CN211954941U - Water pathogen enrichment facility - Google Patents
Water pathogen enrichment facility Download PDFInfo
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- CN211954941U CN211954941U CN201921687093.4U CN201921687093U CN211954941U CN 211954941 U CN211954941 U CN 211954941U CN 201921687093 U CN201921687093 U CN 201921687093U CN 211954941 U CN211954941 U CN 211954941U
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Abstract
The utility model discloses a water body pathogen concentration device, which comprises a water tank, a water pump, a pathogen concentrator and a connecting pipeline for connecting the components, wherein, the water outlet of the water tank is communicated with the water inlet of the pathogen concentrator, the first water outlet of the pathogen concentrator is communicated with the water inlet of the water tank, and the water pump is positioned between the water outlet of the water tank and the water inlet of the pathogen concentrator; the pathogen concentrator comprises a shell and an inorganic ceramic ultrafiltration membrane filter element arranged in the shell, and further comprises a second water outlet. The device of the utility model has simple structure, small volume and easy carrying, is particularly suitable for rapidly and continuously enriching the pathogens in the environmental water body in field sites such as fields and the like, and leads the pathogens to reach the detectable degree; the device can ensure that the pathogens in the water body are concentrated or completely collected as much as possible, and ensure the activity of the pathogens and the reliability of detection results.
Description
Technical Field
The utility model relates to a microbiological detection technical field, concretely relates to water pathogen enrichment facility.
Background
Water resources are important material bases on which human beings live and develop, and the quality of the water environment is one of the most important and key barriers in a water and food safety system, so that water environment pollution is always one of the focuses of public and environmental scientific research. The pollution of pathogens in water is an important problem of water environment pollution, and pathogens in natural water can survive for a long time and infect human bodies through various ways such as drinking water, diet or skin contact, thereby being harmful to human production and human health.
The detection of pathogens in water is a large technical index for evaluating water treatment, and is also an important detection standard influencing the occurrence of diseases in the next year in agricultural production. However, because the water volume is large, the concentration of pathogens is relatively low, and most pathogens are attached to particles in water, which is more difficult to detect than clinical specimens, and the pathogens in the water are usually concentrated and enriched effectively by chemical methods or special devices to reach the detectable degree. The existing method for concentrating pathogens in water mainly comprises the following steps: the concentration method has the advantages of the concentration method, but has the limitations, such as effective application range, limited water treatment amount, easy pathogen inactivation, false negative detection result and the like, and the existing method usually needs to collect the water body to be detected and then adopts a concentration device for concentration after being transported to a laboratory or a laboratory, so that the collection and transportation of the water body are difficult due to the large volume of the water body, and certain inconvenience is caused to the development of field water body detection work. Therefore, the development of a simple and convenient device with strong operability and capable of directly concentrating the pathogens of the water body on site has important significance for detecting the pathogens in the environmental water body.
Disclosure of Invention
Based on the above description, the utility model aims at providing a simple and convenient, strong operability, can be in the direct water pathogen enrichment facility who uses in the field.
As a first aspect of the utility model, the utility model provides a water pathogen's enrichment facility.
Preferably, the apparatus comprises: the water tank, the water pump, the pathogen concentrator and be used for connecting the connecting tube of above-mentioned part, wherein, the delivery port of water tank with the water inlet of pathogen concentrator is linked together, the first delivery port of pathogen concentrator with the water inlet of water tank is linked together, the water pump is located the delivery port of water tank with between the water inlet of pathogen concentrator.
Preferably, the pathogen concentrator comprises a housing and an inorganic ceramic ultrafiltration membrane cartridge disposed in the housing, wherein the pathogen concentrator further comprises a second water outlet.
Preferably, the water inlet and the first water outlet of the pathogen concentrator are respectively arranged at two opposite ends of the pathogen concentrator, and the second water outlet is positioned on the side wall of the shell between the water inlet and the first water outlet.
Preferably, the pathogen concentrator is removably attached to the device.
Preferably, the pathogen concentrator has external threads or internal threads at two ends of the shell corresponding to the water inlet and the first water outlet, and the connecting pipeline for communicating the pathogen concentrator with the water pump and the water inlet of the water tank is provided with matched internal threads or external threads.
Preferably, a movable connector is arranged on a connecting pipeline for communicating the pathogen concentrator with the water pump and the water tank water inlet, and the connector is provided with internal threads or external threads for connecting the pathogen concentrator.
Preferably, the water tank is of a double-wall structure, a space for containing cooling water is arranged between the outer wall and the inner wall of the water tank, one end of the outer wall of the water tank is provided with a cooling water inlet, and the other end of the outer wall of the water tank is provided with a cooling water outlet.
Preferably, a first pressure gauge, a pressure regulating valve and/or a temperature detector are arranged on a connecting pipeline which is communicated with the first water outlet of the pathogen concentrator and the water inlet of the water tank.
Preferably, a second pressure gauge is arranged on a connecting pipeline which is communicated with the water inlet of the pathogen concentrator by the water pump.
Preferably, the device further comprises a water outlet communicated with the water outlet of the water tank.
The utility model has the advantages that:
(1) the device of the utility model has simple structure, small volume and easy carrying, is particularly suitable for rapidly and continuously enriching the pathogens in the environmental water body in field sites such as fields and the like, and leads the pathogens to reach the detectable degree; moreover, the device can ensure that the pathogens in the water body are concentrated or completely collected as much as possible, and ensure the activity of the pathogens and the reliability of the detection result.
(2) The utility model discloses an use inorganic ceramic milipore filter to carry out the physics concentration to the pathogen in the water, because inorganic ceramic milipore filter is uncharged, have and do not influence pathogen self characteristic and repeated advantage that uses many times.
(3) The utility model discloses a connection can be dismantled to each part of device, the change of the milipore filter of being convenient for and make the device easily carry.
Drawings
Fig. 1 is a schematic plan view of the pathogen concentrating device of the present invention.
Fig. 2 is a schematic diagram of the inorganic ceramic ultrafiltration membrane of the present invention.
FIG. 3 is a graph showing the results of a color reaction experiment for raw water, a concentrated solution and PMMoV virus particles.
Fig. 4 is a schematic view of a pathogen concentrator housing.
FIG. 5 is a graph showing the results of the colony counts of raw water and 500nm filtrate.
FIG. 6 is a graph showing the results of the cell count in the 500nm filtrate and the concentrate.
FIG. 7 is a graph showing results of the diameters of colonies in raw water and a concentrated solution, wherein (A) is a graph showing results of the diameters of colonies in a concentrated solution, and (B) is a graph showing results of the diameters of colonies in raw water.
FIG. 8 is a graph showing the results of bacterial colonies in the raw water and the filtrate.
Reference numerals: the device comprises a device 1, a 10 water tank, a 101 water tank water inlet, a 102 water tank water outlet, a 103 cooling water inlet, a 104 cooling water outlet, a 20 water pump, a 30 pathogen concentrator, a 301 shell, a 302 inorganic ceramic ultrafiltration membrane, a 303 pathogen concentrator water inlet, a 304 pathogen concentrator first water outlet, a 305 pathogen concentrator second water outlet, a 40 connecting pipeline, a 401 connecting head, a 402 valve, a 50 first pressure gauge, a 60 temperature detector, a 70 pressure regulating valve, an 80 second pressure gauge, a 90 water outlet and a 100 control valve.
Detailed Description
The technical solutions of the present invention will be described clearly and completely with reference to the accompanying drawings, and it should be understood that the described embodiments are some, but not all embodiments of the present invention. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
It should be noted that in the description of the present invention, the terms "upper", "lower", "left", "right", "vertical", "horizontal", "inner", "outer", etc., which indicate the orientation or positional relationship based on the orientation or positional relationship shown in the drawings, are only used for convenience of description and simplification of description, and do not indicate or imply that the device or element referred to must have a specific orientation, be constructed and operated in a specific orientation, and thus, should not be construed as limiting the present invention.
It should be noted that, in the description of the present invention, unless otherwise explicitly specified or limited, the terms "mounted," "connected," and "connected" are to be construed broadly, and may be, for example, fixedly connected, detachably connected, or integrally connected; they may be connected directly or indirectly through intervening media, or they may be interconnected between two elements. The specific meanings of the above terms in the present invention can be understood in specific cases to those skilled in the art.
Example 1: water pathogen enrichment facility
Referring to fig. 1-4, the present invention provides a device 1 for concentrating water pathogens, said device 1 comprising: a water tank 10, a water pump 20, a pathogen concentrator 30 and a connecting pipe 40 for connecting the above components, wherein the water outlet 102 of the water tank is communicated with the water inlet 303 of the pathogen concentrator, the first water outlet 304 of the pathogen concentrator is communicated with the water inlet 101 of the water tank, and the water pump 20 is positioned between the water outlet 102 of the water tank and the water inlet 303 of the pathogen concentrator. In the embodiment, the water to be concentrated is injected into the water tank 10 through the water tank water inlet 101, the water outlet 102 of the water tank is connected with the water pump 20, the water pump 20 is used for pumping the water in the water tank 10 into the pathogen concentrator 30 for concentrating or separating pathogens, and part of the water passing through the pathogen concentrator 30 can enter the water tank 10 again from the water tank water inlet 101 through the first water outlet 304 of the pathogen concentrator for circulating concentration, so that the pathogens in the water can be completely concentrated or separated, and the accuracy of the detection result is guaranteed.
In the present embodiment, the water pump 20 may be a diaphragm pump, a peristaltic pump, a turbine pump, or other water pumps commonly used in the art, and the water pump 20 is provided with a power supply (not shown) connected with direct current or powered by a storage battery. The flow rate and rate of water pumped into the virus concentrator 30 can be regulated by the pressure of the water pump 20.
In some preferred embodiments, the pathogen concentrator 30 includes a housing 301 and an inorganic ceramic ultrafiltration membrane cartridge 302 disposed in the housing 301, and the concentration or separation of the pathogens is achieved by the inorganic ceramic ultrafiltration membrane cartridge 302. The inorganic ceramic ultrafiltration membrane 302 is an asymmetric membrane prepared from an inorganic ceramic material by a special process, a plurality of channels are arranged in the middle of the membrane, liquid to be filtered is pumped into the channels of the inorganic ceramic ultrafiltration membrane 302, under the action of pressure, the ultrafiltration membrane intercepts pathogens with the particle size larger than the membrane aperture on the ultrafiltration membrane, and pathogens with the particle size smaller than the membrane aperture penetrate through the membrane layer and enter into filtrate, so that the pathogens in the water body can be separated, concentrated and purified. In the present application, part of the liquid in the water tank does not pass through the membrane layer of the inorganic ceramic ultrafiltration membrane 302, but flows through the middle channel of the inorganic ceramic ultrafiltration membrane 302, and the flowing direction of the part of the liquid is vertical to the seepage direction of the filtrate, so that cross-flow filtration is formed. The liquid flowing through the middle channel of the inorganic ceramic ultrafiltration membrane 302 may carry a large amount of pathogens, and the part of the liquid enters the water tank 10 again from the first water outlet 304 of the pathogen concentrator 30 and is pumped into the virus concentrator 30 again for concentration. Meanwhile, the pressure at two ends of the inorganic ceramic ultrafiltration membrane in the internal circulation can be controlled by the pressure regulating valve, so that the water flow speed and the membrane permeability penetrating through the ultrafiltration membrane 302 are controlled, a large number of pathogens are attached to the wall of the middle channel of the inorganic ceramic ultrafiltration membrane, and finally, a certain volume of water or buffer solution, such as 1 multiplied by PBS, is used for flushing the inner wall of the channel to obtain the concentrated solution with the highest concentration.
The pore size of the inorganic ceramic ultrafiltration membrane 30 may be selected according to the size of the pathogen to be concentrated or separated, and may be, for example, 10 to 1000 nm.
In some preferred embodiments, the pathogen concentrator 30 further includes a second water outlet 305, and the second water outlet 305 is used for discharging the filtrate passing through the membrane layer of the inorganic ceramic ultrafiltration membrane 302. In some embodiments, the second water outlet 305 is connected to a filtrate drain (not shown) for draining the filtrate. In some forms, the filtrate drain is a plastic or rubber hose. In one case, a part of the liquid passing through the membrane layer of the inorganic ceramic ultrafiltration membrane 302 may not be discharged from the second water outlet 305, but is discharged from the first water outlet 304 through the gap between the inorganic ceramic ultrafiltration membrane 302 and the housing 301 under the action of the pump, and remains in the connecting pipeline together with a part of the liquid passing through the middle through hole of the inorganic ceramic ultrafiltration membrane 302, and enters the water tank 10 again, and the part of the liquid also contains a large amount of viruses, so that the part of the liquid entering the water tank 10 is subjected to circulating filtration, so as to ensure that the original liquid is concentrated to the maximum extent, and ensure the accuracy of the detection result.
In some preferred embodiments, the inlet 303 and the first outlet 304 of the pathogen concentrator are disposed at opposite ends of the pathogen concentrator 30, i.e., the inlet 303 is disposed at one end of the pathogen concentrator 30, the first outlet 304 is disposed at the other end of the pathogen concentrator 30, and the second outlet 305 is disposed on a side wall of the housing between the inlet 303 and the first outlet 304.
In some preferred embodiments, the pathogen concentrator 30 is removably attached to the device, and in particular, the housing 301 of the pathogen concentrator is removably attached to the other components of the device by threads, snaps, or clasps, thereby facilitating replacement of the filter cartridge in the housing of the pathogen concentrator.
In some preferred forms, the housing of the pathogen concentrator 30 corresponding to the water inlet 303 and the first water outlet 304 has external or internal threads at both ends, and the connecting pipe for connecting the pathogen concentrator 30 to the water pump 20 and the water inlet 101 of the water tank has matching internal or external threads, and the pathogen concentrator 30 is detachably connected to the apparatus or other parts of the apparatus through threads. In some preferred forms, the housing of the pathogen concentrator 30 has external threads at both ends thereof, the connecting pipe for connecting the pathogen concentrator 30 to the water pump 20 and the connecting pipe for connecting the first outlet 304 of the pathogen concentrator to the inlet 101 of the water tank have internal threads matching the external threads at both ends of the housing of the pathogen concentrator.
In some preferred embodiments, a movable connector 401 is disposed on a connecting pipe for connecting the pathogen concentrator 30 with the water pump 20 and the water inlet 101 of the water tank, and the connector 401 has an internal thread or an external thread for connecting with the pathogen concentrator 30. The movable connection head 401 here means that the connection head 401 is movably connected to the connection pipe 40, and can move up and down and/or rotate on the connection pipe 40, and the movable connection head 401 facilitates the connection and disconnection of the pathogen concentrator 30 and the connection pipe 40. In some preferred forms, the pathogen concentrator housing has external threads on both ends and the connector 401 has matching internal threads. In some preferred forms, there is a valve 402 in the connecting line for securing the connector 401 to the connecting line 40, and when it is desired to replace the cartridge, the valve 402 is opened and the pathogen concentrator 30 is removed from the apparatus by rotating the connector 401 and the pathogen concentrator housing.
In some preferred embodiments, the water tank 10 has a double-wall structure, and a space for containing cooling water is formed between the outer wall and the inner wall of the water tank, wherein one end of the outer wall of the water tank is provided with a cooling water inlet 103, and the other end of the outer wall of the water tank is provided with a cooling water outlet 104. Specifically, the water pitcher is hollow, and has outer wall and inner wall, forms the space that holds the cooling water between outer wall and the inner wall, for holding the space of treating concentrated water within the inner wall, the bottom of water pitcher has delivery port 102, and this delivery port 102 is used for with the water of treating concentrated in the tank body discharge water pitcher 10. The water tank is characterized in that a cooling water inlet 103 is formed in the outer wall of the water tank close to the top of the water tank, a cooling water outlet 104 is formed in the outer wall of the water tank close to the bottom of the water tank and opposite to the cooling water inlet 103, the cooling water inlet 103 is connected with cooling water, and the water to be concentrated in the water tank 10 is cooled by introducing the cooling water. In one case, after the water containing pathogens passes through the pathogen concentrator 30, part of the water enters the water tank 10 again for cyclic concentration, the pressure of the water pump 20 will cause the temperature of the part of the water to rise, and if the temperature is too high, the pathogens in the water can be inactivated, so that the cooling water cools the water entering the water tank 10, and the pathogens are prevented from being heated and inactivated. In some preferred modes, the temperature of the water body is controlled to be 10-40 ℃.
In some preferred modes, the power of the cooling circulation is supplied by a circulating pump, and the circulating flow and the circulating pressure are set in the whole circulation process.
In some preferred embodiments, the first pressure gauge 50, the pressure regulating valve 70 and/or the temperature detector 60 are disposed on the connecting pipe 40, which communicates the first outlet 304 of the pathogen concentrator with the inlet 101 of the water tank. Wherein, the first pressure gauge 50 is used for detecting the effluent pressure of the first water outlet 304 of the pathogen concentrator, and is used for judging the osmotic pressure, the filtrate flow rate and the water temperature of the inorganic ceramic ultrafiltration membrane in the pathogen concentrator 30, if the data displayed by the first pressure gauge 50 is low, the osmotic pressure of the inorganic ceramic ultrafiltration membrane 302 is small, the filtrate flow rate is slow, the heat production is low and the water temperature is low; the pressure can be increased through the pressure regulating valve 70, at the moment, the osmotic pressure of the inorganic ceramic ultrafiltration membrane 302 is increased, the flow rate of the filtrate is accelerated, the temperature of the heat-producing water is high, and meanwhile, the cooling water system is matched to cool the water body which enters the water tank 10 again so as to ensure the activity of pathogens in the water body; wherein, the temperature detector 60 is a thermometer for detecting the temperature of the water body. In some preferred forms, the pressure regulating valve 70 is a needle valve.
In some preferred embodiments, a second pressure gauge 80 is disposed on the connection pipe 40 of the water pump 20 and the pathogen concentrator water inlet 303, and the second pressure gauge 80 is used for detecting the water outlet pressure of the water pump 20. In some preferred modes, the pressure of the water pump 20 is controlled to be 0.1-1.0 MPa. In some preferred embodiments, the water pump 20 is at a pressure of 0.2 MPa.
In some preferred embodiments, the device further comprises a drain 90, the drain 90 being in communication with the pitcher outlet 102. In some preferred forms, there is a control valve 100 between the water outlet 90 and the water outlet 102 of the water tank, and when the control valve 100 is opened, the water in the water tank 10 can be drained from the water outlet 90 out of the water tank 10 and finally drained or collected in a container. In some preferred forms, the control valve 100 is a manual ball valve.
In some preferred embodiments, the device 1 of the present invention is made of engineering plastic or stainless steel material.
In some preferred embodiments, the connection can be dismantled between each part that constitutes the utility model discloses device, when going on business in the field, can dismantle each part, portable.
Adopt the utility model discloses a device 1 can be used for the concentration of specific size pathogen in the water, it should be understood that, the concentration in this application include but not limited to carry out concentration, filtration and separation to the pathogen in the water, wherein, the concentration is that the pathogen of specific cell volume size carries out the enrichment in the water, makes the pathogen in the water reach the ground step that can be qualitative or even quantitative determination; the filtration is to remove pathogens with specific cell volume in the water body through the device; the separation is to classify pathogens in the water body according to cell size, or separate pathogens with different cell sizes in the water body, for example, separating pathogens with cell size of 200-500 nm from pathogens with cell size of 500-700 nm in the water body, thereby performing comprehensive analysis on the water body.
Take 50 ~ 500nm pathogens in the concentrated water as an example, briefly state the utility model discloses a device's work engineering as follows:
(1) setting an inorganic ceramic ultrafiltration membrane 302 with the aperture of 500nm in the pathogen concentrator 30, closing a control valve 100 at a water outlet 102 of a water tank, injecting raw water collected from the field into the water tank 10 from a water inlet 101 of the water tank, starting a water pump 20, allowing the water in the water tank 10 to enter the pathogen concentrator 30 from the water outlet 102 of the water tank under the pressure action of the water pump 20, discharging a part of water from a second water outlet 305 of the pathogen concentrator 30 through a membrane layer of the inorganic ceramic ultrafiltration membrane 302, and collecting the part of water for later use (the part of water is filtrate containing pathogens smaller than 500 nm); and the other part of water flows out through the middle channel of the inorganic ceramic ultrafiltration membrane 302 and the liquid flowing out from the gap between the inorganic ceramic ultrafiltration membrane 302 and the shell 301 is discharged from the first water outlet 304 of the pathogen concentrator 30, enters the water tank 10 from the water inlet 101 of the water tank through the connecting pipeline 40 for circulating concentration, collects filtrate, and opens the control valve 100 to discharge the residual water in the water tank 10 from the water outlet 90 until the concentration is not needed any more. During the circulation concentration, cooling water is introduced from the cooling water inlet 103 to cool the water body in the water tank 10.
In some preferred cases, the volume of the filtrate collected after the end of the concentration is equal to the volume of the raw water entering the water tank 10.
(2) Replacing a filter element in the pathogen concentrator 30 with an inorganic ceramic ultrafiltration membrane 302 with the aperture of 50nm, injecting the filtrate containing the pathogens with the particle size of less than 500nm collected in the step (1) into the water tank 10, circularly concentrating, taking out the inorganic ceramic ultrafiltration membrane 302 after filtering is finished, washing with water or buffer solution such as PBS buffer solution for multiple times, and collecting washing liquid to obtain concentrated solution containing the pathogens with the particle size of 50-500nm, wherein the concentrated solution can be directly used for a subsequent detection test.
In some preferred modes, the water collected from the field is pre-filtered by a mesh screen to filter large particles such as duckweed and gravel, and then is injected into a water tank for concentration. In some preferred modes, a 600-mesh stainless steel net screen is adopted to filter large particles such as duckweed and gravel.
Example 2: concentration detection of PMMoV plant virus in water body
The concentration device is provided with an inorganic ceramic ultrafiltration membrane with the aperture of 500nm, firstly, a water body to be measured (50L raw water) is filtered through a stainless steel mesh with the size of 600 meshes to filter duckweed, gravel and other large particles, and the filtered water body is slowly injected into the tank body. Firstly, using 500nm aperture inorganic ceramic ultrafiltration membrane (pressure 0.2MPa, temperature 10-40 deg.C) to retain filtrate (called 500nm filtrate). Slowly injecting the 500nm filtrate into the tank again, and filtering with 50nm inorganic ceramic ultrafiltration membrane (pressure 0.2MPa, temperature 10-40 deg.C). After filtration, the ultrafiltration membrane was removed and washed several times with 20-50mL 1 XPBS using a 50mL syringe, the final wash was concentrated. The raw water, the concentrated solution, and the purified PMMoV virions were each pipetted at 5. mu.L, directly adsorbed onto a positively charged nylon membrane, blocked with 20mL of PBS (containing 2% BSA) for 30 minutes, washed with 20mL of PBS-T (containing 0.05% Tween-20) for 15 minutes on a shaker, and washed 3 times repeatedly. 20mL of the primary antibody reaction solution (10. mu.L of PMMoV-CP antibody, 0.5% BSA) was reacted for 30 minutes, followed by shaking for 15 minutes with 20mL of PBS-T (containing 0.05% Tween-20), and washing was repeated 3 times. After 20mL of the secondary antibody reaction solution (10. mu.L of rabbit anti-alkaline phosphatase, 0.5% BSA) had reacted for 30 minutes, the reaction solution was subjected to shaking washing with 20mL of PBS-T (containing 0.05% Tween-20) for 15 minutes, and the washing was repeated 3 times. Adding 1mL of NBT/BCIP color developing solution to the washing liquid membrane, and developing for 10 minutes in the dark. The results showed that the sample from 50L of raw water had no color reaction, while 50mL of the concentrate and PMMoV virions had a color reaction (FIG. 3). The method can well concentrate the virus in the water body.
Example 3: bacterial filtration
The concentration device is provided with an inorganic ceramic ultrafiltration membrane with the aperture of 500nm, the water body to be measured is firstly filtered through a stainless steel mesh with the mesh of 600 to filter large particles such as duckweed and gravel, and the filtered water body is slowly injected into the tank body. Firstly, using an inorganic ceramic ultrafiltration membrane with the aperture of 500nm (the pressure is 0.2MPa, and the temperature is 10-40 ℃) to leave filtrate. 100 mu L of the raw water and 500nm filtrate are respectively taken and coated on an LB culture medium, and cultured for 48h at 28 ℃, and the result shows that the colony number of the raw water is obviously higher than that of the filtered water (figure 5), which shows that the device can intercept most of bacteria.
Example 4: bacterial concentration
The concentration device is provided with an inorganic ceramic ultrafiltration membrane with the aperture of 500nm, firstly, the water body to be measured is filtered by a stainless steel mesh with 600 meshes to remove large particles such as duckweed and gravel, and the filtered water body is slowly injected into the tank body. Firstly, using an inorganic ceramic ultrafiltration membrane with the aperture of 500nm (the pressure is 0.2MPa, and the temperature is 10-40 ℃) to leave filtrate. Slowly injecting the 500nm filtrate into the tank again, and filtering with 50nm inorganic ceramic ultrafiltration membrane (pressure 0.2MPa, temperature 10-40 deg.C). After filtration, the ultrafiltration membrane was removed and washed several times with 20-50mL 1 XPBS using a 50mL syringe, the final wash was concentrated. And respectively taking 100 mu L of the 500nm filtrate and 100 mu L of the concentrated solution, coating the filtrate and the concentrated solution on an LB culture medium, and culturing at 28 ℃ for 48h, wherein the result shows that the thallus content in the concentrated solution is obviously higher than that of the 500nm filtrate (figure 6), which indicates that the device can be used for concentrating bacteria in a water body.
Example 5: size separation of bacteria
The concentration device is provided with an inorganic ceramic ultrafiltration membrane with the aperture of 500nm, firstly, the water body to be measured is filtered by a stainless steel mesh with 600 meshes to remove large particles such as duckweed and gravel, and the filtered water body is slowly injected into the tank body. Firstly, using an inorganic ceramic ultrafiltration membrane with the aperture of 500nm (the pressure is 0.2MPa, and the temperature is 10-40 ℃) to leave filtrate. Slowly injecting the 500nm filtrate into the tank again, and filtering with 50nm inorganic ceramic ultrafiltration membrane (pressure 0.2MPa, temperature 10-40 deg.C). After filtration, the ultrafiltration membrane was removed and washed several times with 20-50mL 1 XPBS using a 50mL syringe, the final wash was concentrated. After diluting 100. mu.L of each of the original and concentrated solutions 10-fold, 100. mu.L of each of the solutions was applied to LB medium and cultured at 28 ℃ for 48 hours, colonies shown in 1-4 were selected and observed by negative-staining electron microscopy, which revealed that the diameter of bacteria No. 1-4 was between 107 and 167nm (FIG. 7(A)), and that the diameter of bacteria No. 5 was about 652nm (FIG. 7 (B)). The raw water is filtered and concentrated by the 500nm and 50nm inorganic ceramic ultrafiltration membranes, so that bacteria with the diameter of 50-500nm in the raw water can be effectively separated.
Example 6: isolation of bacteria of specific size
The concentration device is provided with an inorganic ceramic ultrafiltration membrane with the aperture of 500nm, firstly, the water body to be measured is filtered by a stainless steel mesh with 600 meshes to remove large particles such as duckweed and gravel, and the filtered water body is slowly injected into the tank body. Firstly, using an inorganic ceramic ultrafiltration membrane with the aperture of 500nm (the pressure is 0.2MPa, and the temperature is 10-40 ℃) to leave filtrate. Slowly injecting the 500nm filtrate into the tank again, and filtering with 50nm inorganic ceramic ultrafiltration membrane (pressure 0.2MPa, temperature 10-40 deg.C). When half of the water body is filtered, the pressure is adjusted (the pressure is 0.4MPa, the temperature is 10-40 ℃) for filtering, and the filtrate is directly reserved from the second water outlet of the pathogen concentrator. Taking 100 μ L of the stock solution and the filtrate directly left at the second water outlet of the pathogen concentrator, diluting by 10 times, spreading 100 μ L on LB culture medium, and culturing at 28 deg.C for 48 h. The culture results showed that the low concentration of the disadvantaged bacterial colony a in the raw water precipitated a large amount at the second outlet of the pathogen concentrator under the high filtration pressure of 50nm, and the bacterial cells were uniform and single (FIG. 8).
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that fall within the spirit and principle of the present invention are intended to be included therein.
Claims (10)
1. A water pathogen concentrating device, the device comprising: water pitcher, water pump, pathogen concentrator and be used for connecting the connecting tube of water pitcher, water pump and pathogen concentrator, wherein, the delivery port of water pitcher with the water inlet of pathogen concentrator is linked together, the first delivery port of pathogen concentrator with the water inlet of water pitcher is linked together, the water pump is located the delivery port of water pitcher with between the water inlet of pathogen concentrator.
2. The device of claim 1, wherein the pathogen concentrator comprises a housing and an inorganic ceramic ultrafiltration membrane cartridge disposed in the housing, wherein the pathogen concentrator further comprises a second water outlet.
3. The apparatus of claim 2, wherein the inlet port and the first outlet port of the pathogen concentrator are disposed at opposite ends of the pathogen concentrator, and the second outlet port is located on a side wall of the housing between the inlet port and the first outlet port.
4. The device of claim 2 or 3, wherein the pathogen concentrator is removably attached to the device.
5. The apparatus according to claim 4, wherein the pathogen concentrator has external or internal threads at both ends of the housing corresponding to the water inlet and the first water outlet, and a connecting pipe for connecting the pathogen concentrator to the water pump and the water tank has matching internal or external threads.
6. The apparatus according to claim 5, wherein a movable connector is provided on a connection pipe for connecting the pathogen concentrator with the water pump and the water tank inlet, and the connector has an internal thread or an external thread for connecting with the pathogen concentrator.
7. The apparatus according to claim 1, wherein the water tank has a double-walled structure with a space for receiving cooling water between an outer wall and an inner wall of the water tank, wherein the outer wall of the water tank is provided with a cooling water inlet at one end and a cooling water outlet at the opposite end.
8. The apparatus according to claim 1, wherein a first pressure gauge, a pressure regulating valve and/or a temperature detector is provided on the connecting pipe connecting the first water outlet of the pathogen concentrator and the water inlet of the water tank.
9. The apparatus as claimed in claim 1, wherein a second pressure gauge is provided on a connection pipe connecting the water pump and the water inlet of the pathogen concentrator.
10. The apparatus according to claim 1, further comprising a drain opening in communication with the tank outlet.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201921687093.4U CN211954941U (en) | 2019-10-10 | 2019-10-10 | Water pathogen enrichment facility |
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| CN201921687093.4U CN211954941U (en) | 2019-10-10 | 2019-10-10 | Water pathogen enrichment facility |
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| CN211954941U true CN211954941U (en) | 2020-11-17 |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
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| CN110631888A (en) * | 2019-10-10 | 2019-12-31 | 宁波大学 | Water pathogen concentrating device and method |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110631888A (en) * | 2019-10-10 | 2019-12-31 | 宁波大学 | Water pathogen concentrating device and method |
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