Title of Invention

METHOD FOR CONTROLLING A WASTE WATER CONCENTRATION OF CLEANING SOLUTION CONTAINING PHOSPHORUS

Abstract A method of controlling the concentration of P of cleaning solution waste water starts with providing a waste water buffer tank capable of either sending the waste water to a waste water treatment plant or storing the waste water after the waste water is accepted. The concentration of P in the cleaning solution is set within a target concentration range, and matter to be treated is treated. The concentration of P in the waste water is measured in the waste water buffer tank. When the measured value of the concentration of P is less than a tolerable upper limit, the waste water is sent from the waste water buffer tank to the waste water treatment plant. When the measured value of the concentration of P is higher than the tolerable upper limit, sending the waste water to the waste water treatment plant is stopped, and the waste water is stored in the waste water buffer tank. The concentration of P is reduced to a value within the target concentration range, and the matter to be treated is treated.
Full Text Description
METHOD FOR CONTROLLING A WASTE WATER CONCENTRATION OF CLEANING
SOLUTION CONTAINING PHOSPHORUS
TECHNICAL FIELD
The present invention relates to a method for controlling
the concentration of P (phosphorus) in cleaning solution waste
water.
BACKGROUND ART
The processing steps for fabricating steel products
generate various kinds of waste waters that are discharged.
Hazardous substances may be contained in those waste waters
if they remain untreated. Waste water containing hazardous
substances are sent from various processing steps to a waste
water treatment process. In a waste water treatment plant,
the waste water is neutralized, sedimented, and otherwise
treated, and hazardous components are treated as refractory
substances and separated by sedimentation (see patent
references 1 and 2).
For example, a surface treatment or activating process
is performed as a post treatment of a galvanizing process in
a hot-dip galvanizing line. In the surface treatment,
galvanized steel sheets are rinsed with a surface treatment
liquid containing P after a cleaning process (see, for example,
patent reference 3). Since the surface treatment liquid and
the waste water from the rinsing water contain a P component
of the surface treatment or activating process, it is
impossible to drain out them directly. Therefore, waste water
from a surface treatment or activating process is drained to
a drainage pit within the galvanizing line. The waste water
is sent from the drainage pit to a waste water treatment plant,
where the waste water is neutralized, sedimented and otherwise
treated. The waste water is sedimented and separated while
treating the P component as a refractory substance.
However, if the P concentration of the waste water sent
to the waste water treatment plant is high, it is impossible
to neutralize, sediment and otherwise treat the waste water
in the waste water treatment plant. Consequently, an upper
limit of the P concentration of the waste water that can be
sent into the waste water treatment plant is established. It
is necessary to immediately stop sending of the waste water
into the waste water treatment plant if the P concentration
of the waste water from the drainage pit exceeds the upper limit
of P concentration. If the flow of waste water into the waste
water treatment plant is stopped, operation of the galvanizing
line is typically stopped.
It is therefore customary to employ a waste water buffer
tank capable of storing the waste water to prevent operation
of the hot-dip galvanizing line from being stopped when waste
water exceeding the upper limit of P concentration is produced.
Feeding the waste water into the waste water treatment plant
is stopped when the P concentration of the waste water exceeds
the upper limit of P concentration. The waste water is then
stored in the waste water buffer tank.
However, if the operation is run after stopping the flow
of waste water into the waste water treatment plant, the
operation can run only for a short time until the waste water
buffer tank becomes full.
It is also possible to dilute the waste water by adding
diluting water into a waste water buffer tank such that the
P concentration of the waste water becomes lower than the upper
limit of P concentration such that the waste water can be sent
to a waste water treatment plant. The thus diluted waste water
can be sent to the waste water treatment plant. However, this
method has the problem that the amount of waste water increases .
Patent reference 1: JP-A-7-268659
Patent reference 2: JP-A-2002-200494
Patent reference 3: JP-A-2007-92093
DISCLOSURE OF THE INVENTION
It is an object of the present invention to provide a
method for controlling the concentration of P in cleaning
solution waste water in such a way that sending waste water with

high P concentrations and large amounts of waste water
containing P into a waste water treatment plant can be prevented.
This can assist in avoiding interrupting the operation of the
galvanizing line.
To achieve the above-described object, the present
invention provides a method for controlling the concentration
of P in cleaning solution waste water, the method comprising
the steps of:
providing a waste water buffer tank which, after
receiving waste water of the cleaning solution containing P,
can send the waste water to a waste water treatment plant or
store the waste water;
treating matter to be treated while setting the
concentration of the cleaning solution containing P within a
target concentration range;
measuring the concentration of P in the waste water of
the cleaning solution in the waste water buffer tank;
sending the waste water of the cleaning solution
containing P from the waste water buffer tank to the waste water
treatment plant when the measured value of the P concentration
is less than a tolerable upper limit; and
stopping the flow of the waste water of the cleaning
solution containing P to the waste water treatment plant,
storing the waste water in the waste water buffer tank, and
treating the matter to be treated while reducing the

concentration of the cleaning solution containing P to a value
within the target concentration range when the measured value
of the P concentration is higher than the tolerable upper limit.
A method for controlling the concentration of P in
cleaning solution waste water.
In the above-described method for controlling
concentration of P in the waste water, if the measured value
of the concentration of P in the waste water stored in the waste
water buffer tank becomes less than the tolerable upper limit,
it is desired to send the waste water to the waste water treatment
plant from the waste water buffer tank.
Furthermore, in the above-described method, when sending
the waste water from the waste water buffer tank to the waste
water treatment plant is begun, it is desired to increase the
P concentration to a value within the target range.
According to the present invention, when the
concentration of P in the cleaning solution waste water has
reached the tolerable upper limit, the concentration of P can
be reduced to below the tolerable upper limit by reducing the
concentration of P to a target lower limit. Therefore, it is
possible to prevent waste water having high P concentrations
and large amounts of waste water containing P from being sent
to the waste water treatment plant while continuing the
operation.

BRIEF DESCRIPTION OF THE DRAWINGS
Fig. 1 is a schematic diagram illustrating a surface
treatment or activating process in a production process for
fabricating hot-dip galvanized steel sheets; and
Fig. 2 is a diagram illustrating transition of the P
concentration of waste water according to a method of the present
invention.
Symbols described in Fig. 1 are as follows:
1: hot-dip galvanized steel sheet;
2: surface treatment or activating apparatus;
3: rinsing apparatus;
4: drier;
5: drainage pit;
6: waste water buffer tank;
7: surface treatment tank;
11: surface treatment stock solution supply tank;
12, 15: pure water supply tubes;
13, 16: sprayers;
14, 17: P concentration meters;
18: drain tube;
21-24: pumps;
25: wringer roll
BEST MODE FOR CARRYING OUT THE INVENTION

Embodiments of the present invention are described taking
a surface treatment or activating step as an example, the
surface treatment or activating step being performed after a
hot-dip galvanizing step on a hot-dip galvanizing line. The
surface treatment or activating step is performed to improve
the press moldability at the customer's site.
Fig. 1 is a schematic diagram illustrating the surface
treatment or activating step on the hot-dip galvanizing line.
In Fig. 1, there is shown a steel sheet (hot-dip galvanized
steel sheet) 1, a surface treatment or activating apparatus 2,
a rinsing apparatus 3, a drier 4, a drainage pit 5, a waste water
buffer tank 6, and a surface treatment tank 7.
The surface treatment tank 7 holds a surface treatment
or activating liquid containing P. With respect to the
concentration of P of the surface treatment or activating liquid,
a target concentration median CM, a target upper limit value
CU, and a target lower limit value CL are set, taking account
of the quality of the galvanized steel sheet, operability, and
so on. The target upper limit value CU and target lower limit
value CL are set to concentrations at which the operation and
quality present no problems if a concentration within the range
is adopted as a P concentration-set value (described later) of
the surface treatment or activating liquid. CU to CL give the
target concentration range.
The surface treatment tank 7 has a surface treatment

stock solution supply tank 11 that stores the surface treatment
liquid stock solution in the surface treatment tank 7, a pure
water supply tube 12 that supplies pure water, a P concentration
meter 14, and a liquid level meter (not shown) that detects
the liquid level, controls the concentration of the surface
treatment or activating liquid, and controls the liquid level.
The liquid level control is provided as follows. Two
kinds of liquid level, or a low liquid level and a high liquid
level, are set. When the liquid level becomes the low liquid
level, pure water is supplied. When the liquid level becomes
the high liquid level, the supply of pure water is stopped.
Thus, the liquid level is kept roughly between the low and high
liquid levels.
With respect to the concentration control, when the
concentration of P measured by the P concentration meter 14
is less than the set value of the concentration of P (this
concentration is referred to as the set value of P
concentration) of the controlled surface treatment liquid, the
surface treatment liquid stock solution is supplied from the
surface treatment stock solution supply tank 11, based on the
difference between the set value of P concentration and the
measured value of P concentration such that the P concentration
in the surface treatment tank 7 becomes the set value of P
concentration. In normal operation, the target concentration
median CM is adopted as the set value of P concentration of the

surface treatment or activating liquid.
The surface treatment or activating apparatus 2 sprays
the surface treatment liquid containing P received in the
surface treatment tank 7, using a pump 22, from a sprayer 13
to the steel sheet 1, and squeezes out the surface treatment
liquid by the wringer roll 25 located at the exit. Then, the
steel sheet 1 exiting from the surface treatment or activating
apparatus 2 is introduced into the rinsing apparatus 3. The
rinsing apparatus 3 sprays the pure water supplied from the pure
water supply tube 15 to the steel sheet 1 from a sprayer 16.
The water is squeezed out by the wringer roll 25 located at the
exit. The steel sheet 1 is made to exit from the rinsing
apparatus 3 and dried by the drier 4. Then, the sheet is wound
up by a winder on the exit side.
The surface treatment liquid containing P and supplied
to the surface treatment or activating apparatus 2 and the
rinsing water from the rinsing apparatus 3 flow into the drainage
pit 5 through the drain tubes 18 connected, respectively, with
lower portions of the apparatuses. The waste water from the
drainage pit 5 is sent to the waste water buffer tank 6.
The drainage pit 5 is equipped with a pump 23 that sends
the waste water to a waste water buffer tank 6 and with a liquid
level meter (not shown) that detects the liquid level of the
waste water. When the liquid level of the waste water becomes
the preset high liquid level, the pump 23 sends the waste water

to the waste water buffer tank 6. When the level becomes the
preset low liquid level, the pump 23 is stopped.
The waste water buffer tank 6 receives waste water from
the drainage pit 5 and sends the waste water to a waste water
treatment plant or stores the water in the waste water buffer
tank 6. The waste water buffer tank 6 is made larger in capacity
than the drainage pit 5. The tank capacity is appropriately
determined taking account of the amount of stored waste water.
The upper limit (hereinafter referred to as the "tolerable upper
limit") of the concentration of P that can be sent from the waste
water buffer tank 6 to the waste water treatment plant has been
determined previously.
The waste water buffer tank 6 has a pump 24 that sends
the waste water to the waste water treatment plant, a P
concentration meter 17 that detects the concentration of P in
the waste water in the waste water buffer tank 6, and a liquid
level meter (not shown) that detects the liquid level of the
waste water. With respect to the liquid level, a low liquid
level 1 used when the waste water is sent to the waste water
treatment plant, a low liquid level 2 (the low liquid level 1
is lower than the low liquid level 2) , and a maximum liquid level
(limit liquid level of the stored liquid) are set. Making the
positions of the low liquid level 1 and low liquid level 2 as
low as possible compared with the position of the maximum liquid
level is advantageous in increasing the amount of the liquid

stored in the waste water buffer tank 6.
The waste water buffer tank 6 measures the concentration
of P in the waste water with the P concentration meter 17, and
sends the waste water to the waste water treatment plant with
the pump 24 when the measured value of the concentration of P
is lower than the tolerable upper limit. When the waste water
is sent to the waste water treatment plant, if the liquid level
of the waste water becomes the low liquid level 2, the pump 24
engages. The pump 24 is stopped if the level becomes the low
liquid level 1.
When the concentration of P measured by the P
concentration meter 17 is higher than the tolerable upper limit,
the pump 24 is stopped and the flow of waste water to the waste
water treatment plant is stopped. The waste water is stored
in the waste water buffer tank 6.
If the processing described above is performed, the
liquid level of the surface treatment liquid in the surface
treatment tank 7 drops and the following control of the liquid
level and control of the concentration are carried out. Pure
water is supplied from the pure water supply tube 12 when the
liquid level becomes a low liquid level. The flow of pure water
is stopped when the liquid level becomes a high liquid level.
The concentration of P of the surface treatment liquid drops
because of the supply of pure water. Then, the surface
treatment liquid stock solution is supplied from the surface

treatment stock solution supply tank 11. The surface treatment
liquid stock solution containing a high concentration of P is
supplied from the surface treatment liquid stock solution
supply tank 11 using the pump 21 according to the difference
between the measured value of the concentration of P measured
by the P concentration meter 14 and the set value of the
concentration of P. Control is provided such that the
concentration of P in the surface treatment tank 7 becomes the
preset value of concentration of P.
When this control is performed with the surface treatment
tank 7, the P concentration becomes higher when the surface
treatment liquid stock solution is supplied. The P
concentration of the waste water sent to the waste water buffer
tank 6 increases correspondingly when the P concentration in
the surface treatment tank 7 becomes high.
The pump 24 is stopped when the concentration of P in the
waste water buffer tank 6 measured by the P concentration meter
17 becomes higher than the tolerable upper limit. The flow of
water to the waste water treatment plant is stopped. The waste
water is stored in the waste water buffer tank 6.
At the same time, the set value of the concentration of
P in the surface treatment tank 7 is modified and reduced to
a value within the target concentration range. Preferably, the
P concentration is set to the target lower limit value CL. The
P concentration of the waste water flowing into the waste water

buffer tank 6 immediately diluted with pure water is reduced
to below the tolerable upper limit by reducing the set value
of P concentration in the surface treatment tank 7 (preferably,
by modifying the target lower limit value CL).
The waste water which is stored in the waste water buffer
tank 6 and has a concentration of P exceeding the tolerable
concentration is diluted with newly pumped waste water having
a concentration of P less than the tolerable upper limit. The
pump 24 engages if the P concentration measured by the P
concentration meter 17 in the waste water buffer tank 6 becomes
lower than the tolerable upper limit. The waste water stored
in the waste water buffer tank 6 is sent to the waste water
treatment plant. The pump 24 is stopped when the liquid level
drops to the low liquid level 1. Subsequently, the waste water
flows to the waste water treatment plant by a normal method of
disposing of waste water, i.e., the pump 24 engages at the low
liquid level 2 and the pump 24 is stopped at the low liquid level
1.
When the concentration of P in the waste water buffer tank
6 measured by the P concentration meter 17 becomes lower than
the tolerable upper limit and the operation of the pump 24 in
the waste water buffer tank 6 is resumed, the set value of P
concentration in the surface treatment tank 7 is modified and
increased to a value within the target concentration range from
the target lower limit value CU. Preferably, the value is set

to the original target concentration median CM.
By performing steps as described above, sending waste
water having high concentrations of P and large amounts of waste
water containing P to the waste water treatment plant can be
prevented while continuing upstream operations. If the amount
of waste water from the waste water buffer tank 6 reaches the
maximum liquid level before the P concentration measured by the
P concentration meter 17 becomes lower than the tolerable upper
limit, the upstream operation is stopped and disposal of the
waste water from the surface treatment step is stopped.
The method of the present invention can be used as a method
for controlling the concentration of P in waste water of general
cleaning solution containing P, as well as of waste water
produced from the above-described processing steps and
containing P.
Example
In the surface treatment step on the hot-dip galvanizing
line shown in Fig. 1, the processing was done under the
following conditions. In the present embodiment, the upper
limit (tolerable upper limit) of the concentration of P in the
waste water that can be sent to the waste water treatment plant
is 6 mass ppm.
(1) Surface treatment or activating apparatus
P concentration of surface treatment liquid: 10 mass ppm

(target concentration median) ± 5 mass ppm (target range)
Target lower limit value CL: 5 mass ppm
Flow rate of surface treatment liquid: 5 m3/Hr
(2) Rinsing apparatus
Flow rate of pure water: 5 m3/Hr
(3) Waste water buffer tank
Capacity: 100 m3
The tank capacity of 100 m3 is a capacity permitting about
10-hour operation taking account of processing of materials
requiring surface treatment and materials not requiring surface
treatment.
When the surface treatment step is performed while the
value of the concentration of P in the surface treatment tank
7 is set to 10 mass ppm (target concentration median) , if the
concentration of P in the waste water buffer tank 6 increases
and becomes equal to the tolerable upper limit of the waste
buffer tank 6, i.e., 6 mass ppm, the flow of waste water to the
waste water treatment plant is stopped and the waste water is
stored in the waste water buffer tank 6. At the same time, the
set value of the concentration of P in the surface treatment
tank 7 is modified from 10 mass ppm to 5 mass ppm (target lower
limit value).
Fig. 2 shows one example of transition of set values of
the concentration of P of the surface treatment liquid in the
surface treatment tank 7, concentration of P measured by the

P concentration meter, and concentration of P measured by the
P concentration meter in the waste water buffer tank 6 before
and after the set value of the concentration of P in the surface
treatment tank 7 was modified from 10 mass ppm to 5 mass ppm.
The target value (concentration preferable for disposal of
waste water) of the concentration of P in the waste water buffer
tank 6 in the present embodiment is 3 mass ppm.
Because the set value of concentration of P in the surface
treatment tank 7 was modified from 10 mass ppm to 5 mass ppm,
the concentration of P in the waste water buffer tank 6 decreased
from 6 mass ppm to 3 mass ppm. At the instant when the
concentration of P in the waste water buffer tank 6 dropped to
3 mass ppm, the flow of waste water to the waste water treatment
plant was resumed. During this interval, the liquid level of
the waste water in the waste water buffer tank was lower than
the maximum liquid level. The operation was continued without
stopping the line.
The P concentration in the waste water buffer tank 6
increased to 6 mass ppm under the condition where the set value
of the concentration of P in the surface treatment tank 7 was
10 mass ppm, for the following reason. The liquid level in the
surface treatment tank 7 dropped and pure water was supplied.
Then, the surface treatment liquid stock solution was supplied
from the surface treatment stock solution supply tank 11,
increasing the concentration of P.

INDUSTRIAL APPLICABILITY
The present invention can be used as a method for
controlling the concentration of P in waste water in such a way
that the flow of waste water having high P concentrations and
large amounts of waste water containing P to a waste water
treatment plant can be prevented when matter to be treated is
treated using a cleaning solution containing P. This can assist
in avoiding interrupting operation of the galvanizing line.

What is claimed is:
1. A method for controlling the concentration of P in
cleaning solution waste water, the method comprising the steps
of:
providing a waste water buffer tank which, after
receiving waste water of the cleaning solution containing P,
can send the waste water to a waste water treatment plant or
store the waste water;
treating matter to be treated while setting the
concentration of the cleaning solution containing P within a
target concentration range;
measuring the concentration of P in the waste water of
the cleaning solution containing P in the waste water buffer
tank;
sending the waste water of the cleaning solution
containing P from the waste water buffer tank to the waste water
treatment plant when the measured value of the P concentration
is less than a tolerable upper limit; and
stopping the flow of the waste water of the cleaning
solution containing P to the waste water treatment plant,
storing the waste water in the waste water buffer tank, and
treating the matter to be treated while reducing the
concentration of the cleaning solution containing P to a value
within the target concentration range when the measured value

of the P concentration is higher than the tolerable upper limit.
2. The method for controlling a waste water concentration
of cleaning solution containing P according to claim 1,
wherein when the measured value of the concentration of P
in the waste water and stored in the waste water buffer tank
becomes less than the tolerable upper limit, the waste water
is sent from the waste water buffer tank to the waste water
treatment plant.
3. The method for controlling a waste water concentration
of cleaning solution containing P according to claim 2,
wherein if sending the waste water from the waste water
buffer tank to the waste water treatment plant is started, the
concentration of P in the cleaning solution is increased to a
value within the target range.


A method of controlling the concentration of P of
cleaning solution waste water starts with providing a waste
water buffer tank capable of either sending the waste water
to a waste water treatment plant or storing the waste water
after the waste water is accepted. The concentration of P in
the cleaning solution is set within a target concentration
range, and matter to be treated is treated. The concentration
of P in the waste water is measured in the waste water buffer
tank. When the measured value of the concentration of P is
less than a tolerable upper limit, the waste water is sent from
the waste water buffer tank to the waste water treatment plant.
When the measured value of the concentration of P is higher
than the tolerable upper limit, sending the waste water to the
waste water treatment plant is stopped, and the waste water
is stored in the waste water buffer tank. The concentration
of P is reduced to a value within the target concentration range,
and the matter to be treated is treated.

Documents:

3929-KOLNP-2009-(25-10-2013)-CORRESPONDENCE.pdf

3929-KOLNP-2009-(25-10-2013)-EXAMINATION REPORT REPLY RECIEVED.pdf

3929-KOLNP-2009-(25-10-2013)-OTHERS.pdf

3929-KOLNP-2009-(26-03-2014)-CORRESPONDENCE.pdf

3929-KOLNP-2009-(27-03-2014)-PETITION UNDER SECTION 8 (1).pdf

3929-kolnp-2009-abstract.pdf

3929-kolnp-2009-claims.pdf

3929-KOLNP-2009-CORRESPONDENCE 1.1.pdf

3929-KOLNP-2009-CORRESPONDENCE-1.2.pdf

3929-kolnp-2009-correspondence.pdf

3929-kolnp-2009-description (complete).pdf

3929-kolnp-2009-drawings.pdf

3929-kolnp-2009-form 1.pdf

3929-KOLNP-2009-FORM 18.pdf

3929-kolnp-2009-form 2.pdf

3929-kolnp-2009-form 3.pdf

3929-kolnp-2009-form 5.pdf

3929-kolnp-2009-international publication.pdf

3929-kolnp-2009-others pct form.pdf

3929-KOLNP-2009-PA.pdf

3929-kolnp-2009-pct priority document notification.pdf

3929-kolnp-2009-pct request form.pdf

3929-kolnp-2009-specification.pdf

3929-KOLNP-2009-TRANSLATED COPY OF PRIORITY DOCUMENT.pdf

abstract-3929-kolnp-2009.jpg


Patent Number 262934
Indian Patent Application Number 3929/KOLNP/2009
PG Journal Number 39/2014
Publication Date 26-Sep-2014
Grant Date 24-Sep-2014
Date of Filing 12-Nov-2009
Name of Patentee JFE STEEL CORPORATION
Applicant Address 2-3, UCHISAIWAI-CHO 2-CHOME, CHIYODA-KU, TOKYO 100-0011 JAPAN
Inventors:
# Inventor's Name Inventor's Address
1 TAKAHIRO SUGANO C/O. INTELLECTUAL PROPERTY DEPARTMENT, JFE STEEL CORPORATION, 2-3, UCHISAIWAI-CHO 2-CHOME, CHIYODA-KU, TOKYO 100-0011 JAPAN
2 SATOSHI YONEDA C/O. INTELLECTUAL PROPERTY DEPARTMENT, JFE STEEL CORPORATION, 2-3, UCHISAIWAI-CHO 2-CHOME, CHIYODA-KU, TOKYO 100-0011 JAPAN
3 NOBUYUKI SATO C/O. INTELLECTUAL PROPERTY DEPARTMENT, JFE STEEL CORPORATION, 2-3, UCHISAIWAI-CHO 2-CHOME, CHIYODA-KU, TOKYO 100-0011 JAPAN
PCT International Classification Number C02F1/00; C23C2/26; C02F1/00
PCT International Application Number PCT/JP2008/063711
PCT International Filing date 2008-07-24
PCT Conventions:
# PCT Application Number Date of Convention Priority Country
1 2007-197268 2007-07-30 Japan