ENVIRONMENTALLY IMPROVED PROCESS FOR BLEACHING LIGNOCELLULOSIC MATERIALS

Abstract: A process for delignifying and bleaching a lignocellulosic pulp without the use of elemental chlorine by partially delignifying the pulp to a K No. of about 10 or less and a viscosity of greater than about 13 cps; and further delignifying the partially delignified pulp with an effective amount of ozone for a sufficient time to obtain a substantially delignified pulp having a K No. of about 5 or less, a viscosity of greater than about 10, and a GE brightness of at least about 50 %. The substantially delignified pulp may be brightened by the addition of a bleaching agent such as chlorine dioxide or a peroxide to obtain a final product having a GE brightness of at least about 65 %, preferably above 70 % to as high as 90 %. Because of the absence of elemental chlorine in this sequence, filtrate from all stages but the chlorine dioxide stage (if used) can be recovered without sewering. Major environmental improvements are thus achieved.

Description: ENVIRONMENTALLY IMPROVED PROCESS FOR BLEACHING LIGNOCELLULOSIC MATERIALS Field of the Invention This invention relates to a novel, environmentally acceptable process for delignifying and bleaching lignoσellulosic pulp which does not require the use of elemental chlorine and which produces a pulp of acceptable strength. Use of this process also reduces the amount of environmental pollutants. Background of the Invention Wood is comprised of two main components - a fibrou carbohydrate, i.e., cellulosic portion, and a non-fibrous component. The polymeric chains forming the fibrous cellulos portion of the wood are aligned with one another and form strong associated bonds with adjacent chains. The non-fibrou portion of the wood comprises a three-dimensional polymeric material formed primarily of phenylpropane units, known as lignin. Part of the lignin is between the cellulosic fibers, bonding them into a solid mass, although a substantial portio of the lignin is also distributed within the fibers themselve For use in paper-making processes, wood must first reduced to pulp. Pulp may be defined as wood fibers capable being slurried or suspended and then deposited upon a screen form a sheet, i.e., of paper. The methods employed to accomplish the pulping step usually involve either physical o chemical treatment of the wood, or a combination of these two treatments, to alter the wood's chemical form and to impart desired properties to the resultant product. There are thus two main types of pulping techniques, i. :-, mechanical pulpin and chemical pulping. In mechanical pulping, the wood is physically separated into individual fibers. In chemical pulping, the wood chips are digested with chemical solutions solubilize a portion of the lignin and thus permit its removal. The commonly utilized chemical pulping processes are broadly classified as: (1) the soda process, (2) the sulfite process, and (3) the Kraft process, with the latter process being most commonly used and being capable of a variety of well-known modifications as described below. The soda process is well known in the art. It employs sodium hydroxide (NaOH) as the active reagent to break down the lignin and to assist in its removal. The sulfite process is also well known in the art (see, e.g., Handbook for Pulp & Paper Technologists - Chapter 6: Sulfite Pulping (TAPPI U.S.A.) . The Kraft process together with its numerous variations is the principle chemical process utilized in paper manufacturing. The basic Kraft process, as described in the Handbook For Pulp and Paper Technologists - Chapter 7: Kraft Pulping (TAPPI, U.S.A.), involves digesting the wood chips in an aqueous solution of sodium hydroxide (NaOH) and sodium sulfide (Na_S) . This process is highly effective in the pulping of even difficult woods such as southern softwoods, as well as the other more readily pulped species of wood such as northern hardwoods and softwoods. The Kraft process likewise generally produces a relatively high-strength pulp since its use results in a diminished attack on the cellulose component of the wood. The modified Kraft techniques can result in even les degradation in the polymeric structure of the cellulosic fiber during pulping and therefore the strength loss in the resultan paper product is diminished as compared to that occurring with the standard Kraft process. One modified Kraft pulping proces is known as "extended delignification", which is a broad term used in the art to encompass a variety of modified Kraft techniques, such as adding the pulping chemicals in a specific defined sequence, or at different locations within the digeste apparatus, or at different time periods, or with a removal and reinjection of cooling liquors in a prescribed sequence, so a to more effectively remove a greater amount of lignin while reducing the severity of the pulping liquor's chemical attack on the cellulosic fibers. Another modification of the Kraft process is the Kraft-AQ process, wherein a small amount of anthraquinone is added to the Kraft pulping liquor to accelerate delignification while limiting the attack upon the cellulosic fibers which comprise the wood. A variety of additional extended delignification techniques are known in the art and include Kamyr Modified Continuous Cooking (MCC) as described by V.A. Kortelainen and E.A. Backlund in TAPPI, vol. 68 (11), 70 (1985); Beloit Rapid Displacement Heating (RDH) as reported by R. S. Grant in TAPP vol. 66 (3), 120 (1983); and Sunds Cold Blow Cooking as reported by B. Pettersson and B. Ernerfeldt in Pulp and Paper vol. 59 (11), 90 (1985). Digestion of the wood by a Kraft or modified Kraft process results in the formation of a dark colored slurry of cellulose fibers known as "brownstock". The dark color of th brownstock is attributable to the fact that not all of the lignin has been removed during digestion and has been chemically modified in pulping to form chro ophoric groups. Thus, in order to lighten the color of the brownstock pulp, i.e., to make it suitable for use as printing and writing and other white paper applications, it is necessary to continue t removal of the remaining lignin by the addition of delignifyi materials and by chemically converting any residual lignin in colorless compounds by a process known as "bleaching" or "brightening". Prior to bleaching the pulp, however, the digested material is conventionally transferred to a separate blow tan after the chemical treatments involved in the pulping process are completed. Within the blow tank, the pressure developed during the initial chemical treatment of the lignocellulosic material is relieved and the pulp material is separated into a fibrous mass. The resulting fibrous mass is then subjected to a series of washing steps to remove the combination of any residual chemicals and the soluble materials (such as the lignin) which were separated from the fibrous materials in the pulping process. Frequently, the pulp also undergoes one or more screening steps designed to separate out the larger portions of undefibered wood for special processing (recooking mechanical grinding, etc.). The residue obtained from the washing process, commonly referred to as black liquor, is collected, concentrated, and then incinerated in an environmentally safe manner in a recovery boiler. The technique for the collection concentration and burning of the black liquor is conventional and is well known in the art. The delignification and bleaching processes are conducted on the washed fibrous mass in a series of steps, using selected combinations of chemical reactants. In the prior art, various combinations of chemical treatments have been suggested. Furthermore, individual treatment steps have been rearranged in an almost limitless number of combinations and permutations. Therefore, in order to simplify the explanation of the various bleaching processes and systems, th use of letter codes is conventionally employed in combination to describe the particular chemical reactants employed and the sequence of the steps of the process. The letter codes which will be used hereafter, where appropriate, are as follows: C = Chlorination - Reaction with elemental chlorine in acidic medium. E = Alkaline - Dissolution of reaction products Extraction with NaOH. E = Oxidative - Dissolution of reaction products Alkaline with NaOH and Oxygen. Extraction D = Chlorine Reaction with C10 2 in acidic Dioxide medium. P = Peroxide Reaction with peroxides in alkaline medium. O = Oxygen Reaction with elemental oxygen in alkaline medium. O = Modified Uniform alkali treatment of low Oxygen to medium consistency pulp followed b reaction of high consistency pulp wit oxygen. Z = Ozone Reaction with ozone. Z = Modified Uniform reaction with ozone. Ozone C/D Admixtures of chlorine and chlorine dioxide. H -= Hypochlorite - Reaction with hypochlorite in an alkaline solution. O and Z are modified processes according to the present invention and are described further in the Detailed Description of the Invention. It has been conventional for many years to delignif and bleach wood pulp by using elemental chlorine. Exemplifyi the bleaching of lignocellulosic pulps are the processes disclosed in, for example, U.S. Pat. Nos. 1,957,937 to Campbe et al., 2,975,169 to Cranford et al. and, 3,462,344 to Kindro et al. ; and Handbook For Pulp and Paper Technologists - Chapt 11: Bleaching (§11.3) (TAPPI, USA). However, although elemental chlorine has proven to an effective bleaching agent, it is difficult to handle and potentially hazardous to both mill personnel and equipment. For example, the effluents from chlorine bleaching processes contain large amounts of chlorides produced as the by-product of these processes. These chlorides readily corrode processi equipment, thus requiring use of costly materials in the construction of such mills. Further, the build-up of chlorid within the mill precludes recycling the washer filtrate after chlorination stage in a closed system operation without employing recovery systems requiring extensive, and therefore expensive, modifications. In addition, concern about the potential environmental effects of chlorinated organics in effluents, which the U.S. Environmental Protection Agency believes to be toxic to humans and animals, has caused significant changes in government requirements and permits for bleach mills which include standards that may be impossible to meet with conventional bleaching or pollution control technology. To avoid these disadvantages, the paper industry has attempted to reduce or eliminate the use of elemental chlorine and chlorine-containing compounds from multi-stage bleaching processes for lignocellulosic pulps. Complicating these efforts is the requirement that high levels of pulp brightness are required for many of the applications for which such pulp is to be used. In this connection, efforts have been made to develo a bleaching process in which chlorine-containing agents are replaced, for example, by oxygen for the purpose of bleaching the pulp. The use of oxygen does permit the recycling of effluent from this stage for recovery and does permit a substantial reduction in the amount of elemental chlorine used A number of processes for bleaching and delignifying pulp with oxygen have been proposed, such as Richter U.S. Pat. 1,860,432 Grangaard et al. U.S. Pats. 2,926,114 and 3,024,158, Gaschke e al. U.S. Pat. 3,274,049, Meylan et al. U.S. Pat. 3,384,533, Watanabe U.S. Pat. 3,251,730, Rerolle et al. U.S. Pat. 3,423,282, Farley U.S. Pat. 3,661,699, Kooi U.S. Pat. 4,619,73 and P. Christensen in "Bleaching of Sulphate Pulps with Hydrogen Peroxide", Norsk Skogindustri, 268-271 (1973). Alkaline pretreatments of pulp prior to oxygen delignification are suggested by U.S. Pat. No. 4,806,203 to Elton. The use of oxygen, however, is not a completely satisfactory solution to the problems encountered with elemental chlorine. Oxygen is not as selective a delignification agent as elemental chlorine, and the K No. of the pulp, using conventional oxygen delignification methods, can be reduced only a limited amount until there is a disproportionate, i.e., unacceptable, attack on the cellulosi fibers. Also, after oxygen delignification, the remaining lignin has heretofore typically been removed by chlorine bleaching methods to obtain a fully-bleached pulp, but using much reduced amounts of chlorine. However, even at such reduced chlorine concentrations, the corrosive chlorides woul soon reach unacceptable concentration levels in a closed cycl operation. To avoid the use of chlorine bleaching agents, the removal of such remaining lignin with the use of ozone in the bleaching of chemical pulp has previously been attempted. Although ozone may initially appear to be an ideal material f bleaching lignocellulosic materials, the exceptional oxidativ properties of ozone and its relative high cost have heretofor limited the development of satisfactory ozone bleaching processes for lignocellulosic materials, especially southern softwoods. Ozone will readily react with lignin to effective reduce the K No., but it will also, under most conditions, aggressively attack the carbohydrate which comprises the cellulosic fibers and substantially reduce the strength of th resulting pulp. Ozone, likewise, is extremely sensitive to process conditions such as pH with respect to its oxidative a chemical stability, and such changes can significantly alter the reactivity of ozone with respect to the lignocellulosic materials. Since around the turn of the century, when the delignifying capabilities of ozone were first recognized, the has been substantial and continuous work by numerous persons the field to develop a commercially suitable method using ozo in the bleaching of lignocellulosic materials. Furthermore, numerous articles and patents have been issued in this area an there have been reports of attempts at conducting ozone bleaching on a non-commercial pilot scale basis. For example, U.S. Pat. 2,466,633 to Brabender et al., describes a bleaching process wherein ozone is passed through a pulp having a moisture content (adjusted to an oven dry consistency) of between 25 and 55 per cent and a pH adjusted to the range of 4 to 7. Other non-chlorine bleach sequences are described by S. Rothenberg, D. Robinson & D. Johnsonbaugh, "Bleaching of Oxygen Pulps with Ozone", Tappi, 182-185 (1975) - Z, ZEZ, ZP and ZP_(P -peroxyacetic acid); and N. Soteland, "Bleaching of Chemical Pulps With Oxygen and Ozone", Pulp and Paper Magazine of Canada; T153-58 (1974) - OZEP, OP and ZP. Also, U.S. Pat. No. 4,196,043 to Singh discloses a multi-stage bleaching process which also attempts to eliminate the use of chlorine compounds, and includes examples specifically directed to hardwoods. It is well known to those skilled in the art that hardwoods are easier to bleach than most softwoods. This process is characterized by from one to three ozone bleaching stages and a final treatment with alkaline hydrogen peroxide, each stage being separated by an alkaline extraction. One such sequence may be described in t common shorthand nomenclature of the paper industry as ZEZEP. In accordance with this process, the effluent from each treatment stage may be collected and recycled for use in bleaching operations, preferably at an earlier stage than tha from which it was obtained. This patent also provides a so- called countercurrent effluent flow. Despite all of the research conducted in this area, no commercially feasible process for the manufacture of ozone bleached lignocellulosic pulps, especially southern softwood, has heretofore been disclosed, and numerous failures have bee reported. The present invention provides novel combinations o pulping and bleaching steps which overcome the problems encountered in the prior art as discussed herein and which essentially eliminate the discharge of chlorinated organics a minimizes color and BOD releases to produce a high grade bleached pulp in a commercially feasible manner. Summary of the Invention Accordingly, it is an object of the present inventi to provide a multi-stage process for delignifying and bleachi lignocellulosic pulp without the use of elemental chlorine bleaching agents to substantially reduce or eliminate polluti of the environment while optimizing the physical properties o the pulp in an energy efficient, cost effective process. The present invention can work on virtually all wood species, including the difficult-to-bleach southern U.S. softwoods. The process of the present invention is composed of three or more steps with a number of possible variations with and between the steps. These steps can be described as follows: A first step involves delignification of wood chips into a lignocellulosic pulp, using any one of several chemica pulping processes, followed by a washing removal of most of t dissolved organics and cooking chemicals for recycle and recovery. Usually included is a screening of the pulp to remove bundles of fibers that have not been separated in pulping. This delignification step is conducted so that, for southern U.S. softwood, for example, pulp with a K No. in the range of about 20-24 (target of 21) , a cupriethylenediamine ("CED") viscosity in the range of about 21-28, and a GE brightness in the range of about 15-25 is typically obtained. For southern U.S. hardwood, pulp with a K No. in the range of about 10-14 (target 12.5) and a CED viscosity of about 21-28 typically obtained. Among, but not limited to, the effective embodiments of this first step are: a. Kraft pulping using either a continuous or batc digestion stage; b. Continuous digestion kraft pulping with extende delignification using staged alkali addition an countercurrent final cooking; c. Batch digestion kraft pulping with extended delignification using rapid liquor displacement and cold blowing techniques; or d. Kraft-AQ pulping to achieve extended delignification using either a continuous or batch digestion stage. The extended delignification techniques discussed in (b) and (c) above, may include, for example, the Kamyr MCC, th Beloit RDH and Sunds Cold Blow Cooking techniques described in the background portion of this specification. Depending upon the type of lignocellulosic material used, the soda and sulfit processes mentioned above may be used. second step of the process includes an oxygen delignification treatment to further remove lignin without an accompanying significant loss in cellulosic fiber strength. This would include a washing removal of the dissolved organics and alkali for recycle and recovery. Pulp screening is also performed at times after oxygen delignification. During the oxygen delignification step, the K No. of the increased consistency pulp is decreased by at least about 45% (for 0) to at least about 60% (for 0 ) without significantly damaging the cellulose component of the pulp. Also, the ratio of K No. to viscosity of the pulp is typically decreased by at least 25%. For the softwood pulp described above using 0 , a K No. of about 7 to 10 and a viscosity of above about 13 is _. mm easily achieved. For hardwood pulp, a K No. of about 5 to 8 and a viscosity above about 13 is achieved after the oxygen delignification step. Among, but not limited to, the possible embodiment to this step are: a. Conventional oxygen delignification, comprised an alkaline oxygen treatment of the pulp at either low, medium, or high pulp consistency ( or b. The preferred embodiment of an alkaline treatm at low to medium pulp consistency, i.e., less than about 10% by weight, followed by high pul consistency oxygen treatment, i.e,. greater th about 20% by weight (0 ) . For pulp end uses that do not require brightnesses above about 35% GEB (often referred to as semi-bleached pulp) it is possible to use pulp that has been processed only thro step 2 directly in the paper-making process. A third step of the process includes an acidic, gaseous ozone bleaching treatment (Z or Z ) under defined process parameters to provide a highly selective removal and bleaching of lignin with minimal degradation of cellulose. Among the process parameters are chelating agents for metal i control, pH control, pulp particle size control, pulp consistency, ozone concentration and gas/pulp contact control Prior to treatment with ozone, the chelating agent, for examp oxalic acid, diethylenetriamine pentaacetic acid ("DTPA") or ethylene diaminetetraacetic acid ("EDTA") may be added to the pulp to substantially bind with metal ions contained therein. Further, the pH of the pulp is preferably adjusted to a range of between about 1-4 prior to the third step. This may be accomplished by adding to the pulp a sufficient quantity of a acidic material. Advantageously, the consistency of the pulp is increased to between about 35-45% by weight and the partic size of the fiber floes are comminuted to a size of about 5 mm or less prior to the ozone delignification step. Included is dissolved organic washing stage for recycle and recovery. During the ozone step, the pulp is preferably maintained at ambient temperature or at least at a pulp temperature of less than about 120 β F. The ozone may be provided by an ozone-containing gas which may comprise, for example, oxygen or air. When an ozone/oxygen mixture is used, the ozone concentration is preferably between about 1 and 8 percent by volume, whereas for ozone/air mixtures, an ozone concentration of between about 1 and 4 percent by volume is acceptable. Within the ozone reactor vessel, the substantiall delignified pulp is advanced in a manner which subjects substantially all of the pulp particles to the ozone in a uniform fashion. It has been found that pulps with K Nos. greater tha about 10 after the second step are not suitable for this third step, because of the substantial amounts of ozone required to reduce the K No. to the desired level, which typically results in the properties of the pulp being adversely and deleteriousl affected by excessive ozone degradation of the cellulose fiber of the pulp. When pulp having a K No. of less than 10 is ozonated, a lesser concentration of ozone is used, with only a minimal amount of cellulose degradation occurring. The produc from this ozonation step for either the starting southern U.S. softwood or hardwood described above is a pulp having a K No. of less than about 5 and generally in the range of about 3 to (target of 3.5), a viscosity of above about 10, and a GE brightness of at least 50% (typically about 54% or higher for softwood and 63% or higher for hardwood) . Among, but not limited to, the effective embodiments for this step are: a. Treatment of the acidified pulp by countercurrent contact of ozone in an oxygen or air carrier gas; or b. Treatment of the acidified pulp by cocurrent contact of ozone in an oxygen or air carrier gas. An additional bleaching step may then be used to bring the pulp to a desired fully bleached state, i.e., one having GE brightness levels of about 70 to 95% using any numb of possible, well recognized bleaching and extraction processes. Among, but not limited to, the effective embodiments are: a. A conventional extraction stage with washing followed by a peroxide stage with washing; (i.e., EP) ; b. Conventional alkali extraction and washing stages followed by a conventional chlorine dioxide stage with washing (i.e., ED) ; c. A conventional alkali extraction and washing stage followed by a conventional chlorine dioxide stage with washing, followed by a repe of the extraction and chlorine dioxide stages (i.e., EDED) ; or d. An extraction stage, augmented with either oxygen or oxygen and peroxide, followed by a conventional chlorine dioxide stage: i.e., (E Q or (E )D. The extraction stage may comprise, in a further embodiment, combining the substantially delignified pulp with an effective amount of an alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to solubilize a substantial portion of any lignin which remains in the pulp. Thereafter, a portion of t aqueous alkaline solution may be extracted to remove substantially all of the solubilized lignin therefrom. Following the extraction stage, the substantially delignified pulp may be treated in the additional bleaching step to raise the GE brightness of the resultant pulp to at least about 70%. Preferred brightening agents include chlorin dioxide or a peroxide. The (Eo)D, (Eo )D or EDED embodiments will achieve the highest brightness levels. For the ED embodiment, the chlorine dioxide stage filtrate cannot, without treatment, be recycled for chemical recovery because of the presence of the inorganic chlorides. Since this is the only required sewered filtrate from the process, however, dramatic reductions in effluent volume, color, COD, BOD, and chlorinated organics ar achieved. Color of less than 2 pounds per ton, B0D 5 of less than 2 pounds per ton and total organic chloride (TOCl) of les than 2 and preferably less than 0.8 can be achieved. It is also possible to treat the chlorine dioxide stage filtrate wi a membrane filtration process which will allow essentially complete recycle. In the EP embodiment, no chlorinated materials are formed in the bleaching process and virtually a the liquid filtrates can be recycled and recovered, producing an almost effluent-free process. Brief Description of the Drawings FIG. 1 is a block flow diagram of the preferred methods of this invention wherein a solid line represents pul flow and a broken line represents effluent flow; FIG. 2 is a schematic representation of a preferred method of the invention; FIG. 3 is a cross-sectional drawing of a portion of an ozonation apparatus shown in Fig. 2, taken along line 3—3 FIG. 3A is a cross-sectional drawing of a portion o a preferred ozonation apparatus shown in Fig. 2, taken along line 3—3; and FIG. 4 is a comparison of the recycle and waste streams for a variety of pulp treatment processes. Detailed Description of the Invention The present invention relates to novel methods for delignifying and bleaching pulp while minimizing the degree o attack upon the cellulosic portion of the wood, thus forming product having acceptable strength properties for the manufacture of paper and various paper products. For convenience in understanding the improvement over the prior a offered with the use of the presently disclosed delignificati and bleaching process, provided below are the definitions of several parameters involved in the various stages in any delignification/bleaching process. A. General Definitions Throughout this specification, the following definitions will be used: "Consistency" is defined as the amount of pulp fibe in a slurry, expressed as a percentage of the total weight of the oven dry fiber and water. It is sometimes also referred as pulp concentration. The consistency of a pulp will depend upon operation of and the type of dewatering equipment used. The following definitions are based on those found in Rydholm Pulping Processes, Interscience Publishers, 1965, pages 862-8 and TAPPI Monograph No. 27, The Bleaching of Pulp, Rapson, Ed The Technical Association of Pulp and Paper Industry, 1963, pages 186-187. "Low consistency" includes ranges up to 6%, usually between 3 and 5%. It is a suspension that is pumpable by an ordinary centrifugal pump and is obtainable using deckers and filters without press rolls. "Medium consistency" is between about 6 and 20%. Fifteen percent is a dividing point within the medium- consistency range. Below 15% the consistency can be obtained by filters. This is the consistency of the pulp mat leaving vacuum drum filter in the brownstock washing system and the bleaching system. The consistency of a slurry from a washer, either a brownstock washer or a bleaching stage washer, is 9- 15%. Above about 15%, press rolls are needed for dewatering. Rydholm states that the usual range for medium consistency is 5 10-18%, while Rapson states it is 9-15%. The slurry is pumpable by special machinery even though it is still a coherent liquid phase at higher temperatures and under some compression. "High consistency" is above about 20% up to about 10 50%. Rydholm states that the usual range is 25-35% and Rapson states that the range is from 20-35%. These consistencies are obtainable only by the use of presses. The liquid phase is completely absorbed by the fibers, and the pulp can be pumped only very short distances. 15 Further, in this specification "pulping" is used in its conventional sense to refer to a digestion of lignocellulosic material to form brownstock. Pulping would include, for example, Kraft, the Kraft-AQ process and forms of extended delignification. 20 The term "modified Kraft process" is used herein to include extended delignification and all other modified Kraft processes with the exception of the Kraft-AQ process, since this process has achieved a special status and acceptance in the art and is separately known by that name. Also, the oxyge 25 delignification step following completion of pulping will not be considered as an extended delignification; rather, we have chosen to call it a first step of a delignification process fo bleaching or brightening the pulp. Further, there are two principal types of 30 measurements to determine the completeness of the pulping or bleaching process, i.e., the "degree of delignification" and the "brightness" of the pulp. The degree of delignification normally used in connection with the pulping process and the early bleaching stages. It tends to be less precise when onl 35 small amounts of lignin are present in the pulp, i.e., in the later bleaching stages. The brightness factor is normally us in connection with the bleaching process because it tends to more precise when the pulp is lightly colored and its reflectivity is high. There are many methods of measuring the degree of delignification but most are variations of the permanganate test. The normal permanganate test provides a permanganate o "K No." which is the number of cubic centimeters of tenth normal potassium permanganate solution consumed by one gram o oven dried pulp under specified conditions. It is determined by TAPPI Standard Test T-214. There are also a number of methods of measuring pul brightness. This parameter is usually a measure of reflectivity and its value is expressed as a percent of some scale. A standard method is GE brightness which is expressed as a percentage of a maximum GE brightness as determined by TAPPI Standard Method TPD-103. Moreover, where appropriate, the letter codes described in the Background Art section will be utilized to designate the various stages of pulp treatment throughout thi Detailed Description of the Invention. B. The Process Steps of the Invention The values (i.e., K No., viscosity and GE brightnes obtained by use of the present pulping, delignification and bleaching process, as set forth below, demonstrate the abilit of this process to enhance the degree of lignin removal from the pulp while minimizing the resultant degradation of the cellulose. After the oxygen delignification step, and prior brightening, the pulp has been partially delignified to a K N of about 5 to 10, preferably between about 7 to 10 for U.S. softwoods and about 5 to 7 for U.S. hardwoods. This partiall delignified pulp has a viscosity of above about 10, generally more than 13 and preferably, at least 14 (for softwood pulp) 15 (for hardwood pulp) . This partially delignified material thus has good strength and suitable viscosity so that it can withstand the effects of ozone. The partially delignified pul is subjected to ozone to further delignify the pulp, thus reducing the K No. of the pulp to about 3 to 4 for both softwoods and hardwoods while increasing the GE brightness of the pulp to at least about 50-70%. For softwood pulp, a GE brightness of about 54% or higher is typically achieved, while for hardwood pulp, values of about 63% or more are attained. Thereafter, the brightness of the pulp is further increased by an alkali extraction and an additional bleaching step using chlorine dioxide or peroxide. For convenience in understanding the present invention therefore. Fig. 1 sets forth, in schematic form, the various stages utilized in pulping, delignifying and brightening a pulp according to the invention. As illustrated in Fig. 1, the invention comprises a multi-stage process including the steps of: (a) pulping the lignocellulosic material whereby th pulping chemicals may be recovered and reused i a manner well-known in the art; (b) washing the pulp to remove chemical residues from the pulping liquor together with residual lignin and usually including a screening of the pulp to remove fiber bundles that have not bee separated during pulping; (c) alkaline oxygen delignification (i.e., 0 or 0 ) of the pulp; (d) washing the partially delignified pulp obtaine in step (c) above to remove dissolved organics from the oxygen treatment; optionally, screeni may be done at this point, while also recyclin at least a portion of the effluent from this step to a previous step; (e) chelation and acidification of the pulp to bin metal ions and to adjust the pH to a preferred level; (f) contacting the pulp with ozone (i.e., Z or Z ) to further delignify and to partially bleach this material; (g) washing the ozonated pulp, while recycling at least a portion of the effluent from this step to a previous step; (h) caustic extraction to remove residual lignin; (i) washing the extracted pulp while recycling at least a portion of the effluent to a previous step; (j) adding a second bleaching agent (i.e., D or P brighten and bleach the pulp) ; (k) washing the bleached pulp to obtain a bleached product having a GE brightness of about 70-90%; and (1) recycling at least a portion of the effluent from the P bleaching stage to a previous step; or sewering the effluent from the D bleaching stage or, after appropriate treatment, recyclin this effluent to a previous step. 1. Pulping The first stage in the method of the present invention wherein procedures can be utilized which improve the amount of lignin removed from the lignocellulosic material while minimizing the amount of degradation of the cellulose, i in the pulping step. The particular pulping process used in the method of the invention is, to a large extent, dependent o the type of lignocellulosic materials and, more particularly, the type of wood which is used as a starting material. Moreover, as illustrated in Fig. 1, the pulping liquor used in chemical pulping techniques may be recovered and reused in a manner well-known in the art. This step is typically followed by washing to remove most of the dissolved organics and cookin chemicals for recycle and recovery, as well as a screening stage in which the pulp is passed through a screening apparatu to remove bundles of fibers that have not been separated in pulping. The Kraft process is generally acceptable for use with all woods as compared to the other noted processes, as th final pulps obtained from the Kraft process have acceptable physical properties, although the brownstock pulp is also darker in color. Depending upon the lignocellulosic starting material the results obtained with conventional Kraft processes may be enhanced by the use of extended delignification techniques or the Kraft-AQ process. Moreover, these techniques are preferre for obtaining the greatest degree of reduction in K No. of the pulp without deleteriously affecting the strength and viscosit properties of the pulp. When using the Kraft-AQ technique, the amount of anthraquinone in the cooking liquor should be an amount of at least about 0.01% by weight, based on the oven dried weight of the wood to be pulped, with amounts of from about 0.02 to abou 0.1% generally being preferred. The inclusion of anthraquinon in the Kraft pulping process contributes significantly to the removal of the lignin without adversely affecting the desired strength characteristics of the remaining cellulose. Also, th additional cost for the anthraquinone is partially offset by the savings in cost of chemicals in the subsequent Z , E and D or P steps. Alternatively, or perhaps even additively to Kraft- AQ, is the use of techniques for extended delignification such as the Kamyr MCC, Beloit RDH and Sunds Cold Blow Methods for batch digesters. These techniques also offer the ability to _ _ remove more of the lignin during pulping without adversely affecting the desired strength characteristics of the remaini cellulose. 2. Oxygen Delignification The next step in the method of the present inventio concerns the portion of the bleaching process which primarily involves removal of the residual lignin from the brownstock pulp being processed. In the method of this invention, this stage comprises an oxygen delignification step. The solid materials removed in this stage are oxygenated materials whic can, like the black liquor, be collected, concentrated, and then incinerated in an environmentally safe manner in a conventional recovery boiler. At least a portion of the liqu phase is recycled as illustrated in Fig. 1. It has been found that the oxygen delignification step can be conducted in the manner which allows for the removal of increased percentages of the remaining lignin in t brownstock pulp without causing an unacceptable corresponding decrease in the viscosity of the pulp. Broadly, the process which has been identified is practiced by treating the brownstock pulp from the pulping process at low to medium consistency, as described below, with the required amount of alkali necessary for the oxygen delignification step so as to ensure uniform application of the alkali, and thereafter raising the consistency and delignifying at high consistencie Although high consistency delignification is preferred, low o medium consistency oxygen delignification techniques may be utilized in place of high consistency delignification. The high consistency oxygen delignification step is preferably carried out in the presence of an aqueous alkaline solution at a pulp consistency of from about 25% to about 35%, and even more preferably, at about 27%. This improved proces (O ) allows for the removal of at least 60% of the residual lignin from the brownstock pulp, compared to the 45-50% removable with conventional oxygen delignification steps, without the heretofore expected undesirable decrease in the relative viscosity. Because of the unique process capabilitie of this modified process, it clearly constitutes the preferred oxygen process for use in the method of this invention. The treatment step of the modified oxygen process (0 ) comprises substantially uniformly combining wood pulp, preferably Kraft brownstock pulp, with an aqueous alkaline solution while maintaining the consistency of the pulp at less than about 10% and preferably less than about 5% by weight. The aqueous alkaline solution is preferably present in an amount sufficient to provide from about 0.5% to about 4% activ alkali by weight after thickening based upon the oven dry pulp weight of the brownstock pulp, and even more preferably about 2.5% active alkali by weight after thickening based upon the oven dry weight of the brownstock pulp. This step uniformly distributes the aqueous alkaline solution throughout the low consistency brownstock and ensures that substantially all the brownstock fibers are exposed to a uniform application of alkaline solution. Surprisingly, the brownstock pulp treated in this manner is not substantially delignified in the treatment step, but it is more effectively delignified in the subsequent high consistency oxygen delignification step than brownstock that is treated with alkaline solutions at high consistency according to the metho conventionally employed. The localized inhomogeneities in th distribution of alkali in conventional high consistency pulp are avoided, thus eliminating attendant non-uniform oxygen delignification. This homogeneous distribution step thus preferably comprises uniformly combining the pulp with an aqueous alkaline solution for at least about 1 minute and preferably no more than about 15 minutes. It is believed that treatment times of less than about 1 minute will not generally provide sufficient time to attain substantially uniform distribution whereas treatment times in excess of about 15 minutes are no expected to produce substantial further benefit. Moreover, the preferred alkaline treatment of pulp according to the present invention may be carried out over a wide range of temperature conditions. According to a preferred practice, the treatment step is carried out at a temperature of from about room temperature to about 150°F, with temperatures ranging from about 90°F to about 150°F being even more preferred. Atmospheric pressure or elevated pressure may be employed. The treatment step is completed when the aqueous alkaline solution is substantially uniforml distributed throughout the low consistency pulp. The amount aqueous alkaline solution present in the treatment step can vary greatly according to the particular process parameters the delignification reaction. The amount of the alkaline solution effective for the purpose of the present invention will depend primarily upon the extent of delignification desired in the oxygen bleaching step and the strength of the particular solution being used. The aqueous alkaline soluti preferably used comprise a sodium hydroxide solution having concentration of from about 20 to about 120 g/1. This solut is mixed with the low consistency pulp, so that the overall mixture has a concentration of alkaline material of between about 6.5 and 13.5 g/1, and preferably around 9 g/1. Thus, f a 5 to 15 minute treatment of a 3 to 5 percent consistency pu at temperatures between 120 to 150°F at these concentrations alkaline material, a uniform distribution of such alkaline material is obtained throughout the pulp. According to a preferred embodiment of the present invention, an aqueous sodium hydroxide solution is added to t low consistency pulp in an amount sufficient to provide from about 15% to about 30% by weight of sodium hydroxide based on dry pulp weight. Other alkaline sources having an equivalent sodium hydroxide content, such as oxidized white liquor from the conventional Kraft recovery and regeneration cycle, may also be employed. Following the low consistency caustic treatment step described above, the consistency of the treated pulp is increased to greater than about 20%, preferably from about 25% to about 35%. Several methods are available and well known in the art for increasing the consistency of the pulp, such as pressing the wood pulp to remove liquid therefrom. Thereafter, oxygen delignification is conducted on the high consistency pulp. Methods are available and well known in the art for dissolving gaseous oxygen into the liquid phase of high consistency pulp to affect delignification thereof. It is contemplated that any of these well known methods are adaptable for use according to the present invention. It is preferred, however, that oxygen delignification according to the present invention comprise introducing gaseous oxygen at about 80 to about 100 psig into the liquid phase of the high consistency pulp while maintaining the temperature of the pulp between about 90 β C and 130°C. The average contact time between the high consistency pulp and the gaseous oxygen is preferably from about 20 minutes to about 60 minutes. By following the preferred process according to the present invention, it is possible to obtain a reduction in K No. for the pulp after the oxygen delignification step of at least about 60% with essentially no damage to the cellulose portion of the pulp. By comparison, conventional oxygen delignification can only achieve reductions in K No. of about 50% before degradation of cellulose occurs. Thus, the present preferred process unexpectedly provides an increase of at least 20% in delignification compared to prior art delignification processes: i.e., from 50% to at least about 60% reduction of the K No. for the incoming pulp. Reductions of 70% and more can even be achieved with minimal cellulose degradation. The avoidance of deterioration of the cellulose component of the pulp is evident by the minimal change in viscosity of pulp which is treated in accordance with the present invention. Upon entering the oxygen delignification step, pulp K Nos. for the particular pulp range from about 10-26 depending upon the type of wood (e.g., for Kraft pulping, about 10-14, target 12.5 for hardwood and about 20-24, target 21, for softwood) , while after oxygen delignifi¬ cation, the K No. is generally in the range of about 5-10. A processing scheme for carrying out the method of the present invention is depicted in schematic form in Fig. 2. The steps depicted therein represent a preferred operating system that tends to maximize certain benefits of the present invention. Wood chips 2 are introduced into a digester 4 where they are cooked in a liquor such as a liquor of sodium hydroxide and sodium sulfide. The cooking unit 4 produces a Kraft brownstock 8 and a black liquor 6 containing the reaction products of lignin solubilization. The brownstock is treated in washing units comprising, preferably, blow tank 10 and washer 12 where residual liquor contained in the pulp is removed. Many methods are available and well known in the art for washing brownstock, such as diffusion washing, rotary pressure washing, horizontal belt filtering, and dilution/extraction. These methods are all within the scope of the present invention. Also, screening of brownstock is often done either before or after the washing steps in order to remove larger portions of undefibered wood for special processing. The washed brownstock is introduced into a treatment unit 14 where it is treated with an alkaline solution and maintained at a consistency of less than about 10% and preferably less than about 5%. The process of the present invention preferably includes means for introducing make-up caustic 16 into the treatment stage to maintain the desired caustic application level. The treated pulp 18 is forwarded to a thickening unit 20 where the consistency of the pulp is increased, by pressing for example, to at least about 20% by weight and preferably to about 25% to about 35%. The liquid 22 removed from the thickening unit 20 is preferably returned to washing unit 12 for further use. The high consistency "pressed" brownstock 24 produced in the thickening unit 20 is forwarded to the oxygen delignification reactor vessel 26 where it is contacted with gaseous oxygen 28. The delignified brownstock 30 is preferably forwarded through blow tank 32 and then to a second washing unit 34 wherein the pulp is washed with water to remove any dissolved organics and to produce high quality, low color pulp 36. At least a portion of the effluent 38 from this washing step is preferably returned to washing unit 12 for use therein. The effluent 13 from washing unit 12 may be recycled alone or optionally with all or a portion of effluent 38, to either the blow tank 10 or ultimately black liquor line 6. Additionally, the partially delignified pulp obtained after oxygen delignification may be screened to remove fiber bundles from the pulp that have not separated for further treatment such as mechanical grinding. From here, pulp 36 could be sent to subsequent bleaching stages to produce a fully bleached product. In a particularly preferred method of the present invention as shown in Fig. 2, in order to successfully utiliz ozone bleaching, Kraft pulping of the wood may be carried out, followed by the modified low-consistency alkali treatment/hig consistency oxygen delignification procedure (0 ) described above. For softwoods, as noted above, this combination resul in a pulp with a K No. of about 8 to 10, preferably 9, and a viscosity of greater than about 13 to 14. Alternatively, it possible to subject the wood to Kraft AQ pulping followed by conventional oxygen delignification step (i.e., 0, high consistency alkaline treatment followed by high consistency oxygen delignification) to achieve a pulp having similar characteristics. In place of Kraft AQ pulping, it is also possible to use extended delignification processes, followed a standard oxygen delignification step to achieve pulp with t desired properties. Also useful, although less preferred due to increased costs or process steps, is the combination of Kraft pulping with extended delignification techniques such a Kamyr MCC, Beloit RDH or the Sunds Cold Blow Cooking process, as described in the Background Art section of this specification, followed by conventional oxygen delignificatio Any of a wide variety of pulping and oxygen delignification steps can be used in combination as long as they achieve the above K No. and viscosity values prior to th ozone step. Conventional Kraft pulping followed by conventional oxygen delignification is generally not acceptable in this invention, except for certain hardwoods such as aspen which a relatively easy to delignify and bleach, since for a given wo species the combination of these conventional techniques normally requires the use of the greatest amount of ozone in the ozonation step with concomitant greater cellulose degradation. By use of the present invention, the ozone consumption may be reduced by using a number of alternate routes, such as standard kraft cooking followed by a modified oxygen delignification step (0 ) , or modified kraft pulping with extended delignification (such as Kamyr MCC, Beloit RDH Sunds Cold Blow) followed by a conventional oxygen delignification step (O) , or by Kraft AQ cooking followed by conventional oxygen delignification step (O) as discussed above. An even greater reduction in ozone consumption will b achieved both with the use of modified Kraft pulping with extended delignification (Kamyr MCC, Beloit RDH or Sunds Cold Blow) followed by a modified oxygen delignification step (O ) , or alternately when a Kraft AQ cooking process with extended delignification (Kamyr MCC, Beloit RDH or Sunds Cold Blow) is followed by a conventional oxygen delignification step (0) . Using all of these techniques together in one process, i.e., Kraft AQ cooking modified by extended delignification (Kamyr MCC, Beloit RDH or Sunds Cold Blow) , followed by a modified oxygen delignification step (0 ) , reduces the amount of ozone consumed even further. Reduction in the amount of ozone consumed generally permits the viscosity of the pulp to be maintained at acceptable levels. The advantages of using the modified high consistenc oxygen delignification bleaching step (0 ) described above are clearly illustrated by comparison of the K Nos. and viscositie obtained using southern softwoods to related processes under otherwise substantially identical process conditions. Using a conventional Kraft pulping procedure and conventional high consistency oxygen delignification bleaching, the resulting pulps obtained will typically have a K No. of about 12 to 14 and a viscosity of about 15. This K No. is too large to permi later delignification using the ozone stage of the present invention. However, the use of conventional Kraft pulping wit the modified high consistency oxygen bleaching surprisingly results in a pulp having a K No. of less than about 9, while the viscosity of the pulp is above about 12 to 14. This preferred pulp K No. permits utilization of the ozone delignification bleaching stage of the invention. 3 _ The Ozone Step The next step in the method of this invention is ozone delignification and bleaching of the oxygen-delignified brownstock pulp. This ozonation takes place in an ozone reactor which is described below in detail and illustrated in Figs. 2, 3 and 3A. Prior to treatment of the pulp with the ozone, the pulp is conditioned so as to ensure the most effective selective delignification of the pulp and to minimiz the chemical attack of the ozone on the cellulose. The incoming pulp 36 is directed into a mixing chest 40, where it is diluted to a low consistency. An acid 42 such as sulfuric acid, formic acid, acetic acid or the like, is added to the l consistency pulp to decrease the pH of the pulp in mixing che 40 to the range of about 1 to 4 and preferably between 2 and 5 The pH is adjusted as described above since it is known that the relative effectiveness of ozone bleaching of pulps is dependent upon the pH of the pulp mixture. Lower pH values d not appear to have any beneficial effect on the further processing of the pulp, whereas increasing the pH to above in about 4 to 5 causes a decrease in viscosity and an increase i ozone consumption. The acidified pulp is treated with chelating agent to complex any metals or metal salts which may be present in the pulp. This chelating step is used to render such metals 15 non-reactive or harmless in the ozone reactor so that they wi not cause breakdown of the ozone, thus decreasing the efficiency of the lignin removal and also reducing the viscosity of the cellulose. Chelating agents are known per se and include, for 0 example, polycarboxylate and polycarbόxylate derivatives such as the di-, tri-, and tetra-carboxylates, amides, and the lik Preferred chelating agents for this ozone treatment, for reasons of cost and efficiency, include DTPA, EDTA and oxalic acid. Amounts of these chelating agents ranging from about 5 0.1% to about 0.2% by weight of oven dry pulp are generally effective, although additional amounts may be needed when hig metal ion concentrations are present. The effectiveness of the ozone bleaching process is controlled by a number of inter-related process parameters, 0 including the pH level and the amount of metal salts in the pulp as discussed above- Another very important parameter is the consistency of the lp during the ozone bleaching proces The pulp which is to be bleached must contain sufficient wate so that the water exists as a continuous phase through the 5 individual fibers, that is, the fiber should be sufficiently saturated with water. The water in the fiber allows the transfer of the ozone from the gaseous ozone atmosphere to bot treat the outer surface of the fibers, and possibly more importantly, for the ozone to be transferred via the water phase to the less accessible interior portion of the individua fibers and thereby provide more complete removal of lignin fro the fibers. The consistency, on the other hand, should not be so low that the ozone is diluted and tends to chemically break down rather than bleach the pulp. The preferred range of consistency, especially for southern U.S. softwood, has been found to be between about 28% and about 50%, with the optimum results being obtained at between about 38% and about 45%. Within the above ranges, preferred results are obtained as indicated by the relative amount of delignification, the relatively low amount of degradation of the cellulose, and the noticeable increase in the brightness of the treated pulps. The reaction temperature at which the ozone bleachin is conducted is likewise an important controlling factor in th process of the present invention. The ozone step can be effectively conducted at temperatures up to a certain critical temperature, at which the reaction commences to cause excessiv degradation of the cellulose. This critical temperature will vary significantly depending upon the particular type of wood employed to form the pulp and the history of the prior treatment of the pulp. The maximum temperature of the pulp fiber at which the reaction should be conducted should not exceed the temperature at which excessive degradation of the cellulose occurs, which with southern U.S. softwood is a maximum of about 120 β F - 150 β F. The ozone gas which is used in the bleaching process may be employed as a mixture of ozone with oxygen and/or an inert gas, or can be employed as a mixture of ozone with air. The amount of ozone which can satisfactorily be incorporated into the treatment gases is limited by the stability of the ozone in the gas mixture. Ozone gas mixtures which typically contain about 1-8% by weight of ozone in an ozone/oxygen mixture, or about 1-4% ozone in an ozone/air mixture, are suitable for use in this invention. The higher concentration of ozone in the ozone gas mixture allows for the use of relatively smaller size reactors and shorter reaction time to treat equivalent amounts of pulp, thereby lessening the capit cost required for the equipment. However, ozone gas mixtures containing lower amounts of ozone tend to be less expensive t produce and may reduce operating costs. A further controlling factor is the relative weight of the ozone used to bleach a given weight of the pulp. This amount is determined, at least in part, by the amount of lign which is to be removed during the ozone bleaching process, balanced against the relative amount of degradation of the cellulose which can be tolerated during ozone bleaching. In accordance with the preferred method of this invention, an amount of ozone is used which will react with about 50% to 70% of the lignin present in the pulp. The entire amount of ligni in the pulp is not removed in the ozone bleaching step as evidenced by the K No. of about 3 to 4 obtained after this step, because the absence of all lignin in the reaction zone would result in the ozone reacting excessively with the cellulose to substantially decrease the degree of polymerization of the cellulose. In the preferred method of this invention, the amount of ozone added, based on the oven dried weight of the pulp, typically is about from 0.2% to abou 1% to reach the lignin levels of a 3-4 K No. Higher amounts may be required if significant quantities of dissolved solids are present in the system. The time of the reaction used for the ozone bleachin step is determined by the desired rate of completion of the ozone bleaching reaction as indicated by complete or substantially complete consumption of the ozone which is utilized. This time will vary depending upon the concentratio of the ozone in the ozone gas mixture, with relatively more concentrated ozone mixtures reacting more quickly, and the relative amount of lignin which it is desired to remove. The time required is preferably less than two minutes, but the procedure may take substantially longer depending on other reaction parameters. An important feature of the invention is that the pulp is bleached uniformly. This feature is obtained in part, by comminution of the pulp into discrete floe particles of a size which is of a sufficiently small diameter and of a sufficiently low bulk density so that the ozone gas mixture will completely penetrate a majority of the fiber floes, i.e., which comprise agglomerations of fibers. During comminution i is not feasible to completely separate the pulp fibers into distinct fibers. In general, the floe particles resulting fro comminution have a relatively compacted central core surrounde by a plurality of outwardly extending fibers. For purposes of this invention, the floe particle size is determined by measuring what was determined to be the smallest diameter of this relatively unfluffed central core. Bleaching uniformity is to a large extent also dependent on certain of the other process parameters, but it has been found that if the floe particle size is limited to a maximum of 5mm, and preferably even less —for example, 3mm— that uniform treatment of a substantial majority of these particles can readily be achieved, as evidenced by observation of an insignificant number of darker underbleached floe centers. Where the floe particle size was greater than about 5mm, bleaching was non-uniform, as evidenced by a majority of darker unbleached floe centers. Therefore it is important to achieve sufficient comminution so that a majority of the floes measure below an average of about 5 mm for uniform ozone treatment thereof. A still further important process parameter is that during the ozone bleaching process the particles to be bleach should be exposed to the ozone bleaching mixture by mixing so as to allow access of the ozone gas mixture to all surfaces the floes and equal access of the ozone gas mixture to all floes. The mixing of the pulp in the ozone gas mixture give superior results with regard to uniformity as compared to th results obtained with a static bed of floes wherein some of floes are isolated from the ozone gas relative to other floe and thereby bleached less than other floes. The movement of the floes so as to expose them to ozone gas mixture causes uniform treatment of the floes with respect to each other. This treatment results in the desire amount of lignin being removed uniformly from the pulp witho excessive deterioration of the cellulose in the fibers which comprise the floes. The control of the ozone treatment in accordance with this invention by use of a controlled particl size and by turbulent movement during ozone treatment has bee found to result in a final pulp typically having less than about a 5% variation in GE brightness, K No. and viscosity. comparison, if the treatment is non-uniform, as typically occurs in static bed reactors (that is, reactors wherein the particles are not agitated during ozone treatment) , some portions of the bed are substantially over-bleached while oth portions remain relatively unreacted because the flow of the ozone gas mixture through the static bed reactor is not uniform. Treating pulp at high consistencies with ozone without paying particular attention to the comminution of the pulp fibers or to the proper contact between the individual fibers and the reactant gas stream invariably results in a non-uniform ozone bleaching of the fibers. The present application designates such a non-uniform ozone treatment wit the letter "Z". The use of a modified ozone technique according to the present invention, as discussed above, in which the fibers are comminuted to a size of about 5 mm or le and are properly and uniformly contacted with the ozone gas stream, has been designated herein as "Z ". Pulp exiting the ozone reactor has a GE brightness o about at least 50 percent and generally around 50 to 70 percent, with hardwoods usually being above about 55 percent. The pulp (for hardwoods or softwoods) also has a K No. of 5 between about 3 and 4 (target of 3.5), which is entirely satisfactory for pulp at this stage of the process. An apparatus which is especially suitable for ozone bleaching in accordance with the present invention is illustrated in Figs. 2, 3 and 3A. As described above, washed Q pulp 36 is directed to mixing chest 40 where it is treated wit an acid 42 and a chelating agent 44. The acidified, chelated low-consistency pulp 46 is introduced into thickening unit 48 for removing excess liquid 50 from the pulp, such as a twin roll press wherein the consistency of the pulp is raised to th 5 desired level. At least a portion of this excess liquid 50 ma be recycled to mixing chest 40, with a remaining portion being directed to blow tank 32. The resulting high consistency pulp 52 is then passed through screw feeder 54 which acts as a gas seal for the ozone gas and thereafter through a comminuting unit 56, such as a fluffer, where the pulp is comminuted to pulp fiber floes 60 of a pre-determined size which, as noted above, should measure about 5 mm or less in size. The comminuted particles are then introduced into a dynamic ozone reaction chamber 58 which, as illustrated, is a conveyor 62 5 powered by motor 64. Conveyor 62 is specifically designed fo mixing and transporting the pulp particles 60 so as to allow the entire surface of the particles to become exposed to the ozone gas mixture 66 during movement of the pulp. As further shown in Fig. 2, pulp fiber floes 60 after treatment are 0 allowed to fall into dilution tank 68. Fig. 3 is a cross-sectional view through ozone reactor 58 illustrating the arrangement of the pulp particles 60 as they are carried through the reactor by conveyor 62. 35 Fig. 3A is a cross-sectional view of a preferred conveyor utilizing a paddle-like arrangement to move the comminuted particles through reaction chamber 58. The process in Fig. 2 shows the pulp being treated with ozone cocurrently with the ozone-gas mixture. Alternately, however the portion of the pulp which has been bleached to the greatest extent may initially be contacted wi the newly introduced ozone mixture containing the maximum amount of ozone by passing the ozone-containing gas in a direction counter-current to the flow of pulp 60. The pulp entering the reactor has the highest lignin content and initially contacts the exiting, nearly exhausted ozone mixtur thereby providing the optimum chance to consume virtually all of the ozone. This is an efficient method for stripping ozon from the ozone/oxygen or ozone/air mixture. When the ozone 66 is contacted with the pulp xa a coeurrent manner, as shown in Fig. 2, the remaining spent ozo gas 70 can be recovered from dilution tank 68. In tank 68, dilution water 72, which also serves as an ozone gas seal, is added to reduce the consistency of the pulp to a low level to facilitate movement of the bleached pulp 74 through the subsequent process steps. The spent ozone gas 70 from dilution tank 68 is directed to a carrier gas pretreatment stage 76 where a carri gas 78 of oxygen or air is added. This mixture 80 is directe to ozone generator 82 where the appropriate amount of ozone i generated to obtain the desired concentration. The proper ozone/air mixture 66 is then directed to ozone reactor 58 for delignification and bleaching of the pulp. After completion of the ozone bleaching step, the substantially delignified pulp 74 is again thoroughly washed washer 84 as shown in Fig. 2 and at least a portion of the water 86 which is recovered is recycled to washing unit 34 of the process, thereby producing major environmental benefits from the elimination of sewered liquid. The bleached low consistency pulp 74 after ozonatio will have a reduced amount of lignin, and therefore, a lower No. and an acceptable viscosity. The exact values for the K No. and the viscosity which are obtained are dependent upon t particular processing to which the pulp has been subjected. For example, a southern U.S. softwood pulp which is pulped wi a conventional Kraft method, initially delignified by modifie high consistency oxygen delignification (0 ) , and subsequentl further delignified with ozone, preferably by a modified uniform ozone treatment (Z ) , will typically have a K No. of about 3-4 and a viscosity of about 10. Southern U.S. softwoo pulp which is subjected to Kraft AQ pulping and then to modified high consistency oxygen bleaching (O ) and modified uniform ozone treatment (Z ) will typically have a K No. of about 2 and a viscosity of greater than about 12. The resulting pulp 74 will be noticeably brighter than the starting pulp. For example, southern softwood, afte the pulping process, has a GE brightness of about 15% to 25%; after the oxygen bleaching process, a GE brightness of about 25 % to 45%; and after the ozone bleaching process, a GE brightness of about 50% to 70%. 4. Alkaline Extraction The washed pulp 88 from the ozone stage is then combined with a sufficient amount of alkaline material 90 in • extraction vessel 92 to effect extraction. Thus, pulp 88 is subjected to an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to solubilize a substantial 0 portion of any lignin which remains in the pulp, in vessel 92 This extraction process also increases the brightness of the pulp, typically by about 2 GE brightness points. Thereafter, the alkali treated pulp 94 is directed to washing unit 96, th aqueous alkaline solution is washed from the pulp so as to 5 remove substantially all of the solubilized lignin from the pulp, thus forming a substantially lignin-free pulp. This st is well known to those skilled in the art and no further comment is deemed necessary here. The examples illustrate th preferred extraction parameters for this step of the process. At least a portion of the alkaline solution 98 which is recovered is recycled to washing unit 84. Again, major environmental benefits are achieved from the elimination of sewering of this solution. In some cases, particularly where higher final brightnesses are targeted, the extraction step can be augment by incorporating an oxygen treatment within the caustic extraction step (E ) . This alternative, also well known to those skilled in the art, requires no further comment here. 5. Additional Bleaching Stages For most paper-making purposes, a final brightness i the range of 50 to 65 is unsatisfactory. Accordingly, in ord to further raise the GE brightness to the more desirable rang of about 70 to 95%, the pulp is subjected to brightening bleaching, which is primarily intended to convert the chromophoric groups on the lignin remaining in the pulp into colorless state. After extracting and rewashing the pulp, the brightening bleaching of the ozone-bleached and extracted pul can be performed using a variety of materials. As illustrate in Fig. 2, the washed pulp 100 is combined with the chosen bleaching agent 102 in bleaching vessel 104. The preferred bleaching agent is chlorine dioxide or peroxide. After bleaching, the pulp 106 is washed with water 114 in washing unit 108 and the effluent is either recycled 110 or sewered 112. When recycled, at least a portion of wash water stream 110 is directed to washing unit 96. The resultant bleached pulp 116 may then be collected and used in a variety of applications. One of the principal materials which has heretofore been used, and which is generally highly effective, is chlorin dioxide (D) (see Fig. 1) . In accordance with the invention, a appropriate amount of chlorine dioxide enables high-strength pulps having a GE brightness value greater than about 80% to b obtained. Since the pulps entering the chlorine dioxide stage are relatively low in lignin, the chlorine dioxide brightening bleaching can be carried out in the presence of only from abou 0.25% to about 1% of chlorine dioxide based on the oven dry weight of the pulp. The chlorine dioxide which is utilized in the brightening process should preferably be prepared by a process which is free from elemental chlorine. Alternatively, however and less preferably, chlorine dioxide which does contain a minor amount of elemental chlorine can be used without any substantial increase in the relative amount of undesirable pollutants because of the relatively low amount of lignin present in the ozone-bleached pulp. The effluent from the final bleaching step of this invention when using chlorine dioxide is exceptionally low and can be discharged safely as shown in Fig. 2. If sewering of the effluent from the final chlorine dioxide bleaching step is unacceptable, the stream can, however, be further purified by being treated with a membrane filtration process such as reverse osmosis. This technique provides a clean filtrate that can be recycled back to previou bleaching stages for further use. This has the benefit of reducing fresh water usage. Moreover, the concentrated chloride streams that result from the membrane filtration are relatively low in volume. There may be some cases when extremely high pulp brightnesses are desired, for example, 92-95% GEB, where additional stages of bleaching may be required. An additiona extraction and chlorine dioxide treatment would be a common choice, thereby creating a 0 Z EDED bleach sequence. Instead of using chlorine dioxide for final brightening, the brightening bleaching may be conducted with hydrogen peroxide, as also shown in Fig. 1. This technique provides a completely chlorine-free bleaching cycle (such as 0,m.Z_mEP sequence) , wherein no chlorinated materials are forme in the bleaching process and the liquid extraction product c be readily recycled without the necessity for cumbersome filtration techniques. When utilizing peroxides as the bleaching agent, however, the K No. of the pulp from either softwood or hardwood should be reduced to a level of about 6 prior to the ozonation step in order to obtain, as a final product following the peroxide bleaching stage, a pulp of acceptable brightness, i.e., a GE Brightness of greater than about 80%, since peroxide is not as effective at bleaching as is chlorine dioxide. Where a completely chlorine/chlorine dioxide-free process is desired, however, peroxide provides acceptable results. Typical peroxide brightening agents and their use i this step are conventional, and one skilled in the art would know the appropriate concentration, types and use of such peroxide agents. Hydrogen peroxide is preferred. The washed, further brightened pulp has a GE brightness of between about 70 and 95%, and preferably betwee about 80 and 95%. Also, the physical properties of this pulp are commensurate with those obtainable by pulp produced by conventional CEDED or OC/DED processes. 6. Washing Effluent Recycle In any pulp process, filtrate management is an important factor in the overall economy or cost of operation the process. The water which is used in the process requires both access to a suitable source and treatment of the effluen prior to discharge. In an effort to reduce the water demand of the process, it is desirable to recycle as much of the effluent a possible. This practice cannot be used with processes utilizing chlorine or multiple steps of chlorine dioxide, sin the effluents produced by these processes contain large amoun of chlorides produced by the by-products of such chemicals. Thus, recycling these effluents causes a build-up of chloride which, in turn, causes either corrosion of processing equipme or the use of expensive materials of construction. In addition, such recycled effluents require substantial treatme before these effluents can be discharged from the mill, thus requiring further expenditures for equipment and treatment chemicals. As illustrated in Fig. 4, use of either the conventional CEDED process or the OC/DED technique results in significant disposal problem with regard to the effluents produced from the washing steps due to the high levels of chloride-containing compounds found therein. As noted above, these streams cannot be recycled, and are preferably treated before discharge into the environment. Recycling of effluent could be used to decrease the amount of water used, but then the process equipment may be subject to increased corrosion rates due to the increased chloride level in the recycled effluent. In contrast, however, use of the 0 Z ED process of the invention results in formation of only a minimal amount o chlorinated material in the wash water, which water can be safely discharged, i.e., sewered, within most environmental protection standards. Alternately, this effluent may be treated by reverse osmosis to provide an even cleaner filtrat that may be recycled to previous bleaching stages as shown fo further use without the build-up of chlorides. When a D bleaching stage is desired, steps may be taken to reduce the demand for chlorine dioxide. An E step may allow the pulp t achieve greater levels of brightness although additional expense is incurred by the use of additional sodium hydroxid and oxygen in this step. Also, there are known industry procedures for preparing chlorine dioxide whereby residual chlorine levels are minimized (e.g., the R8 process vs. the process) . These reduced chlorine level chemicals are prefer for use in the D stage to reduce the chloride levels of the wash water effluent. Instead of OmZmED, one may use the OmzmEP process the invention to obtain additional substantial advantages ov the prior art in that no chlorinated compounds whatsoever ar produced. This enables all of the effluent to be recycled without experiencing the problems of chloride build-up in th process wash water streams. Accordingly, the process of the present invention achieves substantial advantages with respect to reductions in effluent volume, color, COD, BOD and chlorinated organics. Moreover, since the effluent used in the washing steps contai significantly reduced chloride levels compared to prior art processes which utilize chlorine, the washing unit vents will not be carrying chlorinated organic compounds or gases which require treatment prior to discharge. EXAMPLES The scope of the invention is further described in connection with the following examples which are set forth for purposes of illustration only and which are not to be construed as limiting the scope of the invention in any manner. Unless otherwise indicated, all chemical percentages are calculated on the basis of the weight of oven dried (OD) fiber. Also, one skilled in the art would understand that the target brightness values do not need to be precisely achieved, as GEB values of plus or minus 2% from the target are acceptable. In all the examples having a D stage, except Example 11, an R-3 type of chlorine dioxide solution, known to contain a 6:1 ratio of dioxide to elemental chlorine, was used. EXAMPLE 1 (Comparative) Loblolly pine chips were lab batch cooked according to the conditions in Table I to produce a conventional kraft pulp. The resulting pulp had a K No. of 22.6 and a viscosity of 27.1 cps. The kraft pulp was then subjected to conventional oxygen treatment (Tables II and V) followed by bleaching to a final target brightness of 83 GEB using both a conventional OC/DED sequence (Table III) and an OZ ED bleaching sequence (Tables IV and V) . The ozone bleaching stage was run at 35% consistency with an ozone application of 0.61%. TABLE I LOBLOLLY PINE KRAFT PULPING CONDITIONS CONDITION/STEP PARAMETER PRESTEAM TIME (min.) 2.5 TIME TO TEMPERATURE - 175°C 1 hour TIME AT TEMPERATURE - 175°C 1 hour LIQUOR:WOOD ratio 4:1 SULFIDITY (%) 25.8 ACTIVE ALKALI (%) 17.4 % AA FROM BLACK LIQUOR FILLBACK 0.43 K NO. 22.6 VISCOSITY (cps) 27.1 TABLE II * both for alkali addition and oxygen delignification As shown in Table VI and VII below, OZ ED bleaching und these conditions produced a pulp having acceptable strength properties compared to an 83% GE target brightness OC/DED baseline pulp. Under these conditions, the OZ ED pulp had marginal viscosity of 9.7 cps. The strength properties were measured on an OZ ED pulp where the final D-stage applicatio was 2.5%. Target brightness was reached only with an excessive chlorine dioxide charge. The OZ E pulps response chlorine dioxide treatment shows that higher brightness can only be achieved by significantly increasing the ozone application, which then causes significant viscosity and strength loss of the pulp. TABLE VI PINE KRAFT OC/ 1DED AND KRAFT OZ m ED PROPERTIES COMPARISON OC/DED OZ ED CSF* TEAR BREAKING CSF* TEAR BREAKING FACTOR LENGTH FACTOR LENGTH * Canadian Standard Freeness TABLE VII PINE KRAFT OZmED BRIGHTNESS RESPONSE C10„ (%) 1.3 1.5 1.7 1.9 2.2 2.5 2.8 Bright¬ 48.0 61.3 76.1 . 79.4 81.0 81.8 83.9 83.9 ness (GEB %) EXAMPLE 2 A kraft/AQ brownstock was prepared in a laboratory batch digester from loblolly pine chips as described in Table VIII. The K No. of the resulting brownstock was 18.3 and the viscosity was 20.6 cps. The Kraft/AQ pulping conditions produced a pulp having a significantly lower lignin content than in Example 1 as evidenced by the K No. , without unacceptable deterioration of pulp strength as evidenced by the viscosity. _- _ _- TABLE VIII LOBLOLLY PINE KRAFT/AQ PULPING CONDITIONS CONDITION/STEP PARAMETER PRESTEAM TIME (min.) 2.5 TIME TO TEMPERATURE - 175°C 1 hour TIME AT TEMPERATURE - 175 β C 1 hour LIQUOR: OOD ratio 4:1 SULFIDITY (%) 25.3 ACTIVE ALKALI (%) 18.0 % AA FROM BLACK LIQUOR FILLBACK 0.43 AQ - % ON WOOD 0.025 K NO. 18.3 VISCOSITY 20.6 The Kraft/AQ brownstock was then subjected to further bleaching using the conventional OC/DED sequence and the OZ ED sequence as shown in Tables II, III, IV and V to a target brightness of 83% GEB. Use of the Kraft AQ pulping technology achieved the goal of producing a starting pulp with a low K No. , having acceptable viscosity properties, for the ozone bleaching sequence. The ozone bleaching stage was run at 35% consistency with an ozone application of 0.35% and 1.6% CIO, was used in the final D stage to reach target brightness. As shown in Tables IX and X below, the optical properties as measured by brightness response in the final chlorine dioxide stage were improved and strength properties were acceptable compared to the OC/DED baseline. _-_ -- EXAMPLE 3 (Comparative) A pine Kraft brownstock having a K No. of about 24 was pressed to a consistency of about 30-36% by weight to produ a high consistency mat. The mat of brownstock was sprayed with a 10% sodium hydroxide solution in an amount sufficien to produce approximately 2.5 weight percent sodium hydroxide based on pulp dry weight. Dilution water was added in an amount sufficient to adjust the brownstock mat to about 27% consistency. The high consistency brownstock mat was then subjected to oxygen delignification using the following conditions: 110°C, 30 minutes, 80 psig 0 2 . EXAMPLE 4 Pine Kraft brownstock of Example 3 was introduced into treatment vessel along with a sufficient volume of 10% NaOH solution to effect a 30% NaOH addition based on oven-dried pulp. Sufficient dilution water was added to obtain a brownstock consistency of about 3% by weight in the treatmen vessel. The brownstock and the aqueous sodium hydroxide solution were uniformly mixed at room temperature by a ribbo mixer for about 15 minutes. The treated brownstock was then pressed to a consistency of about 27% by weight. After pressing, the sodium hydroxide on the fiber equaled about 2.5% as in Example 3. The treated brownstock was then delignified according to the oxygen delignification procedur described in Example 3. A comparison is shown in Table XI. TABLE XI COMPARISON OF OXYGEN STAGE BLEACHING RESULTS ON PULPS PRODUCED BY EXAMPLES 3 AND 4 EXAMPLE 3(0) EXAMPLE 4(0 -.m- K No. 1 133 9 Viscosity (cps) 14.8 14.0 As can be seen from a comparison of Examples 3 and 4, a preferred method of the present invention of using a low consistency alkali addition followed by a high consistency oxygen treatment (O ) produced a bleached brownstock having greater delignification (lower K No.) than the prior art methods, without any substantial change in strength properties. As a result of the lower K No. pulp produced by this process, subsequent bleaching steps can be adjusted to accommodate the higher brightness, lower lignin containing pulp. Thus, the bleaching stages for such pulp require less bleaching agents or shorter bleaching times than for pulp which is not treated according to the present invention. EXAMPLE 5: Pulp produced from pine in accordance with the 0 process of Example 4 of the present invention is compared to that produced conventionally (0) (i.e., with no low consistency alkaline treatment step) . The average caustic dosage for high consistency oxygen delignification of brownstock pulp was found to be 45 pounds per oven dried ton (lb/t) or 2.3%. At that level, the average reduction in K No. across the oxygen delignification reactor was 10 units. For the same level of caustic applied to pulp according to a preferred treatment step, an average K No. drop during delignification was found to be 13 units: a 30% improvement compared to the conventional process. This advantage in delignification selectivity can also be shown by a comparision of pulp viscosity. The average K No. and viscosity for conventional pulp was 12.1 and 14.4 cps, respectively. For the preferred treatment process of the invention, the average K No. at essentially the same viscosity (14.0 cps) was 8.3. Delignification selectivity can also be expressed as the change in viscosity versus the change in K No. between brownstock and the corresponding treated pulps. Oxygen delignification selectivity decreases rather rapidly when the change in K No. begins to exceed 10 K No. units. The decrease in selectivity is observed as a rapid increase in the change in viscosity for a given change in K No. As an example, for a change in K No. of 12 units, the corresponding change in viscosity is expected to be 12 to 13 cps. By contrast, for the same change in K No. (12) obtained by delignified pulps which have been treated using the preferred method, the change in viscosity was found to be about 6 cps. The change in viscosity per change in K No. appears to be constant up to a 16 to 17 K No. unit change for pulps obtained using the preferred treatment process of the invention. The results are shown in Table XII. TABLE XII Caustic, lb/t 39.4 46.0 Delignification (%) 44.7 59.5 EXAMPLE 6 A southern pine pulp was produced in an operating 600 TPD fine paper mill using the modified oxygen delignification process (0 ) having the conditions of Table II in combination with the uniform alkali treatment as described in Examples 4 and 5 and the conditions as shown in Table XIII below. The O-stage pulp produced by this novel method had the properties needed to successfully complete the bleaching process using ozone, as described in the embodiment of this invention. The oxygen stage pulp had a K No. of 7.9 (compared to a typical conventional O-stage K No. of about 12) . Viscosity of the delignified pulp was 15 cps and was not significantly reduced by the high degree of delignification obtained by the use of the modified oxygen process. This pulp could then be further bleached with ozone, utilizing any of the numerous process embodiments described herein to produce a pulp having acceptable final strength and optical properties. C/DED bleaching of this pulp was completed in the laboratory, as described in Table XIV, to provide a baseline for comparison of properties. The ozone bleaching stage was carried out in a pilot plant reactor as shown in Fig. 2. Conditions of operation of the pilot plant reactor are shown in Table XV. TABLE XV PILOT PLANT REACTOR TYPICAL OPERATING CONDITIONS OPERATING PARAMETER VALUE OR CONDITION Gas and pulp flows Coeurrent Operating rate 6.50D TPD* Gas flow rate 58 scfm Pulp consistency 42% Ozone application (Note: 1.18% increased ozone amount used due to pulp containing dissolved solids that consume ozone) Pulp residence time 1 minute Z stage viscosity 11.8 cps Z stage brightness 55% GEB * oven dried tons per day The ozone bleached pulp generated in the pilot plant reactor was then treated in extraction and chlorine dioxide stages in the laboratory, as described in Table V above, to produce a final bleached pulp product at target brightness. A final D stage charge of only 1.0 % C10_ was used on the fiber. The strength and optical properties of the ozone bleached pulp were acceptable compared to the conventional OC/DED baseline and the results of the comparison are shown in Tables XVI and XVII below. EXAMPLE 7 To further exemplify the utility and range of applicability of the process of this invention, a southern hardwood fiber, from mixed hardwood comprising predominantly gum and oak, was bleached with ozone in the pilot plant described in Example 6 above. A conventional oxygen stage pulp produced in the 600 TPD mill was treated with ozone in the pilot plant reactor. The oxygen stage pulp had a K No. of 5.7 and a viscosity of 14.1. A portion of the 0 stage pulp was final bleached by the conventional C/DED sequence in the laboratory to provide a baseline for comparison. The C/DED conditions are shown in Table XVIII. The ozone reactor treatment conditions are shown in Table XIX. The pilot plant Z stage pulp was then final bleached by conventional E and D stages as shown in Table XX to a target brightness. A D-stage C10_ charge of only 0.35% was used on OD fiber. Strength and brightness properties were acceptable compared to the baseline as shown in Tables XXI and XXII. TABLE XIX HARDWOOD PILOT PLANT REACTOR OPERATING CONDITIONS OPERATING PARAMETER VALUE OR CONDITION Gas and pulp flows Coeurrent Operating rate 9 OD TPD Gas flow rate 60 scfm Pulp consistency 36% Ozone application (Note: 0.86% increased ozone amount used due to pulp containing dissolved solids that consume ozone) TABLE XXI HARDWOOD OC/DED AND OZ -πrED PROPERTIES COMPARISON OC/DED OZmED F TEAR BREAKING CSF TEAR BREAKING FACTOR LENGTH FACTOR LENGTH CIO. (%) 0.35 Brightness (GEB%) 64.0 84.4 EXAMPLE 8: Comparison tests similar to Example 5 were carried out for laboratory produced Kraft hardwood pulp, from mixed hardwood comprising predominantly gum and oak. Again, it was found that a significantly larger K No. drop across the oxygen delignification reactor using the modified oxygen process (O ) is achieved compared to conventional oxygen processing (O) . The average caustic dosage for hardwood was 27 lb/t, or 1.4%. This produced a K No. drop of about 5 units during the oxygen step. For the same level of caustic utilized according to the modified oxygen process of the present invention, an average K No. drop of about 7.3 units was obtained, an increase of almost 50%. This advantage in delignification selectivity can also be shown by comparing pulp viscosity. The average hardwood No. and viscosity were found to be 7.6 and 16 cps, respectively. For the invention, a K No. of 6 and a viscosity of 17.7 was obtained. Also, the K No. at the same viscosity as the non-treated pulp (16 cps) , was found to be 5.8. Delignification selectivity can also be expressed in terms of the change in viscosity versus the change in K No. between brownstock and the corresponding modified oxygen treated pulps. In comparing pulps which are conventionally oxygen treated with those of the invention, there is a greater decrease in delignification selectivity for increase degrees of delignification. For a change in K No. of 4 units, the average change in viscosity was 4 cps for pulps produced by the conventional process. By contrast, the change in K No. for the same change in viscosity for pulps produced by the modified oxygen method was 7 units. Expressed in terms of a delignification selectivity ratio, the selectivity for the modified method was 1.8 K No./cps an that for the conventional process was 1 K No./cps, an increase of 80%. Results are shown in Table XXIII. TABLE XXIII PULP PROPERTY COMPARISON (HARDWOOD) A series of experiments were carried out in the pilot plant reactor using pulp from a 600 TPD fine paper mill with a conventional oxygen delignification stage (0) . These experiments were performed to illustrate the effect of pH on the ozone bleaching process using southern hardwoods. Reactor operating conditions were held constant at the conditions shown in Table XXIV with the pH of the ozone stage being the only variable. TABLE XXIV HARDWOOD PILOT PLANT REACTOR TYPICAL OPERATING CONDITIONS OPERATING PARAMETER VALUE OR CONDITION Gas and pulp flows Coeurrent Operating rate 9 OD TPD Gas flow rate 40 scfm Pulp consistency 40% 0 Ozone application (Note: 1% increased ozone amount used due to pulp containing dissolved solids that consume ozone) Pulp residence time 1 minute 5 As can be seen from Table XXV below, the effect of pH on the ozone bleaching process is significant with lower pH beneficially improving the selectivity of the bleaching 0 process. TABLE XXV EFFECT OF pH ON HARDWOODS g PARAMETER pH 5 pH 4 pH 3 pH 2 CHANGE IN K NO. ACROSS THE -2.79 -3.17 -3.16 -3.67 Zm STAGE CHANGE IN BRIGHTNESS +12.1 +15.0 +11.7 +17.4 ACROSS THE Z STAGE (GEB) m 0 CHANGE IN VISCOSITY ACROSS -6.0 -7.1 -4.9 -4.4 THE Z STAGE (cps) m r 5 EXAMPLE 10 A number of comparative properties are of interest to illustrate the beneficial effects of producing fully bleached pulps using the OZ ED process. Typical operating data and effluent measurements were collected from operating mills using the CEDED and OC/DED bleaching sequences on Southern pine. These properties were compared to those of effluents produced by the OZ ED sequence, using the OZ ED pulp and effluent prepared in Example 1. For the conventional CEDED sequence see Table XXVI, for the conventional OC/DED sequence see Tables II and III above and for the oz ED sequence see Tables IV and V above. It should be noted that the CEDED sequence effluent is the combined C, E., D., E 2 and D 2 effluent. The OC/DED effluent is the C/D, E and D combined effluent and the OZ ED effluent is the D stage effluent, each representing the several effluent properties. As shown in Table XXVII below, the ozone bleaching sequence substantially reduces the environmental impact of the effluent from the bleaching process. To determine color, EPA method 110.2 was used. From this data, it can be seen that the present invention provides a discharge effluent having a color of no greater than about 2 pounds per ton, a BOD., value of no greater than about 2 pounds per ton and an amount of total organic chloride of no greater than about 2 and preferably less than about 0.8 * Southern pine kraft pulp was bleached using three modifications of the basic OZED sequence. In the first sequence (OZ ED) , the pulp was bleached as in Tables IV and with conventional oxygen, modified ozone, caustic extraction and chloride dioxide as produced in the R-3 sequence with a CIO /Cl 2 ratio of 6:1. In the second sequence, the modified oxygen process (O ) was utilized and again the final stage used an R-3 type of chlorine dioxide. In the third sequence, the modified oxygen process (O ) was used once again, and an R-8 chlorine dioxide solution was employed with 95:1 ratio in the final stage. Table XXVIII demonstrates the positive environmental impact offered with the use of the modified oxygen process (0 ) . The R-8 bleach liquor also had a positive effect. TABLE XXVIII EFFLUENT FROM BLEACHING OF PINE KRAFT PULPS Sequence O Z^^ED °M Z M ED -M^ ^°- Ratio C10 2 /C1 2 6:1 6:1 95:1 in Last Stage TOCl, lb/ton 0.8 0.3 0.2 EXAMPLE 12 Southern loblolly pine pulps were prepared by the kraft and kraft/AQ pulping processes as described in Tables I and VIII above. These pulps were further subjected to conventional and modified oxygen delignification as described in Examples 4 and 5 to show the effect of combining these processes (for extending delignification with minimal impact on pulp strength) on the ozone bleaching sequence. As can readily be seen from Table XXIX, these processes produce an additive effect. Extremely ■ * low 0mzmE K Nos. can be reached with little impact on final viscosity. Conversely, the amoun of ozone needed to reach a targ 3 et 0mZmE K No. of about 3.5 for the previously described ozone bleaching process can be substantially reduced. In addition, the additive effect produces a southern pine pulp that can be fully bleached by a 0mzmEP process where a very low omzmE K No. is required for a functional peroxide stage. OZONE APPLICATION OF 0.5% TO EACH CASE Southern softwood, i.e., loblolly pine, was bleached to target brightness of 83 GEB using the conventional CEDED sequence as shown in Table XXVI, using the conventional OC/DE sequence as shown in Tables II and III above and using the OZ ED sequence as shown in Tables IV and V above. Wood based dirt was refined and added to the OZ ED starting brownstock a a level of 0.75% by weight to examine the ability of this sequence to remove dirt compared to CEDED and OC/DED bleachin Dirt properties of the three sequences, measured as Effective Black Area, bark and shives, were equivalent. Example 14 This example illustrates the range of applicability of t ozone bleaching process of the invention. Bleached pulps can be produced over a wide range of product brightnesses, utilizing appropriate combinations of ozone and chlorine dioxide charges to minimize environmental impacts and operati costs. As shown in Table XXX below, products having brightnes from above 65% GEB can be produced by various combinations of ozone and chlorine dioxide while retaining reasonable strengt properties. TABLE XXX 0Z-.ED BLEACHING CONDITIONS - * Viscosity values after the 0 stage are interpolated values based on established data. While it is apparent that the invention herein disclosed is well calculated to fulfill the objectives stated above, it will be appreciated that numerous modifications and embodimen may be devised by those skilled in the art, and it is intende that the appended claims cover all such modifications and embodiments as fall within the true spirit and scope of the present invention.

Claims: CLAIMS We Claim: 1. A process for the manufacture of a bleached pu having a certain GE brightness and a certain strength as indicated by a certain viscosity which comprises: chemically digesting a lignocellulosic material to provide a pulp; oxygen delignifying the pulp to remove a substanti portion of the lignin; the combination of the chemical digesting and oxyg delignifying steps being selected to provide an intermediate pulp containing a specified amount of lignin and having a specified viscosity; and ozone delignifying the intermediate pulp by adjust the consistency and pH of the intermediate pulp to predetermined values, comminuting the intermediate pulp into discrete particles of a size having a sufficiently small diameter and a sufficiently low density to facilitate substa tially complete penetration of a majority of the particles b ozone, and bleaching the particles with ozone in an amount sufficient to remove a substantial portion, but not all, of t lignin by intimately contacting and mixing the discrete particles with the ozone for a sufficient time and at a temperature sufficient to obtain substantially uniform delignification and bleaching throughout a majority of the particles to form a bleached pulp; wherein the specified amount of lignin of the intermediate pulp is such that, after ozone delignification, the leached pulp attains the certain GE brightness, and wherein the specified viscosity of the intermediate pulp is sufficiently high to compensate for viscosity decreases durin ozone delignification, thus permitting the bleached pulp to attain the certain strength. 2. The process of claim 1 wherein the pulp particl have a size of less than about 5mm. 3. The process of claim 1 or 2 which comprises chemically digesting the lignocellulosic material by Kraft pulping, Kraft AQ pulping or extended delignification. 4. The process according to claim 1 wherein the oxygen delignification step comprises forming a low to medium consistency pulp; treating the low to medium consistency pulp with an aqueous solution of an alkaline material for a predetermined time and at a predetermined temperature relativ to the quantity of the alkaline material to substantially uniformly distribute the alkaline material throughout the low to medium consistency pulp; raising the consistency of the pu to a high consistency; and subjecting the resulting high consistency pulp to high consistency oxygen delignification t obtain the intermediate pulp. 5. The process of claim 1 wherein the certain GE brightness is at least about 50%, the certain viscosity at th certain strength is greater than about 10 cps, and wherein th specified amount of lignin is indicated by an intermediate pu K No. of about 10 or less and the specified viscosity is greater than about 13 cps. 6. The process of claim 1 wherein the lignocellulosic material is a softwood, the certain GE brightness is at least about 50%, the certain viscosity at th certain strength is greater than about 10 cps, and wherein th specified amount of lignin is indicated by an intermediate pu K No. of about 7-10 and the specified viscosity is greater th about 13 cps. 7. The process of claim 1 wherein the lignocellulosic material is a hardwood, the certain GE brightness is at least about 55%, the certain viscosity at t certain strength is greater than about 10 cps, and wherein t specified amount of lignin is indicated by an intermediate p K No. of about 5-8 and the specified viscosity is greater th about 13 cps. 8. The process of claim 5, 6 or 7 wherein the amo of lignin contained in the pulp after ozone delignification indicated by a bleached pulp K No. of about 3 to 4. 9. The process of claim 1 which further comprises bleaching the pulp after ozone delignification with a brightening agent to increase the GE brightness of the bleach pulp. 10. The process of claim 9 which further comprises combining the bleached pulp with an effective amount of alkaline material in an alkaline aqueous solution at a predetermined temperature, correlated to the amount of alkali material combined, to solubilize a substantial portion of any lignin remaining in the bleached pulp; and thereafter extracting a portion of the aqueous alkaline solution so as t remove substantially all of the solubilized lignin therefrom and form an extracted pulp prior to bleaching with the brightening agent. 11. The method of claim 9 wherein the brightening agent is chlorine dioxide or a peroxide. 12. A process for delignifying and bleaching a lignocellulosic material to a pulp having a certain GE brightness and a certain strength as indicated by a certain viscosity, which comprises: digesting a lignocellulosic material to form a pulp having first K No. and first viscosity value; delignifying said pulp with oxygen to form a partially delignified pulp having a second K No. lower than said first K No. , and which is sufficient to enable the partially delignified pulp to be further delignified with ozon while maintaining viscosity at a level such that cellulose components of said partially delignified pulp have not been significantly chemically degraded by the oxygen delignification; and further delignifying the partially delignified pulp by applying thereto a sufficient amount of ozone for a sufficient time correlated to the amount of ozone applied to said partially delignified pulp to obtain a substantially delignified pulp having a third K No. significantly reduced below said second K No. of said partially delignified pulp and a GE brightness value substantially above that of the partiall delignified pulp while maintaining viscosity and without agressively chemically attacking cellulose components of the pulp to avoid substantially reducing the strength of the pulp. 13. The process of claim 12 wherein the partially delignified pulp contains an amount of lignin which, after ozone delignification, permits the pulp to attain the certain GE brightness, and also has a viscosity which is sufficiently high to compensate for viscosity decreases during ozone delignification, thus permitting the substantially delignified pulp to attain the certain strength. 14. The process of claim 12 which further comprises combining the substantially delignified pulp with an effective amount of alkaline material in an alkaline aqueous solution at a predetermined temperature, correlated to the amount of alkaline material combined, to solubilize a substantial portio of any lignin remaining in the substantially delignified pulp; and thereafter extracting a portion of the aqueous alkaline solution so as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin-free pulp. 15. The process of claim 14 which further comprise bleaching the substantially lignin-free pulp to a brightness value which is substantially higher than that of the substantially delignified pulp. 16. The process of claim 12 wherein the viscosity said partially delignified pulp is maintained at greater than about 13 cps. 17. The process of claim 16 wherein said partially delignified pulp is maintained at a viscosity decrease of abo 30% or less of said first value. 18. The process of claim 12 wherein said lignocellulosic material is a hardwood. 19. The process of claim 18 wherein said first K N is between about 10-14. 20. The process of claim 18 wherein said first viscosity value is between about 21-28 cps. 21. The process of claim 18 wherein said second K No. is between about 5-8. 22. The process of claim 21 wherein said third K N is less than about 5. 23. The process of claim 12 wherein said lignocellulosic material is a softwood. 24. The process of claim 23 wherein said first K No is between about 20-24. 25. The process of claim 23 wherein said second K No. is between about 7-10. 26. The process of claim 12 wherein the oxygen delignification treatment is carried out on pulp of medium consistency. 27. The process of claim 12 wherein the partial delignification step further comprises: treating said pulp with a quantity of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to substantially complete a substantially uniform distribution of the alkaline material throughout the pulp; increasing the consistency of the pulp after th completion of the treating step; and subjecting the increased consistency alkaline material containing pulp to high consistency oxygen delignification to obtain a partially delignified pulp. 28. The process of claim 12 wherein the viscosity o said substantially delignified pulp is maintained at greater than about 10 cps. 29. The process of claim 28 wherein said substantially delignified pulp is maintained at a viscosity decrease of about 30% or less of the viscosity of said partially delignified pulp. 30. The process of claim 12 wherein the further delignifying step additionally comprises: increasing the consi- _cy of said partially delignified pulp; comminuting said increased consistency pulp to predetermined particle size; and uniformly contacting said comminuted pulp with said effective amount of ozone as the pulp is advanced throug the process. 31. The process of claim 30 wherein the particle size of said increased consistency pulp is comminuted to one that facilitates uniform contact with ozone without causing significant degradation of the cellulose components of the pulp. 32. The process of claim 31 wherein the pulp is comminuted to about 5 mm and advanced through the process in manner to avoid a non-uniform application of the ozone to the pulp. 33. The process of claim 32 wherein the comminuted pulp is advanced cocurrently with the ozone. 34. The process of claim 32 wherein the comminuted pulp is advanced countercurrently to the ozone. 35. The process of claim 15 wherein the substantially lignin free pulp is bleached with chlorine dioxide. 36. The process of claim 15 wherein the substantially lignin free pulp is bleached with a peroxide. 37. The process of claim 35 or 36 wherein the bleaching step raises the GE brightness of said substantially lignin free pulp to at least about 70%. 38. The process of claim 35 or 36 wherein the bleaching step raises the GE brightness of said substantially lignin free pulp to at least about 80%. 39. The process of claim 35 or 36 wherein the bleaching step raises the GE brightness of said substantially lignin free pulp to at least about 90%. 40. A process for delignifying and bleaching lignocellulosic material which comprises: partially delignifying lignocellulosic material to form a pulp having a K No. of about 10 or less and a viscosit of greater than about 13 cps; and further delignifying said pulp with an effective amount of ozone for a sufficient time to obtain a substantial delignified pulp having a K No. of about 5 or less, a viscosi of greater than about 10 and a GE brightness of at least abou 50%. 41. The process of claim 40 wherein the lignocellulosic material is a softwood and is partially delignified to a pulp having a K No. of about 7 to 10 and a viscosity of above about 13 before further delignification wi ozone. 42. The process of claim 41 wherein the softwood pulp has a K No. of about 3 to 4, a viscosity of above about and a GE brightness of at least about 50% after said further delignification with ozone. 43. The process of claim 40 wherein the lignocellulosic material is a hardwood and is partially delignified to a pulp having a K No. of about 5 to 8 and a viscosity of above about 13 before further delignification wi ozone. 44. The process of claim 43 wherein the hardwood pulp has a K No. of about 3 to 4, a viscosity of above about 10, and a GE brightness of at least about 55% after further delignification with ozone. 45. The process of claim 40 which further compris combining the substantially delignified pulp with effective amount of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material solubilize a substantial portion of any lignin which remains the pulp, and thereafter extracting a portion of the aqueous alkaline solution so as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin free pulp. 46. The process of claim 45 wherein said extracti step raises the brightness of the pulp by about 2%. 47. The process of claim 45 which further compris bleaching the substantially lignin-free pulp with one of chlorine dioxide or a peroxide to raise the GE brightness to least about 70%. 48. The process of claim 47 wherein the GE brightness is raised to at least about 80%. 49. The process of claim 47 wherein the GE brightness is raised to at least about 90%. 50. The process of claim 45 wherein the lignocellulosic material is partially delignified by an oxygen delignification treatment. 51. The process of claim 50 wherein the oxygen delignification treatment is carried out on pulp of medium consistency. 52. The process of claim 45 wherein the lignocellulosic material is partially delignified by: forming a pulp having a relatively low consistency less than 10% by weight; treating the low consistency pulp with a quantity o alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to substantially complete a substantially uniform distribution o the alkaline material throughout the pulp; increasing the consistency of the pulp to at least about 20% by weight after completion of the treating step; an subjecting the increased consistency alkaline material containing pulp to high consistency oxygen delignification to obtain a partially delignified pulp having K No. of about 9 or less and a viscosity of about 13 or highe 53. A process for delignifying and bleaching lignocellulosic material which comprises: partially delignifying a lignocellulosic material t form a pulp; reducing the consistency of the pulp to a low consistency of less than 10% by weight; treating the low consistency pulp with a quantity o alkaline material in a aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to substantially complete a substantially uniform distribution o the alkaline material throughout the pulp; increasing the consistency of the pulp to at least about 20% by weight after completion of the treating step; subjecting the increased consistency alkaline material containing pulp to high consistency oxygen delignification to obtain a partially delignified pulp havin K No. of about 9 or less and a viscosity of greater than abo 13 cps; further delignifying said partially delignified pul with an effective amount of ozone for a sufficient time to obtain a substantially delignified pulp having a K No. of abo 5 or less, a viscosity of greater than about 10 and a GE brightness of at least about 50%; combining the substantially delignified pulp with a effective amount of alkaline material in a aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material t solubilize a substantial portion of any lignin which remains the pulp; extracting a portion of aqueous alkaline solution s as to remove substantially all of the solubilized lignin therefrom and form substantially lignin-free pulp; and bleaching the substantially lignin-free pulp to rai the GE brightness thereof to at least about 70%. 54. The process of claim 53 wherein the GE brightness is raised to at least about 80%. 55. The process of claim 53 wherein the GE brightness is raised to at least about 90%. 56. The process of claim 53 wherein the lignocellulosic material is a softwood and is partially delignified to a K No. of about 8 to 9 and a viscosity of greater than about 14 before further delignification with ozone. 57. The process of claim 56 wherein the softwood pulp has a K No. of between about 3 to 4, a viscosity of abov about 10, and a GE brightness of at least about 54% after sai further delignification with ozone. 58. The process of claim 53 wherein the lignocellulosic material is a hardwood and is partially delignified to a K No. of about 6 to 7 and a viscosity of abo about 15 before said further delignification with ozone. 59. The process of claim 58 wherein the hardwood pulp has a K No. of between about 3 to 4, a viscosity of abov about 10, and a GE brightness of at least about 63% after sai further delignification with ozone. 60. The process of claim 53 wherein the partially delignified lignocellulosic material is obtained by Kraft pulping, Kraft-AQ pulping or extended delignification of a lignocellulosic material. 61. The process of claim 53 which comprises decreasing the K No. of the increased consistency pulp by at least about 60% during the oxygen delignification step withou significantly damaging the cellulose components of the pulp. 62. The process of claim 53 wherein the pulp is subjected to the high consistency oxygen delignification without substantially changing the viscosity of the pulp. 63. The process of claim 53 which comprises decreasing the ratio of K No. to viscosity of the pulp during the oxygen delignification step by at least 25%. 64. The process of claim 53 wherein the consisten of the pulp which is treated with the aqueous alkaline solut prior to oxygen delignification ranges between about 1 and 4 by weight. 65. The process of claim 53 wherein the consisten of the pulp is increased to between about 25 and 35% by weig prior to the oxygen delignification step. 66. The process of claim 53 wherein the amount of alkaline material distributed throughout the low consistency pulp prior to oxygen delignification ranges from about 15 to 30% by weight based on the dry weight of the pulp. 67. The process of claim 66 wherein the aqueous alkaline solution has a concentration of alkaline material o between about 20 and 120 g/1, so that the concentration of alkaline material in the low consistency pulp ranges from ab 6.5 to 13 g/1. 68. The process of claim 53 wherein the alkaline treating step is conducted for a time of between about 1 and minutes at a temperature of between about 90 and 150°F. 69. The process of claim 53 wherein the initially formed pulp is brownstock pulp and further wherein at least a portion of the liquid obtained from the alkaline solution during the pulp consistency increasing step is recycled to th alkaline treating step. 70. A process for delignifying and bleaching a lignocellulosic material which comprises: forming a brownstock pulp having a K No. of from about 10-24 by Kraft pulping, Kraft-AQ pulping or extended delignification of a lignocellulosic material; decreasing the consistency of said pulp to about 1 4.5% by weight; treating the decreased consistency pulp with a quantity of alkaline material in an aqueous alkaline solution having a concentration of alkaline material of between about and 120 g/1, for a time of between about 1 and 15 minutes and at a temperature of between about 90 and 150 β F such that the concentration of alkaline material in the decreased consisten pulp during this treating step ranges from about 6.5 to 13 g/ so as to substantially complete a substantially uniform distribution of the alkaline material throughout the pulp; increasing the consistency of the alkaline treated pulp to between about 25 to 35% by weight; subjecting the increased consistency pulp to high consistency oxygen delignification without substantially changing the viscosity of the pulp to form a partially delignified pulp having a K No. of about 10 or less and a viscosity of greater than about 13, wherein the ratio of K No. to viscosity of said pulp is decreased by at least about 25% during oxygen delignification; further delignifying said oxygen delignified pulp with an effective amount of ozone for a sufficient time to obtain a substantially delignified pulp having a K No. of abo 5 or less, a viscosity of greater than about 10 and a GE brightness of at least about 50%; combining the substantially delignified pulp with a effective amount of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material t solubilize a substantial portion of any lignin which remains the pulp; extracting a portion of aqueous alkaline solution s as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin-free pulp; and bleaching the substantially lignin-free pulp to ra the GE brightness thereof to at least about 70%. 71. The process of claim 70 wherein the GE m brightness is raised to at least about 80%. 72. The process of claim 70 wherein the GE brightness is raised to at least about 90%. 73. The process of claim 70 which comprises decreasing the K No. of the increased consistency pulp by at least about 60% during the oxygen delignification step witho significantly damaging the cellulose components of the pulp. 5 74. The process of claim 70 wherein the substantially lignin-free pulp is bleached with chlorine dioxide or a peroxide. 75. The process of claim 74 wherein the peroxide hydrogen peroxide. 76. The process of claim 70 which further compris adding a chelating agent to said pulp prior to ozone delignification to render metal ions substantially non-react to ozone. 77. The process of claim 76 wherein the chelating agent is DTPA, EDTA or oxalic acid. 78. The process of claim 7C - * hich further compris adjusting the pH of the pulp to a rang, f about 1 to 4 by adding to the pulp a sufficient quantit 7 of an acidic materi prior to ozone delignification. 79. The process of claim 70 which further comprise increasing the consistency of the pulp to between about 25-50 by weight prior to ozone delignification. 80. The process of claim 79 wherein the consistenc of the pulp is increased to between about 35-45% by weight prior to ozone delignification. 81. The process of claim 70 which comprises comminuting said pulp to a diameter of less than about 5 mm after oxygen delignification and prior to ozone delignification. 82. The process of claim 70 which further comprise maintaining the pulp at a temperature of less than about 120 β during ozone delignification. 83. The process of claim 70 wherein the ozone is provided by a mixture comprising ozone and oxygen. 84. The process of claim 83 wherein the ozone concentration in the mixture is between about 1 and 8 percent by volume. 85. The process of claim 70 wherein the ozone is provided by a mixture of ozone and air. 86. The process of claim 85 wherein the ozone concentration is between about 1 and 4 percent by volume. 87. The process of claim 70 which comprises advancing the partially delignified pulp during the ozone delignification step in a manner which subjects substantially all the pulp to ozone. 88. The process of claim 87 which comprises introducing the ozone countercurrently to the advancing pulp. 89. The process of claim 87 which comprises introducing the ozone cocurrently with the advancing pulp. 90. A process for delignifying and bleaching a lignocellulosic material which comprises: partially delignifying a lignocellulosic material by pulping to form a pulp and delignifying said pulp with oxygen to form a partially delignified pulp having a K No. of about 10 or less and a viscosity of greater than about 13 cps; adding a chelating agent to said pulp to render metal ions therein substantially non-reactive to ozone; adjusting the pH of said pulp to a range of about 1 and 4 by adding a sufficient quantity of an acidic material thereto; increasing the consistency of said pulp to between about 25 and 50%; comminuting said increased consistency pulp to a diameter of less than about 5 mm; further delignifying said increased consistency pulp with an effective amount of ozone for a sufficient time by advancing the comminuted pulp in a manner which subjects substantially all the pulp to the ozone to obtain a substantially delignified pulp having a K No. of about 5 or less, a viscosity of greater than about 10 and a GE brightness of at least about 50%; combining the substantially delignified pulp with an effective amount of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to solubilize a substantial portion of any lignin which remains in the pulp; extracting a portion of aqueous alkaline solution so as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin-free pulp; and bleaching the substantially lignin-free pulp with chlorine dioxide to raise the GE brightness thereof to at least about 70%. 91. The process of claim 90 wherein the GE brightness is raised to at least about 80%. 92. The process of claim 90 wherein the GE brightness is raised to at least about 90%. 93. The process of claim 90 wherein the pulping step comprises Kraft pulping and the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulose components of the pulp or without substantially changing the viscosity of the pulp. 94. The process of claim 93 wherein the pulping step comprises Kraft AQ pulping. 95. The process of claim 94 wherein the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulose components of the pulp or without substantially changing the viscosity of the pulp. 96. The process of claim 90 wherein the pulping step comprises the combination of Kraft AQ pulping and extended delignification, and the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulose components of the pulp or without substantially changing the viscosity of the pulp. 97. The process of claim 90 wherein during ozone delignification the pulp is advanced in a manner so that the pulp is maintained at a temperature of less than about 120 β F. 98. The process of claim 90 wherein the chelating agent and acid are added to said pulp in a mixing chest. 99. The process of claim 98 wherein at least a portion of the liquid separated from the pulp during the consistency increasing step is recycled to the mixing chest. 100. The process of claim 98 wherein the pulp is advanced coeurrently with the ozone. 101. The process of claim 98 wherein the pulp is advanced countercurrently with the ozone. 102. A process for delignifying and bleaching a lignocellulosic material which comprises: partially delignifying a lignocellulosic material by pulping to form a pulp and delignifying said pulp with oxygen to form a partially delignified pulp having a K No. of about 10 or less and a viscosity of greater than about 13 cps; adding a chelating agent to said pulp to render metal ions therein substantially non-reactive to ozone; adjusting the pH of said pulp to a range of about 1 and 4 by adding a sufficient quantity of an acidic material thereto; increasing the consistency of said pulp to between about 25 and 50%; comminuting said increased consistency pulp to a diameter of less than about 5 mm; further delignifying said increased consistency pulp with an effective amount of ozone for a sufficient time to obtain a substantially delignified pulp having a K No. of about 5 or less, a viscosity of greater than about 10 and a GE brightness of at least about 50%; combining the substantially delignified pulp with an effective amount of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to solubilize a substantial portion of any lignin which remains in the pulp; extracting a portion of aqueous alkaline solution so as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin-free pulp; and bleaching the substantially lignin-free pulp with a peroxide to raise the GE brightness thereof to at least about 70%. 103. The process of claim 102 wherein the GE brightness is raised to at least about 80%. 104. The process of claim 102 wherein the GE brightness is raised to at least about 90%. 105. The process of claim 102 wherein the pulping step comprises Kraft pulping and the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulose components of the pulp or without substantially changing the viscosity of the pulp. - - 106. The process of claim 102 wherein the pulpin step comprises Kraft AQ pulping. 107. The process of claim 106 wherein the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulos components of the pulp or without substantially changing th viscosity of the pulp. 108. The process of claim 102 wherein the pulping step comprises the combination of Kraft AQ pulping and extended delignification, and the oxygen delignification step decreases the K No. of the pulp by at least about 60% without significantly damaging the cellulose components of the pulp or without substantially changing the viscosity of the pulp. 109. The process of claim 90 or 102 wherein the ozone delignification reduces the K No. of the pulp by at least 50%. 110. The process of claim 90 or 102 wherein the bleaching step raises the GE brightness of the pulp by at least 50%. 111. The process of claim 110 wherein the GE brightness of the pulp is increased to at least 83%. 112. A process for delignifying and bleaching a lignocellulosic material which comprises: partially delignifying a lignocellulosic material by pulping to form a pulp, washing said pulp, and delignifying said pulp with oxygen to form a partially delignified pulp having a K No. of about 10 or less and a viscosity of greater than about 13 cps; washing the partially delignified pulp; further delignifying said partially delignified pulp with an effective amount of ozone for a sufficient time to obtain a substantially delignified pulp having a K No. of about 5 or less, a viscosity of greater than about 10 and a GE brightness of at least about 50%; washing the substantially delignified pulp; combining the substantially delignified pulp with an effective amount of alkaline material in an aqueous alkaline solution for a predetermined time and at a predetermined temperature correlated to the quantity of alkaline material to solubilize a substantial portion of any lignin which remains in the pulp; extracting a portion of the aqueous alkaline solution so as to remove substantially all of the solubilized lignin therefrom and form a substantially lignin-free pulp; washing the substantially lignin-free pulp; bleaching the substantially lignin-free pulp with one of chlorine dioxide or a peroxide to raise the GE brightness thereof to at least about 70%; and washing the bleached pulp. 113. The process of claim 112 wherein the GE brightness is raised to at least about 80%. 114. The process of claim 112 wherein the GE brightness is raised to at least about 90%. 115. The process of claim 112 wherein the bleached pulp washing step comprises washing said pulp with fresh water, and separating the pulp from the resulting wash water effluent. 116. The process of claim 112 wherein the bleaching step utilizes chlorine dioxide and the bleached pulp wash water effluent is discharged. 117. The process of claim 112 wherein the bleaching step utilizes chlorine dioxide and the bleached pulp wash water effluent is treated by reverse osmosis to form a treated filtrate and at least a portion of said treated filtrate is then directed to the substantially lignin-free pulp washing step. 118. The process of claim 112 wherein the bleaching step utilizes a peroxide and at least a portion of the bleached pulp is recycled to the step wherein the substantially lignin-free pulp is washed. 119. The process of claim 117 or 118 wherein the substantially lignin-free pulp washing step comprises washing said pulp with bleached pulp wash water, separating the pulp from the resulting wash water and directing at least a portion of said wash water to the substantially delignified pulp washing step. 120. The process of claim 119 wherein the substantially delignified pulp washing step comprises washing said pulp with the substantially lignin-free pulp wash water, separating the pulp from the resulting wash water and directing at least a portion of said wash water to the partially delignified pulp washing step. 121. The process of claim 120 wherein the partially delignified pulp washing step comprises washing said pulp with substantially delignified pulp wash water, separating the pulp from the resulting wash water and directing at least a portion of said wash water to the pulp washing step. 122. The process of claim 121 wherein the pulp washing step comprises washing said pulp with partially delignified pulp wash water, separating the pulp from the resulting wash water, and collecting and concentrating said wash water prior to incineration in a recovery boiler. 123. The process of claim 112 or 122 wherein the bleaching step utilizes chlorine dioxide having a minimum chlorine content. 124. The process of claim 112 or 122 wherein the water demand for the washing steps is substantially reduced compared to conventional CEDED or OC/DED processes. 125. The process of claim 116 wherein the discharge effluent has a color of no greater than about 2 pounds per ton, a B0D 5 value of no greater than about 2 pounds per ton and an amount of total organic chlorides of no greater than about 2.

Inventors: GANDEK THOMAS P, GRIGGS BRUCE F, PIKULIN MICHAEL A, ROSEN ALLEN, GANDEK, THOMAS, P., GRIGGS, BRUCE, F., PIKULIN, MICHAEL, A., ROSEN, ALLEN
Applicants: UNION CAMP CORP, UNION CAMP CORPORATION
Application year: 1990
Main classification: D21C9
IPC codes: D21C9