[0001] The invention relates to a process for paper making.
[0002] Such a process comprises the steps of providing a pulp suspension, comprising pulp,
water and a calcium salt of the carbonic acid, particularly CaCO
3, filtrating the pulp suspension, wherein at least a fraction of the added water is
separated from the pulp suspension, and particularly pressing and/or drying the filtrated
pulp suspension yielding paper or board.
[0003] The packaging paper and board production is experiencing the fastest growth of all
paper grades in the world. The utilisation of recycled fibres is more and more important,
and many of the packing mills are using up to 100 % recycled material. Mills in developed
countries mostly have high restrictions on fresh water usage, and they use less and
less fresh water per kg paper produced. This causes accumulation of disturbing substances
in the process water, both of inorganic and organic nature. Furthermore, the pH in
these processes is normally relatively low due to a high load of acid producing bacteria,
the increasing concentration of VFA (volatile fatty acid) in the process, mainly acetic
acid. The low process pH caused by the activity of these bacteria induces the dissolution
of solid CaCO
3, which enters the process with the recycled raw material. This results in a high
process water hardness caused by dissolved calcium ions, which further increases with
increasing closure of the water circuit.
[0004] Particularly, as organic acids, VFA cause partial dissolution of CaC03, but they
also are able to form complexes with calcium ions (e.g., Ca2+ CH3COO
- ↔ Ca(CH3COO)
+), so that CaCO
3 dissolution is further enhanced (compared with noncomplexing acid at the same pH).
[0005] The dissolved calcium ions and the dissolved organic compounds that are contributing
to the COD (chemical oxygen demand) have negative impacts on the paper/board making
process. The dissolved calcium ions also have negative effects on the waste water
treatment plant. In developed countries a wastewater treatment plant of this kind
of paper/board mill commonly comprises a combination of anaerobic and aerobic treatment.
If the waste water is characterized by a high hardness, the dissolved calcium ions
can precipitate in the anaerobic reactor, particularly on the pellets, blocking their
pores, so that the microbes have less access to the waste water. This reduces the
efficiency of the anaerobic treatment. The treated water exiting the anaerobic reactor
contains a substantial amount of carbon dioxide that was formed in the reactor. The
formed carbon dioxide keeps a high concentration of calcium ions in solution due to
the low pH of the water. In the subsequent aeration carbon dioxide is stripped from
the water causing the pH to rise and the CaCO
3 to precipitate. This reduces the available water volume of the aerobic treatment,
reducing its efficiency. Furthermore, CaCO
3 precipitates on cooling towers, heat exchangers and in pipes resulting particularly
in false flow measurements and blocking of pipes.
[0006] For preventing problems caused by dissolved calcium ions in the wastewater treatment
plant of paper/board mills several technical solutions have been proposed:
In the so called lime trap method, NaOH is added to the wastewater, which is then
led to a dissolved air flotation unit, wherein CaCO3 is floated and separated from the water.
A drawback of the method is that rather often CaCO3 precipitates in the pipes and pumps after the flotation unit.
[0007] In the aerobic cyclic softening (as described in
EP 1120380 A2), wastewater leaving the anaerobic treatment step is fed into a reactor. Then, NaOH
is fed into the reaction and some already precipitated CaCO
3 is recycled into the reactor to act as seeds. There is a circular movement in the
reactor for increasing the speed of precipitation and stripping some of the carbon
dioxide from the water.
[0008] According to another method known in the art, calcium hydroxide and NaC0
3 is fed to the waste water, which then is fed into a high rate clarifier. After this
the water is acidified with HCl.
[0009] The above described solutions are technically difficult and/or expensive. Furthermore,
the suggested solutions only solve the problem in the wastewater treatment, not in
the production process, unless some of the treated water is taken back into the production
process.
[0010] Another possibility is the addition of biocide to the process to reduce the bacterial
count and to increase the redox potential. This significantly reduces the formation
of acetic acid and therefore significantly the hardness. However, it may have a negative
impact on the yield of biogas in the anaerobic reactor. Additionally, many mills want
to avoid the use of biocides because of environmental reasons.
[0011] Therefore, the problem underlying the present invention is to provide a simple and
cost efficient method that reduces the afore-mentioned disadvantages in an environment-friendly
manner.
[0012] This problem is solved by adding an alkaline agent consisting of or comprising CaO
and/or Ca(OH)
2 to the pulp suspension before filtrating the latter until the pH of said pulp suspension
is above 8, particularly above 9, more particular above 10, even more particular above
11, yet more particular between 8 and 12, and adding CO
2 to the pulp suspension after adding the alkaline agent and before filtrating to adjust
the pH to a value between 6.5 and 8, more particular between 7.0 and 7.5.
[0013] Particularly, by raising the pH as described above the chemical equilibrium between
bicarbonate and carbonate is shifted towards carbonate, which then rapidly forms insoluble
salt with bivalent calcium ions resulting in precipitation of CaCO
3. On the other hand present solid CaCO
3 is kept in its insoluble form.
[0014] Particularly, after adding of the alkaline agent the pulp suspension is kept at the
above mentioned pH at least close to the point when the equilibrium between the calcium
salts is reached or as far as possible within reasonable time limits, and particularly
until the maximal possible concentration of insoluble CaCO
3 has been formed, before CO
2 is added to the pulp suspension.
[0015] By adding carbon dioxide to the pulp suspension, CO
2 is converted to carbonic acid, which rapidly dissociates into hydronium ions and
bicarbonate and carbonate anions leading to acidification of the pulp suspension to
the above mentioned pH value. Advantageously, the pH is shifted to a value that is
suitable for the following paper making process, but at which already precipitated
CaC03 at least mainly is kept in its insoluble form. Moreover, bicarbonate and carbonate
ions serve as a buffer system keeping the pulp suspension at the pH value suitable
for the paper making process. Additionally, further carbonate is provided for precipitating
remaining bivalent calcium ions, to prevent dissolution of CaC03 and/or to precipitate
(at least part of) the remaining Ca ions.
[0016] The precipitated CaCO
3 is kept in the pulp suspension until it is incorporated into the paper or board product
of the process of the invention. Beside the precipitation of CaCO
3, some of the dissolved organic matter that may be present in the pulp suspension
is precipitated as well.
[0017] Particularly, the pulp suspension is prepared by adding water to pulp in a pulper
or to recycled papers when the fibers originate from recovered papers. In some embodiments,
the pulp comprises a calcium salt of the carbonic acid, particularly CaCO
3
[0018] In some alternative embodiments, a calcium salt of the carbonic acid, particularly
CaCO
3, is added to the pulp suspension on the paper machine/board machine, to e.g. the
mixing chest or in the short circulation.
[0019] In some embodiments, the alkaline agent is added concomitantly or immediately subsequently
after adding the water to the pulp. Advantageously, CaCO
3 is precipitated during formation of the pulp suspension.
[0020] In some embodiments, the pulp suspension is homogenized, particularly by stirring,
until the pulp suspension exhibits an essentially uniform and constant consistency
(concentration of fibres in water).
[0021] In some embodiments, CO
2 is added to the pulp suspension, after the formation of the pulp suspension is completed,
particularly after the pulp suspension exhibits an essentially uniform and constant
consistency (concentration of fibres in water).
[0022] In some embodiments, a fraction of the added water is separated during pressing from
the pulp suspension.
[0023] In some embodiments, CO
2 is added to the fraction of the added water that is separated during filtration or
pressing. During filtration and/or pressing, the pulp suspension is typically exposed
to the ambient environment, to which some of the added CO
2 emits. The lost amount of CO
2 is replenished to maintain the pH and to provide carbonate to the separated fraction.
[0024] In some embodiments, at least a part of the fraction of the added water that is separated
during filtration is recycled into said pulp suspension, particularly before filtration.
[0025] In some embodiments, the fraction of the water that is separated during filtration
and/or pressing is used to provide another pulp suspension or added to a new pulp
batch for papermaking. The recycling of process water into the papermaking process
lowers the need of fresh water.
[0026] In some embodiments, the alkaline agent comprises or consists of a combination of
Ca(OH)
2 and/or CaO and NaOH. Advantageously, with such a combination an excess of calcium
ions can be avoided. Preferably, NaOH is added first and then CO
2 is added resulting in an in situ formation of NaCO
3.
[0027] In some embodiments, NaOH is comprised within the alkaline agent in a mole fraction
below 0.5 with respect to Ca(OH)
2, CaO or Ca(OH)
2 and CaO.
[0028] In some embodiments, a biocide is added to the pulp suspension. In some embodiments,
the biocide is added before filtrating. In some embodiments, a biocide is added to
the fraction of the added water that is separated during filtration or pressing. Advantageously,
the biocide inhibits the growth of microorganisms in the pulp suspension and the separated
process water. The pulp suspension and the process water comprise nutrients for microorganisms
such as bacteria or fungi. Those microorganisms can produce considerable amounts of
organic matter, e.g., acetic acid, which can lower the pH of the pulp suspension or
the process water.
[0029] In some embodiments, at least another fraction of the added water is separated during
filtration and/or pressing of the pulp suspension before or after wastewater treatment
of the fraction. Particularly, the wastewater treatment is performed in a clarifier.
[0030] Particularly, the term "wastewater treatment" refers to a process, wherein at least
one contaminant (such as e.g. organic matter or suspended solids) is removed from
the process water, before it can be released into the environment.
[0031] Further advantages, features and examples of the present invention shall be described
in the following with reference to the Figure, wherein
- Fig. 1
- shows a scheme of an embodiment of the invention.
Examples:
[0032] The present invention relates to the reduction of the process water hardness and
dissolved or colloidal substances that have an impact on COD. The method of the invention
takes places in the paper and board making process and thus improves not only the
waste water treatment but also the paper and board making process.
[0033] According to the invention, CaO and/or Ca(OH)
2 31 is added to a pulper 11, increasing the pH to > 8, preferable to > 9, more preferably
to > 10, even more preferably to >11, most preferable to a value between 8 and 12.
Hereby CaCO
3 is precipitated and some of the organic matter that contributes to the COD is co-precipitated
with CaCO
3. The result is a reduced process water hardness as well as a reduced water COD level.
The precipitated CaCO3/COD remains within the pulp or pulp suspension 23, respectively,
and leaves the mill as paper 25 of the produced paper/board. A part of the precipitated
organic matter (COD) appears to be recalcitrant organic matter (COD). Thus the coprecipitation
of the organic matter (COD) reduces the COD levels of the effluent water 27 leaving
the water treatment plant 16. For optimum COD removal more CaO (or Ca(OH)
2) 31 needs to be added than required for precipitation of calcium and carbonate ions.
This consumes (almost) all carbonate species in the water phase.
[0034] Preferably, CO
2 32 is added to the pulper 11 to control the pH avoiding a too high pH and pH swings,
and to precipitate excess calcium (from CaO or Ca(OH)
2 addition). Furthermore, the addition of CO
2 32 advantageously increases the buffer capacity of the process water or the pulp
suspension 23, respectively. Furthermore, CO
2 is added to make sure that all added CaO or Ca(OH)
2 is reacted and to reduce pH to such a level that further precipitation is avoided
or at least reduced.
[0035] A second CO
2 32 addition point is advantageous in the short circulation of the paper machine,
wherein at least a part 26* of the separated fraction 26 of the process water is recycled
back into the pulp suspension 23*, since some CO
2 is stripped from the water phase, when the fibre/water mixture 23* is entering the
wire section 12 due to a high contact area between the suspension 23 and the surrounding
air. If this is not compensated for it may lead to precipitation on the paper machine.
[0036] Advantageously, a combination of Ca(OH)
2 and/or CaO and NaOH 31 is added to the pulper 11. The amount of added NaOH 31 is
limited not to cause a high increase in ash content. Production of packing papers
does not benefit from high ash content as this weakens the paper and packaging papers
need to be strong.
[0037] Alternatively, the necessary CO
2 32 is added to the pulper or the pulp suspension in form of process water saturated
with CO
2 32 after the alkaline compounds 31 as described above have been added and have had
some time to react.
[0038] One alternative is to combine the invention with the use of biocides 33 so that only
a fraction of biocide is needed to be added to the pulp suspension or the process
water in order to reduce the bacterial count without having an adverse effect on the
biogas formation (in the anaerobic waste water treatment step).
[0039] Advantageously, the reduction in process water hardness leads to improved paper chemistry,
savings in starch consumption, and less breaks. The reduction is achieved without
getting an unfavourable ratio between Ca and Na in the process water, which could
have a negative impact on the sludge setting properties and COD of the effluent of
wastewater treatment plant.
[0040] Fig 1 shows a preferred embodiment of the method of the present invention. Waste
paper is placed in a pulper with the purpose of disintegrating the fibers to obtain
a recycled paper pulp 21. Water 22 is added. The pulp is suspended in the water 22
such that a pulp suspension 23 forms. To the pulp suspension 23 CaO, Ca(OH)
2 31 or a mixture thereof is added until the pH value of the pulp suspension is above
8, particularly above 9, more particular above 10, even more particular above 11,
yet more particularly between 8 and 12. As a consequence, bicarbonate ions in the
pulp suspension 23 are transformed to a certain extent into carbonate ions, which
then rapidly form an insoluble salt with bivalent calcium ions present in the suspension.
Before entering the machine chest of the paper machine 12, CO
2 is added to the pulp suspension 23. By adding CO
2 the pH of the pulp suspension is adjusted to a value between 6.5 and 8, particularly
between 7 and 7.5, and bicarbonate and carbonate are resupplied to the pulp suspension
23, which may then bind residual bivalent calcium ions under formation of CaCO
3.
[0041] The pulp suspension 23 is then transferred to the machine chest 12. After the machine
chest 12 the pulp suspension 23 is diluted with paper machine white water and led
to the paper machines headbox, from which it is distributed across the width of the
wire section, wherein a fraction 26 of the white water is separated from the pulp
suspension Typically, the pulp suspension 23* is sieved, whereby the fraction 26 of
the process water is drawn of the suspension 23* by mechanical pressure resulting
in a wet web of fibres 24 representing a precursor of the paper/product 25 of the
process.
[0042] The wet web of fibres 24 is then transferred to the pressing section 14, wherein
remaining process water 26 is pressed out of the web of fibres 24 by mechanical forces,
typically applied by rolls, and afterwards dried in a dry section 14, wherein residual
water is removed or heat yielding in dry paper or board 25.
[0043] A part 26* of the process water 26 that was separated in the wire section and/or
the pressing section is recycled to the pulp suspension 23* entering the wire section,
after CO
2 has been added to the part 23*. Additionally or alternatively the part 26* of the
process water 26 is recycled into the pulper 11 or to the pulp suspension 23 exiting
the pulper 11 via one or several process water tanks 17, wherein CO
2 is added before entering the pulper 11 or the pulp suspension 23. Because the majority
of all calcium ions are present in form of insoluble CaCO
3 they remain in the wet web of fibres 24, whereas the amount of calcium ions is reduced
by 30% to 50% or even more in the separated fraction 26, which is then characterized
by a reduced hardness. Since the pulp suspension 23, 23* is exposed to the ambient
air, a part of the added CO
2 emits from the pulp suspension 23, 23*. This loss is compensated by addition of CO
2 32 to the separated fraction 26 as described above.
[0044] The residual fraction 27 of separated process water 26 that is not recycled described
above is subjected to a wastewater treatment 16, wherein contaminants are removed
from the process water before releasing it into the environment.
Reference signs
11 |
pulper |
12 |
machine chest |
13 |
wire section |
14 |
pressing section |
15 |
drying section |
16 |
clarifier |
17 |
process water tank |
|
|
21 |
pulp |
22 |
process water |
23 |
pulp suspension |
23* |
pulp suspension jet |
24 |
filtrated pulp suspension/wet web of fibres |
25 |
paper/board |
26 |
separated process water |
26* |
separated process water for recycling |
27 |
separated process water for disposal |
28 |
treated water for disposal |
|
|
31 |
CaO+Ca(OH)2 /CaO +Ca(OH)2 + NaOH |
32 |
CO2 |
33 |
biocide |
1. Process for manufacturing paper or board comprising the steps of:
- providing a pulp suspension (23, 23*), comprising pulp, water and CaCO3,
- filtrating (12) said pulp suspension (23, 23*), wherein at least a fraction (26)
of said water (22) is separated from said pulp suspension (23, 23*),
- and optionally pressing (14) and/or drying (15) said filtrated pulp suspension (24)
yielding paper (25) or board (25),
characterized in that
- an alkaline agent consisting of or comprising CaO and/or Ca(OH)2 (31) is added to said pulp suspension (23) before filtrating (13) until the pH of
said pulp suspension (23) is above 8, particularly above 9, more particular above
10, even more particular above 11, yet more particular between 8 and 12, and
- CO2 (32) is added to said pulp suspension (23) after adding said alkaline agent (31)
and before filtrating (12) to adjust the pH to a value between 6.5 and 8, particularly
to a value between 7 and 7.5.
2. The process according to claim 1, wherein said pulp suspension (23) is provided by
adding water (22) to a pulp (21) or to waste paper or to paper products, wherein said
pulp (21) comprises CaCO3, and wherein preferably said pulp is obtained from waste paper.
3. The process according to claim 1 or 2, characterized in that CO2 (33) is added to said fraction (26) of said water (22).
4. The process according to any one of the preceding claims, characterized in that said alkaline agent consists of or comprises a combination of Ca(OH)2 and/or CaO and NaOH (31).
5. The process according to any one of the preceding claims, characterized in that at least a part (26*) of said fraction (26) of said water (22) is recycled into said
pulp suspension (23, 23*).
6. The process according to any one of the preceding claims, characterized in at least another part (26*) of said fraction (26) of said water (22) is used to provide
another pulp suspension.
7. The process according to any one of the preceding claims, characterized in that a biocide (33) is added to said pulp suspension (23), particularly before filtrating
(12), or to said fraction (26) of said water (22).
8. The process according to any one of the preceding claims for reducing the COD level
of said fraction (26) of said water (22) which is separated from said pulp suspension
(23, 23*).
9. The process according to any one of the preceding claims for reducing the hardness
of said fraction (26) of said water (22) which is separated from said pulp suspension
(23, 23*).