Title of Invention

PROCESS FOR IN-SITU CLEANING OF DRINKING WATER FILTRATION MEDIA

Abstract The present invention provides a process to clean water filtration media in a filtration bed. The process includes applying a granular cleaner to the water filtration media (120) and applying an activator to the water filtration media (30). This causes a chemical reaction between the granular cleaner, activator and water filtration media resulting in the cleaning of the water filtration media. The residual granular cleaner and activator, along with suspended and dissolved contamination from the water filtration media, are removed by rinsing with water (40).
Full Text FIELD OF THE INVENTION
[0002! Tne present invention is generally directed toward a cleaning process-
More specifically, the present invention is directed toward a process for cleaning granular
water filtration media, such as various types of sand, anthracite coal or activated carbon,
BACKGROUND OF THE INVENTION
[0003] Filtration is an essential step in the treatment of drinking and industrial
water supplies, Filtration is carried out to remove contaminants which are either
introduced with the source water or are produced during the treatonent process and which
can affect water quality. Most commonly large-scale filtration involves passing the water
either through granular filter media, such as various types of sand, anthracite coal,
granular activated carbon or combinations thereof arranged in layers in a filter media Ded.
[0004] Contaminants removed during filtration accumulate within a granular filter
media bed. Over time, this accumulation leads to increased filter backpressure
(measured by increased head loss), increased turbidity of the low-through or in the worst
case scenario, to breakthrough of contaminants, Regular backwashing is used to remove
accumulated filtrate in an effort to maintain filter performance and capacity.
[0005] However, like every surface in contact with water, fitter media particles will
over time accumulate deposits of biological and non-biological material which cannot be
removed by backwashing and can significantly interfere with the filter's function. Thus, it
is important to dean the filter bed not only of the loose particles removable by
backwashing but also of these surface deposits.
[0000| Depending on the water source and environmental conditions, these
surface deposits on the fitter particles, can consist predominantly of organic matter
(biofilm), metal oxides, or calcium carbonate scale. Heavy fouling or scaling will
eventually reduce fitter performance. The consequences can be higher backwash
frequency, reduced flow-rates, increased water turbidity, breakthrough of contaminants or
a combination of these effects. If the deposits are not removed, the filter performance will
decline below tolerable levels and filter media exchange becomes necessary.
[0007] However, an exchange of the filtration media is very expensive in terms of
filtration media and downtime cost and may not be a practical maintenance solution for
water treatment installations which are exclusive to a number of consumers and have
only a single filtration bed. Thus, maintenance procedures allowing for the cleaning of the
filtration media as an alternative replacement are required.
[0008] Mechanical methods of filtration media cleaning include filter bed aeration
during backwash and spraying water on top of the filter bed to disperse soft aggregates.
This does not remove persistent surface deposits such as biofilm and scale. Chemical
treatments include washing the media in strong acids and bases, sometimes in
combination with surfactants. These chemical treatments can be satisfactory for certain
types of contamination, such as calcium carbonate scale. However, mixed deposits,
which include metal oxides and biological films, are either not removed efficiently or
require highly corrosive and hazardous cleaning agents which are difficult to use and may
leave residue not acceptable in drinking water processing installations. This generates a
need for alternative cleaning procedures, and products, which are sufficiently efficient and
convenient to present an alternative to media replacement.
[0009] Prior art filtration media cleaning methods of the chemical treatment type
generally include the steps of applying an aqueous solution of a strong acid or base to the
filtration media. However, the treatment liquid flows through the filtration media too
quickly for the cleaning reaction to be completed. Therefore, the treatment liquid must be
applied repeatedly, requiring vast amounts of treatment liquid, or the treatment liquid
must be circulated through the filtration media until the clearing reaction is completed,
requiring specialized and expensive circulation equipment. These approaches, although
an alternative to extended plant shut-down for filter media replacement, do not offer an
economical alternative to filter media replacement.
SUMMARY OF THE INVENTION
[0010] It is an object of the present invention to provide an efficient and
economical alternative to the prior art filtration media cleaning methods and products. The
present invention provides a product and process for the removal of surface deposits
from granular filter media. More particularly, the invention provides a product and
process for the in-situ cleaning of filter media used in drinking water treatment systems,
especially a product and process which is NSF certified for such use.
{0011J In a preferred embodiment, the invention is directed toward a cleaning
process for the cleaning of all types of granular water filtration media, such as sand,
gravel, manganese greensand, anthracite coal, granular activated carbon (GAC), and ion
exchange media or ceramic beads.
[0012] The invention preferably provides a process for the in-siiu cleaning of
water filtration media contained within a filtration bed. The preferred process includes the
steps of applying a granular cleaner onto the filtration media while the media is located
within the filtration bed and applying an activator compound thereafter for activation of the
cleaning composition. The granular cleaner reacts in conjunction with the activator
resulting in the cleaning of the media. After the cleaning has occurred, the residual
cleaner and activator are washed away in a rinsing step along with any suspended and
dissolved contamination which was removed from the filtration media. The granular
cleaner is preferably wetted after application to dissolve the cleaner and initiate the
cleaning reaction.
[0013] The activator can be applied in granular or liquid form. Preferably, the
activator is applied as an aqueous solution. In a variant of the preferred embodiment of
the process, the steps of applying the activator and wetting the cleaner are combined by
applying the activator in aqueous solution.
[0014] In another preferred embodiment, the process includes the further steps of
draining the water filtration bed prior to applying the granular cleaner. Preferably, the step
of wetting the granular cleaner is carried out by spraying water onto the cleaner or by
filling the filtration bed with water until the cleaner is submerged. The step of rinsing the
water filtration bed is preferably conducted through backwashing said filtration bed. The
process preferably includes the further step of allowing the chemical reaction to proceed
for at least 1 hour prior to rinsing the filtration bed. The rinsing step is preferably delayed
until the dissolved cleaner has reached a bottom of the filtration bed.
[0015] In a further preferred embodiment, the process includes the additional
steps of determining the degree of surface contamination of the filtration media and
calculating the amount of granular cleaner to be applied for insuring removal of the
surface contaminants. The determination of the degree of contamination preferably
includes the steps of taking a representative core sample from the filtration media, the
sample having a known volume, and the step of calculating the amount of cleaner
includes the steps of measuring the amount of cleaner required for removal of the surface
contaminants from the filtration media in the sample and extrapolating to the whole
filtration bed by multiplying the measured amount of cleaner by the ratio of filtration bed
volume/sample volume.
[0016] In a preferred embodiment of the process of the invention, the granular
cleaner includes an acid component for dissolving scale and metal oxides on and
removing biodeposits from the filtration media and optionally at least one component
selected from the group of a free flow additive for preventing clumping of the cleaner, a
surfactant for enhancing contact of the cleaner with the filtration medfa, an inhibitor for
protecting exposed metal surfaces from corrosion by the acid component, and a dye The
cleaner is preferably in the form of a free-flowing powder with a particle size of s O.Smm
for easy spreading of the cleaner on the filtration media,
[0017] In a preferred embodiment of the cleaner, the acid component is sulfamic
acid. In another preferred embodiment, the granular cleaner includes at least one
additional component selected from the group of citric acid, phosphoric acid, corrosion
inhibitor, free-flow additive and surfactant. Preferably the granular cleaner includes the
[0018] In the process above, the activator used is an activated oxygen donor, For
the purpose of this disclosure, the term activated oxygen donor defines compounds which
in aqueous solution decompose to generate oxygen radicals. Numerous activated oxygen
donors of this type are known and need not be listed in detail. The activated oxygen
donor is preferably selected from peroxides, most preferably hydrogen peroxide,
peracetic acid, precursors of peroxides, hydrogen peroxide and peracetic acid and
combinations thereof. The activator is most preferably either 5-50% hydrogen peroxide,
or 0.2 - 10% peracetic acid, or a combination of hydrogen peroxide and peracetic acid,
with the balance being water.
[0019] In a preferred embodiment of the process of the invention, the activator
can be in a liquid or dry state prior to its introduction into the filtration bed.
[0020] In a further preferred embodiment, the invention provides a granular
cleaner composition, comprising a granular cleaner as defined above and an activated
oxygen donor as defined above.
[0021] In another preferred embodiment of the process of the invention, the
rinsing step is preferably carried out by a backwashing procedure.
[0022] Further objects and features of the present invention will be apparent to
those skilled in the art upon reference to the accompanying drawings and upon reading
the following description of the preferred embodiments.
BRIEF DESCRIPTION OF THE DRAWINGS
[0023] Preferred embodiments of the invention will now be further described by
way of example only and with reference to the attached drawings, wherein
[0024] FIG, 1 Is a schematic flow diagram of a preferred process in accordance
with the present invention;
[0025] FIG. 2 is a schematic flow diagram of a variant of the process of FIG.1;
[0026] FIG. 3 is a schematic illustration of a fitter bed being cleaned with the
process of the invention and at commencement of the process of FIG. 1;
[0027] FIG. 4 is a schematic illustration of the filter bed of FIG. 3 at a later stage in
the cleaning process; and
[0028] FIG. 5 illustrates an alternative method of applying the granular cleaner.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS
(0029] Before explaining the present invention in detail, it is to be understood that
the invention is not limited to the preferred embodiments contained herein. The invention
is capable of other embodiments and of being practiced or carried out in a variety of
ways. It is to be understood that the phraseology and terminology employed herein are
for the purpose of description and not of limitation.
[0030] FIG, 1 is a schematic flow diagram of a preferred embodiment of a process
in accordance with the invention for the cleaning of water filtration media 110 contained
within a filtration bed 114 (see Fig. 4). In this embodiment, the process includes a first
application step 20 in which a granular cleaner is applied to the water filtration media
while the media is located within the filtration bed. In a wetting step 22, the granular
cleaner is wetted with an aqueous medium to dissolve the cleaner and promote its
vertical spread through the filtration media during the ensuing cleaning reaction.
Thereafter, an activator is applied onto the granular cleaner in a third application step 30
In a reaction step 40, the cleaner chemically reacts in conjunction with the activator
resulting in the cleaning of the media. The duration of reaction step 40 varies depending
on the degree of contamination of the media. However, the reaction step 40 is preferably
carried out for at least one hour, preferably the reaction step is conducted over night.
Most preferably, the reaction step 40 is carried out until the dissolved cleaner has
reached a bottom of the filtration bed and the filtration media is completely cleaned. The
point in time at which the filtration media is completely cleaned can be determined by
visual inspection to check for any foaming which would indicate an ongoing cleaning
reaction and/or by measuring the supernatant pH or metal content.
[0031] The inventors of the present process surprisingly discovered that the
automatic gradual advancement of the dissolved cleaner through the filtration media in
combination with the even spreading of the cleaner on the top surface of the filtration bed
completely obviates the need for circulation or re-circulation of the dissolved cleaner to
ensure an even distribution of the dissolved cleaner during the reaction step. Agitation of
the filtration bed during cleaning is also neither necessary nor desirable with the process
in accordance with the invention. This provides the process of the current invention with
significant economical and practical advantages.
[0032] After the cleaning step 40, any residual granular cleaner and activator are
washed away along with the suspended and dissolved contamination which was removed
from the water filtration media by rinsing the filtration media with water in a rinsing step
50. The rinsing step can be carried out by spraying water onto the filtration media or by
backwashing the filter bed. Backwashing is the preferred method of rinsing the filtration
media. The rinsing step 50 is best carried out until all residual cleaner and activator and
all dissolved and suspended contaminants such as scale, metal oxides and biocontaminants
have been removed. Completion of the rinsing step 50 can be determined
by monitoring the turbidity, pH and dissolved metal content of the backwash water, for
example. Since the filtration bed is not disturbed during the cleaning step, no settling
period is required and the filtration bed can be returned to production after the rinsing
step, the same as after a regular backwash cycle, providing the process of the invention
with yet another advantage over prior art processes involving agitation of the filtration
media during cleaning.
[0033] In the first application step 20, the granular cleaner is preferably evenly
spread on the top layer of the filtration media to promote an even distribution and
concentration of the dissolved cleaner during the reaction step 40. In the wetting step 30,
the filtration bed is filled with water until all the filter material is submerged. This can be
done by initiating a slow backwash flow until the desired water level is reached. The
backwash flow should be maintained sufficiently low to avoid agitation of the filter bed and
mixing of the granular cleaner with the filter material. For filters with very light filter
material which may be easily agitated by backwashing. the wetting step is preferably
carried out by spraying water onto the cleaner.
[0034] An even wetting of the cleaner over the whole area of the filtration media
top surface is desirable in order to achieve an even dissolution and concentration of the
cleaner throughout. The same applies for the activator, which is preferably evenly spread
on the granular cleaner to ensure the same ratio of cleaner to activator throughout the
filtration bed during the reaction step 40, The activator can be applied in granular or liquid
form. When the activator is applied in granular form, the cleaner and activator may be
mixed prior to application to produce a granular cleaner composition, which allows for the
combination of the first and third application steps 20 and 30 into a single application step
for the application of the cleaner composition. However, in the most preferred
embodiment of the process, the activator is applied as an aqueous solution, which allows
the compression of the steps of applying the activator and wetting the cleaner into a
single second application step. In another preferred embodiment of the process of the
invention the filtration bed is completely drained prior to the granular cleaner application
step 20.
[0035] The rinsing step 50 is preferably conducted through backwashing of the
filtration bed.
[0036] A further preferred embodiment of the process of the invention as
illustrated in Fig. 2 includes an analysis step 10 for determining the degree of surface
contamination of the filtration media and a calibration step 12 for calculating the amount
of granular cleaner to be applied for ensuring that the whole filtration media are exposed
to unreacted cleaner during the cleaning step 40. The analysis step 10 preferably
includes the step of taking a representative core sample from the filtration media, the
sample having a known volume, while the calibration step 12 preferably includes the
steps of first measuring the amount of cleaner required for substantially complete removal
of the surface contaminants from the filtration media in the sample and then extrapolating
to the amount required for the whole filter bed by multiplying the measured amount of
cleaner by the ratio of filtration bed volume/sample volume. Preferably, the core sample is
taken in an area of maximum or at least average contamination and represents a
cylindrical sample extending from the top to the bottom of the filtration bed. Adjusting the
amount of cleaner used to the respective contamination conditions provides the process
of the invention with a significant economical advantage, since substantially no excess
cleaner will be used, reducing the cost of the cleaning materials as well as the cost of
disposing any unreacted cleaner and activator. Furthermore, less backwashing is
required, reducing the time required for the rinsing step 50 and, thus, the overall cleaning
process. This is very important to the operator of drinking water treatment facilities who is
desirous to achieve the shortest down times possible.
[0037] The granular cleaner of a preferred embodiment of the invention includes
an acid component for dissolving scale and metal oxides on and removing biodeposits
from the filtration media; and at least one additional component selected from the group
of a free flow additive for preventing clumping of the cleaner, a surfactant for reducing
surface tension and enhancing contact of the cleaner with the filtration media, an inhibitor
for protecting exposed metal surfaces from corrosion by the acid component, and a
coloring agent.
[0038] The acid component of the preferred granular cleaner is either sutfamic
acid or a combination of a major amount of sulfamic acid with a minor amount of a
granular acid, such as phosphoric acid, sodium bisutfate, or citric acid. The acid
component is preferably substantially free of hydrochloric acid, in the preferred
embodiment, the additional components are at least one of citric acid, phosphoric acid,
corrosion inhibitor, free-flow additive and surfactant.
[0039] Numerous free flow additives applicable for use in the granular cleaner of
the present invention are commercially available. However, it is preferable to use inert
free flow additives. Free flow additives preferred for use in a granular cleaner of the
invention are fumed silicas which adsorb to the cleaner particles to inhibit clumping and
are NSF certifiable for use in drinking water processing installations,
[0040] Surfactants useful for inclusion in a granular cleaner in accordance with
the invention can be selected for the group of anionic, cationic, non-ionic and amphoteric
surfactants in granular form. Useful anionic surfactants include, by way of non-limiting
example, alkali metal salts, ammonium salts, amine salts, aminoalcohol salts, fatty acid
salts. Particularly preferred surfactants are isopropanol and isobutanol. Surfactants
which are NSF certifiable for use in drinking water processing installations are preferred.
[0041] Corrosion inhibitors useful for inclusion in a granular cleaner in accordance
with the invention can be selected from the group of nitrogen containing organic
compounds, such as amines, quaternary ammonium compounds, heterocyclic nitrogen
compounds, urea, thiourea, amide, or mixtures thereof. The most preferred inhibitors are
Inhibitor 60S, commercially available from Thoma, Inc. and Rodine 102, from Parker
Amchem,
[0042] Numerous coloring agents useful for inclusion in the granular cleaner of
the invention are commercially available. The preferred coloring agent is a dye
commercially available under the name Phylam Acid Red LX-6515 from Phylam
Chemicals.
[0043] In the process above, the activator used is an activated oxygen donor,
preferably selected from hydrogen peroxide, peracetic acid, precursors of hydrogen
peroxide and peracetic acid and combinations thereof. Examples of granular precursors
of activated oxygen donors are sodium percarbonate and BSC 8080, available from
Buckman Laboratories. The activator is preferably either 5-50% hydrogen peroxide,
- 10% peracetic acid with the balance being water. The activator can be in a liquid or dry
state prior to its introduction into the filtration bed.
[0044] The cleaner in accordance with the invention preferably includes the
following components at the indicated amounts:
As will be readily understood from the indicated volume ranges, all components having a
volume range with a lower value of 0 are optional components.
[0045] The mineral or organic acid components of the granular cleaner
composition of the invention are present in their respective crystalline form.
{0046] Although the granular cleaner composition is preferably in the form of a
free-flowing powder with a particle size of s 0.5mm for ease of spreading of the cleaner
on the filtration media, the granular cleaner may also be in the form of compressed pellets
or granules, especially for application in the form of a slurry, as will be described in more
detail further below.
[0047] Exemplary formulations illustrating preferred embodiments of the above
general cleaner formulation are described in detail in the following:
[0048] The constituents of the granular cleaners described herein are known in
the art and are commercially available from various sources including those described in
McCutcheon's Functional Materials (Vol.2), North American Edition, 1991; and in Kirk-
Othmer, Encyclopedia of Chemical Technology, 3rd edition, Vol. 22, the contents of which
are herein incorporated by reference. For any particular cleaner, the optional components
used should be compatible with all other ingredients included in the cleaner.
[0049] As shown in FIG. 4, the granular cleaner 100 in a preferred embodiment of
the process of the invention is spread evenly on the top surface 112 of the filtration media
110 in the filtration bed 114 during the first application step 10 (see FIG. 1). The cleaner
100 is wetted to achieve dissolution of the cleaner. The activator 116 is then evenly
spread on top of the cleaner 100 either in granular or liquid form. The dissolved cleaner
and the activator together move downward through the filtration bed 114. This generates
a moving cleaning front 120 of concentrated acid and activator as shown in FIG. 5 which
illustrates the filtration bed 114 during the reaction step 40 (see FIG. 1). The cleaning
front 120 is the front edge of the dissolved cleaner/activator mixture. The cleaning front
120 normally advances through the filtration bed 114 at a constant speed which is
dependent on the type and particle size of the filtration media 110, the degree of media
contamination and the cleaning chemical dosage. In stratified filter beds including several
strata of different filtration media, the speed of advance of the cleaning front 120 may
change from one stratum to the next, again depending on the properties of the filtration
media in the adjacent strata. Not only will the cleaning front 120 and, thus, the dissolved
cleaner 100 and the activator 116, automatically move through the filtration bed 114, the
even application of both together with the movement of the mixture around the filtration
media particles ensures an even concentration and admixture of both components.
Furthermore, the advancement of the cleaning front 120 is slowed sufficiently by the
friction created during movement of the mixture though the filtration bed 114 to achieve
more than sufficient residence time of the mixture on the filtration media particles to
ensure a full cleaning thereof. Moreover, any unreacted mixture will continue to move
downward until it comes in contact with a contaminated filtration media surface or the
filtration bed 114 is completely cleaned. This provides several significant advantages over
the prior art. The circulation equipment required with the prior art cleaning processes
using liquid cleaning compositions to ensure complete spread of the cleaner and
sufficient residence time is obviated with the process of the present invention, resulting in
a significant economical advantage. Significant overdosing of the cleaning compounds as
required in the prior art cleaning processes to ensure all contamination is removed is not
necessary with the process of the invention, since alt of the cleaning mixture will 'drain1
from the filtration bed, which means it will automatically move through the whole bed and
can get used up completely. Additional advantages of the present method over the prior
art are a minimized corrosion of metal parts and minimized formation of hazardous
fumes.
[0050] For large filtration beds, where it may be difficult to reach all locations of
the bed's top surface, It may be challenging to spread the granular cleaner or granular
cleaner composition in a dry form as described above. In those situations, the granular
cleaner can be applied to the filtration media in the form of a slurry. The slurry is prepared
by mixing the dry granular cleaner or cleaner composition with approximately the same
volume of water at a mixing station 200 (see Fig.5} and then spread on the top surface of
the filtration bed by way of a pressure pump 210 connected to the mixing station 200,
delivery hoses 220 emanating from the pump 210 and an optional spreader nozzle 230.
The granular cleaner shipping containers can be used as the mixing station 220 by filling
the containers with water to the top. Various types of slurry mixing and pumping
equipment are commercially available and need not be described in more detail herein.
[0051] While the invention has been described with a certain degree of
particularity, it is understood that the invention is not limited to the embodiments set forth
herein for purposes of exemplification, but is to be limited only by the scope of the
attached claims or including the full range of equivalency to which each element thereof is
entitled.
[0052] The above-described embodiments of the present invention are intended
to be examples only. Alterations, modifications and variations may be effected to the
particular embodiments by those of skill in the art without departing from the scope of the
invention, which is defined solely by the claims appended hereto.


We claim:
1. A process for removing surface contaminants from water filtration media
contained in a water filtration bed, comprising the steps of:
applying a granular cleaner onto said water filtration bed;
wetting the granular cleaner for permitting the granular cleaner to dissolve and being vertically moved through the filtration media;
applying an active oxygen donor activator to said water filtration bed for initiating a chemical reaction between the granular cleaner, the activator and the surface contaminants on the water Filtration media; and
rinsing the filtration bed with water for removing residua! granular cleaner and residual activator along with suspended and dissolved contamination from the water filtration media.
2. The process of claim 1 wherein said activator is applied in granular or liquid
form.
The process of claim 2 wherein the activator is applied as an aqueous liquid.
The process of claim 1, wherein the steps of applying the activator and
wetting the cleaner are carried out by applying an activator in aqueous liquid form.
The process of claim 1, further comprising the step of draining the water
filtration bed prior to applying the granular cleaner.
The process of claim 5, wherein the step of wetting the granular cleaner is
carried out by spraying water onto the cleaner or by filling the filtration bed with water
until the cleaner is submerged,
The process of claim 1, wherein the step of rinsing the water filtration bed is
conducted through backwashing said filtration bed without agitating the filter media.
The process of claim 1, further comprising the step of allowing the chemical
reaction to proceed for at least 1 hour prior to rinsing the filtration bed.
The process of claim 1, wherein the rinsing step is delayed until the dissolved
cleaner has reached a bottom of the filtration bed.
The process of claim 1, comprising the further steps of determining the
degree of surface contamination of the filtration media and calculating the amount of
granular cleaner to be applied for insuring removal of the surface contaminants.
The process of claim 10, wherein the step of determining the degree of
contamination includes the steps of taking a representative core sample from the
filtration media, the sample having a known volume, and the step of calculating the
amount of cleaner includes the steps of measuring the amount of cleaner required for
removal of the surface contaminants from the filtration media in the sample and
multiplying the measured amount of cleaner by the ratio of filtration bed
volume/sample volume.
A granular cleaner for use in the process of claim 1, comprising
a free-flowing granular acid component for dissolving scale and metal oxides on and removing biodeposits from the filtration media; and
at least one additional component selected from the group of a free flow
additive
for preventing clumping of the cleaner, a surfactant for enhancing contact of the cleaner with the filtration media, an inhibitor for protecting exposed metal surfaces from corrosion by the acid component, and a coloring agent.
13. A granular cleaner composition for use in the process of claim 1, comprising
a granular acid component for dissolving scale and metal oxides on and
removing biodeposits from the filtration media;
an activated oxygen donor selected from the group of peroxides, peracetic acid, precursors of peroxides and peracetic acid and combinations thereof; and
at least one additional component selected from the group of a free flow additive for preventing clumping of the cleaner, a surfactant for enhancing contact of the cleaner with the filtration media, an inhibitor for protecting exposed metal surfaces from corrosion by the acid component, and a coloring agent.
14. The granular cleaner of claim 12, wherein the acid component includes
sulfamic acid.
15. The granular cleaner of claim 14, wherein the acid component includes a
major amount of sulfamic acid and a minor amount of a mineral acid.
16. The granular cleaner of claim 15, wherein the acid component consists
entirely of sulfamic acid.
17. The granular cleaner of claim 16, consisting entirely of sulfamic acid.
The granular cleaner composition of claim 13, wherein the peroxide is
hydrogen peroxide.
The granular cleaner composition of claim 13, wherein sulfamic acid is used
as the acid component and the active oxygen donor is selected from the group
consisting of and having a volume in the range of the following: 5-50% hydrogen
peroxide, 0.2 - 10% peracetic acid, or combinations of hydrogen peroxide and
peracetic acid; water accounting for the balance of volume.
The granular cleaner of claim 12, wherein sulfamic acid is used as the acid
component and each of the additional components is NSF certifiable for use in
drinking water facilities.
Use of an active oxygen donor activator for initiating a chemical reaction
between (he granular cleaner, the activator and the surface contaminants on the
water filtration media in the process of claim 1, the activator comprising a first
component selected from the group consisting of and having a volume in the range of
the following: 5-50% hydrogen peroxide, 0.2 -10% peracetic acid, or combinations of
hydrogen peroxide and peracetic acid; and a second component being water, said
water accounting for the balance of volume.
A filtration bed cleaning kit, comprising the cleaner of claim 12 and
instructions for carrying out the process of claim 1.
The kit of claim 22, further comprising an activator including a first component
selected from the group consisting of and having a volume in the range of 5 to 50%
hydrogen peroxide, 0.2 -10% peracetic acid, or combinations of hydrogen peroxide
and peracetic acid; and a second component being water, said water accounting for the balance of volume.
The process of claim 1, wherein the granular cleaner is used for cleaning a
water filtration bed including at feast one of sand, gravel, manganese greensand,
anthracite, granular activated carbon (GAG), ion exchange media and ceramic
beads.
The granular cleaner of claim 19, which is NSF certifiable for use in drinking
water facilities.

Documents:

137.pdf

138.pdf

1623-delnp-2007-abstract.pdf

1623-DELNP-2007-Assignment.pdf

1623-delnp-2007-Claims-(16-10-2014).pdf

1623-delnp-2007-Claims-(21-07-2014).pdf

1623-delnp-2007-claims.pdf

1623-delnp-2007-Correspondence Others-(06-09-2012).pdf

1623-delnp-2007-Correspondence Others-(07-08-2013).pdf

1623-delnp-2007-Correspondence Others-(10-07-2014).pdf

1623-delnp-2007-Correspondence Others-(16-10-2014).pdf

1623-delnp-2007-Correspondence Others-(20-03-2013).pdf

1623-delnp-2007-Correspondence Others-(21-07-2014).pdf

1623-delnp-2007-Correspondence Others-(24-07-2014).pdf

1623-delnp-2007-Correspondence Others-(30-06-2014).pdf

1623-delnp-2007-Correspondence-Others-(05-03-2014).pdf

1623-delnp-2007-Correspondence-Others-(23-05-2013).pdf

1623-DELNP-2007-Correspondence-Others.pdf

1623-delnp-2007-description (complete).pdf

1623-delnp-2007-Drawings-(24-07-2014).pdf

1623-delnp-2007-drawings.pdf

1623-delnp-2007-form-1.pdf

1623-delnp-2007-Form-2-(24-07-2014).pdf

1623-delnp-2007-form-2.pdf

1623-delnp-2007-form-26.pdf

1623-delnp-2007-Form-3-(05-03-2014).pdf

1623-delnp-2007-Form-3-(06-09-2012).pdf

1623-delnp-2007-Form-3-(20-03-2013).pdf

1623-delnp-2007-Form-3-(30-06-2014).pdf

1623-DELNP-2007-Form-3.pdf

1623-delnp-2007-form-5.pdf

1623-delnp-2007-pct-101.pdf

1623-delnp-2007-pct-210.pdf

1623-delnp-2007-pct-301.pdf

1623-delnp-2007-pct-304.pdf

1623-delnp-2007-pct-306.pdf

1623-delnp-2007-pct-401.pdf

1623-delnp-2007-pct-409.pdf

FER Response_1623DELNP2007.pdf

Others.pdf

Revised Claims.pdf


Patent Number 263479
Indian Patent Application Number 1623/DELNP/2007
PG Journal Number 44/2014
Publication Date 31-Oct-2014
Grant Date 30-Oct-2014
Date of Filing 28-Feb-2007
Name of Patentee BLUE EARTH LABS, LLC
Applicant Address 5055 WEST PATRICK LANE, SUITE 102, LAS VEGAS, NEVADA 89118, U.S.A.
Inventors:
# Inventor's Name Inventor's Address
1 ZWANZIGER, WOLFGANG, FRIEDRICH 3109 SW 131st STREET, OKLAHOMA CITY, OK 73072, USA.
2 REIMANN-PHILIPP, ULRICH 4109 STONEHURST STREET, NORMAN, OK 73072, USA.
3 SCHULHOFF, JEFFREY 8112 S.W. 8th STREET, OKLAHOMA CITY, OK 73128, USA.
PCT International Classification Number B01D 24/46
PCT International Application Number PCT/IB2005/002477
PCT International Filing date 2005-08-22
PCT Conventions:
# PCT Application Number Date of Convention Priority Country
1 10/926,272 2004-08-24 U.S.A.