WO1997001643A1 - Toxicity detection - Google Patents

Toxicity detection Download PDF

Info

Publication number
WO1997001643A1
WO1997001643A1 PCT/GB1996/001539 GB9601539W WO9701643A1 WO 1997001643 A1 WO1997001643 A1 WO 1997001643A1 GB 9601539 W GB9601539 W GB 9601539W WO 9701643 A1 WO9701643 A1 WO 9701643A1
Authority
WO
WIPO (PCT)
Prior art keywords
bacteria
detector
fluid
detector according
actions
Prior art date
Application number
PCT/GB1996/001539
Other languages
French (fr)
Inventor
John Edmund Upton
Stephen Roy Pickin
Original Assignee
Severn Trent Water Limited
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Severn Trent Water Limited filed Critical Severn Trent Water Limited
Priority to AU62356/96A priority Critical patent/AU710100B2/en
Priority to AT96920986T priority patent/ATE256752T1/en
Priority to DE69631140T priority patent/DE69631140T2/en
Priority to NZ311113A priority patent/NZ311113A/en
Priority to EP96920986A priority patent/EP0837947B1/en
Publication of WO1997001643A1 publication Critical patent/WO1997001643A1/en
Priority to NO976075A priority patent/NO976075L/en

Links

Classifications

    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00—Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/18—Water
    • G01N33/186—Water using one or more living organisms, e.g. a fish
    • G01N33/1866—Water using one or more living organisms, e.g. a fish using microorganisms
    • C—CHEMISTRY; METALLURGY
    • C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
    • C12Q—MEASURING OR TESTING PROCESSES INVOLVING ENZYMES, NUCLEIC ACIDS OR MICROORGANISMS; COMPOSITIONS OR TEST PAPERS THEREFOR; PROCESSES OF PREPARING SUCH COMPOSITIONS; CONDITION-RESPONSIVE CONTROL IN MICROBIOLOGICAL OR ENZYMOLOGICAL PROCESSES
    • C12Q1/00—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions
    • C12Q1/02—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms
    • C12Q1/025—Measuring or testing processes involving enzymes, nucleic acids or microorganisms; Compositions therefor; Processes of preparing such compositions involving viable microorganisms for testing or evaluating the effect of chemical or biological compounds, e.g. drugs, cosmetics
    • G—PHYSICS
    • G01—MEASURING; TESTING
    • G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N2520/00—Use of whole organisms as detectors of pollution

Definitions

  • This invention relates to the detection of toxic substances, and finds application in the detection of substances toxic to bacteria in waste water.
  • the invention relates particularly, but not exclusively, to the detection of substances toxic to nitrifying, denitrifying and carbon-degrading bacteria.
  • a widely used method of controlling ammonia levels in water is the biological oxidation of ammonia to nitrate using nitrifying bacteria.
  • these bacteria are very sensitive to, and are easily inhibited by, a wide range of toxic substances, for example organic compounds and heavy metals.
  • other bacteria types are used to control the levels of other harmful materials in waste water. These also are susceptible to toxic substances.
  • Waste water carrying such substances can have devastating effects if allowed to enter waste water treatment plants, where bacteria are often used. There is therefore a need for a method of detecting these toxic substances prior to the waste water entering the plant. This may be achieved by assessing the effect of such substances on bacteria, for example the inhibition of bacteria may be measured.
  • the invention provides, in one of its aspects, a method of testing a fluid for the presence of substances which are toxic to selected bacteria in which bacteria held immobilised by encapsulation in a polyvinyl alcohol medium are exposed to the fluid and the effects of the fluid on one or more actions of the bacteria are assessed.
  • bacteriological actions may be assessed, for example biological nitrification, denitrification, phosphate uptake and release, and general carbonaceous actions.
  • a number of encapsulation techniques may be used with this medium.
  • the chosen technique should preferably allow rapid recovery of bacteria activity after encapsulation.
  • the technique should also preferably allow nutrients and gases, for example oxygen, to reach the bacteria.
  • a freeze/thaw encapsulation technique is used. This method enables the production of large volumes of encapsulated bacteria.
  • Polyvinyl alcohol is used as the medium for encapsulation for several reasons. It is non toxic to at least nitrifying bacteria. It has good structural integrity, and resists breaking up e.g. when fluidised by air. Polyvinyl alcohol gives a polymer medium which is non ionic, and does not therefore selectively absorb compounds onto its surface. In addition, polyvinyl alcohol is a bulk commodity, which is readily available and low in cost.
  • the bacteria are preferably distributed amongst many small pieces of the polyvinyl alcohol medium, e.g. small cubes or spheres. Preferably, these have a long shelf-life and can be easily stored.
  • Encapsulation allows complete specificity of the type of bacteria held within the medium, ensuring a standard reaction for all detectors, which is reproducible. It also allows a high number of bacteria to be quickly captured and retained in the medium, giving effective detectors with good response times. Depending on the encapsulation technique used, the time taken for the bacteria to become fully active may be short, giving detectors with good start-up times.
  • Using a suitable form of the polyvinyl alcohol medium makes the immobilised bacteria easy to store. Bacteria in a detector can therefore be quickly replaced if necessary, thereby restoring detector function in a short period of time.
  • Various conditions in the fluid essential to the well-being of the bacteria e.g. temperature, pH level and oxygen level may be monitored.
  • the invention provides, in another of its aspects, a method of constructing a detector for use in testing a fluid for the presence of substances which are toxic to selected bacteria, comprising immobilising bacteria by encapsulation in a polyvinyl alcohol medium and introducing the encapsulated bacteria into a detector vessel whereby the effects of the fluid on them can be assessed.
  • the method may further comprise monitoring one or more actions of the bacteria after introduction into the detector vessel until such action or actions reaches a threshold value.
  • a detector for the detection of substances which are toxic to selected bacteria comprising a detector vessel in which bacteria immobilised by encapsulation in a polyvinyl alcohol medium are situated and into which a fluid to be tested can be introduced, and means for assessing effects of the fluid on one or more actions of the bacteria.
  • the means for assessing effects of the fluid on one or more actions of the bacteria may comprise means to which substances indicative of action of the bacteria are fed from the detector vessel.
  • the means for assessing the effects of the fluid may comprise means arranged to assess substances within the detector vessel which are indicative of action of the bacteria.
  • the detector vessel may comprise an outlet through which substances indicative of action of the bacteria can leave the detector. Such substance or substances may each be fed to an appropriate monitor, where the action or actions of the bacteria are assessed. This information can then be used to determine if any toxic substances are present in the fluid under test. Additionally or alternatively a monitor or monitors may be provided within the detector vessel which may assess the action or actions of the bacteria.
  • the detector vessel may be of any suitable shape, for example a tubular body. It may be manufactured from any suitable material, for example plastic, and in a preferred form is made from transparent plastic.
  • the encapsulated bacteria may take any suitable form, and are preferably distributed amongst many small pieces of the medium e.g. small cubes or spheres. These may be immersed in a liquid within the detector, which liquid may be water. The encapsulated bacteria preferably occupy approximately 50% of the volume of the detector vessel.
  • the detector may further comprise means for monitoring conditions essential to the well-being of the bacteria within the detector vessel. This may take any suitable form.
  • monitoring means may be provided within the detector vessel, or substances indicative of the conditions fed to external monitoring means.
  • Various conditions within the detector may be monitored. For example, the pH level, the temperature or the oxygen level may be measured.
  • the conditions within the detector which require monitoring will depend on the type of bacteria used.
  • the detector may further comprise means for controlling the conditions within the detector vessel, for example, a heater may be provided to maintain the temperature at a suitable level, or a pH controller may be provided.
  • the levels of various gases may be controlled depending on the conditions required by the bacteria.
  • means for introducing oxygen e.g. an air compressor and air stone may be provided in the detector ves ⁇ el to maintain a suitable level of dissolved oxygen therein.
  • the output of any monitor may be fed to any suitable data processor, which may display this information in any suitable form, for example, visually on a screen.
  • the data processor may also determine other data, for example the percentage inhibition of the bacteria.
  • the output of the monitor or monitors may alternatively or in addition to the above, be used to generate a warning which may for example be an audio or visual warning.
  • the detector thus provided is effective yet simple to manufacture and install. It is easy to replace and has no lengthy start-up or down-time as in other detectors. Unlike flask tests and fixed film detectors, standard and reproducible results may be obtained.
  • Nitrifying bacteria are widely present in waste water treatment plants and it is important to be able to determine if water intended for discharge to such plants contains any toxic substances harmful to these bacteria.
  • a detector 1 comprises a 1.5 litre clear plastic tubular body forming a detector vessel 2. This contains Nitrosomonas and Nitrobacter nitrifying bacteria encapsulated in 2-3mm cubes of polyvinyl alcohol, the cubes being immersed in water. An air compressor pumps air to an air stone 3 situated within the detector. This is used to fluidise the cubes and maintain the dissolved oxygen level above 5.0 mg/l. A dissolved oxygen monitor 4 is also provided, information from which is relayed to a data processor 5, and used to determine the oxygen conditions within the detector vessel 2. A heater 6 is also provided within the detector, to maintain the temperature of the water and encapsulated bacteria at a suitable level.
  • An inlet 7 is provided on the detector 1. This is connected to a feed pump 8 which is arranged to draw from a feed tank 9.
  • An outlet 10 is also provided on the detector 1. This is connected to an ammonia monitor 11.
  • a pH monitor 12 is also provided. The outputs of the ammonia monitor and the pH monitor are relayed to the data processor 5.
  • a waste water sample which requires testing is passed into the feed tank 9 and fed by the pump 8 via the inlet 7 into the detector body 2.
  • the ammonia level discharged through the outlet 10 is measured by the ammonia monitor 11.
  • the output from this monitor is relayed to the data processor 5, where it is used to calculate the percentage inhibition of the nitrifying bacteria, and hence determine if any toxic substances are present in the water sample.
  • the detector is manufactured as follows.
  • a suitable culture of nitrifying bacteria can be obtained commercially.
  • the nitrifying bacteria are then immobilised by encapsulation in polyvinyl alcohol as follows, using a known freeze thaw technique.
  • One litre of fully settled nitrifying bacteria is filtered overnight with a Whatman No. 1 filter paper and funnel, forming a paste on the filter paper.
  • a 20% (weight/volume) aqueous solution of polyvinyl alcohol, of a suitable grade, is added to tap water.
  • the paste is added to the polyvinyl alcohol and thoroughly mixed.
  • the resultant mixture is then poured into a flat tray and frozen at-20°C for 24 hours.
  • the resultant water-insoluble sheet of bacteria in polyvinyl alcohol is then allowed to thaw for 24 hours and cut into 2-3mm cubes. The cubes are washed with tapwater for 24 hours to remove any surplus polyvinyl alcohol.
  • cubes may be manufactured in this way. These may be easily stored at 4°C, and have a shelf-life of between 8 and 12 months.
  • the cubes may be stored in a cartridge, which can easily be placed in a detector to replace bacteria which have been killed by a toxic shock.
  • the detector vessel is filled with tap water and cubes of encapsulated bacteria, the cubes occupying approximately 50-55% of the volume.
  • the detector vessel is aerated to fluidise the cubes and maintain the dissolved oxygen level above 5.0 mg/l.
  • the detector is fed ammonium carbonate (at 20.0 mg/l N-NH 3 ) and potassium dihydrogen ortho phosphate (at 2.0 mg/l P-P0 4 ) .
  • the flow to the detector is increased in gradual increments over a 2 to 3 day period to a point where the residence time is approximately 30 minutes. At this residence time the outlet ammonia level should be below 5.0 mg/l N-NH 3 . Once the outlet has stabilised to give an ammonia level below this threshold value, the detector is ready for use.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Bioinformatics & Cheminformatics (AREA)
  • Proteomics, Peptides & Aminoacids (AREA)
  • Physics & Mathematics (AREA)
  • Analytical Chemistry (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • Zoology (AREA)
  • Immunology (AREA)
  • Wood Science & Technology (AREA)
  • Microbiology (AREA)
  • Medicinal Chemistry (AREA)
  • Biotechnology (AREA)
  • General Engineering & Computer Science (AREA)
  • Toxicology (AREA)
  • Molecular Biology (AREA)
  • Food Science & Technology (AREA)
  • Pathology (AREA)
  • General Physics & Mathematics (AREA)
  • Biophysics (AREA)
  • Genetics & Genomics (AREA)
  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Luminescent Compositions (AREA)
  • Electrotherapy Devices (AREA)
  • Apparatus Associated With Microorganisms And Enzymes (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)

Abstract

A method and detector for testing a fluid for the presence of substances toxic to selected bacteria is disclosed. The bacteria are immobilised by encapsulation in a polyvinyl alcohol medium, placed in the detector and exposed to the fluid. The effects of the fluid on one or more actions of the bacteria are then assessed, and this information used to determine the presence or absence of toxic substances in the fluid. Various bacteria types can be used, e.g. nitrifying, denitrifying and carbon-degrading bacteria. Encapsulation allows a high number of specific bacteria to be quickly captured and retained within the medium, giving detectors which have a standard reaction and which are effective and have good response times. Polyvinyl alcohol as a medium gives advantages of non toxicity to a range of bacteria, resistance to breaking up and wide availability.

Description

TOXICITY DETECTION
This invention relates to the detection of toxic substances, and finds application in the detection of substances toxic to bacteria in waste water. The invention relates particularly, but not exclusively, to the detection of substances toxic to nitrifying, denitrifying and carbon-degrading bacteria.
Various legislation exists which seeks to control the amount of harmful materials present in waste water for example limiting the levels of ammonia which can be discharged to water courses. These have been introduced to protect water courses from the harmful environmental effects of ammonia.
A widely used method of controlling ammonia levels in water is the biological oxidation of ammonia to nitrate using nitrifying bacteria. However, these bacteria are very sensitive to, and are easily inhibited by, a wide range of toxic substances, for example organic compounds and heavy metals. Similarly, other bacteria types are used to control the levels of other harmful materials in waste water. These also are susceptible to toxic substances.
Waste water carrying such substances can have devastating effects if allowed to enter waste water treatment plants, where bacteria are often used. There is therefore a need for a method of detecting these toxic substances prior to the waste water entering the plant. This may be achieved by assessing the effect of such substances on bacteria, for example the inhibition of bacteria may be measured.
Various methods for assessing the inhibition of nitrifying bacteria already exist. For example batch flask tests using liquid cultures are often used. However, a wide range of sources of nitrifying bacteria are employed in these, and this, and the inherent variability of such tests, makes them difficult to standardise and reproduce.
Fixed film detectors have also been proposed. In these, nitrifying cultures are grown on fixed, solid media. However, a number of problems exist with these detectors. For example, the media used can take a long time to be sufficiently colonised to achieve the high number of bacteria and therefore the high rate of nitrification required for an effective detector. This start-up time could be as long as eight weeks. Should the bacteria be killed off by a toxic shock, requiring replacement of the media, an eight-week down-time would ensue before the detector became operational again. In addition, even if sufficient nitrifying bacteria are colonised within such media, they do not adhere well to these media. It is therefore difficult to retain high numbers of bacteria in the detector, which limits detector effectiveness and response time. Of particular importance is the fact that the culture which develops on a medium can not be fully standardised; each detector may grow a slightly different culture. Results from such detectors are therefore difficult to standardise and reproducibility is poor.
The invention provides, in one of its aspects, a method of testing a fluid for the presence of substances which are toxic to selected bacteria in which bacteria held immobilised by encapsulation in a polyvinyl alcohol medium are exposed to the fluid and the effects of the fluid on one or more actions of the bacteria are assessed.
Various bacteriological actions may be assessed, for example biological nitrification, denitrification, phosphate uptake and release, and general carbonaceous actions.
A number of encapsulation techniques may be used with this medium. The chosen technique should preferably allow rapid recovery of bacteria activity after encapsulation. The technique should also preferably allow nutrients and gases, for example oxygen, to reach the bacteria. In a preferred embodiment, a freeze/thaw encapsulation technique is used. This method enables the production of large volumes of encapsulated bacteria.
Polyvinyl alcohol is used as the medium for encapsulation for several reasons. It is non toxic to at least nitrifying bacteria. It has good structural integrity, and resists breaking up e.g. when fluidised by air. Polyvinyl alcohol gives a polymer medium which is non ionic, and does not therefore selectively absorb compounds onto its surface. In addition, polyvinyl alcohol is a bulk commodity, which is readily available and low in cost.
The bacteria are preferably distributed amongst many small pieces of the polyvinyl alcohol medium, e.g. small cubes or spheres. Preferably, these have a long shelf-life and can be easily stored.
Using such a method to test for toxic substances has several advantages. Encapsulation allows complete specificity of the type of bacteria held within the medium, ensuring a standard reaction for all detectors, which is reproducible. It also allows a high number of bacteria to be quickly captured and retained in the medium, giving effective detectors with good response times. Depending on the encapsulation technique used, the time taken for the bacteria to become fully active may be short, giving detectors with good start-up times. Using a suitable form of the polyvinyl alcohol medium makes the immobilised bacteria easy to store. Bacteria in a detector can therefore be quickly replaced if necessary, thereby restoring detector function in a short period of time.
Various conditions in the fluid essential to the well-being of the bacteria (e.g. temperature, pH level and oxygen level) may be monitored.
The invention provides, in another of its aspects, a method of constructing a detector for use in testing a fluid for the presence of substances which are toxic to selected bacteria, comprising immobilising bacteria by encapsulation in a polyvinyl alcohol medium and introducing the encapsulated bacteria into a detector vessel whereby the effects of the fluid on them can be assessed.
The method may further comprise monitoring one or more actions of the bacteria after introduction into the detector vessel until such action or actions reaches a threshold value.
According to a third aspect of the invention, there is provided a detector for the detection of substances which are toxic to selected bacteria comprising a detector vessel in which bacteria immobilised by encapsulation in a polyvinyl alcohol medium are situated and into which a fluid to be tested can be introduced, and means for assessing effects of the fluid on one or more actions of the bacteria.
The means for assessing effects of the fluid on one or more actions of the bacteria may comprise means to which substances indicative of action of the bacteria are fed from the detector vessel. Alternatively, the means for assessing the effects of the fluid may comprise means arranged to assess substances within the detector vessel which are indicative of action of the bacteria.
The detector vessel may comprise an outlet through which substances indicative of action of the bacteria can leave the detector. Such substance or substances may each be fed to an appropriate monitor, where the action or actions of the bacteria are assessed. This information can then be used to determine if any toxic substances are present in the fluid under test. Additionally or alternatively a monitor or monitors may be provided within the detector vessel which may assess the action or actions of the bacteria.
The detector vessel may be of any suitable shape, for example a tubular body. It may be manufactured from any suitable material, for example plastic, and in a preferred form is made from transparent plastic.
The encapsulated bacteria may take any suitable form, and are preferably distributed amongst many small pieces of the medium e.g. small cubes or spheres. These may be immersed in a liquid within the detector, which liquid may be water. The encapsulated bacteria preferably occupy approximately 50% of the volume of the detector vessel.
The detector may further comprise means for monitoring conditions essential to the well-being of the bacteria within the detector vessel. This may take any suitable form. For example, monitoring means may be provided within the detector vessel, or substances indicative of the conditions fed to external monitoring means. Various conditions within the detector may be monitored. For example, the pH level, the temperature or the oxygen level may be measured. The conditions within the detector which require monitoring will depend on the type of bacteria used. The detector may further comprise means for controlling the conditions within the detector vessel, for example, a heater may be provided to maintain the temperature at a suitable level, or a pH controller may be provided. The levels of various gases may be controlled depending on the conditions required by the bacteria. For example, for bacteria which require aerobic conditions, means for introducing oxygen e.g. an air compressor and air stone may be provided in the detector vesεel to maintain a suitable level of dissolved oxygen therein.
The output of any monitor may be fed to any suitable data processor, which may display this information in any suitable form, for example, visually on a screen. The data processor may also determine other data, for example the percentage inhibition of the bacteria.
The output of the monitor or monitors may alternatively or in addition to the above, be used to generate a warning which may for example be an audio or visual warning.
The detector thus provided is effective yet simple to manufacture and install. It is easy to replace and has no lengthy start-up or down-time as in other detectors. Unlike flask tests and fixed film detectors, standard and reproducible results may be obtained.
There now follows a description, to be read with reference to the accompanying drawing, of a detector which illustrates the invention by way of example. The drawing is a schematic representation of the detector and associated apparatus.
Nitrifying bacteria are widely present in waste water treatment plants and it is important to be able to determine if water intended for discharge to such plants contains any toxic substances harmful to these bacteria.
A detector 1 comprises a 1.5 litre clear plastic tubular body forming a detector vessel 2. This contains Nitrosomonas and Nitrobacter nitrifying bacteria encapsulated in 2-3mm cubes of polyvinyl alcohol, the cubes being immersed in water. An air compressor pumps air to an air stone 3 situated within the detector. This is used to fluidise the cubes and maintain the dissolved oxygen level above 5.0 mg/l. A dissolved oxygen monitor 4 is also provided, information from which is relayed to a data processor 5, and used to determine the oxygen conditions within the detector vessel 2. A heater 6 is also provided within the detector, to maintain the temperature of the water and encapsulated bacteria at a suitable level.
An inlet 7 is provided on the detector 1. This is connected to a feed pump 8 which is arranged to draw from a feed tank 9. An outlet 10 is also provided on the detector 1. This is connected to an ammonia monitor 11. A pH monitor 12 is also provided. The outputs of the ammonia monitor and the pH monitor are relayed to the data processor 5. A waste water sample which requires testing is passed into the feed tank 9 and fed by the pump 8 via the inlet 7 into the detector body 2. The ammonia level discharged through the outlet 10 is measured by the ammonia monitor 11. The output from this monitor is relayed to the data processor 5, where it is used to calculate the percentage inhibition of the nitrifying bacteria, and hence determine if any toxic substances are present in the water sample.
The detector is manufactured as follows. A suitable culture of nitrifying bacteria can be obtained commercially. The nitrifying bacteria are then immobilised by encapsulation in polyvinyl alcohol as follows, using a known freeze thaw technique.
One litre of fully settled nitrifying bacteria is filtered overnight with a Whatman No. 1 filter paper and funnel, forming a paste on the filter paper. A 20% (weight/volume) aqueous solution of polyvinyl alcohol, of a suitable grade, is added to tap water. The paste is added to the polyvinyl alcohol and thoroughly mixed. The resultant mixture is then poured into a flat tray and frozen at-20°C for 24 hours. The resultant water-insoluble sheet of bacteria in polyvinyl alcohol is then allowed to thaw for 24 hours and cut into 2-3mm cubes. The cubes are washed with tapwater for 24 hours to remove any surplus polyvinyl alcohol.
It will be appreciated that a large number of cubes may be manufactured in this way. These may be easily stored at 4°C, and have a shelf-life of between 8 and 12 months. The cubes may be stored in a cartridge, which can easily be placed in a detector to replace bacteria which have been killed by a toxic shock.
The detector vessel is filled with tap water and cubes of encapsulated bacteria, the cubes occupying approximately 50-55% of the volume. The detector vessel is aerated to fluidise the cubes and maintain the dissolved oxygen level above 5.0 mg/l. The detector is fed ammonium carbonate (at 20.0 mg/l N-NH3) and potassium dihydrogen ortho phosphate (at 2.0 mg/l P-P04) . The flow to the detector is increased in gradual increments over a 2 to 3 day period to a point where the residence time is approximately 30 minutes. At this residence time the outlet ammonia level should be below 5.0 mg/l N-NH3. Once the outlet has stabilised to give an ammonia level below this threshold value, the detector is ready for use.

Claims

1. A method of testing a fluid for the presence of •substances which are toxic to selected bacteria in which bacteria held immobilised by encapsulation in a polyvinyl alcohol medium are exposed to the fluid and the effects of the fluid on one or more actions of the bacteria are assessed.
2. A method according to Claim 1 in which the action assessed is biological nitrification or denitrification.
3. A method according to Claim 1 or Claim 2 in which the actions assessed are phosphate uptake and phosphate release.
4. A method according to Claim 1 or Claim 2 or Claim 3 in which the actions assessed are carbonaceous actions.
5. A method according to any preceding claim in which the bacteria are immobilised by an encapsulation technique which allows nutrients and gases to reach the bacteria.
6. A method according to any preceding claim in which the bacteria have been immobilised by encapsulation using a freeze/thaw technique.
7. A method according to any preceding claim in which the bacteria exposed to the fluid are distributed amongst many small pieces of the medium.
8. A method according to any preceding claim which comprises monitoring conditions in the fluid essential to the well-being of the bacteria.
9. A method according to Claim 8 in which the conditions monitored include temperature and/or pH level and/or oxygen level.
10. A method of constructing a detector for use in testing a fluid for the presence of substances which are toxic to selected bacteria, comprising immobilising bacteria by encapsulation in a polyvinyl alcohol medium and introducing the immobilised bacteria into a detector vessel whereby the effects of the fluid on them can be assessed.
11. A method according to Claim 10 which further comprises monitoring one or more actions of the bacteria after introduction into the detector vessel until such action or actions reaches a threshold value.
12. A detector for the detection of substances which are toxic to selected bacteria comprising a detector vessel in which bacteria immobilised by encapsulation in a polyvinyl alcohol medium are situated and into which a fluid to be tested can be introduced, and means for assessing effects of the fluid on one or more actions of the bacteria.
13. A detector according to Claim 12 in which the means for assessing effects of the fluid on one or more actions of the bacteria comprises means to which substances indicative of action of the bacteria are fed from the detector vessel.
14. A detector according to Claim 12 or Claim 13 in which the means for assessing effects of the fluid on one or more actions of the bacteria comprises means arranged to assess substances within the detector vessel which are indicative of action of the bacteria.
15. A detector according to any of Claims 12 to 14 in which the detector vessel comprises a tubular body.
16. A detector according to Claim 15 in which the tubular body is of transparent plastic.
17. A detector according to any of Claims 12 to 16 in which the bacteria are distributed amongst many small pieces of the medium.
18. A detector according to any of Claims 12 to 17 in which the encapsulated bacteria are immersed in a liquid.
19. A detector according to Claim 18 in which the liquid is water.
20. A detector according to any of Claims 12 to 19 in which the encapsulated bacteria occupy approximately 50% of the volume of the detector vessel.
21. A detector according to any of Claims 12 to 20 which further comprises means for monitoring conditions essential to the well-being of the bacteria.
22. A detector according to claim 21 in which the means for monitoring conditions essential to the well-being of the bacteria are arranged to monitor temperature and/or pH level and/or oxygen level.
23. A detector according to any of Claims 12 to 22 which further comprises means for controlling conditions within the detector vessel.
24. A detector according to Claim 23 in which the means for controlling conditions comprises a heater.
25. A detector according to Claim 23 in which the means for controlling conditions comprises a pH controller.
26. A detector according to Claim 23 in which the means for controlling conditions comprises means for controlling the level of a gas or gases within the detector vessel.
27. A detector according to Claim 23 comprising means for introducing oxygen into liquid in the detector vessel.
28. A detector according to any of Claims 12 to 27 in which the output of any monitor is fed to a data processor.
29. A detector according to Claim 28 in which the data processor displays the output.
30. A detector according to Claim 28 or Claim 29 in which the data processor generates an audio or visual warning.
31. A detector according to Claim 28 or Claim 29 or Claim 30 in which the data processor uses the output of the monitor or monitors to determine further data.
32. A detector according to Claim 31 in which the data processor determines the percentage inhibition of the bacteria.
33. A detector substantially as described herein with reference to the accompanying drawing.
PCT/GB1996/001539 1995-06-28 1996-06-27 Toxicity detection WO1997001643A1 (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
AU62356/96A AU710100B2 (en) 1995-06-28 1996-06-27 Toxicity detection
AT96920986T ATE256752T1 (en) 1995-06-28 1996-06-27 TOXICITY DETECTION
DE69631140T DE69631140T2 (en) 1995-06-28 1996-06-27 TOXICITY DETECTION
NZ311113A NZ311113A (en) 1995-06-28 1996-06-27 Use of bacteria in a detector to test fluids for substances that are toxic to the bacteria
EP96920986A EP0837947B1 (en) 1995-06-28 1996-06-27 Toxicity detection
NO976075A NO976075L (en) 1995-06-28 1997-12-23 Toxicity Detection

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
GB9513123.1 1995-06-28
GBGB9513123.1A GB9513123D0 (en) 1995-06-28 1995-06-28 Toxicity detection

Publications (1)

Publication Number Publication Date
WO1997001643A1 true WO1997001643A1 (en) 1997-01-16

Family

ID=10776778

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/GB1996/001539 WO1997001643A1 (en) 1995-06-28 1996-06-27 Toxicity detection

Country Status (9)

Country Link
EP (1) EP0837947B1 (en)
AT (1) ATE256752T1 (en)
AU (1) AU710100B2 (en)
CA (1) CA2221111A1 (en)
DE (1) DE69631140T2 (en)
GB (1) GB9513123D0 (en)
NO (1) NO976075L (en)
NZ (1) NZ311113A (en)
WO (1) WO1997001643A1 (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0320483A2 (en) * 1987-12-11 1989-06-14 Monsanto Company Encapsulation method
EP0486443A1 (en) * 1990-11-15 1992-05-20 GENESIS S.r.L. Method of detecting toxic compositions in water by monitoring the metabolism of selected living cells as microorganisms

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0320483A2 (en) * 1987-12-11 1989-06-14 Monsanto Company Encapsulation method
EP0486443A1 (en) * 1990-11-15 1992-05-20 GENESIS S.r.L. Method of detecting toxic compositions in water by monitoring the metabolism of selected living cells as microorganisms

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
DATABASE WPI Section Ch Week 9344, Derwent World Patents Index; Class D04, AN 93-349028, XP002000522 *
E. ARVIN ET AL.: "A mini-nitrification test for toxicity screening, MINNTOX.", WATER RESEARCH, vol. 28, no. 9, 28 September 1994 (1994-09-28), pages 2029 - 2031, XP000451467 *
P. A. VANROLLEGHEM ET AL.: "An on-line respirographic biosensor for the characterization of load and toxicity of wastewaters.", JOURNAL OF CHEMICAL TECHNOLOGY AND BIOTECHNOLOGY, vol. 59, no. 4, April 1994 (1994-04-01), pages 321 - 333, XP000440851 *

Also Published As

Publication number Publication date
DE69631140D1 (en) 2004-01-29
EP0837947B1 (en) 2003-12-17
NO976075D0 (en) 1997-12-23
NZ311113A (en) 1998-08-26
EP0837947A1 (en) 1998-04-29
CA2221111A1 (en) 1997-01-16
AU710100B2 (en) 1999-09-16
ATE256752T1 (en) 2004-01-15
AU6235696A (en) 1997-01-30
NO976075L (en) 1998-02-24
DE69631140T2 (en) 2004-09-02
GB9513123D0 (en) 1995-08-30

Similar Documents

Publication Publication Date Title
US6936170B2 (en) Methods and apparatus for biological treatment of aqueous waste
US4162195A (en) Biological testing device and method of measuring toxicity of sewage
Pai et al. Monitoring and assessing variation of sewage quality and microbial functional groups in a trunk sewer line
US20070000825A1 (en) Process and apparatus for microbial filtration and bacterial injection for one or more environmental contaminants
He et al. Improving the performance of sequencing batch reactor (SBR) by the addition of zeolite powder
EP1652824B1 (en) Method and apparatus for treating ammonium-containing liquid
WO2001070637A1 (en) Method for direct clarification of ground water polluted with nitrate
Kors et al. Nitrification and low temperature in a raw water reservoir and rapid sand filters
Levstek et al. Estimation of the Specific Surface Area for a Porous Carrier.
Nyholm et al. Estimation of kinetic rate constants for biodegradation of chemicals in activated sludge wastewater treatment plants using short term batch experiments and μg/L range spiked concentrations
EP0837947B1 (en) Toxicity detection
Tian et al. Meso and micro-scale effects of loading and air scouring on nitrifying bio-cord biofilm
CA2243190C (en) Method for monitoring biological activity in fluids
Chen et al. Response of dissolved oxygen to changes in influent organic loading to activated sludge systems
JP2003000238A (en) Pva-inclusively immobilized microbe carrier, method for manufacturing the same and method for purifying environment by using the carrier
JP4623295B2 (en) Method and apparatus for measuring reaction ratio
JP6811360B2 (en) Water treatment method
JP2003265170A (en) Microorganism-immobilized carrier and method for purifying environment therewith
Talinli et al. Oxygen uptake rate inhibition test: a modified method for priority pollutants
Manning et al. Field Demostration of Slurry Reactor Biotreatment of Explosives-contaminated Soils
Boe-Hansen et al. Substrate turnover at low carbon concentrations in a model drinking water distribution system
Yaghmaei Studies on Treatment of Carbonaceous Wastewater by Fixed Film Aeration Tank
JP2000206087A (en) Method and device for detecting nitrification-blocking substance in sewage and discharged water
Himebaugh Microorganism inventory in activated sludge control
Lee et al. Backwash based methodology for the estimation of solids retention time in biological aerated filter

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A1

Designated state(s): AU CA GB JP KR NO NZ US

AL Designated countries for regional patents

Kind code of ref document: A1

Designated state(s): AT BE CH DE DK ES FI FR GB GR IE IT LU MC NL PT SE

DFPE Request for preliminary examination filed prior to expiration of 19th month from priority date (pct application filed before 20040101)
121 Ep: the epo has been informed by wipo that ep was designated in this application
ENP Entry into the national phase

Ref document number: 2221111

Country of ref document: CA

Ref country code: CA

Ref document number: 2221111

Kind code of ref document: A

Format of ref document f/p: F

WWE Wipo information: entry into national phase

Ref document number: 311113

Country of ref document: NZ

WWE Wipo information: entry into national phase

Ref document number: 1996920986

Country of ref document: EP

WWP Wipo information: published in national office

Ref document number: 1996920986

Country of ref document: EP

WWG Wipo information: grant in national office

Ref document number: 1996920986

Country of ref document: EP