Abstract:
A procedure for arranging water circulations in an integrated paper mill, the paper making process of which having three partly separate process phases concerning the water circulations (I, II, III). In the first phase, the fiber raw material is pretreated, defibered and cleaned for producing mechanical, chemi-mechanical and recycled pulp, in the second phase the pulp is treated further for improving the quality, and in the third phase it is made into paper or board. The circulation waters of the first process phase are concentrated by circulating the filtrates of the concentration and pressing phases counter-current inside the water circulation (I), and the circulation water thus concentrated is conducted into an effluent evaporation plant to be concentrated and then burnt in a combustion boiler. The water quantity discharged from the water circulation (I) of the first process phase is replaced by conducting such circulation waters of the paper mill into the front dilution of the press.

Description:
FIELD OF THE INVENTION 
     The present invention relates to a procedure for arranging water circulations in an integrated paper mill, including a pulp mill based on refiner mechanized pulp and/or groundwood pulp and/or waste paper and/or chemical pulp, and paper and/or board manufacturing lines. 
     BACKGROUND OF THE INVENTION 
     Various impurities enter the water circulations in a paper mill in different phases of the pulp and paper production process. Fouling of water is mainly caused by organic ingredients accumulating from fiber raw material and, on the other hand, mainly by inorganic chemicals added therein in different phases. As unwanted chemical agents, such impurities, in high proportions, are detrimental to the operation of the process and the quality of the paper produced. 
     A paper making process can be divided into two or three main phases being partly separate in water circulations, the first phase thereof including pretreatment, defibering and cleaning of fibre raw material and preferably also pulp thickening and pressing. The second phase includes improving of pulp quality, and paper manufacture. Currently, also the water circulation of the paper manufacture has been separated, whenever needed, from the water circulation of the quality improvement phase into a third water circulation by arranging pulp thickening and/or pressing between the process phases. The second quality improvement phase includes, depending on the need, pulp processing phases such as dispersing, bleaching and sorting. 
     The pretreatment may include various operations, such as barking, washing of chip, thermal and chemical treatment, waste paper pulping and pulp cleaning. 
     In pretreating raw material, namely in the defibering, pulping and cleaning phases, addition of chemicals can be employed, or the phases can be carried out without any chemicals. When producing mechanical pulp, about 2 to 5 per cent of the wood material is dissolved or dispersed as colloid particles in the process water. Most of the process water fouling takes place in connection with chip treatment and defibering, whereby, for instance, the water coming from the mass suspension of a TMP grinder contains dissolved and colloid organic matter in great quantities. Moreover, when using waste paper, paper fillers and additive agents from the raw material end up into the circulation water in the defibering and cleaning phases, in addition to organic agents, additive agents used in converting paper, and completely foreign agents accumulated in the use or recycling of paper. Particularly difficult foreign agents are sticky agents which are adhesive in nature and originated from various adhesives and plastics. 
     Inorganic chemicals enter the water circulation in the pulp quality improvement phase, in bleaching and in the wet end of the paper machine, in which phases also organic matter is dissolved. In addition, in different phases of producing recycled mass, chemicals are used in great quantities e.g. for chalking print dye pigments, as auxiliary foaming agents, in pulp bleaching, and in end acidification. 
     In different phases of a paper making process, great quantities of water are needed for various purposes, such as for dilution of pulp and chemicals, transport and cleaning. In addition, water is needed e.g. for cooling and sealing. By circulating the process waters of the paper mill, endeavors are made to recover and to reuse the useful ingredients originated from the process and contained in the circulation water, such as fibers, fines, filling agents and paper making chemicals, as well as heat. Some of the water needed by the paper mill is generally provided from outside the mill as raw water which has to be cleaned prior to introduction to use and heated if need be to appropriate temperature. Clean water is needed e.g. for certain washing jets in the paper machine and for dilution of chemicals. 
     In order to maintain the contents of unwanted agents below the risk limits, fresh water is usually brought into the process at the same time as part of the circulation water is removed from the system as effluent. When the paper mill process waters are generally circulated counter-current from the paper machine towards the pulp mill, the organic and inorganic agents entered in the circulation water in different phases of the process are usually concentrated most in the circulation and effluent waters of the defibering phase of the pulp. On the other hand, the organic and inorganic matter released in different process phases travels to some extent downstream together with the pulp to the paper machine, which travelling is attempted to be reduced by the thickening, dilution and pressing apparatus positioned between the pretreatment, defibering and cleaning phases and the pulp quality improvement phase, which systems have currently been positioned, whenever needed, also between the pulp quality improvement phase and the paper making phase. With the aid of presses, the pulp can be thickened, depending on the apparatus, to about 25 to 35% thickening, whereas the thickening achieved with the aid of thickening apparatus is only about half thereof. 
     In Finnish patent applications Nos. 962176, 962177, 062178, an arrangement is described in which some of the fresh water amount usually needed by the paper mill is replaced by jet waters selectively recovered from the waters fouled in the paper mill and by waters to be cleaned locally, and the concentrates thus obtained from the water cleaning phases are utilized whenever appropriate by making them flow counter-current relative to the raw material flow for reuse in the paper mill, by means of which measures the level of the quantities of unwanted agents circulating in the paper mill is controlled. By said arrangement, unwanted agents are transferred counter-current from the water circulation of the paper machine into the water circulation of the pulp mill, wherefrom they can be conducted to an effluent evaporation plant and concentrated for combustion at the same time as the cooling water circulation of the evaporation plant is advantageously connected to the cooling and jet water system of the paper mill and the clean condensate is conducted as jet water for substitution of fresh water. 
     The organic and inorganic matter circulates in due time in the water circulations of the mill and is finally discharged from the process mainly among the effluents and to a lesser extent with the paper and into the atmospheric air. The main fractions of the effluents are formed by the controlled overflow of the filtrate of the circulation water system of the pretreatment /defibering /cleaning phases and by the reject waters of the cleanings of the pulp and the water circulations in different phases, in addition to which sporadic emissions occur to some extent. 
     Pressure towards reducing the consumption of fresh water by closing water circulations are on one hand caused by the costs of raw water and the effluent, and on the other hand, by the availability of raw water and by the emission restrictions concerning effluents. A complete shut-off of a paper mill is not possible because emissions of effluents are needed for removal of unwanted agents from the process. When reducing the consumption of the fresh water entering into the water circulation of the paper machine mainly through jets and dilution targets, an excessive temperature rise and concentration of colloid and dissolved organic and inorganic unwanted agents, particularly salts, in the water circulations of the paper machine and of the pulp mill may become a problem to the extent which is detrimental to the quality and production of pulp and paper. If e.g. the content of unwanted agents in the circulation water of the paper machine is increased too much, the action of the retention chemicals will be weakened, the formation of interfiber bonds will be impaired and the strength of paper being manufactured will suffer. A first drawback lies therein, that for instance with the increased content of the agents dissolved in the circulation water used for pulp bleaching, the degree of brightness may drop or the consumption of bleaching chemicals may grow, which, in turn, will increase the amount of organic and inorganic matter ending up in the circulation and effluent waters. 
     With the most commonly used water purification methods within the paper mill, fibre, pigment, resin or sticky agent particles are in general removed using filtering, clarification and flotation techniques. However, removal of unwanted colloid agents is incomplete, and separation of dissolved agents hardly ever occurs, instead, the agents travel into different fractions mainly in proportion of liquid flows. A more thorough removal of colloid matter and dissolved organic and inorganic matter requires costly special arrangements such as membrane filtering and/or evaporation. 
     By evaporation, biologically undecomposable organic matter, micromolecular agents and volatile components and salts can be removed from the unclean water, the separation whereof would otherwise be difficult. The water achieved through evaporation may be even purer than the chemically treated fresh water. The use of evaporation as a process-internal water cleaning method is particularly advantageous when the waters being cleaned are warm and concentrated, and the process yields waste heat in great quantities appropriate for use as an energy source. Utilization of waste heat can advantageously be intensified by means of surface condensation and cooling tower connection of the evaporation as disclosed in FI patent application No. 962178. When the filtrate of the thickening phase subsequent to the defibering is strong and hot, owing to the counter-current connection of the circulation waters, and its quantity is small, it is advantageous to lead it to the evaporation plant to be concentrated further. From the evaporation plant the concentrated solution can be conducted to the combustion unit, whereby the organic matter is utilized in the energy production of the paper mill and the inorganic matter, such as sodium and sulphur, in the chemical circulation of the mill. The foul condensates of the evaporation plant can be conducted to biological effluent treatment. 
     In manufacturing mechanical pulp, great quantities of expansion steams are formed, for instance, in making refiner mechanical pulp, about 2 tons of steam are released per pulp ton. Another drawback lies therein, that merely 1 ton of pure steam per mass ton can be produced with expansion steam with the aid of a steam generator, said steam being used in the process for replacing fresh steam. The rest of the thermal energy of the expansion steam is wasted in heat losses and discharged with the unclean condensate into the circulation waters and effluents. 
     In a paper mill provided with conventional counter-current connection of circulation waters, the effluents contain great quantities of inorganic salts, a majority of which being compounds melting at a low temperature, such as sodium. Another drawback in this case is that an effluent concentrate cannot be burnt together with mill waste or other fuel in the ancillary boiler available which can be of grate type, or nowadays most frequently, fluidized bed or circulated type, in which sodium and potassium cause sintration of bed sand and chloride, boiler corrosion. Yet another drawback is that burning such concentrate requires a soda boiler which may not always be available in conjunction with the mill. Another drawback is that in such instances detrimental and corroding unwanted agents, such as potassium and chloride, may be concentrated into the chemical circulation of the pulp mill. When the bleaching waters of pulp mills are concentrated and conducted into a soda recovery boiler, endeavors are made to reduce concentration of said agents by means of crystallization techniques and by opening chemical and water circulations. Another drawback is that the evaporation concentrate has a low dry matter content (20 to 40%), and decreases the efficiency of the electricity and steam production of the high-pressure ancillary boiler or soda recovery boiler. 
     OBJECTS AND SUMMARY OF THE INVENTION 
     The object of the present invention is to achieve a procedure, with the aid of which the above drawbacks can be avoided and simultaneously, the water consumption of the paper mill and effluent emissions can be reduced. 
     Another object the present invention is to achieve a procedure with which the combustion of agents ending up in the concentrate of the effluent evaporation plant, utilization of combustion waste or the amount of agents detrimental to recovery of chemicals can be limited. 
     Yet another object of the present invention is to achieve a procedure with the aid of which the contents of colloid and dissolved organic and inorganic unwanted agents can be reduced in the water circulations of the pulp quality improvement phases and of the paper machine when reducing the fresh water consumption of the mill. 
     A further object of the present invention is to provide for a more efficient utilization of the heat of expansion steams of the process and the condensate and energy contents of effluents. 
     In the procedure according to the present invention, the circulation water of the water circulation of the first process phase is concentrated by circulating the filtrate of the pulp thickening phase after the defibering and cleaning phases back into the pretreatment and defibering of the raw fiber material. The concentration of the circulation water is intensified by adding the dilution and pressing of the pulp after the pulp thickening phase after the cleaning. In addition, a second pulp dilution/press phase can be added in the process immediately after the defibering. The water circulation of the first process phase is separated into a water circulation of its own, within which the overflow connection between the water circulations of the thickening phases is arranged counter-current relative to the pulp flow so that the filtrate of the pressing passes into the pulp dilution on the front side of the thickening and the filtrate of the thickening goes into the dilution of the pulp prior to potential pressing after the defibering. The pretreatment of the raw material may comprise, for instance in chip treatment, removal of impurities and washing, absorption and heat treatment with the aid of water and steam and/or with the aid of chemicals, whereto the filtrate from the pressing and/or thickening is conducted. The pretreatment of raw material may also include other operations such as barking or waste paper pulpering and cleaning. 
     The strongest filtrate obtained as overflow of the pretreatment and from pulp pressing and/or thickening after the defibering phase is concentrated in the evaporation plant and the concentrate burnt. 
     The evaporation concentrate can be burnt in a fluidized or circulated bed type ancillary boiler when chemicals harmful to combustion or causing corrosion are not conducted into the first water circulation, nor the circulation waters including such agents are not conducted counter-current relative to the traveling of the pulp or from the water circulations of the paper machine or the quality improvement phase. 
     The evaporation concentrate can be burnt in a soda recovery boiler when a concentrate contains, due to the chemical selections of the process phases or the water connections, compounds melting at low temperature, such as sodium, but not in excessive quantities corrosion-causing chemicals or chemicals detrimental to recovery of chemicals and unwanted agents. 
     The evaporation concentrate can be dispersed into drops or burnt in a melt fuel furnace with auxiliary fuel when the concentrate contains compounds causing corrosion or melting at low temperature when it should not cause harm to the burning, chemical circulation or efficiency of power production. The inorganic molten salts obtained from the bottom of the furnace can be dissolved in residual water to be taken into biological purification or solidified into solid state to be taken to recycling or to a dump in separation or mixed with other waste. 
     For the energy source in the effluent evaporation plant, electricity, steam and preferably the hot, unclean waste steams of a refiner plant or a pressure grinding plant can be used, being conducted through steam wash directly into the evaporation phase. With the aid of steam wash, the fibre matter is prevented from entering on the heat-exchange surfaces of the evaporation plant. In this manner both the amount and the heat of expansion steams of the pulp production and the heat content of the effluent can be utilized more efficiently than before. The clean condensate formed from unclean steams and circulation water is used for pulp dilution prior to the press phase. The unclean condensate formed in cleaning the main condensate is conducted into the effluent treatment together with the reject fractions of the first process phase. The water quantity leaving the water circulation together with the pulp, entering into the effluent and the atmospheric air, is replaced by other waters free from said detrimental agents, such as by the circulation water of the paper manufacturing, but not by the bleaching water of the quality improvement phase containing sodium in great quantities. Preferably, clean cooling water heated in the cooling/condensing apparatus can be used for this purpose. Said make-up water together with the clean condensate is conducted into the pulp dilution prior to the pressing preceding the quality improvement phase, whereby the washing of pulp is carried out preferably with water which is as clean as possible. 
     The pulp can be properly washed, in this manner, before the bleaching or dispersing of the pulp quality improvement phase, which will improve the quality of pulp and paper, especially clearness and microbiological purity, reduce the quantities of detrimental agents transferring to the paper machine and the use of chemicals, and water emissions from the water circulations of the quality improvement phase and the paper machine. The overflow of the paper machine water circulation is conducted primarily into the dilution before the pressing of the pulp after the quality improvement phase. Between said phases, the counter-current principle can thus be maintained, so that the effluent formed therefrom is mainly comprised of controlled overflow of the filtrate of the quality improvement phase, reject waters of the phases, and spurious emissions. 
     From about 50% to a majority of the organic effluent load of the plant is dissolved in the first water circulation being separated as a separate water circulation. When said effluent is concentrated by evaporation into a small volume and the concentrate is burnt, the energy content of the organic matter can be recovered. Hereby, also the amount of the water to be discharged as effluent from the process is reduced, as well as the amount of agents difficult to decompose biologically or of those agents which will not decompose, so that the efficiency of the biological treatment is improved and problems related to sludge elimination are reduced. 
     The procedure of the invention is advantageously appropriate for use in an integrated paper mill in which the use of expansion steams of thermomechanical pulp and pressure groundwood can be intensified by conducting them into an effluent evaporation plant, but the procedure is also applicable in a mill utilizing waste paper as raw material, when the water circulation to be concentrated includes a pulp concentration phase after the cleaning, and the dilution and pressing, or, in addition thereto, as an advantageous embodiment, a second pulp dilution and pressing immediately after the pretreatment, pulpering and defibering phases. For the evaporation energy, electricity, fresh steam and thermal energy partly recoverable from flue gases can be used. 
     When the waste paper mass is washed according to the invention as early as in the first process phase on the counter-current principle two or three times, the ending up of impurities with the pulp in the paper machine is lessened radically. In the pulp thickening and/or pressing subsequent to the second, that is, the quality improvement process phase, the circulation water conducted from the third process phase, that is, the water as a controlled overflow from the paper machine, is advantageously used for the front dilution water. The discharge of impurities is also increased in that the water circulation of the pulp mill is in this manner divided into two parts in separation from each other, and the effluent of the second water circulation, that is, of the pulp improvement phase, is conducted into an external effluent treatment plant. When at this stage the counter-current principle is abandoned, the impurities ended up in the circulation waters in the second and the third phase of pulp production, such as sticky agents which are known to be very harmful in the production of recycled pulp and dispersed in the water in the dispersing phase, are not returned unpurified into the process, instead, they can be discharged efficiently. 
    
    
     BRIEF DESCRIPTION OF THE DRAWINGS 
     The invention is described below in greater detail with the aid of FIGS. 1-6, to the details of which the invention is not intended to be restricted. 
     FIG. 1 is a schematic drawing represents a water circulation system of a paper mill according to the present state of the art; 
     FIG. 2 is a drawing of a more advanced version of the paper mill presented in FIG. 1; 
     FIG. 3 is a schematic drawing of an example of the arrangement of the circulation of water according to the present invention; 
     FIG. 4 is a schematic drawing of a second embodiment according to the present invention for arranging the circulation of water in a paper mill; 
     FIG. 5 is a schematic drawing of a third embodiment according to the present invention for arranging the circulation of water in a paper mill; and 
     FIG. 6 is a schematic drawing of a fourth embodiment according to the present invention for arranging the circulation of water in a paper mill. 
    
    
     DETAILED DESCRIPTION OF THE INVENTION 
     FIG. 1 represents a water treatment circulation system for a paper mill according to the present state of the art. The paper making process and its water circulation are for the purposes of illustration divided into three consecutive parts I, II and III, the limits whereof being marked with broken lines. On the left side of each broken line is located said part of the water circulation marked with numeral I, II III. 
     As a main principle known in the art, the first process phase includes the following main phases: pretreatment of raw material  1 , defibering  2 , cleaning of pulp  3 , thickening  4 , and  5  pressing  7 . The water circulation I of the first process phase includes moreover circulation water tanks  5 ,  6  and  8 . The second process phase includes pulp quality improvement  9 , thickening  10  and pressing  13 , and its water circulation II includes further circulation water tanks  11 ,  12  and  14 . In the third process phase, the paper making is carried out in the paper machine, the main phases of which are indicated by reference numerals  18 ,  19 ,  20  and  22 . The water circulation III of the third process phase includes circulation water tanks  16 ,  17 ,  32  and  21 , and a disc filter  15 . The overflows  121  and  122  of the water circulations II and III are conducted counter-current relative to the pulp travelling to the water circulation I, and the concentrated effluent  39 ,  49  is discharged from the water circulation I to an effluent treatment plant  27 . The effluent treatment plant  27  and the reject slurries  39 ,  43 ,  69 ,  132 ,  103  are concentrated with a sludge press  28  and burnt in a residue combustion boiler  29 , located in the site or outside. Inorganic matter is discharged from the water circulation mainly together with the effluent  102  into the waterways. The consumption of fresh water in an exemplary modem plant is about 10 m 3 /paper ton and the chemical oxygen use load of the effluent into an effluent treatment plant is about 21 t/24 hrs and into the waterways about 4 t/24 hrs. 
     First, the progress of the fibre matter is described more in detail below in FIG.  1 . The fibre raw material is brought via connector  35  to the raw material pretreatment phase  1 , wherefrom it passes via connector  36  to the defibering  2  and, further, along connector  42  to the pulp cleaning  3 . Thereafter, the pulp passes along connector  44  to the thickening  4  and therefrom along connector  51  to the press phase  7 . Via connector  54  the pulp enters the quality improvement phase  9 , wherefrom it passes along connector  56  to the thickening  10  and therefrom, along connector  62  to the press phase  13 . Via connector  65 , the pulp is conducted to the pulp unit  18  of the paper machine, wherefrom it passes along connector  78  to the cleaning  19  and therefrom along connector  81  to the paper machine wire section and press section, that is, to the wet end  20 , wherefrom the paper web  89  formed from the pulp is transferred to the drying section  22 . Uncoated reject  92  is separated from the paper web. Subsequent to the drying section  22 , coating  95  is brought onto the paper web, and from the coated paper web  94 , coated reject  93  is separated. The rejects are conducted along connector  79  to the pulp section  18 . 
     Secondly, the progress of the waters of the water circulation III presented in FIG. 1 is described in more detail below. The fresh water enters along connector  97  to the water cleaning  25 , wherefrom cold water runs along connector  98  to the cooling system  26 . Therefrom, some of the water is discharged in the form of vapor  99  into the outdoor air, and the returning of cooling water is conducted in heated state along connector  100  through the water cleaning  25  and connector  96  to the heat recovery section  23  of the paper machine, which transfers heat from the wet discharge air  90  of the drying section  22  into fresh water passing to the fresh water jets of the paper machine along connector  88  and into the dilution of chemicals, and for use as sealing and make-up water along connector  77 . Via a discharge connector  91  of the heat recovery unit  23 , water steam is discharged into the atmospheric air. 
     From the wet end  20  of the paper machine, the filtrate water and the jet waters are collected along connectors  83 ,  84 ,  85  to the short-circulation water system  21 , wherefrom circulation water is taken along connector  80  for the dilution of the pulp  78  on the way to the paper machine. The excess water of the short circulation is conducted along connector  70  to a disc filter  15  and mixed with auxiliary pulp brought to the disc filter  15  along line  68 . The solid matter recovered by the disc filter  15  passes along connector  74  to the pulp section  18 , the turbid filtrate passes along connector  71  into a turbid filtrate tank  16  and the clear filtrate along connector  72  to a clear filtrate tank  17 , and the super clear filtrate along connector  73  to a super clear filtrate tank  32 . The circulation water from the turbid filtrate tank  16  runs along connector  131  to the front dilution of the disc filter  15  and it is mixed with the auxiliary pulp brought along line  68 . From the super clear filtrate tank  32 , the circulation water passes along line  76  to the paper machine. From the clear filtrate tank  17 , circulation water of the water circulation III is conducted along connector  67  via a pulp collecting connector  66  from the press  13  along line  65  to the collection of the entering pulp, and the excess is conducted to the front dilution line  64  of the press  13  and along connector  122  to the water circulation II, into the front dilution line  53  of the press  7 . 
     Third, the progress of the waters of the water circulation II presented in FIG. 1 is described below more in detail. Filtrate from the press  13  passes along connector  63  into a filtrate tank  14 , wherefrom circulation water is taken along connector  64  for the dilution of the pulp entering the press  13  via line  62 . The overflow of the filtrate tank  14  passes via the turbid filtrate tank  11  of the disc filter  10  along connector  57  into the dilution of the pulp  56  entering the filter. The pulp concentrated by the disc filter  10  passes along connector  62  to the press  13 , the turbid filtrate passes along connector  58  into the turbid filtrate tank  11  and the clear filtrate along connector  59  into the clear filtrate tank  12 . From the clear filtrate tank  12  the overflow passes along connector  121  into the front dilution line  53  of the press  7 . 
     Fourth, the progress of the waters of the water circulation I presented in FIG. 1 is described below more in detail. The filtrate from the press  7  passes along connector  52  to a filtrate tank  8 , wherefrom circulation water is taken along connector  53  to the dilution of the pulp entering the press  7  along line  51 . The overflow of the filtrate tank  8  passes via connector  50  and via the turbid filtrate tank  5  of the disc filter  4  along connector  48  to the pulp dilution when passing through the connector  42  and the cleaning  3  along connector  44  to the concentration  4 . The pulp concentrated with the disc filter  4  passes along connector  51  to the press  7 , the turbid filtrate via connector  46  to the turbid filtrate tank  5  and the clear filtrate via connector  47  to the clear filtrate tank  6 . From the clear filtrate tank  6 , circulation water is conducted to the raw material pretreatment  1  along connector  38  and into the defibering  2  along connector  41 . The overflow of the tank  6  is conducted via connector  49  into the drain  101 . 
     Fifth, the effluent treatment presented in FIG. 1 is described below more in detail. The overflow  49  of the water circulation I and the reject waters  39 ,  43 ,  69 ,  132  from different process phases are conducted via the drain  101  to an effluent treatment unit  27 , wherefrom the sludges are conducted along connector  103  to a sludge press  28 , and the purified effluent via a discharge connector  102  into the waterways. The filtrate from the sludge press  28  is returned to the effluent treatment  27  along connector  104 , and the concentrated sludge enters along connector  105  into a residue combustion boiler  29 , wherefrom steam is discharged along with flue gases  106  into the atmospheric air. The inorganic matter of the chemicals separated from the raw materials  35 ,  95  of the paper making process and brought into the process via connectors  37 ,  55 ,  75  is discharged via connector  107  together with the ash. The consumption of fresh water is about 10 m 3 /paper ton and the chemical oxygen consumption load of the effluent into the effluent treatment unit is about 21 t/24 hrs, into the waterways about 4 t/24 hrs. 
     FIG. 2 presents an enhanced process, which is based on the design as in FIG. 1 but which on the basis of the FI patent applications Nos. 962176, 962177, 962178 have been improved by changes described more in detail below. Some of the fresh water amount  96  needed by the paper mill is replaced by paper machine jet waters  83 ,  88  recovered selectively, being conducted along connector  86  to a local purification unit  24 , and from there along connector  87  to a fresh water line  77  to replace fresh water in appropriate targets, these being, for instance, dilution of chemicals, sealing and make-up waters, and paper machine jets. The overflow of the water circulation III is conducted along line  67  counter-current relative to the course of the pulp to the water circulation II, the overflow of which passes along line  121  counter-current relative to the course of the pulp to the water circulation I and it is concentrated in the defibering and pretreatment phases  1  and  2 . Some of the concentrated and heated filtrate passes along connector  108  to the overflow of the pretreatment  1 , from where the fractions pass along connector  39  via a solid matter filter  30  and connector  110  to an effluent evaporation plant  31 . The concentrate of the effluent evaporation plant  31  is conducted along connector  113  for burning in a soda recovery boiler  122  located in site or elsewhere, and the clean condensate is conducted along connector  114  via the water treatment  25  and connector  96  to the paper machine. The unclean condensate of the effluent evaporation plant  31  is conducted via connector  112  to the drain  101 . In the evaporation  31 , the heat and amount of the expansion steams conducted via connector  40 , preferably directly from the defibering  2 , and the heat content of the effluent obtained via connector  110  are utilized. If needed, the need of energy of the evaporation  31  can be complemented with fresh steam or electricity along connector  111 . From the clear filtrate tank  6  of the water circulation I no concentrated filtrate is conducted directly into the drain  101 . The purification plant slurries and reject slurries  43 ,  69 ,  103 ,  109 ,  82 ,  132  are concentrated with a sludge press  28  and burnt in the residue combustion boiler  29 , wherefrom steam is discharged together with flue gases  106  into the atmospheric air. The inorganic matter of the sludges is discharged via connector  107  together with ash. The inorganic matter of the chemicals separated from raw materials  35 ,  95  and entered via connectors  37 ,  55 ,  75  enters with the concentrate along connector  113  into the soda recovery boiler  122 , and it is recovered into the chemical circulation via connector  124 . Depending on the evaporation quantity, the consumption of fresh water is about 4-5 m 3 /paper ton and the chemical oxygen consumption load of the effluent into the effluent purification plant is 6-11 t/24 hrs, into the waterways about 1-2 t/24 hrs, and into the soda recovery boiler about 10-15 t/24 hrs. In the present instance and in those below, the evaporation quantity is varied in the range 20 to 30 liters per second. 
     FIG. 3 presents a procedure of the invention which is based on the designs as in FIGS. 1 and 2 but which has been improved by means of changes described more in detail below. The water circulation I is separated into a separate water circulation ending in the thickening  4  and the press  7 . On the front side of the press  7 , clean condensate of the effluent evaporation plant  31  is conducted into the pulp dilution—washing line  53  along connector  114 . In addition, circulation water from the water circulation I is conducted for make-up water into the dilution—washing line  53  along connector  115  when it contains no chemicals harmful to combustion in an ancillay or soda recovery boiler. If needed, make-up water can be conducted into the dilution—washing line  53 , additionally or solely, along connector  116  from the cooling water system  26  in line  100  of discharging clean and warm cooling water. The make-up water replaces the water balance difference discharging from the water circulation I through connectors  40 ,  43 ,  54 ,  109 , and when it is conducted to the front side of the press  7  together with the clean condensate  114  of the evaporation plant  31  to pulp dilution washing, the running of unwanted agents into the pulp quality improvement phase  9  and to the paper machine can be essentially reduced. In the exemplary case, the chemical oxygen consumption of the filtrate of the press  7  is about 1,900 to 2,000 mg/l in the process of FIG. 1, about 4,000 to 6,000 mg/l in the process of FIG. 2 depending on the amount of evaporation, and with the process connection of the invention presented in FIG. 3, it is about 2,100 to 3,400 mg/l depending on the amount of evaporation. 
     The effluent concentrated in the water circulation I is discharged through connector  110  to the effluent evaporation plant  31 , wherefrom the concentrate is conducted along connector  113  for combustion in the residue combustion boiler  29  or along connector  133  for combustion in a soda recovery boiler. The type of the boiler to be used in burning the concentrate is on one hand dependent on whether a residue combustion boiler or a soda recovery boiler is available, and on the other hand, also on the pulping process used. If chemicals containing sodium and sulphur are used in the pulping process, the soda recovery boiler is most appropriate for recovering the chemicals. The essential feature of the invention lies in that the entry of agents harming combustion, utilization of combustion residue and/or recovery of chemicals is limited into the water circulation I. Harmful agents are at least chlorides and to some extent also potassium and silicates. The overflow  60  of the water circulation II is conducted via the drain  101  to the effluent treatment plant  27 . The fresh water consumption is about 7 m 3 /paper ton and the chemical oxygen consumption load of the effluent into the effluent treatment plant is about 11 to 14 ton/24 hrs, depending on the amount of evaporation, about 2 to 3 ton/24 hrs into the waterways, and about 7 to 10 ton/24 hrs into either boiler. 
     FIG. 4 presents a second embodiment of the procedure of the invention, based on the designs shown in FIGS. 1,  2  and  3  but improved by changes described more in detail below. Regarding FIG. 3, an additional dilution and a press  33  have been added in the water circulation I for the pulp entering along connector  42  immediately after the defibering  2 , the filtrate whereof passing along connector  118  through a filtrate tank  34  and connector  117  to the front dilution of the pulp. The pulp is discharged from the press  33  along connector  120  and it is diluted with turbid filtrate conducted from the turbid filtrate tank  5  along connector  45  prior to being conducted via the purification  3  along connector  44  to the disc filter  4 . From the clear filtrate tank  6  of the filter  4 , make-up water is conducted into the water circulation  117  of the press  33  via connector  49 . Within the water circulation I, an overflow connection  50 ,  45 ,  49  between the water circulations of the thickening phases  7 ,  4 ,  33  is arranged counter-current relative to the traveling of the pulp so that the filtrate  52 ,  50  of the press  7  preceding the pulp quality improvement phase  9  passes to the pulp dilution on the front side of the thickening  4  along connector  45 , and the filtrate  47  of the thickening passes to pulp dilution prior to the press  33  after the defibering  2  along connector  49 ,  117 . In this manner, the effluent within a water circulation can be concentrated to a greater extent than earlier before it is discharged along connector  110  to the effluent evaporation plant  31 . Simultaneously, the pulp can be washed better than earlier in the press  7  before the pulp quality improvement phase  9 . The chemical oxygen consumption of the filtrate of the press  7  is, in the exemplary case in the process of FIG. 4, only about 1,000 to 1,800 mg/l depending on the amount of evaporation. Travelling of unwanted agents into the pulp quality improvement phase and to the paper machine will in this manner be reduced highly significantly, which is assumed to have a considerable impact on the quality of pulp and paper, production and chemical consumption. The fresh water consumption is about 7 m 3 /paper ton and the chemical oxygen consumption load of the effluent into the effluent treatment plant is about 10 to 12 t/24 hrs, depending on the amount of evaporation, about 2 to 2.5 t/24 hrs into the waterways and about 9 to 11 t/24 hrs into the combustion, either into the residue combustion boiler  29  or into the soda recovery boiler  122 . 
     FIG. 5 presents a third embodiment of the procedure of the invention, based on designs in FIGS. 1,  2 ,  3  and  4  but improved by means of changes described more in detail below. The evaporation concentrate coming from the evaporation plant  31  along connector  113  is disintegrated into drops and burnt with auxiliary fuel in the melt combustion furnace  125  when the concentrate contains corroding compounds or those melting at low temperature, which are not desired to cause any harm to combustion, chemical circulation or the effectiveness of the power production of the residue combustion boiler  29  and the soda recovery boiler  122  shown in FIGS. 2 and 4. The inorganic salts entering, in molten state from the bottom of the furnace  125  along connector  128 , into the dissolving unit  126  can be dissolved into the partial flow of the effluent entering along connector  129 , which takes the inorganic salts into biological purification along connector  130 . The salts can also be taken out from the melt combustion furnace  125  along connector  128  and solidified into solid state for recovery or taken to a dumping area separately or mixed with other residue. The fresh water consumption is about 5 to 7 m 3 /paper ton and the chemical oxygen consumption load of the effluent into the effluent purification unit is about 6 to 12 t/24 hrs depending on the amount of evaporation and the target for the clean condensate, about 1 to 1.25 t/24 hrs into the waterways and about 9 to 15 t/24 hrs into the melt combustion furnace. 
     FIG. 6 presents a fourth embodiment of the procedure according to the invention, based on the designs presented in FIGS. 1,  2 ,  3 ,  4  and  5  but improved by means of changes described more in detail below. As shown in the figures, the circulation water  39  of the raw material pretreatment  1  is separated from the circulation water of the water circulation I passing to the evaporation plant  31  along line  108 . Circulation water passes to the pretreatment I from the filtrate tank  17  of the water circulation III along connectors  67  and  134 , but it can also be taken from the filtrate tank  12  of the water circulation II. Circulation water passes to the evaporation plant  31  from the filtrate tank  34  along connector  108  to the solid matter filter  30  and therefrom along connector  110 . If there is no press  33  and filtrate tank  34  available, the circulation water is taken into connector  108  from the filtrate tank  6  shown in FIGS. 2,  3 ,  4  and  5 . Hereby, from the inorganic matter entering the residue combustion boiler  29 , the soda recovery boiler  122  or the melt combustion furnace  125  the inorganic matter can be separated when coming from the raw material pretreatment  1 . In addition, the chemical oxygen consumption of the concentrate on the way to the combustion is greater by about 0.1 to 0.5 t/24 hrs, owing to the concentration of the water circulation I. The chemical oxygen combustion load to the waterways is smaller by an equal amount. 
     The invention is described above referring merely to the advantageous embodiment examples thereof, to the details of which the invention is not, however, intended to be exclusively restricted. A number of modifications and variations are conceivable within the scope of the inventive idea of the claims below. As such, the examples provided above are not meant to be exclusive and many other variations of the present invention would be obvious to those skilled in the art, and are contemplated to be within the scope of the appended claims.