[0001] The present invention relates to a paper capable of being completely combusted with
a less amount of combustion residues or cinders, and being inhibited from generating
harmful substances, upon incineration thereof.
[0002] Hitherto, human lives have a close relationship to papers to such an extent that
the consumption of papers would indicate a degree of culture of the country. At present,
papers have been widely used in various applications such as books, printed matters,
wrapping materials, industrial materials or the like. There is a recent tendency that
the consumption of papers is more and more increased. With such a tendency, various
papers having new functions have been successively developed and marketed. Although
various studies have been conducted to improve functions and performances of papers,
there are almost no studies for developing those papers suitable for waste disposal
after use. Main reasons therefor are that the disposal of papers is not considered
to cause any environmental pollution since the papers are inherently made from wood
pulps as main raw materials; the papers can be naturally decomposed when buried in
the earth for a long period time; and the papers are relatively easy to burn, and
free from the generation of harmful substances upon incineration thereof since the
papers are made from the substantially same material as wood.
[0003] On the other hand, in waste disposal treatments, especially in waste incineration
treatments, the discharge of exhaust gases containing carbon monoxide and/or nitrogen
oxides and the generation of dioxins cause significant social problems. In order to
solve these problems, earnest studies have been directed to the reduction of wastes
and the improvements in incinerators and incineration methods. Simultaneously, various
material makers have made efforts for developing materials which show excellent combustion
properties and are prevented from causing incomplete combustion and generation of
harmful substances upon incineration, from such a viewpoint that these materials must
be inevitably incinerated after use. For example, there have been proposed a plastic
waste bag made from a thermoplastic resin film containing specific iron oxide particles
having a good combustion-promoting capability in an amount of 0.1 to 20.0% by weight
(Japanese Patent Application Laid-Open (KOKAI) No. 7-257594(1995)). However, such
proposals have been limited to plastic waste bags only, and there have not been studied
any method of improving combustion properties of papers which occupy a considerable
part of wastes treated in an incinerator.
[0004] Thus, conventionally, the problems caused upon incineration of papers have not positively
been studied for such a reason that the papers are considered to be identical in nature
to that of natural wood materials. However, when many stacked papers, e.g., books,
pamphlets, catalogues or the like are incinerated, there is a tendency that only the
surface portion of the stacked papers can be burned and the inside portion thereof
remains unburned. In such a case, there also arises the problem due to incomplete
combustion. Further, in the case where chlorine-based compounds used in paper making
processes or lignin contained in wood pulps still remain in papers, there might be
caused such a problem that precursors of dioxin are produced from these substances
upon incineration of the papers.
[0005] As a result of the present inventors' earnest studies for solving the above problems,
it has been found that by coating a paper with an iron compound catalyst comprising
iron oxide hydroxide particles or iron oxide particles having an average particle
size of 0.01 to 2.0 µm, the obtained paper can be completely combusted with a less
amount of combustion residues or cinders and inhibited from generating harmful substances
upon incineration thereof. The present invention has been attained on the basis of
this finding.
[0006] It is an object of the present invention to provide a paper capable of not only maintaining
inherent functions as papers, but also being completely burned and inhibited from
generating harmful substances upon incineration thereof after use.
[0007] To accomplish the aim, in a first aspect of the present invention, there is provided
a paper having an iron compound catalyst in an amount of 0.1 to 20% by weight,
said iron compound catalyst comprising iron oxide hydroxide particles or iron oxide
particles having an average particle size of 0.01 to 2.0 µm; and having a catalytic
activity capable of converting not less than 15% by weight of carbon monoxide into
carbon dioxide, when 2.8 X 10
-4 mole of iron oxide particles obtained by heat-treating said iron compound catalyst
at a temperature of 800°C for 15 minutes in air, are instantaneously contacted with
6.1 X 10
-7 mole of carbon monoxide at a temperature of 250°C at a space velocity (SV) of 42,400
h
-1 in an inert gas atmosphere using a pulse catalytic reactor.
[0008] The present invention will now be described in detail below.
[0009] The iron compound catalyst used in the present invention has an average particle
size of usually 0.01 to 2.0 µm, preferably 0.05 to 1.0 µm, more preferably 0.05 to
0.5 µm.
[0010] When the average particle size of the iron compound catalyst is less than 0.01 µm,
the iron compound catalyst be difficult to handle, and further the yield of paper-making
process may be deteriorated. When the average particle size of the iron compound catalyst
is more than 2.0 µm, the obtained paper may be deteriorated in surface smoothness.
In addition, since a specific surface area of such an iron compound catalyst becomes
small, the oxidation activity thereof for converting carbon monoxide into carbon dioxide
may be also deteriorated, thereby failing to attain the aimed effect of causing the
obtained paper to be completely combusted.
[0011] The iron compound catalyst used in the present invention has a BET specific surface
area value of usually 0.2 to 200 m
2/g, preferably 0.5 to 200 m
2/g, more preferably 0.5 to 100 m
2/g.
[0012] The iron compound catalyst used in the present invention comprises at least one material
selected from the group consisting of iron oxide hydroxide particles such as goethite
particles, akaganeite particles and lepidocrocite particles, and iron oxide particles
such as hematite particles, maghemite particles and magnetite particles. Among these
materials, goethite particles is preferred.
[0013] The shape of the iron oxide hydroxide particles or iron oxide particles constituting
the iron compound catalyst used in the present invention is a granular shape, a spherical
shape, a spindle shape, an acicular shape or the like. Among these particles, the
use of spindle-shaped particles is preferred.
[0014] The iron compound catalyst used in the present invention has a phosphorus content
of usually 0.0001 to 0.02% by weight, preferably 0.0001 to 0.01% by weight, more preferably
0.0001 to 0.005% by weight. When the phosphorus content is more than 0.02% by weight,
the catalyst poison ability of the phosphorus may become large, so that the oxidation
activity for converting carbon monoxide into carbon dioxide may be deteriorated, thereby
failing to obtain the aimed effect of causing the obtained paper to be completely
combusted. Meanwhile, although the phosphorus content is preferably as low as possible,
it is difficult to industrially produce such an iron compound catalyst having a phosphorus
content of less than 0.0001% by weight.
[0015] The iron compound catalyst used in the present invention has a sulfur content of
usually 0.001 to 0.3% by weight, preferably 0.001 to 0.1% by weight, more preferably
0.001 to 0.07% by weight. When the sulfur content is more than 0.3% by weight, the
catalyst poison ability of the sulfur may become large, so that the oxidation activity
for converting carbon monoxide into carbon dioxide may be deteriorated, thereby failing
to obtain the aimed effect of causing the obtained paper to be completely combusted.
Meanwhile, although the sulfur content is preferably as low as possible, it is difficult
to industrially produce such an iron compound catalyst having a sulfur content of
less than 0.001% by weight.
[0016] The iron compound catalyst used in the present invention has a sodium content of
usually 0.001 to 0.3% by weight, preferably 0.001 to 0.2% by weight, more preferably
0.001 to 0.15% by weight. When the sulfur content is more than 0.3% by weight, the
catalyst poison ability of the sodium may become large, so that the oxidation activity
for converting carbon monoxide into carbon dioxide may be deteriorated, thereby failing
to obtain the aimed effect of causing the obtained paper to be completely combusted.
Meanwhile, although the sodium content is preferably as low as possible, it is difficult
to industrially produce such an iron compound catalyst having a sodium content of
less than 0.001% by weight.
[0017] The iron compound catalyst used in the present invention exhibits a catalytic activity
capable of converting usually not less than 15% by weight, preferably not less than
18% by weight, more preferably not less than 20% by weight of carbon monoxide into
carbon dioxide, when 2.8 × 10
-4 mole of iron oxide particles obtained by heat-treating said iron compound catalyst
at a temperature of 800°C for 15 minutes in air, are instantaneously contacted with
6.1 × 10
-7 mole of carbon monoxide at a temperature of 250°C at a space velocity (SV) of 42,400
h
-1 in an inert gas atmosphere using a pulse catalytic reactor. The upper limit of the
catalytic activity for converting the carbon monoxide into carbon dioxide is 50% by
weight.
[0018] As the paper used in the present invention, a paper produced by the followings may
be exemplified.
[0019] Ground pulps, alkaline pulps, sulfite pulps, chemical ground pulps and semi-chemical
ground pulps are obtained from plant-based raw materials such as wood chips, straws,
reed, bagasse or bamboo, waste papers or rags, which wood chips may be optionally
subjected to pre-treatments such as bleaching treatment with chlorine, hypochlorite,
sodium chlorite, chlorine dioxide, hydrogen peroxide, sodium peroxide or the like,
and screening treatment. At least one material selected from the above-described pulps
is appropriately hammer-crushed (after being mixed together, if two or more pulp materials
are used) in order to vary or modify a fiber shape and colloidal property thereof.
The hammer-crushed materials are further mixed with colorants, sizing agents or fillers
to prepare a paper material. The paper material is then subjected to a paper-making
process and then to finishing treatment, thereby producing the paper.
[0020] The paper of the present invention has the above iron compound catalyst in an amount
of usually 0.1 to 20.0% by weight, preferably 0.5 to 10.0% by weight, more preferably
0.5 to 5.0% by weight based on the weight of the paper of the present invention. When
the amount of the iron compound catalyst is less than 0.1% by weight, it may be difficult
to obtain the aimed effect of the present invention. When the amount of the iron compound
catalyst is more than 20.0% by weight, the obtained paper may be considerably deteriorated
in coloring property, strength and surface smoothness.
[0021] The paper of the present invention has a combustion velocity of preferably not more
than 3.0 minutes, more preferably not more than 2.5 minutes; an amount of the residual
combustible components of preferably not more than 10.0 % by weight, more preferably
not more than 9.0 % by weight based on the weight of the initially charged combustible
components; and a low-temperature combustion property of preferably not more than
530°C, more preferably not more than 520°C, which are measured by the combustion test
described in the Example 1.
[0022] Next, the process for producing the iron compound catalyst used in the present invention
is described.
[0023] Among the iron compound catalysts used in the present invention, the goethite particles
may be produced, for example, by passing an oxygen-containing gas such as air through
a suspension containing a ferrous iron-containing precipitate such as hydroxides of
iron or iron carbonates which are produced by reacting a ferrous salt with at least
one compound selected from the group consisting of alkali hydroxides, alkali carbonates
and ammonia. In case of using ferrous sulfate, the obtained goethite particles are
desired to be subject to purifying treatment, i.e. sufficient washing treatment with
water in order to lessen the sulfur content.
[0024] Examples of the ferrous salts may include ferrous nitrate, ferrous acetate, ferrous
oxalate, ferrous sulfate or the like. Among these ferrous salts, the use of ferrous
nitrate, ferrous acetate, ferrous oxalate, etc. which are free from elements acting
as catalyst poisons such as phosphorus, sulfur or the like, is preferred.
[0025] Examples of the alkali hydroxides may include sodium hydroxide, potassium hydroxide,
calcium hydroxide, magnesium hydroxide or the like. Examples of the alkali carbonates
may include sodium carbonate, potassium carbonate or the like.
[0026] Among the iron compound catalysts used in the present invention, the hematite particles
may be produced, for example, by heat-dehydrating or heat-treating the above obtained
goethite particles at a temperature of usually 200 to 800°C in air; the magnetite
particles may be produced, for example, by heat-reducing the above obtained hematite
particles at a temperature of usually 300 to 800°C in a reducing atmosphere; and the
maghemite particles may be produced, for example, by heat-oxidizing the above obtained
magnetite particles at a temperature of usually 200 to 600°C in air.
[0027] In the production of the iron compound catalyst used in the present invention, it
is necessary to lessen the contents of phosphorus, sulfur and sodium as catalyst poisons
to not more than predetermined amounts. More specifically, the contents of phosphorus,
sulfur and sodium should be reduced by avoiding the use of sodium hexametaphosphate
usually added as a sintering preventive upon heat-calcination step, and by removing
sulfur ions derived from the raw ferrous materials or sodium ions derived from alkali
hydroxides or the alkali carbonates by means of purification treatments such as washing
with water or the like.
[0028] The paper of the present invention has the above iron compound catalyst in an amount
of usually 0.1 to 20.0% by weight, preferably 0.5 to 10.0% by weight, more preferably
0.5 to 5.0% by weight based on the weight of the paper of the present invention. When
the amount of the iron compound catalyst is less than 0.1% by weight, it may be difficult
to obtain the aimed effect of the present invention. When the amount of the iron compound
catalyst is more than 20.0% by weight, the obtained paper may be considerably deteriorated
in coloring property, strength and surface smoothness.
[0029] The paper of the present invention can be produced by the following method.
[0030] As the raw material of the paper, there may be usually used, for example, at least
one material selected from the group consisting of ground pulps, alkaline pulps, sulfite
pulps, chemical ground pulps, semi-chemical ground pulps and the like. These pulps
are obtained from plant-based raw materials such as wood chips, straws, reed, bagasse
or bamboo, waste papers or rags, which wood chips may be optionally subjected to pre-treatments
such as bleaching treatment with chlorine, hypochlorite, sodium chlorite, chlorine
dioxide, hydrogen peroxide, sodium peroxide or the like, and screening treatment.
At least one material selected from the above-described pulps is appropriately hammer-crushed
(after being mixed together, if two or more pulp materials are used) in order to vary
or modify a fiber shape and colloidal property thereof. The hammer-crushed materials
are further mixed with colorants, sizing agents or fillers to prepare a complete paper
material. The paper material is then subjected to a paper-making process and then
to finishing treatment, thereby producing the paper. The iron compound catalyst may
be introduced into the paper material by replacing a part or whole of the colorants
and/or fillers used.
[0031] Alternatively, in the case where the aimed paper is a coated paper, the iron compound
catalyst may be added to a coating solution or an adhesive, and then the obtained
coating solution or adhesive is coated on the paper to produce a coated paper. Further,
in the case of the laminated paper, the iron compound catalyst may be incorporated
into plastic films to be laminated on the paper. However, the present invention is
not limited to those papers produced by the above-specified processes, and may be
extensively applied to various kinds of papers and various application fields.
[0032] The reason why the paper having the iron compound catalyst according to the present
invention can exhibit excellent combustion properties, is considered by the present
inventors as follows.
[0033] The combustion mechanism of the present invention is considered as follows. That
is, iron atoms present on the surface of each iron compound catalyst particle are
initially kept stable by surface hydroxyl groups capable of dissociating and adsorbing
water. When these hydroxyl groups undergo dehydration by the heating in the combustion
process, coordination-unsaturated iron ions and oxygen ions are produced. Then, the
thus produced coordination-unsaturated active sites can activate oxygen due to the
oxygen adsorption thereto caused during the combustion process, and show a good catalytic
activity in a series of reaction steps such as dehydrogenation reaction from organic
substances or the like, thereby exhibiting a good combustion-promoting effect.
[0034] The paper having the iron compound catalyst according to the present invention has
the following advantages. That is, when the paper is incinerated after its inherent
use as paper, the iron compound catalyst can exhibit a good combustion-promoting effect
such that the paper can be completely combusted with less amounts of combustion residues
(cinders) and residual ashes without significant deterioration of combustion efficiency
even in the case where an incinerator is operated under low-temperature and low-oxygen
concentration conditions which are considered to be effective for reducing the amount
of NOx and preventing damage to the incinerator.
[0035] Further, even when chlorine-based compounds used in paper-making process or lignin
contained in wood pulps still remain in the paper, it is possible to inhibit the production
of dioxin precursors upon incineration.
EXAMPLES
[0036] The present invention is described in more detail by Examples and Comparative Examples,
but the Examples are only illustrative and, therefore, not intended to limit the scope
of the present invention.
[0037] Various properties were measured by the following methods.
[0038] (1) The
average particle size of the iron compound catalyst was expressed by the average of values measured from
an electron micrograph. The
specific surface area of the iron compound catalyst was expressed by the value measured by a BET method.
[0039] (2) The
contents of phosphorus and sodium contained in particles constituting the iron compound catalyst were expressed by
the values measured by an inductively coupled plasma atomic emission spectrometer
(SPS-4000 Model, manufactured by Seiko Denshi Kogyo Co., Ltd.).
[0040] (3) The
content of sulfur contained in particles constituting the iron compound catalyst was expressed by the
value measured by a Carbon-Sulfur Analyzer (EMIA-2200 Model, manufactured by Horiba
Seisakusho Co., Ltd.).
[0041] (4) The
catalytic activity of the iron compound catalyst was measured by the following method.
[0042] That is, 2.8 × 10
-4 mole of iron oxide particles (α-Fe
2O
3) obtained by heat-treating the iron compound catalyst at a temperature of 800°C for
15 minutes in air, were instantaneously contacted with 6.1 × 10
-7 mole of carbon monoxide at a temperature of 250°C at a space velocity (SV) of 42,400
h
-1 in an inert gas atmosphere using a pulse catalytic reactor. The catalytic activity
of the iron compound catalyst was expressed by the percentage (conversion) of carbon
monoxide converted into carbon dioxide in the above process.
[0043] Here, the space velocity (SV) represents the value obtained by dividing a flow rate
of the reaction gas by a volume of the catalyst, and is expressed by a unit of an
inverse number of time (h
-1).
[0044] The pulse catalytic reactor used comprises a reactor portion and a gas chromatography
portion which is constituted by Gas Chromatography GC-16A (manufactured by Shimadzu
Seisakusho Co., Ltd.).
[0045] Meanwhile, the above evaluation method was conducted by referring to methods described
in the literatures (e.g., R. J. Kobes, et al, "J. Am. Chem. Soc.",
77, 5860(1955) or "Experimental Chemistry II-Reaction and Velocity" edited by Chemical
Society of Japan and published by Maruzen, Tokyo (1993)).
Example 1:
<Production of paper>
[0046] A filter paper (weight: 0.50 g; No.2, manufactured by Advantec Toyo Co., Ltd.) for
laboratory chemical experiments was coated with a coating solution prepared by dispersing
1.0 g of goethite particles as iron compound catalyst A (average particle size: 0.25
µm; phosphorus content: 0.002 % by weight; sulfur content: 0.05 % by weight; sodium
content: 0.08 % by weight; BET specific surface area: 85 m
2/g; catalytic activity by the above evaluation method: 20 %) in 100 ml of water, and
then dried in air at a temperature of 60°C for 1 hour, thereby obtaining a paper having
5.0 mg of the iron compound catalyst (1.0 % by weight).
<Combustion test>
[0047] 10 mg of the thus obtained paper having the iron compound catalyst was weighed, and
heated at a temperature rise rate of 10°C/minute in air supplied at a flow rate of
300 ml/minute. The change in weight of the paper during the heating treatment was
measured by a thermogravimetric analyzer (manufactured by Seiko Denshi Kogyo Co.,
Ltd.). The combustion properties of the paper were evaluated by measuring the combustion
velocity, amount of residual combustible components and low-temperature combustion
property.
[0048] Here, the combustion velocity represents the time required from the initiation of
abrupt reduction in weight up to the termination thereof (the combustion of the paper
is considered to take place during such a time).
[0049] The amount of residual combustible components (it is considered that the lower the
value, the smaller the amount of combustion residues (cinders) or residual ashes after
the incineration), is expressed by the residual weight percentage (wt%) calculated
as the percentage of combustible components which still remain unburned upon the termination
of abrupt reduction in weight, based on the weight of initially charged combustible
components.
[0050] The low-temperature combustion property (which is considered to be a temperature
at which organic substances are completely burned out) is expressed by the temperature
at which the reduction in weight is no longer caused.
[0051] The combustion velocity was 2.1 minutes; the amount of residual combustible components
was 7.5 % by weight; and the low-temperature combustion property was 495 °C.
Examples 2 to 7 and Comparative Examples 1 to 3:
[0052] The same procedure as defined in Example 1 was conducted except that the filter paper
for laboratory chemical experiments was surface-coated with coating solutions respectively
containing the iron compound catalysts shown in Table 1, thereby obtaining papers
each containing the predetermined amount of the iron compound catalyst in the filter
paper.
[0053] The thus obtained papers were subjected to the combustion test by the same method
as defined in Example 1. The combustion properties of the obtained papers are shown
in Table 2.