter portion 19 of the housing 16. 7A and 7B, the plurality of baffles 26c shown in FIG. 11 extend from the inner surface 68 of the enlarged diameter portion 19 of the housing 16 across the enlarged diameter portion 19 of the housing 16. Further, the plurality of baffles 26c are spaced apart from each other along the central axis 17 so that the baffle 26c divides the large-diameter chamber 21 into a plurality of sections. The orifices 28 in each baffle 26c allow the flow of gas exhaust 10 to pass through the baffles 26c. The plurality of pieces 26g-26j are arranged between the adjacent baffles 26c (that is, are arranged in the plurality of sections of the expanded chamber 21).

  As shown in FIGS. 11 and 12A to 12D, the reactant mass 24 is formed by the plurality of pieces 26g to 26j. The plurality of fragments 26g-26j are sized differently and grouped with those of the same size (i.e., fragments 26g, 26h, 26i, and 26j are grouped separately), May be separated by a baffle 26c. For example, the group of the pieces 26g-26j may be arranged such that the size of the pieces 26g-26j moves away from the entrance 18 of the housing 16 and becomes smaller as approaching the exit 20 of the housing 16. That is, the size of the debris 26g-26j of each group may be gradually changed so that the size of the gas discharge 10 in the entire flow direction in the enlarged diameter portion 19 of the housing 16 may be reduced. In one example, the pieces 26g-26j are made of zinc. For example, fragments 26g-26j can be formed by dropping molten zinc into a cooling liquid to create a popcorn-shaped structure having a very large surface area and a random mossy texture. In another example, different sized pieces 26g-26j may be mixed together and not separated based on size.

  FIGS. 13A-13C show some other shapes of obstruction elements 26k-26m as incompressible material, in addition to or in addition to the debris 26d and 26g-26j shown in FIGS. Can be used instead. FIG. 13A shows an example in which an obstacle 26k forms a reactant mass 24 and has an asterisk shape similar to “Jacks”, a children's toy. FIG. 13B shows another form of obstruction element 26k-26m forming a reactant mass 24 and disposed in the enlarged diameter portion 19, similar to the housings 16 and 26g-26j shown in FIGS. An example is shown where there are a plurality of crystal flakes 261 (only one is shown). The crystal flake 261 has a shape similar to a snowflake. FIG. 13C shows another form of obstacle element 26k-26m is a plurality of wire coils 26m (only one shown) forming a reactant mass 24 and housings 16 and 26g shown in FIGS. The example which may be arrange | positioned in the diameter expansion part 19 like -26j is shown. The obstacle 26k and the plurality of crystal flakes 261 may be made of zinc or a non-zinc material coated with zinc using, but not limited to, lost wax forging and 3D printing. Is also good. The plurality of wire coils 26m can be formed, for example, by winding a zinc wire around a mandrel core like a spring, and then making a cut along the entire length of the mandrel core around the coil of the wound wire, thereby forming a ring for each coil. May be made by obtaining The different shape obstacle elements 26k-26m may or may not be completely filled in the enlarged diameter chamber 21.

  The various obstacle elements 26a to 26k described above may be mixed to form various combinations. Examples of this mixed combination include one or more baffles 26a-26c shown in FIGS. 5, 6A, 6B, 7A and 7B, and a plurality of fragments 26d and 26g-26j shown in FIGS. And in combination. Another example of a combined combination includes combining the plurality of entangled yarns 26e shown in FIG. 9 with the plurality of pieces 26d and 26g-26j shown in FIGS. Other configurations combining the various obstruction elements 26a-26k described above with other filter elements such as activated carbon are also possible. Activated carbon, like a sponge, collects contaminants by surface contact. Therefore, a limited amount of activated carbon may be introduced into the enlarged diameter portion 19 of the housing 16 to act together with the various obstacle elements 26a to 26k described above. Preferably, the obstruction elements 26a-26k retain the activated carbon in the enlarged portion 19 of the housing 16 such that the activated carbon is relatively statically disposed throughout the enlarged chamber 21. This configuration is the opposite of a conventional emission control system that releases activated carbon into the stream of gaseous emissions 10. Since the activated carbon does not flow freely with the gas emission, it is possible to use the activated carbon more efficiently. One skilled in the art will appreciate that the disclosed example of a reverse venturi device 15 is merely exemplary and that many combinations beyond the several examples disclosed herein are possible and desirable to accommodate a particular application. That will be easy to understand.

  Referring to FIG. 14, another exemplary inverted Venturi device 15 'is shown having two enlarged diameter portions 19, 19' connected in series by a conduit 38. One enlarged portion 19 of the housing 16 extends between the inlet 18 of the housing 16 and the conduit 38, and the other enlarged portion 19 ′ extends between the conduit 38 and the outlet 20 of the housing 16. Extend. Therefore, the bent channel 27 of the gas discharge 10 is extended. According to this configuration, the gas effluent 10 is sent from the enlarged portion 19 through the conduit 38 to the enlarged portion 19 ′, where additional contaminants are collected and / or captured. The present disclosure is not limited to using only one or two enlarged diameter portions 19, 19 'in series. This is because in some applications with large emissions and / or high levels of contaminants, it may be necessary to connect a number of expansions in series.

  Referring to FIG. 15, another exemplary inverted Venturi device 15 '' with two enlarged diameter portions 19, 19 '' connected in parallel is shown. A three-way inlet valve 39 controls the flow of gaseous effluent 10 and causes gaseous effluent 10 to flow into conduit 41 or conduit 42. The three-way outlet valve 40 allows the gaseous effluent 10 to flow out of the conduit 41 or 42 without direct backflow from the conduit 41 to the conduit 42 or directly from the conduit 42 to the conduit 41. When the gas discharge 10 is sent from the conduit 41, the gas discharge 10 flows into the enlarged diameter portion 19 from the inlet 18 and flows out from the outlet 20. The gas effluent 10 flows from the inlet 18 ″ into the enlarged diameter portion 19 ″ and out of the outlet 20 ″ when the gas effluent 10 is sent from the conduit 42. One of the advantages of this reverse venturi device 15 ″ shown in FIG. 15 is that one of the enlarged diameter portions 19, 19 ″ can maintain the operation, so that the maintenance is performed on one of the enlarged diameter portions 19, 19 ″. In the event that repair or cleaning becomes necessary, it can be isolated and taken offline without shutting down the entire system.

  Over time, the chemical reaction and / or physical entrapment of contaminants that occur on the outer reaction surface 25 of the reactant mass 24 can cause the reactant mass 24 to reach a saturation point and reduce the efficiency of the reverse venturi apparatus 15 There is. Thus, in the configuration shown in FIG. 15, by removing and replacing and / or cleaning the reactant mass 24 in the enlarged portions 19, 19 '' of the housing 16, the reverse venturi device is not completely shut down. Can be restored to the efficiency before saturation.

  The process of removing contaminants from the saturated reactant mass depends on the specific contaminant type and the type of amalgam forming metal used. Access to the enlarged diameter chambers 21 and 21 ″ arranged inside the enlarged diameter portions 19 and 19 ″ of the housing 16 depends on the type of obstacle used. When relatively small, uncompressed obstructions are used, pouring and / or draining access is required. If the obstacle is a relatively large block, plate, baffle or assembly, proper lifting and handling methods and access are required.

  Still referring to FIG. 15, the reverse venturi device 15 may include one or more spray nozzles 81 that communicate with the enlarged diameter portions 19 and 19 ″ of the housing 16 via fluid. The spray nozzle 81 is arranged at a position for injecting deoxygenated acid onto the reactant mass 24 in the enlarged diameter portions 19 and 19 ″ of the housing 16. In operation, the oxygen scavenger flushes contaminants from the reactant mass 24 to activate the reactant mass 24. Alternatively, the drain 82 is communicated with the enlarged diameter portions 19, 19 '' of the housing 16 via a fluid, and the used oxygen absorber and contaminants are discharged from the enlarged diameter portions 19, 19 '' of the housing 16. May be. Saturated zinc, whether it is coated on steel or a solid zinc structure, is preferred in that it can be recycled and reused. Thus, the materials used in the obstacle are reusable. In addition, many of the trapped contaminants, especially heavy metals such as mercury, can be reused for lighting and chlorine production.

  Referring to FIG. 16, another exemplary inverted venturi apparatus 15 is shown wherein the expanding chamber 45 has a significantly greater volume as compared to the volume of the inlet conduit 43 and the outlet conduit 44. The enlarged diameter portion 46 may provide an enlarged tortuous channel 77 for gas exhaust flowing through the enlarged diameter portion 46 so as to be circular, square, triangular, elliptical, or virtually any number of shapes desired. (A rectangular shape is shown).

  Referring to FIG. 17, a block diagram of a typical gas emission control system is shown. The gas exhaust is introduced from a furnace 47 into an electrostatic precipitator (ESP) 48, a fluidized gas desulfurization (FGD) unit 49, and a fiber filter (FF) unit 50, and then discharged to the atmosphere via a chimney 51. Is done. A first contaminant concentrate 52 is removed from the gaseous effluent at ESP 48. Similarly, a second contaminant concentrate 53 is removed from the gaseous effluent in the FGD unit 49. The second concentrate 53 produced by the FGD unit 49 often contains mercury and other heavy metals and usually flows into wastewater. The third contaminant concentrate 54 is removed from the gaseous effluent in the FF unit 50.

  Referring to FIGS. 18A and 18B, the block diagram of FIG. 17 is modified in that an adsorbent injection point is introduced and the gas exhaust is provided with an additional step of passing through the reverse venturi apparatus 15 described above. I have. In FIG. 18A, a first sorbent introduction point 55 is shown between the furnace 47 and the ESP. Alternatively, in FIG. 18B, the second adsorbent introduction point 56 is shown between the FGD unit 49 and the FF unit 50. Which option is deemed most preferred for the adsorbent depends on existing structures and plant conditions. In addition to the two options shown in FIGS. 18A and 18B, there are many other entry points or combinations of entry points into which the adsorbent can be introduced, and thus these two options are shown for illustrative purposes. The reverse venturi device 15 in FIGS. 18A and 18B is arranged downstream of the FF unit 50 and upstream of the chimney 51. The reverse venturi device 15 may be configured according to any of the above-described examples as being suitable for various uses. Eventually, the final gas emissions exiting the reverse venturi device 15 and into the atmosphere through the chimney 51 will be able to meet and exceed current and future EPA emission rules and regulations.

  The method shown in FIGS. 18A and 18B involves burning fuel in a furnace 47 to generate a gaseous effluent containing pollutants, flowing the gaseous effluent from the furnace 47 into an ESP 48 and using the ESP 48 to evacuate the gas. Removing the first partial particulate contaminants in the material. Using the ESP 48 to remove the first partial particulate contaminant in the gaseous effluent forms a first concentrate 52 including a first portion of the particulate contaminant removed from the gaseous effluent by the ESP 48. In operation, ESP 48 uses the applied electrostatic charge to remove fine contaminants from gaseous emissions. The method also includes introducing the gaseous effluent from the ESP 48 to the FGD unit 49 and using the FGD unit 49 to remove sulfur dioxide contaminants in the gaseous effluent. The step of removing sulfur dioxide contaminants in the gaseous effluent using the FGD unit 49 forms a second concentrate 53 containing sulfur dioxide contaminants removed from the gaseous effluent by the FGD unit 49. The method further includes introducing the gaseous effluent from the FGD unit 49 into an FF unit 50 (ie, a baghouse) and using the FF unit 50 to remove a second portion of particulate contaminants in the gaseous effluent. including. Removing the second portion of the particulate contaminants in the gaseous effluent by using the FF unit 50, the third concentration including the second portion of the particulate contaminants removed from the gaseous effluent by the FF unit 50 The object 54 is formed. In operation, contaminant particles are removed from the gas exhaust as it passes through one or more fiber filters (not shown) of the FF unit 50.

  According to the present disclosure, the method further includes sending the gaseous effluent from the FF unit 50 to the reverse Venturi apparatus 15 and using the reverse Venturi apparatus 15 to remove heavy metal contaminants in the gaseous effluent. The process of removing heavy metal contaminants in the gaseous effluent using the reverse Venturi apparatus 15 causes the gaseous effluent to pass (ie, flow over) the reactant mass located within the reverse Venturi apparatus 15. The amalgam forming metal in the reactant mass chemically bonds with heavy metal contaminants in the gaseous effluent. Thus, as the heavy metal contaminants combine with the amalgam forming metal in the reactant mass, the reactant mass traps heavy metal contaminants in the reverse venturi apparatus 15. In this method, the gas exhaust from the reverse venturi device 15 is further sent to a chimney 51 which discharges the gas exhaust to the surrounding atmosphere. The reverse venturi device 15 has a relatively small footprint and can be easily installed in harmony between the emission control devices 48, 49, 50 of existing systems and the chimney 51 to the atmosphere. This is advantageous.

  The method may include injecting the sorbent into the gaseous effluent. According to this step, as shown in FIG. 18A, the sorbent may be injected into the gaseous effluent at a first sorbent introduction point 55 located between the furnace 47 and the ESP. Alternatively, as shown in FIG. 18B, the adsorbent may be injected into the gaseous effluent at a second adsorbent introduction point 56 located between the FGD unit 49 and the FF unit 50. The sorbent comprises an amalgam-forming metal and combines with at least some of the heavy metal contaminants in the gaseous effluent before entering the reverse venturi apparatus 15. By injecting the sorbent into the gaseous effluent at the first sorbent entry point 55 or the second sorbent entry point 56, more mercury, heavy metal, and acid gases are brought to a previously unattainable level. The data can be collected in the FF unit 50. As described above, the amalgam-forming metal may be selected from the group consisting of zinc, iron, and aluminum, and the adsorbent may be, for example, a CZTS compound. The sorbent can be regenerated and activated so that hazardous pollutants can be collected and recycled.

  Referring to FIG. 19, a block diagram of a typical non-gas emission control system is shown. The liquid and / or liquid effluent is sent to a lime treatment unit 60 from a fluidized gas desulfurization (FGD) unit 59 and / or a wet gas scrubbing unit 58 before being sent to a settling basin 61. After a suitable time, this non-gaseous effluent is sent from the sedimentation basin 61 into a dry waste preparation / treatment system or dewatering system 62. Non-gas emissions sent through the treatment of dry waste 64 are prepared for disposal in a dump 65. Optionally, the non-gaseous effluent sent through the dewatering system 62 with the recirculation system is prepared for use in a secondary industrial process 63 that may include, for example, gypsum and / or cement production. Non-gas emissions that have not been sent from the settling basin 61 to a process for dehydration system 62 or drying waste 64 are sent to drain through a drain 66. The final non-gas emissions discharged into this drain 66 are not as regulated as they would be in the years to come. The proposed EPA water emission rules and regulations are very restrictive compared to the current discharges that can be discharged into drains. Industries that need to discharge contaminated liquid effluent into drains have current emission control technology, but this is substantially unlikely to meet and / or comply with upcoming EPA regulations.

  Referring to FIG. 20, the block diagram of FIG. 19 is modified by one or more processing tanks 67 containing the above-mentioned adsorbent. After the non-gas emissions are sent from the sedimentation basin 61 and before they are discharged to the drain 66, a treatment tank 67 is arranged. The method shown in FIG. 20 collects non-gas emissions containing pollutants and passes the non-gas emissions through an FGD unit 59 and / or a wet gas scrubber 58 to remove one of the contaminants in the non-gas emissions. The non-gas discharge from the FGD unit 59 and / or the wet gas cleaning device 58 is sent to the lime treatment unit 60, and the non-gas discharge is passed through the lime treatment unit 60, and the non-gas discharge is performed by the Clark method. A step of softening the non-gas emissions. In operation, the lime treatment unit 60 removes certain ions (eg, calcium (Ca) and magnesium (Mg)) from non-gas emissions by settling. This method sends the non-gaseous effluent from the lime treatment unit 60 to the sedimentation basin 61 and sediments and removes some of the contaminants in the non-gaseous effluent. Part of the degassed water is used in the secondary industrial process 63 to remove the second part of the non-gaseous effluent from the sedimentation basin 61, and to dry-dispose this second part of the non-gaseous effluent. 64 is also included. In the step of dewatering a first portion of the non-gaseous effluent in the settling basin and utilizing the dewatered by-product in the secondary industrial process 63, the dewatering step includes recycling the first portion of the non-gaseous effluent. Alternatively, the secondary industrial process 63 may include, for example, a gypsum or cement manufacturing process. In the step of removing a second portion of the non-gas effluent from the settling basin 61 and adding a dry waste treatment 64 to the second portion of the non-gas effluent, the dry waste treatment 64 comprises a second portion of the non-gas effluent. May be included in the waste dump 65.

  In the present disclosure, the method further includes the step of directing a third portion of the non-gas effluent in the settling basin 61 to a treatment tank 67 containing the disclosed adsorbent. The sorbent contains amalgam-forming metals that combine with heavy metal contaminants in non-gas emissions. Thus, the adsorbent traps heavy metal contaminants in the treatment tank 67 as the heavy metal contaminants combine with the adsorbent and precipitate / precipitate from the non-gas effluent. In this method, the non-gas emission may then be sent from the treatment tank 67 to the drain 66 for discharge. The treatment tank 67 may be designed such that non-gas emissions (ie, wastewater streams) can flow out of the treatment tank 67 continuously.

  Several exemplary embodiments are disclosed with respect to the sorbents disclosed herein. These illustrative embodiments are merely examples, and do not represent an exhaustive list of possible variations on the subject.

  As mentioned above, one exemplary adsorbent is elemental zinc powder. Zinc powder is composed of zinc element. Zinc may be used as a powder or as granules. At elevated temperatures, one of the methods used to extend the useful life of zinc powder and / or granules used for any gaseous emissions and to reduce and / or prevent pre-oxidation is to use the granules and / or powders. Is mixed with a solid acid such as sulfamic acid, citric acid and other organic acids, or coated with a solid acid. This powder / acid mixture may be injected into a gaseous effluent (eg, a flue gas stream) and / or placed in a suitable embodiment of the reverse venturi apparatus 15.

  The optimal particle size of the zinc powder ranges from 0.5 nanometers to 7,500 microns. In addition, powder mixtures having different size particle size ranges have proven to be advantageous, especially when the particle size range is from 0.5 nanometers to 7,500 microns. Similarly, the optimal particle size of the zinc granules ranges from 7,500 microns to 3.0 inches. In addition, granule mixtures having different size particle size ranges have been found to be advantageous, especially when the particle size range is 7,500 microns to 3.0 inches.

  In another exemplary embodiment, the sorbent is CZTS, which has the molecular formula Cu2ZnSnS4. CZTS may consist of other phases of copper, zinc, tin and sulfur, which is also advantageous. The CZTS and / or related phases copper, zinc, tin and sulfur may be mixed in stoichiometric proportions, followed by a mechanochemical compounding in a mill. Further, the CZTS may be mixed with either the same proportions of clay, such as bentonite or zeolite, and calcium hydroxide (CaOH). The optimal particle size of the CZTS powder ranges from 0.5 nanometer to 7,500 microns. During testing and development, CZTS powder mixtures having different size ranges have been found to be advantageous, especially when the size range is from 0.5 nanometers to 7,500 microns. For applications where special CZTS granules are preferred, the optimal particle size has been found to be in the range of 7500 microns to 3.0 inches. In addition, CZTS granule mixtures having different size ranges have been found to be advantageous, especially where the size range is from 7,500 microns to 3.0 inches.

  For most contaminants, CZTS has the smallest particle size within the above ranges and is most efficient when the metal phase CZTS is present in large amounts. During the production of CZTS, copper, zinc, tin, and sulfur are not completely converted to CZTS, but become a mixture of each phase (for example, damba ore (CuZn2) and tin sulfide (SnS)).

  In one exemplary method of making CZTS, copper, zinc, tin, and sulfur are added to the grinder, in no particular order. The milling step is accomplished using a ball mill or some type of friction mill, or by a combination of mills that are used sequentially to achieve the desired particle size. Exemplary particle sizes range from 325 standard mesh screen to 100 standard mesh screen (1 standard mesh screen = 7500 microns). The particles obtained are further weighed to a predetermined molar ratio of copper: zinc: tin: sulfur = 1.7: 1.2: 1.0: 4.0. After ascertaining the mesh size and molar ratio, these particles are ground and mechanochemically incorporated into the CZTS and other phases. The milling time is controlled so as to show optimum characteristics depending on the specific application. The pulverization step is performed in an inert gas atmosphere, a wet pulverization step in which a suitable solvent such as glycol ether, ethylene glycol, ammonia or other alcohol is added, or a dry pulverization step performed in an inert gas atmosphere. It can be performed using:

  During the milling process, sampling is performed intermittently to determine the particle size using a particle size analyzer, SEM, XRD, or to determine the phase transformation ratio using the Raman method. The ball diameter of the grinder is important and tests show that it is optimized when the ball-to-powder weight ratio (charge ratio) is at least 5: 1. . Most preferably, the grinding balls are made of a material that achieves size and / or phase transformation without contaminating steel, ceramics, zirconia or other end products. If wet milling is employed, the CZTS is dried. The CZTS is then mixed using a ribbon blender, V-blender or other suitable mixer to evenly mix the bentonite or zeolite and calcium hydroxide.

  According to the method described above, the sorbent is introduced into the gaseous effluent at a temperature of about 750 ° F. or less. The sorbent is introduced into the gaseous effluent by any of a number of methods, including but not limited to injection, fluidized beds, coated filters and traps. The introduction method can be selected based on existing emission control systems in the plant to facilitate installation. One convenient method is to inject CZTS into gaseous emissions instead of activated carbon, and the same injection equipment can be used with or without modification.

  In some applications, the treatment of gaseous emissions is optimized when CZTS is mixed with bentonite to effectively remove contaminants. Alternatively, the treatment of non-gaseous emissions is optimized when CZTS is mixed with zeolite. In addition to the particular materials that are mixed with the CZTS, the proportions of the mixture may be application specific to provide optimal contaminant removal capabilities.

  As shown in FIGS. 18A and 18B, when CZTS is used for gaseous emission treatment, the fiber filter unit 50 is disposed downstream of the CZTS introduction points 55 and 56 so that the fiber filter unit 50 captures adsorbent particles. Increase the contact time between the gaseous effluent and the adsorbent. Depositing the adsorbent on the fiber filters (ie, bugs) of the fiber filter unit 50 allows for longer contact between the gaseous effluent and the adsorbent, and also allows the adsorbent to be collected and subsequently regenerated. Can be. The small particle size of the adsorbent allows the adsorbent to be sent along the flow of the gaseous effluent so that dust is carried by the wind. During the period in which the sorbent is carried in the gaseous effluent stream, the sorbent comes into contact with the contaminants moving in the gaseous effluent stream, thereby causing the contaminants to chemically react and bind with the sorbent become. Upon reaching the fibrous filter unit 50, the gaseous effluent continues to pass through the filter in the fibrous filter unit 50, while the combined adsorbent and contaminant particles are too large to pass through the filter. If the CZTS particles are less than 10 microns, the filters in the fiber filter unit 50 are pre-coated with larger CZTS particles, activated carbon, talc, lime or other suitable material to prevent smaller CZTS particles from passing through the filter. May need to be done. Alternatively, a filter having a smaller micron size may be used for the fiber filter unit 50.

  In other applications for non-gas emissions, the CZTS may be introduced into the processing tank 67 shown in FIG. In this configuration, the CZTS is preferably introduced into the treatment tank 67 and agitated well for a period of time, after which pH adjustment, coagulation, and filtration are added to the non-gas effluent (eg, wastewater) prior to discharge. Thereafter, the CZTS in the processing tank 67 may be subjected to a regeneration step for removing contaminants from the CZTS. Spent CZTS can be regenerated by filtering mercury from CZTS or by vacuum distillation. The resulting pollutants can then be used in other industries. CZTS also offers the advantage that nitrate and nitride levels in non-gas emissions can be reduced.

  Drainage regulations enacted by the EPA in 2016 are much more stringent than those for air. Some of the current EPA regulations listed in units of nanograms / liter (ng / L), micrograms / liter (μg / L), and / or grams / L are as follows: Mercury 119 ng / l; arsenic (As) 8 μg / l; selenium (Se) 10 μg / l; nitrogen dioxide (NO2) and nitrate (NO3) 0.13 g / l. Other heavy metals, such as lead (Pb) and cadmium (Cd), are also included in the proposed EPA regulatory level. In many existing plants, wastewater with a pollution level that exceeds acceptable emission regulations is sent to ponds and / or some other type of sludge reservoir. CZTS can treat solids in the same manner as non-gaseous effluents disclosed herein in a ponds. Depending on the ionic form, sludge composition and / or pH of the heavy metal, the contact time of the CZTS in the ponds can be adjusted appropriately. Sufficient pH adjustment, coagulation, and subsequent filtration allow for normal discharge, disposal and / or use in other industries, none of which was previously possible.

  It should be noted that the adsorbent disclosed herein does not contain any free carbon, including activated carbon currently used in the art. As a result, any metal sulfide formed as a by-product of the disclosed method is not filtered. Therefore, these by-products have high industrial value in gypsum wallboard and cement applications. The metal sulfide filtration test of EPA is known and its use in these products is well documented.

  Although activated carbon is available in some alternative configurations, the limited use of activated carbon in these variants does not allow the activated carbon to escape into the effluent. For example, in one example, the activated carbon is embedded in the filter of the fiber filter unit 50. This activated carbon does not escape freely into the gaseous emission stream. Another limited use of activated carbon is to coat CZTS in crystalline form with activated carbon to produce CZTS having a carbon thin film thickness of 1.0 nanometer or less. This facilitates the capture of very small mercury metal vapor particles. Similarly, crystalline CZTS can be coated with nanometer-like zeolite films or other coatings to target specific hazardous contaminants for specific applications. Again, the activated carbon in this example does not leak freely into the gaseous effluent stream. In another configuration, shown in FIG. 33, the reverse venturi fluidized bed apparatus cleans the adsorbent as a series of adsorbent recycling subsystems for CZTS adsorbents, CZTS alloy adsorbents, and / or carbon-based adsorbents. Equipped with equipment for recycling.

  Referring to FIG. 21, graphically the percentage of contaminants removed from the effluent by known emission control systems and the percentage of contaminants removed by the reverse venturi apparatus and method disclosed herein. . The EPA currently defines a 90% pollutant level 78 for gaseous emissions. Existing emission control systems 79 are effective at removing 88% to 90% of hazardous pollutants. However, the EPA has raised the required minimum pollutant removal rate for several years, many existing emission control systems have failed to meet this requirement, and many other existing emission control systems have It can only meet the requirements when operating at the maximum removal capacity available under current technology.

  Still referring to FIG. 21, an exemplary emissions control system 80 is disclosed herein, or a novel emissions control system based on the reverse venturi apparatus, adsorbent and / or method disclosed herein, or disclosed herein. It may be any of the existing emission control systems modified and reinforced by including a reverse venturi device, adsorbent and / or method. Tests have shown that this exemplary emission control system 80 is capable and capable of removing at least 98% of hazardous pollutants well above current EPA regulatory levels.

  In the exemplary emission control method shown in FIGS. 22 and 24, a contaminated gas source 150 is introduced into the system via one or more pre-fluidized bed filters 151 and a fluidized bed 152, one or more post-fluidized The gaseous effluent is discharged through the chimney 155 through the floor filter 153, via the system discharge 154, in an environmentally controlled manner. It is not necessary to first pass the contaminated gas source 150 through one or more pre-fluidized bed filters 151. However, depending on the particular application, one or more pre-fluidized bed filters 151 may be required.

  The fluidized bed 152 has an inverted Venturi shape, and a specific ratio of the length L to the diameter D is 2.9: 1 at the minimum and 9.8: 1 at the maximum. This ratio is optimized to allow the contaminated gas source 150 to stay longer in the fluidized bed 152 filled with a special adsorbent such as the reactant 164. Reactant 164 is an adsorbent comprising a copper, zinc, tin, sulfur (CZTS) compound and / or an alloy thereof. An example of a preferred ratio of the length L of the fluidized bed 152 to the diameter D is 4.4: 1, which is determined through trial and error.

  Preferably, fluidized bed 152 has a substantially circular cross section. Although not shown in FIG. 24, the fluidized bed 152 may include one or more of the various baffles disclosed herein and / or other special purpose flow restricting obstructions. Fluidized bed 152 has generally outwardly extending convex ends 168 and 169 to facilitate extended residence time while minimizing turbulence through reactant 164. As the flow of the contaminated gas source 150 flows into the fluidized bed 152 at the inlet 165, intimate contact with the reactants 164 is initiated, creating a random non-turbulent flow 166. The random non-turbulent flow 166 backflows to its side by the generally outwardly extending convex ends 168 and 169, thereby causing the non-turbulent flow 166 to exit the fluidized bed 152 through the outlet hole 167 in the fluidized bed 152. The residence time is extended. The reactants 164 that promote the non-turbulent flow 166 form a random tortuous path of the contaminated gas source 150. Note that the length L of the fluidized bed 152 does not include the lengths of the convex ends 168 and 169.

  Fluidized bed 152 has side outlet holes 170 leading to sorbent washing station 156. The sorbent cleaning station 156 is capable of removing spent sorbent 157 from the system for disposal. In addition, contaminants 158 captured by reactant 164 from contaminant gas source 150 and separated from reactant 164 at sorbent cleaning station 156 can be discarded and / or recycled. The sorbent washing station 156 returns the washed reactants 164 to the fluidized bed 152 via the sorbent return port 159. The bulk refill adsorbent container 168 supplies a replenisher of reactant 164 to replace the adsorbent 157 that has been removed and depleted as needed. From the system discharge 154, gaseous emissions are obtained from the exhaust chimney 155 in an environmentally controlled manner. A mechanism for further discharging the trapped waste 160 may be provided as an additional adsorbent recycling subsystem (FIG. 33).

  In the exemplary emission control method shown in FIGS. 23 and 24, a contaminated non-gas source 161 is introduced into the system via one or more pre-fluidized bed filters 151 and a fluidized bed 152, one or more posts. Non-gaseous emissions are discharged through a fluidized bed filter 153, through a system discharge 154, and through an environmentally controlled discharge 162. It is not necessary that the contaminated non-gas source 161 first pass through one or more pre-fluidized bed filters 151. However, depending on the particular application, one or more pre-fluidized bed filters 151 may be required.

  The fluidized bed 152 has an inverted Venturi shape, and a specific ratio of the length L to the diameter D is 2.9: 1 at the minimum and 9.8: 1 at the maximum. This ratio has been optimized to allow the contaminated non-gas source 161 to stay longer in the fluidized bed 152 packed with a special adsorbent such as reactant 164. Reactant 164 is an adsorbent comprising a copper, zinc, tin, sulfur (CZTS) compound and / or an alloy thereof. An example of a preferred ratio of the length L of the fluidized bed 152 to the diameter D is 4.4: 1, which is determined through trial and error.

  Fluidized bed 152 preferably has generally outwardly extending convex ends 168 and 169 to promote extended residence time while minimizing turbulence through reactant 164. As the flow of the contaminated non-gas source 161 flows into the fluidized bed 152 at the inlet 165, intimate contact with the reactants 164 is initiated, creating a random non-turbulent flow 166. The random non-turbulent flow 166 backflows to its side by the generally outwardly extending convex ends 168 and 169, thereby increasing the residence time in the fluidized bed 152 before exiting the fluidized bed 152 from the outlet hole 167. You. The reactants 164 that promote the non-turbulent flow 166 form a random tortuous channel of the contaminated non-gas source 161. Note that the length L of the fluidized bed 152 does not include the lengths of the convex ends 168 and 169.

  Preferably, fluidized bed 152 has a substantially circular cross section. Although not shown in FIG. 24, fluidized bed 152 may include one or more of the various baffles and / or special purpose flow restricting obstructions disclosed herein. Fluidized bed 152 has side outlet holes 170 leading to sorbent washing station 156. The sorbent cleaning station 156 is capable of removing spent sorbent 157 from the system for disposal. In addition, the contaminants 158 captured by the reactants 164 from the contaminated non-gas source 161 and separated from the reactants 164 at the sorbent cleaning station 156 can be discarded and / or recycled. The sorbent washing station 156 returns the washed reactants 164 to the fluidized bed 152 via the sorbent return port 159. The bulk refill adsorbent container 168 supplies a replenisher of reactant 164 to replace the adsorbent 157 that has been removed and depleted as needed. From system exhaust 154, non-gas emissions are obtained that are emitted by environmentally controlled emissions 162. An additional discharge for the trapped waste 163 is also provided.

  FIG. 25 shows that gaseous effluent 250 passes through one or more pre-filters 251, fluidized beds 253, one or more post-filters 255, system exhaust 256, and ultimately from exhaust chimney 257, and / or exhaust 5 illustrates an exemplary method of controlling and discharging as a discharged gaseous emission through a disposal process 262. Fluidized bed 253 is bisected by longitudinal surface 290. The inflow hole P3 and the outlet hole P4 are configured such that when the fluidized bed 253 is aligned with the longitudinal surface 290, the gaseous emission flows in and out. Obstructions (not shown) inside the fluidized bed 253 form a suitable tortuous flow path, which is particularly suitable when gaseous effluent flows in through the inlet port P3 and exits through the outlet port P4. Is done. The inflow hole P3 and the outlet hole P4 are arranged above the longitudinal surface 290 of the fluidized bed 253.

  As shown in FIG. 25, the fluidized bed 253 can be mounted on a truck 254, and is configured to incline the fluidized bed 253 about a rotation axis 252. As the gaseous effluent is treated in the fluidized bed 253, the longitudinal surface 290 of the fluidized bed 253 is substantially horizontal. The adsorbent washing station 258 communicates with the outlet P5 of the fluidized bed 253, where contaminant particles trapped by the adsorbent are removed. The removed contaminants can be recycled or discarded by station 261. The spent sorbent is discarded by the station 259, and the washed sorbent is recycled and returned to the fluidized bed 253 from the sorbent return port 260 through the return port P6.

  FIG. 26 shows that contaminated non-gas emissions 295 are passed through one or more pre-filters 251, fluidized beds 253, one or more post-filters 255, and a system discharge 256, ultimately environmentally controlled. An exemplary method of discharging as a non-gas discharge 273 and / or via a waste disposal process 274 is shown. The inflow hole P2 and the outlet hole P1 are configured so that the non-gaseous exhaust flows in and out. Obstructions (not shown) inside the fluidized bed 253 form a suitable tortuous flow path, particularly suitable when non-gas emissions are introduced through the inlet P2 and the outlet P1. Inlet hole P2 and outlet hole P1 are bisected by longitudinal surface 290 of fluidized bed 253 (ie, aligned with longitudinal surface 290 of fluidized bed 253).

  As the non-gaseous effluent is processed in the fluidized bed 253, the longitudinal surface 290 of the fluidized bed 253 is substantially vertical. The adsorbent washing station 258 communicates with the outlet P5 of the fluidized bed 253, where contaminant particles trapped by the adsorbent are removed. The removed contaminants can be recycled or discarded by station 261. The spent sorbent is discarded by the station 259, and the washed sorbent is recycled and returned to the fluidized bed 253 from the sorbent return port 260 through the return port P6.

  FIG. 27 shows a table comparing the disclosed preferred reactive CZTS alloy adsorbent 341 with other adsorbents including activated carbon 342 and zeolite 343. Pollutants 367 include the main types including nitrogen 368, phosphorus 369, heavy metals 370, sulfur 371, mercury 372, and selenate 373. Contaminants 367 are also listed with each adsorbent tabulated comparing gaseous emissions 344, 346, and 348 with non-gases emissions 345, 347, and 349.

  Tests have shown that the reactive CZTS alloy adsorbent 341 is effective in capturing and removing contaminants 367 in gaseous effluent 344 and / or non-gaseous effluent 345. In contrast, activated carbon 342 is not effective at trapping and removing contaminants 367 in gaseous effluent 346 and / or non-gaseous effluent 347. Similarly, zeolite 343 is not effective in trapping and removing contaminants 367 in gaseous emissions 348 and / or non-gaseous emissions 349.

  FIG. 28 shows an expanded list of adsorbents including other adsorbents including reactive CZTS alloy adsorbent 351 and corrosive 350, ferric oxide 355, and zeolite 356 of the present disclosure. Reactive CZTS alloy adsorbent 351 includes CZTS sulfur alloy 352, CZTS selenate alloy 353, and ferrous oxide CZTS alloy 354. The CZTS alloy adsorbent 351 reacts effectively with all of the following contaminants: Selenate 357, fully ionized sulfur 358, fully ionized nitrogen 359, and fully ionized phosphorus 360. Reactive CZTS alloy adsorbent 351 can capture and remove these contaminants from both gaseous and non-gaseous emissions.

  In contrast, caustic 350 is only effective against fully ionized sulfur 358. Ferric oxide 355 is only effective against selenate 357 and has very slow reaction characteristics with complete nitrogen 359 and fully ionized phosphorus 360 (and acts only on non-gaseous emissions) . Zeolite 356 is only effective against fully ionized nitrogen 359 and fully ionized phosphorus 360. Thus, known adsorbents, such as corrosive 350, ferric oxide 355, and zeolite 356, have limited effective properties compared to the broader properties of the reactive CZTS alloy adsorbent 351 disclosed herein. Having. Even if the known sorbents have a certain level of effectiveness, they are all lower than the effective levels of the reactive CZTS alloy sorbent 351 disclosed herein.

  In FIG. 29, table 364 is post-treated after being used in an emissions control system that captures and removes pollutants 367, including nitrogen 368, phosphorus 369, heavy metals 370, sulfur 371, mercury 372, and selenate 373. 5 shows the performance of a prior art adsorbent 365. The ability to separate contaminants 367 from prior art sorbents in gaseous effluent 374 and / or non-gaseous effluent 375 is very low and virtually absent except for nitrogen 368 in gaseous effluent 374. Similarly, Table 364 shows that the recycle capacity of prior art sorbent 366 after separation of contaminants 367 is virtually absent, except for gaseous effluent 376 containing nitrogen 368.

  In FIG. 30, Table 378 is post-treated after being used in an emissions control system that captures and removes pollutants 367 including nitrogen 368, phosphorus 369, heavy metals 370, sulfur 371, mercury 372, and selenate 373. 4 illustrates the ability of the reactive CZTS alloy sorbent 339 disclosed herein to be effective. It is particularly advantageous that contaminants 367 in gaseous effluent 374 and / or non-gaseous effluent 375 can be separated from the disclosed reactive CZTS alloy adsorbent 339. This means that the contaminants 367 can be more easily disposed of or recycled, and because the reactive CZTS alloy sorbent 339 can be reused in the emission control system (shown in Table 378). It is. Specifically, Table 378 shows that the reactive CZTS alloy sorbent 340 disclosed herein can be reused after being separated from contaminants 367 in gaseous emissions 376 and non-gaseous emissions 377.

  In FIG. 31, a block diagram illustrates a system and method for removing contaminants from a gaseous effluent 250. The gas effluent 250 is monitored and analyzed at step 379 to determine the type and level of contaminants in the gas effluent 250. The monitoring may be a systematic intermittent sampling at regular intervals, or a continuous in-line monitoring and analysis. Based on the type and / or level of contaminants present in the gaseous effluent 250 as determined by step 379, the flow of effluent may be such that the gaseous effluent 250 has an appropriate pre-filter 381, 382, 383, and / or 384. Through the pre-filter inlet manifold 380 to be further directed to Suitable prefilters 381, 382, 383, and / or 384 are selected by the selection method shown in FIG.

  The pre-filter shown in FIG. 31 is filled with the reactive CZTS alloy adsorbent 351 shown in FIG. For example, the prefilter 381 is filled with a sulfur CZTS alloy 352 shown in FIG. The pre-filter 382 is filled with a selenate CZTS alloy 353 shown in FIG. The pre-filter 383 is filled with a ferrous oxide CZTS alloy 354 shown in FIG. The pre-filter 384 is filled with a combination of CZTS alloy adsorbents 352, 353 and / or 354. Additional loaded with different combinations of CZTS alloy adsorbents 352, 353, and / or 354, combined to effectively treat specific levels and / or types of contaminants contained in gaseous emissions 250 May be added to the pre-filter inlet manifold 380.

  After the contaminated gas effluent 250 is sent to a suitable prefilter, the prefilter effluent manifold 385 sends the effluent to a fluidized bed 253. As for the gas discharge 250, the housing of the fluidized bed 253 is arranged in a direction substantially parallel to the gantry 271. The contaminants are separated from the sorbent in step 258 and returned to fluidized bed 253 through sorbent return port 260.

  After the gas effluent 250 exits the fluidized bed 253, a new level and / or type of contaminants remaining in the gas effluent 250 is determined by the post-filter monitoring step 386 and the gas effluent 250 is post-filter inlet manifold 387 It is led to. Suitable post filters 388, 389, 390, and / or 391 are selected by the selection method shown in FIG. The post filter shown in FIG. 31 is filled with the reactive CZTS alloy adsorbent 351 shown in FIG. For example, the post filter 388 is filled with a sulfur CZTS alloy 352 shown in FIG. The post filter 389 is filled with a selenate CZTS alloy 353 shown in FIG. The post filter 390 is filled with a ferrous oxide CZTS alloy 354 shown in FIG. Post filter 391 is filled with a combination of CZTS alloy adsorbents 352, 353 and / or 354. Post-filter outlet manifold 392 routes gas exhaust 250 to gas system exhaust 256a. At the gas system discharge 256a, a portion of the gas discharge 250 is discharged from the controlled gas discharge chimney 257, and a portion of the gas discharge 250 is discharged by a suitable waste treatment process 262.

  Additional loaded with different combinations of CZTS alloy adsorbents 352, 353, and / or 354, combined to effectively treat specific levels and / or types of contaminants contained in gaseous emissions 250 May be added to the post-filter inlet manifold 387.

  All pre-filters 381, 382, 383, 384 and post-filters 388, 389, 390, 391 are sent separately via the sorbent wash step 258 and sorbent return port 260. Step 258 includes separating contaminants from the CZTS alloy adsorbent 351 and discarding 261 the contaminants as recyclable and / or properly recoverable. Any exhausted CZTS alloy adsorbent 351 can be discarded through a disposal step 259. After step 258, the specific CZTS alloy adsorbent 351 may be replaced with each specific pre-filter 381, 382, 383, 384 and / or post-filter 388, 389, 390, 391. Specific path diagrams and / or for sending the sorbent from the sorbent washing step 258 and from the pre-filters 381, 382, 383, 384 and / or post filters 388, 389, 390, 391 to the sorbent washing step 258. The circuit diagram is not shown.

  In FIG. 32, a block diagram illustrates a system and method for removing contaminants from non-gas emissions 295. The non-gas emissions 295 are monitored and analyzed at step 379 to determine the types and levels of contaminants in the non-gas emissions 295. The monitoring may be a systematic intermittent sampling at regular intervals and / or continuous in-line monitoring and analysis. Based on the type and / or level of contaminants present in the non-gas emissions 295 as determined by step 379, the flow of the effluent may be adjusted such that the non-gas emissions 295 have appropriate pre-filters 381, 382, 383, and / or Or through a pre-filter inlet manifold 380 for further guidance to 384. Suitable prefilters 381, 382, 383, and / or 384 are selected by the selection method shown in FIG.

  The prefilter shown in FIG. 32 is filled with the reactive CZTS alloy adsorbent shown in FIG. For example, the prefilter 381 is filled with a sulfur CZTS alloy 352 shown in FIG. The pre-filter 382 is filled with a selenate CZTS alloy 353 shown in FIG. The pre-filter 383 is filled with a ferrous oxide CZTS alloy 354 shown in FIG. The pre-filter 384 is filled with a combination of CZTS alloy adsorbents 352, 353 and / or 354. Different combinations of CZTS alloy adsorbents 352, 353, and / or 354, combined to effectively treat specific levels and / or types of contaminants contained in non-gas emissions 295, were loaded. Additional pre-filters may be added to the pre-filter inlet manifold 380.

  After the contaminated non-gas effluent 295 is sent to a suitable pre-filter, the pre-filter outlet manifold 385 sends the effluent to a fluidized bed 253. As for the non-gas discharge 295, the housing of the fluidized bed 253 is arranged in a direction substantially perpendicular to the gantry 271. The contaminants are separated from the sorbent in step 258 and returned to fluidized bed 253 through sorbent return port 260.

  After the non-gas emissions 295 exit the fluidized bed 253, the post-filter monitoring step 386 determines a new level and / or type of contaminants remaining in the non-gas emissions 295, and the non-gas emissions 295 are post-filtered. It is routed through the inlet manifold 387. Suitable post filters 388, 389, 390, and / or 391 are selected by the selection method shown in FIG. The post filter shown in FIG. 32 is filled with the reactive CZTS alloy adsorbent 351 shown in FIG. For example, the post filter 388 is filled with a sulfur CZTS alloy 352 shown in FIG. The post filter 389 is filled with a selenate CZTS alloy 353 shown in FIG. The post filter 390 is filled with a ferrous oxide CZTS alloy 354 shown in FIG. Post filter 391 is filled with a combination of CZTS alloy adsorbents 352, 353 and / or 354. Post-filter outlet manifold 392 directs non-gas exhaust 295 to non-gas system exhaust 256b. At the non-gas system discharge 256b, a portion of the non-gas discharge 295 is discharged as an environmentally controlled non-gas discharge 273, and a portion of the non-gas discharge 295 is discharged by a suitable waste treatment process 262. You. Different combinations of CZTS alloy adsorbents 352, 353, and / or 354, combined to effectively treat specific levels and / or types of contaminants contained in non-gas emissions 295, were loaded. Additional post filters may be added to the post filter inlet manifold 387.

  All pre-filters 381, 382, 383, 384 and post-filters 388, 389, 390, 391 are sent separately via the sorbent wash step 258 and sorbent return port 260. Step 258 includes separating contaminants from the CZTS alloy adsorbent 351 and discarding 261 the contaminants as recyclable and / or properly recoverable. Any exhausted CZTS alloy adsorbent 351 can be discarded through a disposal step 259. After step 258, the specific CZTS alloy adsorbent 351 may be replaced with each specific pre-filter 381, 382, 383, 384 and / or post-filter 388, 389, 390, 391. Specific path diagrams and / or for sending the sorbent from the sorbent washing step 258 and from the pre-filters 388, 389, 390, 391 and / or post filters 388, 389, 390, 391 to the sorbent washing step 258. The circuit diagram is not shown.

  FIG. 33 illustrates an exemplary emissions control system. The contaminated effluent is introduced into the fluidized bed 152 via the inlet 165. It should be noted that the effluent may first pass through one or more pre-fluidized bed filters 151 (FIGS. 22 and 23), depending on the needs of the particular application.

  The fluidized bed 152 has an enclosure 16 having an inverted venturi shape, with a specific length L to diameter D ratio between a minimum of 2.9: 1 and a maximum of 9.8: 1. . This ratio is optimized to allow the contaminated effluent to stay longer in the fluidized bed 152 packed with a special reactant 164 containing one or more adsorbents. An example of a preferred ratio of the length L of the fluidized bed 152 to the diameter D is 4.4: 1, which is determined through trial and error. One or more exemplary fluidized beds 152 may be connected in series or parallel depending on the needs of a particular application.

  Preferably, fluidized bed 152 has a substantially circular cross section. Although not shown in FIG. 33, fluidized bed 152 may include one or more of the various baffles and / or special purpose flow restricting obstructions disclosed herein. Fluidized bed 152 has generally outwardly extending convex ends 168, 169 to facilitate extended residence time while minimizing turbulence through reactants 164. As the flow of contaminated effluent flows into fluidized bed 152 at inlet 165, intimate contact with reactants 164 is initiated, resulting in random non-turbulent flow 166. The random non-turbulent flow 166 flows back to its side by the generally outwardly extending convex ends 168, 169, whereby the non-turbulent flow 166 exits the fluidized bed 152 through the outlet holes 167 in the fluidized bed 152. The residence time is extended. Reactants 164 that promote non-turbulent flow 166 form a random tortuous flow path of the contaminated effluent. The length L of the fluidized bed 152 does not include the lengths of the convex ends 168 and 169.

  Fluidized bed 152 includes at least one monitoring sensor station 421 (ie, a first monitoring sensor) that provides data, status, and feedback about operating parameters. The monitoring sensor station 421 is configured to monitor emission flow levels, pressures, speeds, temperatures, and many other relevant parameters related to the emission control system. Based on the feedback information, some automatic adjustments are made by the device, but other process and / or system parameters may require manual adjustments. The monitoring sensor station 421 provides information about the efficiency of the sorbent inside the fluidized bed 152 and assists in determining when to clean and / or regenerate the sorbent.

  In an exemplary embodiment of the present disclosure, fluidized bed 152 has at least one side outlet 403, 409, 415 leading to adsorbent recycling subsystems 400, 401, 402, respectively. The adsorbent recycling subsystems 400, 401, and 402 shown in FIG. 33 are disposed outside the fluidized bed 152, but may be disposed inside the fluidized bed 152 instead.

  Fluidized bed 152 includes at least one closed-loop sorbent outlet port monitoring sensor station 422 and at least one closed-loop sorbent return port monitoring sensor station 423 that provide data, status, and feedback about operating parameters. The monitoring sensor station 422 is configured to monitor emission flow levels, pressures, velocities, temperatures, and many other relevant parameters related to the emission control system. Some automatic adjustments are made by the programmable device based on the feedback information, while other process and / or system parameters may require manual adjustments. The monitoring sensor 423 identifies the state of the sorbent as it passes through one of the outlet holes 403, 409, or 415 and enters the subsystem 400, 401, or 402. The monitoring sensor station 423 is configured to monitor emission flow levels, pressures, velocities, temperatures, and many other relevant parameters for the emission control system.

  Some automatic adjustments are made by the programmable device based on the feedback information, while other process and / or system parameters may require manual adjustments. The monitoring sensor 423 identifies the state of the sorbent as it passes through the return port 407, 414, or 420, and / or one of the subsystems 400, 401, or 402 after cleaning and / or regeneration. The monitoring sensor station 424 (ie, the second monitoring sensor) is configured to monitor emission flow levels, pressures, velocities, temperatures, and many other relevant parameters related to the emission control system. Some automatic adjustments are made by the programmable device based on the feedback information, while other process and / or system parameters may require manual adjustments. The monitoring sensor 424 provides the status and final status of the sorbent as the sorbent is processed at each station 404, 410, or 416 in the subsystem 400, 401, or 402 when a cleaning and / or regeneration process is performed. Monitor the volume. The monitoring sensors 421, 422, 423, 424 cooperate with each other to adjust process conditions and / or parameters to achieve and maintain consistency and optimal sorbent efficiency at each station in the emissions control system. . Monitoring the sorbent in the subsystems 400, 401, 402 determines when and how much refill sorbent is required at each station 408, 413, and 419.

  In another exemplary embodiment (not shown), a cleaning and / or regeneration subsystem is installed and configured inside the fluidized bed 152. In this configuration, the functions of the monitoring sensors 421, 422, 423, 424 and the adsorbent recycling subsystems 400, 401, 402 are performed inside the fluidized bed 152.

  In FIG. 33, when the fluidized bed 152 is filled with the reactant 164 composed of the CTZS adsorbent, the adsorbent recycling subsystem 400 is used to maintain the optimal operation state of the CTZS adsorbent. Through the sorbent discharge port 403, the sorbent can move into the sorbent recycling station 404. This sorbent recycling station 404 within the subsystem 400 includes one or more chemical reagents that separate contaminants from the CZTS sorbent as part of the cleaning and regeneration process. As a non-limiting example, the chemical reagent used in the sorbent recycle station 404 may be selected from the group of fatty alcohols. Depleted and / or depleted CZTS sorbent can be disposed of through sorbent disposal station 405. Emission contaminants removed from the effluent can be recycled for use in various industries through contaminant disposal ports 406. A bulk refill station 408, such as a new / fresh sorbent container, provides a replenishment of CZTS sorbent to replace sorbent removed and / or lost during removal of contaminants from the effluent. You. At the CZTS adsorbent return port 407, a closed loop back to the fluidized bed 152 is completed.

  When the fluidized bed 152 is filled with the reactant 164 comprising the CTZS alloy adsorbent, the adsorbent recycling subsystem 401 maintains the CTZS alloy adsorbent in an optimal operating state. Through the sorbent discharge port 409, the sorbent can move into the sorbent recycling station 410. This sorbent recycling station 410 within the subsystem 401 includes one or more chemical reagents that separate contaminants from the CZTS alloy sorbent as part of the cleaning and regeneration process. As a non-limiting example, the chemical reagent used in the sorbent recycling station 410 may be selected from the group of fatty alcohols. The depleted and / or depleted CZTS alloy sorbent can be discarded through station 411. Emission contaminants removed from the effluent can be recycled for use in various industries through contaminant disposal ports 412. The bulk refill station 413 provides a replenisher of CZTS alloy sorbent to replace sorbent removed and / or lost during removal of contaminants from the effluent. At the CZTS alloy adsorbent return port 414, a closed loop back to the fluidized bed 152 is completed.

  When the fluidized bed 152 is filled with the reactant 164 composed of the carbon-based adsorbent, the adsorbent recycling subsystem 402 maintains an optimal operating state of the carbon-based adsorbent. Through the sorbent discharge port 415, the sorbent can move into the sorbent recycling station 416. This sorbent recycling station 416 within subsystem 402 includes one or more chemical reagents that separate contaminants from carbon-based sorbents as part of the cleaning and regeneration process. As a non-limiting example, the chemical reagent used in the sorbent recycle station 416 may be a solvent such as methyl ethyl ketone, methylene chloride and / or methanol. Depleted and / or depleted carbon-based sorbent can be disposed of through sorbent disposal station 417. Emission contaminants removed from the effluent can be recycled for use in various industries through contaminant disposal ports 418. Mass refill station 419 provides a replenishment of carbon-based sorbent to replace sorbent removed and / or lost during removal of contaminants from the effluent. At the carbon-based adsorbent return port 420, a closed loop back to the fluidized bed 152 is completed.

  In one exemplary embodiment of the present disclosure, and as shown in FIG. 33, fluidized bed 152 includes one or more sorbent recycling subsystems 400, 401, 402 configured for one or more sorbents. May be a single unit. According to another exemplary embodiment (not shown), a plurality of fluidized beds 152 are configured in series with each other, with each fluidized bed 152 configured for one or more adsorbent recycling subsystems 400, 401, 402. . According to another exemplary embodiment (not shown), a plurality of fluidized beds 152 are configured parallel to one another, with each fluidized bed 152 configured for one or more adsorbent recycling subsystems 400, 401, 402. .

  Monitoring sensors 421, 422, 423, 424 are just some of the non-exhaustive examples of measuring devices applicable to emissions control systems. One skilled in the art will appreciate that there may be many other types of monitoring sensors located at many other emission control system stations not shown in the illustrated embodiment. Would. The specific monitoring sensor used for gaseous contaminated emissions may be different from the specific monitoring sensor used for non-gaseous contaminated emissions. Similarly, the monitoring sensors required for one type of contaminant may be different than the monitoring sensors required for another contaminant.

  In another aspect of the present disclosure, an emission control method for removing contaminants from emissions is disclosed. This method, shown in FIG. 33, sends the effluent to a treatment system that includes a reverse venturi fluidized bed apparatus 152 that includes one or more adsorbents that chemically bind the contaminants contained in the effluent, where the contaminants are adsorbed. After binding to the agent, a step of directing the effluent away from the reverse venturi fluidized bed apparatus 152 is included. According to this method, the adsorbent is selected from the group of materials including copper, zinc, tin, sulfur (CZTS) adsorbent, copper, zinc, tin, sulfur (CZTS) alloy adsorbent, and carbon-based adsorbent. You. The method also includes delivering the sorbent through one or more sorbent recycling subsystems 400, 401, 402 for cleaning and regeneration. This process separates the depleted and worn adsorbent from the adsorbent sent through the adsorbent recycling subsystems 400, 401, 402, discards the depleted and worn adsorbent, and adsorbent recycling subsystems 400, 401, 402. Separating the contaminants from the adsorbent passed through it, discarding or recycling the contaminants, and returning the recycled adsorbent to the reverse venturi fluidized bed apparatus 152. The method may include the step of sending fresh sorbent to the reverse venturi fluidized bed apparatus 152 to replace depleted and worn sorbent.

  In embodiments where the reverse venturi fluidized bed apparatus 152 comprises a plurality of adsorbent recycling subsystems 400, 401, 402, the method further comprises maintaining different adsorbents in the reverse venturi fluidized bed apparatus 152, At least one process parameter of the reverse venturi fluidized bed apparatus is detected by one or more monitoring sensors 421, 422, 423, and 424, and the at least one process parameter is detected based on the at least one process parameter detected by the monitoring sensors 421, 422, 423, and 424. The process may include sending the effluent to the different adsorbents described above and sending the different adsorbents to different adsorbent recycling subsystems 400, 401, 402 dedicated to processing a particular type of adsorbent. For example, in the illustrated embodiment, the copper, zinc, tin, sulfur (CZTS) sorbent is sent through the first sorbent recycling subsystem 400 and the copper, zinc, tin, sulfur (CZTS) alloy sorbent Is sent through a second adsorbent recycling subsystem 401 and the carbonaceous adsorbent is sent through a third adsorbent recycling subsystem 402.

  Although steps in this method are described and illustrated in a specific order, these steps differ within a scope that does not depart from the scope of the present disclosure, unless the order of the steps is described in another form. It may be performed in order. Similarly, the methods described and illustrated herein can be practiced without all of the above steps or with additional intermediate steps not described without departing from the scope of the present disclosure. .

Many modifications of the present disclosure are possible in light of the above disclosure, and may be embodied in other forms than specifically described within the scope of the appended claims. These preceding statements should be construed as covering any combination for which inventive novelty is useful. The use of the word "the" in device claims refers to an antecedent basis that is a positive statement intended to be included within the scope of the claims, but the word "the" , Preceded by a term that is not intended to be included in the scope of the claims.

Claims (20)

An emissions control system comprising a fluidized bed apparatus for removing contaminants from emissions, comprising:
It has an inverted Venturi shape, an inlet part into which the discharge flows at a predetermined inlet flow rate, an outlet part discharging the discharge at a predetermined outlet flow rate, and is disposed between the inlet part and the outlet part. An enlarged portion for capturing the contaminants in the effluent,
The inlet portion, the outlet portion, and the enlarged diameter portion of the housing communicate with each other via a fluid,
A reactant mass is disposed within the enlarged portion of the housing;
The reactant mass has a reaction outer surface arranged to contact the effluent;
The reactant mass comprises at least one adsorbent;
Disposed in communication with the housing via a fluid, receiving an adsorbent from the housing via an adsorbent discharge port, returning a clean adsorbent to the housing via an adsorbent return port, the at least An emissions control system comprising at least one sorbent recycling subsystem that includes a chemical reagent for separating said contaminants from a sorbent.   2. The emission control system according to claim 1, wherein the casing of the fluidized bed device is permanently installed on site.   2. The emission control system according to claim 1, wherein the casing of the fluidized bed device is transportable.   2. The effluent control system according to claim 1, wherein the housing of the fluidized bed device comprises a substantially horizontal longitudinal surface when the fluidized bed device is configured for gaseous effluent. Characteristic emission control system.   2. The emissions control system of claim 1, wherein the housing of the fluidized bed device has a generally vertically oriented longitudinal surface when the fluidized bed device is configured for non-gas emissions. Emission control system characterized by the following.   2. The emission control system according to claim 1, wherein the at least one adsorbent recycling subsystem is external to the enclosure of the fluidized bed apparatus.   2. The emission control system according to claim 1, wherein the at least one adsorbent recycling subsystem is inside the housing of the fluidized bed apparatus.   The emission control system according to claim 1, wherein the at least one adsorbent recycling subsystem has a closed loop structure.   2. The emissions control system of claim 1, wherein the at least one adsorbent recycling subsystem includes an adsorbent disposal station that separates and discards worn and worn adsorbents. .   2. The emissions control system of claim 1, wherein the at least one sorbent recycling subsystem has a pollutant disposal port for discharging and recycling or discarding the contaminants separated from the effluent. And emission control system.   2. The emissions control system of claim 1, wherein the at least one sorbent recycling subsystem includes a mass refill station that supplies new sorbent to the sorbent return port to replace depleted and worn sorbent. An emission control system comprising:   2. The emissions control system of claim 1, wherein the at least one sorbent recycling subsystem is configured to process copper, zinc, tin, sulfur (CZTS) sorbent. system.   The emissions control system of claim 1, wherein the at least one sorbent recycling subsystem is configured to process copper, zinc, tin, sulfur (CZTS) alloy sorbent. Control system.   The emissions control system of claim 1, wherein said at least one sorbent recycling subsystem is configured to process a carbon-based sorbent. 2. The emissions control system of claim 1, wherein the at least one adsorbent recycling subsystem comprises:
A first adsorbent recycle that is in fluid communication with the enclosure of the fluidized bed apparatus and is connected at a first adsorbent recycle subsystem location and is dedicated to treating copper, zinc, tin, and sulfur (CZTS) adsorbents; Subsystems,
A second adsorbent in fluid communication with the enclosure of the fluidized bed apparatus and connected at a second adsorbent recycling subsystem location and dedicated to processing copper, zinc, tin, sulfur (CZTS) alloy adsorbents A recycling subsystem,
A third adsorbent recycling subsystem that is connected to the third adsorbent recycling subsystem position in communication with the casing of the fluidized bed device via a fluid and that is dedicated to the treatment of the carbon-based adsorbent. And emission control system. 2. The emissions control system of claim 1, further comprising a first monitoring sensor disposed within the enclosure of the fluidized bed device and configured to monitor at least one process parameter of the fluidized bed device. When,
A second monitoring sensor included in the at least one sorbent recycling subsystem and configured to monitor at least one parameter of the sorbent in the sorbent recycling subsystem. Object control system. An emission control method for removing pollutants from emissions, comprising:
Sending the effluent to a treatment system including a reverse venturi fluidized bed apparatus comprising at least one adsorbent that chemically binds to contaminants contained in the effluent;
Sending the effluent away from the reverse venturi fluidized bed apparatus;
The at least one adsorbent is selected from the group of materials comprising copper, zinc, tin, sulfur (CZTS) adsorbent, copper, zinc, tin, sulfur (CZTS) alloy adsorbent, and carbon-based adsorbent;
A method for controlling emissions comprising sending the at least one adsorbent through one or more adsorbent recycling subsystems for chemical cleaning and regeneration. 18. The method of claim 17, further comprising: separating depleted and worn sorbent from the sorbent sent through the sorbent recycling subsystem and discarding the depleted and worn sorbent. And
Separating contaminants from the sorbent sent through the sorbent recycling subsystem and discarding or recycling the contaminants;
Returning the recycled adsorbent to the reverse venturi fluidized bed apparatus;
A method for controlling emissions comprising sending new adsorbent to the reverse venturi fluidized bed apparatus to replace the depleted and worn adsorbent. 19. The method of claim 18, wherein the at least one adsorbent recycling subsystem comprises:
A first adsorbent recycling subsystem dedicated to the treatment of copper, zinc, tin, sulfur (CZTS) adsorbents,
A second adsorbent recycling subsystem dedicated to the treatment of copper, zinc, tin, sulfur (CZTS) alloy adsorbents;
An emission control method, comprising: a third adsorbent recycling subsystem dedicated to carbon-based adsorbent treatment. 20. The method of claim 19, further comprising maintaining different adsorbents in the inverted Venturi fluidized bed apparatus in separate forms;
Detecting at least one process parameter of the reverse venturi fluidized bed apparatus by at least one monitoring sensor;
Sending the effluent through one or more different adsorbents based on the at least one process parameter detected by the at least one monitoring sensor;
Passing copper, zinc, tin, sulfur (CZTS) adsorbent through said first adsorbent recycling subsystem,
Passing copper, zinc, tin, sulfur (CZTS) alloy adsorbent through said second adsorbent recycling subsystem,
An emission control method comprising passing a carbon-based adsorbent through said third adsorbent recycling subsystem.