The invention also relates to a system for utilising waste that contains fibres and combustible material.

In addition, the invention relates to a method for processing fibre in a paper or board mill that utilises recycled fibre pulp.

Conventionally, the options available in waste disposal and processing have been transport to landfill sites, incineration in mass incineration plants and-to a limited extent-recovery of recyclable materials. The last-mentioned option generally requires separation of wastes at source wherein recyclable waste fractions, such as, biowaste, paper and board, glass and metals are separated and collected separately. However, source separation is always insufficient, which means that the amount of mixed waste is now, and will also be in future, considerable.

The form of energy recovery that has become popular recently is one in which recovered and/or refuse-derived fuel (REF, RDF) processed from waste is burned either in conventional boilers together with other fuel or as the main fuel in combustion plants specially designed for recovered/refuse-derived fuel. The wastes most suitable for energy recovery include packaging, paper and plastic wastes from industry and commerce as well as construction wastes, which can constitute as much as 70 to 80 % of the amount of waste usually transported to landfills. Dry household waste can also be used in the production of energy

provided that, among other things, metals, glass and biowaste have been separated from it first.

Most economically, recovered fuel is produced from a source-separated combustible waste fraction, i. e. the so-called energy fraction of waste. The processing stages of this REF fuel (recovered fuel) typically include removal of oversized pieces, crushing of waste, separation of metals as well as removal of sand and stones. Finished REF fuel contains predominantly plastics, wood, paper and board. The proportion of impurities in the fuel may be, for example, of the order of 5 % depending of the sorting process. Recovered fuel can also be produced from unsorted mixed waste by mechanical handling processes, in which case the end product is called RDF fuel (refuse-derived fuel). A difference with respect to the handling of source-separated waste is constituted by a more mixed composition of the waste raw material, which is mainly shown as a higher biowaste content. Consequently, more sorting stages are needed in the production of RDF fuel than at an REF plant, for example, gravimetric separation stages, i. e. sorting stages based on the size and density of particles, whereby heavy matter, such as food scraps, can be efficiently separated from the fraction intended for combustion. The composition of finished RDF fuel is very much like that of REF fuel, but the proportion of impurities in it can be slightly higher, for example, of the order of 8 %.

Energy recovery from waste should not be an end in itself, but rather aim for sensible macroeconomical reclamation of wastes or for making them harmless. In all reclamation of waste, the primary object should be recovery of materials contained in waste when it is economically profitable and, only secondarily, utilisation of waste as fuel. Landfilling should be the very last option.

WO application publication 98/18607 discloses a process for treatment of waste that contains recyclable components, in which process waste is agitated in water employing mechanical force, whereby the size of pieces in waste is reduced and

fibres are suspended in water. The heavy fraction containing metals, the lightweight fraction containing plastics and the fraction containing fibres are separated from the suspension in stages. The process is intended for treatment of packaging waste which contains different plastics and mixed materials, in particular board lined with plastic and/or metal foils, and metal cans. The fibre content of this kind of raw material is generally relatively low, wherefore the special problems associated with the recovery of fibres and with the quality of pulp have not been taken into consideration to a sufficient degree in the process.

The publication has also failed to take into account matters that form an integral part of the recovery of fibres, such as, meeting of energy demand and circulation of waters.

The recovery of fibres from waste is also discussed, among other things, in GB patent 1,364,474 and in published GB application 2,026,019.

One object of the invention is to make it possible to recover a larger and higher quality portion than before of those fibres contained in waste which until now have been either passed to incineration or taken to a landfill site.

With a view to achieving this object as well as those coming out later, the arrangements according to the invention are characterised in that which is stated in the characterising part of the independent claims.

In the method according to the invention, waste is slushed in a continuous- operation high-consistency pulper in order to suspend in water the fibres contained in the waste, and from the pulper are discharged substantially continuously, on the one hand, fibre suspension through a screen plate and, on the other hand, non-defibrable material by means of a mechanical transfer device. The fibre suspension is sorted and cleaned for use as raw material in paper or board and the non-defibrable material as well as the rejects separated from the fibre

suspension in sorting and cleaning stages are used as fuel in energy production and/or utilised as raw material.

Advantageously, the pulper is provided with a screw conveyor, which moves non- defibrable material from the pulper to a reject drum. As the amount of reject is relatively high when slushing mixed waste, conventional arrangements for removal of reject are not sufficient. In order to make the recovery of fibres more effective, this material containing an abundance of plastics is washed first on the screw conveyor and then further in the reject drum and the washing waters used in both washing stages are passed so as to be mixed with the fibre suspension.

Advantageously, the pulper has been arranged to operate at a temperature of about 60 °C, in which connection, on the one hand, defibration is efficient and, on the other hand, bacteria and other micro-organisms carried with waste material do not cause any hygienic harm. Slushing consistency is generally about 10 %. The fibre suspension is discharged from the pulper through a screen plate in which the diameter of holes is 8-15 mm, most advantageously about 10 mm. The particles which are larger than this hole size are passed so as to be mixed with the non- defibrable material.

After slushing, the fibre suspension is course screened to remove the reject particles still remaining in it. In coarse screening, a perforated screen is used in which the diameter of holes is 2-4 mm, most advantageously about 3 mm. In that connection, pulp is sufficiently clean for the next process stage, which is usually centrifugal cleaning. The function of centrifugal cleaning is to remove sand and other heavy particles from the pulp. After that, the pulp is fine screened and possibly fractionated for various uses. As there is an abundance of relatively inexpensive raw material available, in the fibre recovery line according to the invention there is no need to attempt to maximise the yield of fibres, as in conventional recycling processes, but the quality of fibres can be optimised. Thus, fine screening can be enhanced and the amount of reject increased as compared

with conventional fibre recovery processes. Disposal of the increased reject volume presents no problem because said reject can be combusted together with the rejects derived from slushing and coarse screening.

After fine screening, the pulp is washed to improve the quality of the end product.

Advantageously, the washed pulp is compressed in the end to a dry matter content of about 50 %, after which it is ready for transport to a site of use situated at a reasonable distance. Alternatively, the pulp can be dried for transport to a dry matter content of about 90 % or delivered as wet to a paper or board machine located in the immediate vicinity.

The fibre recovery process according to the invention consumes a considerable amount of water, which makes it necessary to clean and recirculate the process waters. The waste waters produced in different process stages are collected, treated and returned to the process. Cleaning can be accomplished, for example, as biological treatment, which is followed by clarification and, when needed, by further treatment stages for part of the water amount. The clean water necessary for the water balance of the system is introduced into the pulp washing stage at which it improves the quality of the end product.

Sand is separated from the reject fractions for transport, for example, to a landfill site or for use as earth filling. Water is removed mechanically from combustible reject fractions and it is passed so as to be cleaned. To combustion can be passed, among other things, the non-defibrable material which comes from slushing and from which sand has been separated in a reject drum, the reject from coarse screening, the reject from fine screening as well as the fibre-containing sludge formed in clarification of waste water.

Advantageously, the waste utilised in the process according to the invention is dry waste or mixed waste that has been pre-treated into a form suitable for recovered/refuse-derived fuel. The possible pre-treatment stages include a

reduction in size of the pieces of waste, for example, by crushing as well as removal of metals and other undesirable waste fractions. The waste raw material can also be replaced partially or totally with paper and/or board waste collected separately. In this case, too, the process differs from prior art fibre recovery lines, among other things, in the respect that the rejects from the fibre line have in it a clear and economically profitable site of use in the production of energy.

The method described above, in which fine screening is enhanced to improve the quality of fibre material and the reject portion increased as a result of it is passed to the energy production of the plant, is also particularly advantageous in the stock circulation of paper and board machines, in particular of OCC board machines, also when recycled fibre pulp is used as raw material. Today, to maximise the yield of fibres, the reject from screening is returned to the main stock flow, in which connection poor material circulates in the process. As a result of this, the runnability of the paper or board machine deteriorates and the quality of the end product decreases. Optimisation of fine screening and passing of the reject to the boiler of the mill offer a new possibility of optimising the quality of the end product in an economical manner.

In the following, the principle of the invention will be further described with reference to the appended figure which shows one system according to the invention for utilising waste.

Pre-treated waste is passed to a fibre separation process, which waste has been crushed and screened and from which non-combustible and undesirable fractions, such as metal, glass, stones, biowaste, etc. have been removed. The waste material is slushed in a continuous-operation high-consistency pulper 10, advantageously at a temperature of about 60 °C. A material stream Pl containing fibres suspended in water and a material stream Rl containing non-defibrable waste are discharged substantially continuously from the pulper 10. A screw conveyor 22 moves the reject fraction Rl from the pulper 10 into a combined washing and drying drum 24

of the reject. The reject is washed by means of circulation water Wo both on the screw conveyor 22 and in the washing drum 24, and fibre-containing washing waters F are returned to be mixed with the fibre suspension Pl.

The fibre fraction Pi taken out of the pulper 10 through a screen plate is passed to coarse screening 12, in which coarse impurities R2 and sand S2 which still remain in the fibre suspension are removed from it. The diameter of the holes in the screen plates used in the pulper 10 is 8-12 mm and most advantageously about 10 mm. In the coarse screening 12 of pulp, screen plates are used in which the diameter of holes is 2-4 mm and most advantageously about 3 mm. A correctly selected hole size is required in order that, on the one hand, the screen shall not retain an excessive amount of fibres and, on the other hand, centrifugal cleaning 14 provided after the coarse screening 12 should function sufficiently well.

In the centrifugal cleaning stage 14, mainly sand and other heavy matter S3 are separated from coarse-screened pulp P2. After the centrifugal cleaning 14, pulp P3 is passed to a fine screening and/or fractionating stage 16, from which reject R3 is passed to a dewatering stage 30 and accept P4 is passed to pulp washing and/or thickening stages 18. The washing of pulp can comprise either one or two stages.

In the last process stage 20, washed pulp P5 is compressed to a dry matter content of about 50 % and packed in transport containers for transport to a location of use situated at a reasonable distance.

Slushing reject R12 washed by means of the conveyor screw 22 and the reject drum 24 is passed to dewatering 26, which can be accomplished, for example, by means of a screw press. The reject R2 from the coarse screening 12 is processed together with the reject R12 coming from the slushing process. After dewatering, rejects R are passed to useful use, for example, to combustion.

Heavy sand-containing waste fractions Sl-S3 are also separated in the reject drum 24, in the coarse screening 12 of pulp and in the centrifugal cleaning 14, and

water is removed from these fractions in a processing stage 28, after which sand S can be transported to a landfill site or used as earth filling.

Rejects R3 produced in the fine screening and fractionating are passed to the dewatering 30, which can be accomplished, for example, by means of a drainage band press, after which the rejects are passed to combustion.

Waste waters are produced, on the one hand, when water is removed from the rejects and sand (filtrates Wi-Ws) and, on the other hand, in washing, thickening and compression of pulp (filtrates W4-W5). These contaminated water fractions W4-W5 are passed to clarification 32, from which fibre-containing sludge R4 is passed together with the reject R3 from the fine screening to the dewatering 30 and further to combustion. Clarified waste water W6 is passed further to a biological treatment stage 34, after which the cleaned water can be circulated to the beginning of the process for use as washing or dilution water in the pulper 10, in the coarse screening 12, on the screw conveyor 22 and/or in the reject drum 24.

Alternatively, part of the biologically treated waste water can be passed to additional treatment stages 36, which may be, for example, ultra-or nanofiltration. The clean water necessary for the water balance of the process is passed to the pulp washing stages 18.

In place of the pulper and the reject drum there may be a drum pulper, which, however, requires a larger space and higher investments than the arrangement shown in the figure. Moreover, removal of sand is more difficult to accomplish in the drum pulper alternative.