Use of Copper Silicate for the Control of Legionella
FIELD OF THE INVENTION
The present invention relates to the use of copper silicate as a bactericide and more particularly for the control of bacteria of the Legionella genus, such as L pneumophila and L. longbeachae. The present invention also relates to Legionella resistant potting mix, soil, compost and air conditioning systems.
BACKGROUND ART
Certain bacteria of the Legionella genus cause a pneumonia-like disease which can be fatal. Legionnaire's disease, which was first recognised in 1976, is one such disease caused by L pneumophila. Whilst L. pneumophila is difficult to cultivate in the laboratory it persists and is disseminated through infected water in air conditioning units. People become infected by breathing in vapour containing spores or bacteria.
L. longbeachae is another bacterial species that has caused a number of fatalities. L. longbeachae can persist in compost environments including potting mixes and has caused the death of a number of people who have inhaled bacteria or spores from infected potting mix.
Copper silicate is a known pesticide and fungicide and in soluble or aqueous form is a particularly useful anti-snail and anti-slug agent. However, the bactericidal properties of copper silicate have, until now, remained unreported.
Moreover, the prior art is silent to the use of copper silicate as an anti-Legionella agent.
Whilst antibiotics may be used to treat Legionella infections, no economical and effective method exists to control Legionella in the environment. It is an object of the present invention to provide a Legionella active composition and methods for
the control of Legionella in environments such as soils, composts and potting mix as well as air conditioning systems.
DISCLOSURE OF THE INVENTION
The present invention provides a method for controlling bacteria of the Legionella genus, the method comprising the step of administering to said bacteria an effective amount of copper silicate.
Throughout this specification, unless the context requires otherwise, the word "comprise", or variations such as "comprises" or "comprising" will be understood to imply the inclusion of a stated integer or group of integers, but not the exclusion of any other integer or group of integers including method steps.
Throughout this specification, unless the context requires otherwise, the word "control", or variations such as "controls" or "controlling" will be understood to encompass the prevention of bacterial growth in environments where there are no bacteria, the inhibition of bacterial growth and the killing of bacteria.
The method of the present invention may be applied to control all Legionella species. However, the method is particularly useful for the control of Legionella selected from the group of species comprising L. longbeachae, L dumoffii, L. gormanii, L. micdadei and L. pneumophila and even more preferably, L. longbeachae and L. pneumophila.
Preferably, the method of the present invention controls the bacteria by at least inhibiting their growth and even more preferably totally preventing their growth. In this regard, the copper silicate may act as a bacteriostatic agent. Alternatively, the copper silicate administered according to the method of the present invention may be lethal to the bacteria and thus act as a bactericide. Whether the copper silicate acts to inhibit growth or kills the bacteria depends at least partially on the amount of copper silicate administered and the medium in which the bacteria is located.
Thus, the present invention also provides a method for killing bacteria of the Legionella genus, the method comprising the step of administering to said bacteria an effective amount of copper silicate.
The copper silicate used in the method of the present invention is particularly useful as a bacte cide due to its ability to provide free copper ions in solution. This ability increases the activity of the copper silicate when compared to other copper compounds. When applied as a solution, the copper silicate adheres to surfaces and persists to extend its active life, thus providing additional advantages over other forms of copper.
The copper silicate may be applied in the method of the present invention in various forms and the particular form used is at least partially dependent upon the medium to which the copper is to be applied. For example, when the copper is applied to potting mix or some other solid or semi-solid medium, the copper silicate is preferably added as a solution. Alternatively, when the copper silicate is to be added to a liquid or fluid medium it may be added as a solid or a solution.
When the copper silicate is applied in the method of the present invention as a solution it preferably comprises an aqueous solution of acidified copper silicate. The acidified copper silicate solution is especially preferred in the method of the present invention as it has a number of advantages when compared to other copper compounds. These include: (i) persistent toxicity when compared to insoluble copper powders; and (ii) ease of application.
The method of the present invention may be applied to control Legionella bacteria wherever they may exist. Environments that may be particularly suitable for the application of the present invention are soils, compost and potting mix, as well as air conditioning systems. These environments are known to support Legionella and have been the source of many cases of Legionnaire's disease.
Thus, the present invention also provides a method for controlling Legionella in a medium containing compost, such as potting mix or soil, the method comprising the step of administering to said medium an effective amount of copper silicate.
In the method immediately above, the Legionella is preferably Legionella longbeachae, which is commonly found in compost environments including potting mix.
The present invention also provides a potting mix or soil composition including an effective amount of copper silicate, said effective amount being adapted to control Legionella.
Whilst it is yet to be confirmed, the copper silicate appears to act in at least one of the following ways. Firstly, the copper silicate may control the growth of amoeba in the compost environment thereby controlling the Legionella who may reproduce within the amoeba. Secondly, the copper silicate may act directly on the Legionella.
The present invention also provides a method for controlling Legionella in an air conditioning system, the method comprising the step of administering to said air conditioning system an effective amount of copper silicate.
In the method immediately above, the Legionella is preferably Legionella pneumophila, which is commonly found in the water used in air conditioning systems.
The copper silicate may be applied to various parts of the air conditioning system as required. For example, the copper silicate may be applied as a coating, such as paint, to the inside surfaces of the tank which holds the reservoir water for the air conditioning system. Alternatively, the copper silicate may be applied directly into the reservoir water.
As mentioned above, the effective amount of copper silicate may be varied depending on the particular application. When the copper silicate is in the form of an aqueous solution of acidified copper silicate, preferably SOCUSIL™ (trade mark of Sheen Biotechnology Pty Ltd and subject of US Patent 5,474,972), the effective amount of copper silicate may be to a final concentration of at least approximately 0.0013% or at least approximately 0.0028%. In one particular form, the final concentration of copper silicate is approximately 0.0013% - 0.0056%.
When the copper silicate is applied to potting mix, the effective amount is to a final concentration of at least approximately 0.011 %, more preferably at least approximately 0.028%, even more preferably at least approximately 0.037% or still more preferably at least approximately 0.056%. In one particular form, the final concentration of copper silicate is approximately 0.011 % - 0.056%.
The effective amounts of copper silicate for use in air conditioning systems may be determined by one of ordinary skill in the art without undue experimentation using appropriate in situ and in vitro experiments. However, it is expected that the effective concentration of copper silicate in air conditioning systems will be comparable to those in soil environments.
The present invention will now be described with reference to examples. The description of the examples is in no way to limit the generality of the preceding description.
EXAMPLES
General Materials
L. longbeachae strains
Several L. longbeachae strains were used in the examples. These included reference strains, clinical isolates, and environmental isolates. Table 1 lists all L.
longbeachae strains used along with their laboratory number, country of origin, and original source All strains were obtained from the freeze dried culture collections at The Western Australian Centre for Pathology and Medical Research (PathCentre)
Table 1 L longbeachae strains used in the examples
Organism Country of Origin Original Source
L longbeachae Australia Potting Mix
L longbeachae Australia Clinical isolate
L longbeachae Australia Mulch
L longbeachae Australia Karri and peat mulch
L longbeachae Australia Jungle mix
L longbeachae USA Reference Strain
Other Legionella species
Several Legionella species apart from L longbeachae were used in the examples These are listed in table 2 with their laboratory number, origin, and type All strains were obtained from the freeze dried culture collections at the PathCentre
Table 2 Other Legionella species used in the examples
All potting mixes used are listed in table 3 All potting mix and dirt samples were stored at room temperature in sealed bags or containers Fresh bags were used in the non-sterile potting mix experiments
Table 3 Potting mixes, dirt, and seed mix used in the examples
Example 1 : Testing of Copper Silicate Against Legionella pneumophila
Reagents
(1 ) Legionella pneumophila serogroup I (ATCC 33152)
(2) Copper silicate solution - 2.8g/L.
Method
(1 ) Prior to use, the copper silicate solution SOCUSIL was autoclaved to remove all existing organisms which were present. Autoclaving was carried out at 121°C and 103.5Kpa.
(2) 0.1 mL of neat suspension of Legionella pneumophila serogroup I organisms (count of 5.5 x 106 CFU/mL) was inoculated aseptically into 10mL of the autoclaved copper silicate solution. This gave a concentration of organisms in the copper solution of 5.4 x 104 CFU/mL.
(3) The mixture was vortexed and placed in the incubator at 36°C.
(4) Samples of 50ul were removed at 1 , 2, 4 and 24 hours and placed onto B.Y.C.E. media and horse blood agar.
(5) These subsamples were incubated at 36°C for 10 days.
(6) Examination of the culture were carried out every second day.
(7) Control cultures on B.Y.C.E media and horse blood agar were performed using 50ul of the suspension of the organisms without the presence of the copper solution.
Results
Table 4
Example 2 - MIC of SOCUSIL (agar dilution method)
Methods
Preparation of media
To determine the MIC of SOCUSIL against L. longbeachae and relative to other copper compounds, BCYE agar was supplemented with various amounts of SOCUSIL, copper sulphate and malachite green. 20ml total volumes were used and each solution was thoroughly mixed before pouring of plates. All plates were made in triplicate to ensure accuracy. Initially 2ml (1 :10 dilution), 0.4ml (1 :50 dilution), 0.2ml (1 :100 dilution), and 0.1 ml (1 :200 dilution) of copper compound was added to BCYE agar. Based on these results, further dilutions were performed as required for each compound until the MIC was determined. Plates were stored at 4°C for 24 to 48 hours before inoculation to reduce the risk of contamination.
Inoculation of plates
Individual suspensions of each of the bacterial strains listed in tables 1 and 2 were prepared in sterile distilled water and adjusted to the turbidity of a 1
McFarland turbidity standard on a Vitek colorimeter 100μl of each suspension was added to 3 wells of a replica plate Plates were inoculated by replica plating using a Denley machine resulting in an inoculum of approximately 106 bacteria/inoculum Two BCYE plates were inoculated in the same manner to act as controls All plates were incubated in candle jars for 5 days at 36°C or until growth appeared on control plates
Results
The MIC of SOCUSIL is shown in table 5 The MIC for SOCUSIL of 0 0028% was the same for all L longbeachae strains tested (refer to table 1 for complete list) and was lower than the MIC for the other copper compounds tested All bacterial strains grew on control plates after four days incubation
Table 5 Minimum inhibitory concentrations (MIC) using the agar dilution method
nt - not tested > = MIC is greater than the concentration tested
Example 3 - MIC of SOCUSIL (in broth)
Methods
To determine the MIC of SOCUSIL in broth, cultures were set up to contain the same concentration of bacteria but varying amounts of SOCUSIL as described in table 6 L longbeachae cultures were set up in sterile distilled water (SDW) A control containing only bacteria was set up for each to ensure the bacteria were alive, as was a purity control to ensure only L longbeachae were present
Table 6 : Preparation of cultures to determine MIC of SOCUSIL in broth
Viable counts were performed on each sample every 2 days for 6 days. Viable counts were performed by serially diluting 10μl amounts from each sample 10 fold until a dilution of 1 :100000 was obtained. Three 10μl amounts from each dilution, including the culture itself, were spot plated and incubated on BCYE plates.
Results
The MICs of SOCUSIL against L longbeachae in broth are shown in table 7. From the results, the MIC of SOCUSIL with a broth initially containing approximately 2x104 L. longbeachae/mϊ was 0.056%.
Table 7 : MIC of SOCUSIL in broth against L .longbeachae
- = No Growth
Example 4 - Effect of SOCUSIL on Legionella in Potting Mix and Dirt
Methods
Preparation of L. longbeachae
L longbeachae suspensions were prepared in sterile distilled water and adjusted to the turbidity of a 0.5 McFarland turbidity standard using a Vitek calorimeter. 5ml of these suspensions was added to 45ml of sterile distilled water and mixed thoroughly. This 1 :10 suspension, approximately 106 L longbeachae/ml, was then used to seed potting mix and dirt samples.
Preparation of potting mix and dirt
5g samples of potting mix A and dirt were weighed out into 50ml centrifuge tubes. All samples were then sterilised by autoclaving for 15 minutes at 121 °C and used that day.
Following sterilisation, sterile distilled water and the copper compound were added (to give a total volume of 2.5ml) to the soil samples to determine their effect in this environment. A starting concentration of four times their MIC in agar, as previously determined, was used, followed by higher amounts as required. The samples were then seeded by the addition of 1ml of the L longbeachae suspension. A sterility control was set up by the addition of 2.5ml of sterile distilled water to a sterile 5g potting mix or dirt sample. A control to ensure bacteria were surviving was set up by the addition of 1.5ml of sterile distilled water and 1 ml of the L. longbeachae suspension to the soil samples. Four samples of each chemical concentration were set up for each soil type to allow long term testing.
Following the addition of all substances, samples were mixed thoroughly by vortexing and then incubated for 1 and 7 days under aerobic conditions at 36°C.
Once the MIC was determined, potting mixes B, C, E, and H were tested in the same manner but using a 0.056% and 0.08% concentration of SOCUSIL only. These samples were incubated overnight.
Results
Results are shown in table 8. Initially only potting mix A and dirt were used to determine the concentration of SOCUSIL required to kill Legionella in their natural environment.
The results obtained are shown in table 8 for potting mix A and table 9 for sterile dirt. After autoclaving, potting mix and dirt samples were sterile as indicated by a lack of growth of any organisms on BCYE and BA plates inoculated with the sterility control samples which contained only SDW.
The concentration required to kill approximately 105 L longbeachae/5g of potting mix for SOCUSIL was 0.056% and for CuSO4 was 0.56%. This value did not change after several days incubation. In sterile dirt, the amount required to kill
the same number of L. longbeachae was slightly less, being 0.028% for SOCUSIL and 0.14% for CuSO4, after seven days incubation.
Table 8 - Effect of SOCUSIL and copper sulphate on L longbeachae in sterile potting mix A.
Day 1
Day 7
Table 9 : Effect of SOCUSIL and copper sulphate on L longbeachae in sterile dirt
Day 1
Once the activity of SOCUSIL was determined, potting mixes A, B, C, E, and H were tested. The results are shown in table 10. At a concentration of 0.056% CuSi some L. longbeachae were recovered from potting mix A. In samples containing 0.056% SOCUSIL, 99% of bacteria, which correlated to approximately 3.6x106 L. longbeachae/ml, were killed. No L. longbeachae were recovered from samples containing 0.084% CuSi.
Table 10 : Effect of SOCUSIL on L. longbeachae in other potting mixes
- = No Growth
Example 5 - Effect of SOCUSIL on Plant Growth
Methods
To determine if SOCUSIL has any negative effects on plant growth, compost (brand I) and potting mix (brand E) samples were made up to contain either 0.5% or 1 % copper silicate. 12 tomato seeds were then planted at the same depth and spacing in the soil samples. The seedlings were then along with tomatoes planted at the same time and in the same manner but in normal seed mix. Growth of all seedlings was then monitored and plants measured and inspected to determine any effects on growth that SOCUSIL may have had compared to growth of plants in a SOCUSIL free environment.
Results
The average heights of the tomato plants are shown in table 1. Statistical analysis of this data is shown in table 12. SOCUSIL had no negative effects on plant growth at a concentration of 0.5% and 1 %, and resulted in plants possessing thicker stems and larger leaves. In some cases, a significant increase in average plant height was observed in seeds planted in soil containing SOCUSIL to that which did not.
Table 1 1 Effect of SOCUSIL on plant growth
E = standard error of mean, E = Proprietary potting mix with no SOCUSIL, F = Proprietary potting mix with 0 5% SOCUSIL, G = Proprietary potting mix with 1 % SOCUSIL, H = Seed Mix with no SOCUSIL, I = Compost with no SOCUSIL, J = Compost with 0 5% SOCUSIL, K = Compost with 1% SOCUSIL, - = no growth
Table 12 Statistical analysis of plant growth
= roprietary potting mix wit no SOC SIL, F = Proprietary potting mix with 0 5% SOCUSIL, G = Proprietary potting mix with 1 % SOCUSIL, H = Seed Mix with no SOCUSIL, I = Compost with no SOCUSIL, J = Compost with 0 5% SOCUSIL, K = Compost with 1 % SOCUSIL, N = no significant difference between the average height of plants in the two different soil types, Y = significant difference between the average height of plants in the two different soil types
The present invention includes any and all modifications and adaptations apparent to one skilled in the art