[0001] The proposed invention deals with pulp and paper production, in particular, with
the process for preparing pulp cooking liquors to manufacture a fibrous semifabricate.
[0002] A method for preparing a pulp cooking liquor by adding a sulfate into a water medium
is known (1).
[0003] Saturation of a water medium with sulfurous anhydride until the required pH-value
is reached represents another well known method to prepare acid cooking liquor (2,3).
[0004] The disadvantages of the methods enumerated are as follows: a considerable amount
of fresh water needed to prepare the cooking liquor, a rather costly treatment needed
for the resultant effluents and a low yield of the final pulp occurs.
[0005] The closest to the proposed invention is a well known method for preparing a cooking
liquor to manufacture a fibrous semifabricate. The method in question requires waste
water that has been treated biologically be used as a water medium. This waste water
that normally contains an excessed activated sludge in the range of 0,5 - 17,0 g/l
is to be withdrawn from a secondary thickener to dissolve sulfates. Should sulfite
or bisulfite cooking methods are used the abovementioned water medium is to be saturated
with sulfurous anhydride until the required pH value is reached (4).
[0006] This method may offer cost advantages resulting from replacement fresh water with
waste one after biological treatment thereof. However, this method leads to a comparatively
low pulp yield and doesn't secure that the required level of its quality parameters
needed now will be reached. Besides, waste water at low activated sludge concentration
is used as a water medium here.
[0007] The proposed invention is aimed at creating a method for preparing a pulp cooking
liquor to manufacture a fibrous semifabricate in a way that makes it possible to increase
the yield of the final product, improve its quality as well as to extend a stock of
row materials needed for preparing sulfite cooking liquors.
[0008] The abovementioned objectives of the invention are reached in such an event when
either soda ash (1,5 - 2,50 % by weight based on Na
2 O) in form of a solution in biologically treated effluents of pulp and paper manufacture
which in turn run between 18 and 40 g/l suspended solids or alkaline hydrolizate generated
at the treatment of the same effluents by a mixture of basic salts (both Na
2CO
3 - 50 - 90 % by weight and CaO - 1,5 - 2,5 % by weight based on Na
2 O) at the temperature of 25 - 40°C accompanied by removal of resulting precipitate
are used as water medium while saturating thereof with sulfurous anhydride at 35-40°C
until its content in the cooking liquor is 2,2-5,5 % by weight based on the total
mass of the solution.
[0009] The proposed method differs from the well known one by the following features: soda
ash (1,5 - 2,50 % by weight based on Na
2 O) in form of a solution in biologically treated effluents of pulp and paper manufacture
running between 18 and 40 g/l suspended solids or alkaline hydrolizate generated at
the treatment of the same effluents by a mixture of basic salts (Na
2CO
3 - 50 - 90% by weight and CaO - 1,5 - 2,5 % by weight based on Na
2 O) at 25 - 40°C accompanied by removal of resulting precipitate are used as a water
medium.
[0010] The usage of either soda ash dissolved in pulp and paper effluents or hydrolizate
originated from the same effluents makes it possible to enhance efficiency of pulping
since the products of alkaline or acid hydrolysis that found their way into the cooking
liquor act as inhibitors thus eliminating the processes of thermo-oxidizing destruction
of carbohydrates.
[0011] When sulfurous anhydride is used to saturate soda ash solution in biologically treated
waste water containing an excessed activated sludge there is an acid hydrolysis of
the bio-organic part thereof occurs there since that part accounts for 83% by weight
based on dry residue.
[0012] Should the mixture of basic salts is used to treat the abovementioned waste water
a reaction of caustization will proceed prior to complete saturation thereof
Na
2CO
3+CaO+H
2O=2NaOH+CaCO
3
accompanied by alkali hydrolysis of bio-organic part of the activated sludge.
The major components of both acid and alkali hydrolizate of activated sludge biomass
are aminoacids and their sodium salts (approximately 68 - 80% by weight based on total
organic substances passed into solution), carboxylic acids or their salts (10 - 15%
by weight), neutral ether-soluble substances (5 - 12% by weight) and phenols (2 -
12% by weght).
[0013] It's necessary to stress that activated sludge biomass from a pulp and paper waste
water treatment plant contains a significant amount of fiber fines, slime-lignin and
saw dast the total amount of which accounts for up to 17% by weight based on dry residue.
[0014] When mixed carefully calcium carbonate produced according the above referred to reaction
of caustization distributes proportionally among solid non-hydrolyxed particles of
activated sludge biomass. As a result, non-hydrolyzed sediments of activated sludge
biomass which normally retain water firmly and therefore can hardly be separated are
bound to obtain a favorable structure that makes it possible to dispose them easily
by filtration or sedimentation.
[0015] The proposed method means the use of industrial waste water after biological treatment
with concentration of activated sludge biomass in the range of 18 - 40g/l. Such concentration
obtained by preliminary consolidation of activated sludge biomass in special settlers,
is optimal since it mantains higher than usual content of acid and alkali hydrolysis
products in a cooking liquor that are formed during its preparation and thus, as it
has been mentioned, making cooking more effective. Besides, the usage of industrial
waste water with high concentration of activated sludge (18-40g/l) allows to utilize
activated sludge biomass.
[0016] Water medium saturation with sulfurous anhydride at 35-40°C up to concentration of
2,5-5,5% by weight first of all makes it possible to reach complete acid hydrolysis
of activated sludge biomass followed by generation of substances that increase the
quality of the cooking liquor, and secondly it means the optimal conditions of cooking
namely the increase of fibrous semi-fabricate yield and the improvement of its mechanical
properties.
[0017] As it has already been mentioned, the usage of alkali hydrolyzate as a water medium
allows to get rid effectively (by means of co-precipitation with calcium carbonate)
from a non-hydrolized part of activated sludge biomass, which makes up to 17% by weight
based on absolutely dry substance thus improving the quality characteristics required
for a fibrous semi-fabricate.
[0018] The proposed conditions for alkali hydrolizate production (treatment by mixed base
salts containing 50-90% of sodium carbonate by weight and 10-15% of calcium oxide
by weght in amount of 1,55-2,50% by weight based on Na
2O at the temperature 25-40°C followed up with removal of sediment) makes it possible
to reach a complete alkali hydrolysis of bio-organic part of activated sludge and
to remove an insoluble slime. All this in turn, increases the efficiency of cooking
process and makes the quality of the fibrous semi-fabricate better.
The method is carried out in the following way:
[0019] Sodium carbonate (in amount that makes its concentration in solution equal to 1,55-2,50%
by weight based on Na
2O) is added to biologically treated waste water of a pulp and paper mill after settling
thereof in a radial or vertical thickener until the activated sludge concentration
in it has reached the level of 18-40g/l. The resultant soda ash solution is sent to
an absorber for saturation with sulfurous anhidride at the temperature 35-45°C until
its concentration is of 2,5-5,5% by weight and organic part of the sludge is dissolved.
Or a pulp and paper mill waste water that has been treated biologically and then stored
in a thickener until the excessed activated sludge concentration in it has reached
the level of 18-40g/l is delivered to a mixer to be treated with a mixed base salts
in amount of 1,55-2,50% by weight based on Na
2O at the temperature of 25-40°C provided that it is accompanied by thorough mixing
until the activated sludge biomass is dissolved completely.
[0020] Then the resulting mixture containing alkali hydrolizate, undissolved slime and calcium
carbonate is to be dewatered by filtration or precipitation. The resultant clarified
alkali hydrolyzate is sent to an absorber for saturation with sulfurous anhydride
at the temperature of 35-45°C until the concentration thereof is 2,5-5,5% by weight
is reached.
The metod is illustrated by the following examples:
Example 1.
[0021] 360 g. of air dry chips were loaded into 15-litre autoclave made of stainless steel
with 9 litres of cooking liquor added in it. The cooking liquor has been prepared
by saturation of a waste water from a pulp and paper mill and the latter has in it
the following: activated sludge biomass in the amount of 30g/l and soda ash in the
amount of 2% by weight based on Na
2O. The saturation is to be proceeded at the temperature of 40°C until sulfurous anhydride
concentration is 4,5% by weight.
[0022] The cooking process was carried out during 2 hours 15 minutes while the temperature
being raised from 25°C to 100°C; then during 45 minutes the temperature was kept at
120°C and during another 1 hour and a half it had been raising from 120°C to 160°C.
Then the process proceeded at that temperature (160°C) for another 1 hour. When the
cooking is over a 75g/l sample of the resultant semifabricate was used to determine
both its whiteness and mechanical characteristics. The results obtained are given
in the Table.
Example 2
[0023] The cooking liquor was prepared in the following way: The waste water from a pulp
and paper mill with activated sludge making up 30g/l in it was treated by a mixed
base containing the equal parts of sodium carbonate and calcium oxide in amount of
2,5% by weight based on Na
2O at the temperatute 35°C. After the sediment had been removed the alkali hydrolyzate
was saturated with sulfurous anhydride at the temperature 40°C until the concentration
thereof was reached 5,5% by weight. The resultant cooking liquor with products yielded
by the alkali hydrolysis of activated sludge had 1,9 pH value. The cooking process
was carried out under the same conditions as it was in the Example 1. The results
are given in the Table.
[0024] The data obtained shows that the combination of the conditions needed for the preparing
of the cooking liquor leads both to the considerable increase in the yield and improving
in mechanical characteristics of the final product in contrast to that of the well
known method.
[0025] Moreover, the usage of fresh water for a cooking liquor preparation is eliminated
and a stock of raw materials for its production is expanded. At the same time it gives
a way of utilizing of all waste water produced by a pulp and paper mill and posing
a real threat to the environment.
TABLE
Example number |
Pulp output, % |
Characteristics of fibrous semi-finished product. |
|
|
Delignification degree, Kappa |
Tearing length, m |
Tearing resistance, g |
Pressing resistance, kg/sm2 |
Whiteness, % |
1 |
73 |
79 |
11 280 |
64 |
3,5 |
58,8 |
2 |
78 |
86 |
11 920 |
67 |
3,8 |
59,7 |
3* |
52 |
57 |
10 360 |
61 |
2,9 |
55,8 |
* Example 3 illustrates a well-known cooking preparation method, according to author
 s certificate of the USSR Nº 746002. |
The cooking process is held in conditions of Example 1. |
REFERENCES
[0026]
1. N.H. Nepenin, 〈〈Pulp Production〉〉, Volume 1, Moscow, 1976, page 142.
2. USSR Author

s Certificate Nº 376507, D21C 3/06, 1973.
3. USSR Author

s Certificate Nº 403795, D21C 3/06, 1974.
4. USSR Author

s Certificate Nº 746002, D21C 3/04, 1980.