CN107990328A - A kind of garbage burning processing method and system - Google Patents
A kind of garbage burning processing method and system Download PDFInfo
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- CN107990328A CN107990328A CN201711251838.8A CN201711251838A CN107990328A CN 107990328 A CN107990328 A CN 107990328A CN 201711251838 A CN201711251838 A CN 201711251838A CN 107990328 A CN107990328 A CN 107990328A
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- rubbish
- garbage
- processing method
- stove
- burning processing
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/50—Control or safety arrangements
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
Abstract
The present invention provides a kind of garbage burning processing method and system, the present invention is adjusted the oven-like state that enters of rubbish, it is ensured that enter the stabilization of Lower heat value needed for stove rubbish by determining required draining amount;This method can adapt to the burning of all kinds of garbage combustion devices, it is ensured that burn must well, combustion process is stablized, with strong points, highly practical, versatile;The system of waste incineration is adapted to rubbish from stove and is adjusted to rubbish adaptation stove, it can be described as indicating a developing direction to get twice the result with half the effort for the development of waste incineration industry, development to country, society, and the improvement of natural environment can play an important role.For waste incineration processing system of the present invention compared with structure of furnace body, required simple in structure, project investment is few, adaptable, adapts to all kinds of incineration treatment of garbage, can meet the needs of any type grate furnace.
Description
Technical field
The present invention relates to technical field of waste treatment, in particular to a kind of garbage burning processing method and system.
Background technology
The fast development of various countries' industry, a large amount of concentrations of population, city is more and more, increasing, human living standard
Continuous improvement, cause tellurian rubbish more and more.The rapid growth of rubbish, is the problem of countries in the world face jointly,
Immeasurable social danger will be caused, growing domestic waste, which has become, restricts the important of China's economic development
One of problem.
According to statistics, the domestic waste that China produces every year in recent years has reached 1.5 hundred million tons, produces house refuse per year per capita
Amount reaches 440kg, and is constantly increased with annual 10% speed.
Beijing is even more rubbish rich and influential family, and the Domestic Refuse produced every year is 2.4 ten thousand tons, per capita rubbish growing amount
For:1400 kgs/year.
House refuse is handled in which way, it is necessary to reference to land resource, the density of population, economic and technical developing water equality
Many factors select.
Japan, Denmark and French waste incineration ratio account for 78%, 71% and 42% respectively.The U.S., Canada and Britain burn
Burning ratio is respectively 19%, 8% and 13%.It can be seen that the country enriched in land resource, based on landfill method, soil money
Source countries and regions in short supply, burning method occupy higher proportion, become the main means of processing municipal refuse.
Waste incineration and generating electricity is to realize garbage disposal minimizing, innoxious, recycling important means, in the world permitted
More countries are obtained for application.For China, government is clear and definite, economically developed eastern region and coastal big and medium-sized cities
The processing of rubbish is based on burning.
Due to habits and customs and the influence of the level of economic development, the domestic waste in China and external house refuse phase
Than calorific value is low, and moisture is big and unstable, the bad control of combustion process.The waste incinerator that early stage introduces, it is usually not acclimatized,
Main performance is that temperature is burnt not up, it is necessary to add auxiliary fuel.
In order to make low heat value, the rubbish of high-moisture can normal combustion, people frequently with technology be according to rubbish
Characteristic, improves the structure of incinerator, and main technological means has the length of increase drying section, increases the stirring intensity of Secondary Air
Deng.But for the garbage combustion device of each, always there is an optimal Lower heat value, the Lower heat value of rubbish is too low, burns
Burning is difficult to independently carry out, and the Lower heat value of rubbish is excessive, may cause the damage of garbage combustion device.
In general, the burning flow of rubbish is to have stored in melt pit 5-7 days mostly, the rubbish of preliminary draining after fermented
Rubbish, directly with grab bucket feeding incinerator in burn, the rubbish Lower heat value caused by this mode it is unstable, necessarily make
Into the fluctuation of combustion process and productivity, cause a series of variation of combustion parameters, add the difficulty of regulation and control, have impact on rubbish
The environment protecting of burning.
In view of this, it is special to propose the present invention.
The content of the invention
The dominant ideas of the present invention are by adjusting Lower heat value needed for entering stove rubbish, it is mutually fitted with garbage combustion device
Should.The present invention carries out refuse furnace pre-treatment, the oven-like state that enters of rubbish is adjusted, it is ensured that enter by determining required draining amount
The stabilization of Lower heat value needed for stove rubbish, just condition is created from the beginning of burning for the stabilization burning of rubbish;This method can
Adapt to the burning of all kinds of garbage combustion devices, it is ensured that burn must well, combustion process is stablized, with strong points, highly practical, versatility
By force;Stable garbage property, reduces the control difficulty of Refuse Incineration Process;Stable combustion state, is conducive to flue gas
Control, reduces the generation of harmful substance;The system of waste incineration from stove is adapted to rubbish it is adjusted to rubbish to adapt to stove, can be with
Say it is to indicate a developing direction to get twice the result with half the effort for the development of waste incineration industry, the development to country, society, and from
The improvement of right environment can play an important role.
In order to realize the above-mentioned purpose of the present invention, spy uses following technical scheme:
A kind of garbage burning processing method, it is characterised in that by determine rubbish higher calorific value, rubbish initial moisture content and
Lower heat value needed for entering stove rubbish, is calculated required draining amount.
Garbage burning processing method technological process of the present invention is simple, by determining that rubbish higher calorific value, rubbish are original aqueous
Measure and Lower heat value needed for entering stove rubbish, be calculated needed for draining amount, carry out refuse furnace pre-treatment, oven-like state entered to rubbish
It is adjusted, it is ensured that enter the stabilization of Lower heat value needed for stove rubbish, just created from the beginning of burning for the stabilization burning of rubbish
Condition;This method can adapt to the burning of all kinds of garbage combustion devices, it is ensured that burn must well, combustion process is stablized, with strong points, real
It is strong with property, it is versatile;Stable garbage property, reduces the control difficulty of Refuse Incineration Process;Stable combustion state, has
Beneficial to the control to flue gas, the generation of harmful substance is reduced;The system of waste incineration is adapted to rubbish from stove and is adjusted to rubbish
Adapt to stove, it may be said that be to indicate a developing direction to get twice the result with half the effort for the development of waste incineration industry, to country, society
Development, and the improvement of natural environment can play an important role.
Alternatively, by determining that total amount of heat, the wet basis total amount for entering stove rubbish and the rubbish of incineration firing releasing are original aqueous
Amount, is calculated rubbish higher calorific value.
Alternatively, by being squeezed to rubbish, rubbish initial moisture content is determined.
Alternatively, by determining the heat total value that garbage combustion device exports and the heat total value filled into, rubbish is calculated
The total amount of heat that rubbish burning is released.
Alternatively, the logistics capacity and stream temperature respectively exported by definite garbage combustion device, is calculated waste incineration
The heat total value of device output.
Alternatively, by determining that garbage combustion device inputs the reset condition parameter of material, waste incineration dress is calculated
Put the heat total value filled into.
Alternatively, by entering stove required by definite rubbish higher calorific value, rubbish initial moisture content and garbage combustion device
Lower heat value needed for rubbish, is calculated when rubbish enters stove and answers remaining water content;
Remaining water content and rubbish initial moisture content are answered when entering stove according to gained rubbish, required draining amount is calculated.
Alternatively, according to required draining amount, with reference to water logging device, draining operating parameter is determined.
Alternatively, draining operation is carried out to rubbish according to required draining amount, then is burned by garbage combustion device.
Using a kind of refuse burning system of above-mentioned garbage burning processing method.
Waste incineration processing system of the present invention enters the means of the state of garbage combustion device using control rubbish, with improvement
Structure of furnace body is compared, and required simple in structure, project investment is few, adaptable, adapts to all kinds of incineration treatment of garbage, can meet to appoint
A kind of what demand of grate furnace, makes any one incinerator to burn must well, it is ensured that the stabilization of combustion process.
Compared with prior art, beneficial effects of the present invention are:
Garbage burning processing method of the present invention is by determining rubbish higher calorific value, rubbish initial moisture content and entering stove rubbish institute
Lower heat value is needed, required draining amount is calculated, carries out refuse furnace pre-treatment, the oven-like state that enters of rubbish is adjusted, it is ensured that
Enter the stabilization of Lower heat value needed for stove rubbish, just condition is created for the stabilization burning of rubbish from the beginning of burning;This method energy
Enough adapt to the burning of all kinds of garbage combustion devices, it is ensured that burn must well, combustion process is stablized, with strong points, highly practical, versatility
By force;Stable garbage property, reduces the control difficulty of Refuse Incineration Process;Stable combustion state, is conducive to flue gas
Control, reduces the generation of harmful substance;The system of waste incineration from stove is adapted to rubbish it is adjusted to rubbish to adapt to stove, can be with
Say it is to indicate a developing direction to get twice the result with half the effort for the development of waste incineration industry, the development to country, society, and from
The improvement of right environment can play an important role.Waste incineration processing system of the present invention enters waste incineration using control rubbish
The means of the state of device, compared with improving structure of furnace body, required simple in structure, project investment is few, adaptable, adapts to all kinds of
Incineration treatment of garbage, can meet the needs of any type grate furnace, any one incinerator is burnt must well, it is ensured that burning
The stabilization of process.
Brief description of the drawings
, below will be to specific in order to illustrate more clearly of the specific embodiment of the invention or technical solution of the prior art
Embodiment or attached drawing needed to be used in the description of the prior art are briefly described, it should be apparent that, in describing below
Attached drawing is some embodiments of the present invention, for those of ordinary skill in the art, before not making the creative labor
Put, other attached drawings can also be obtained according to these attached drawings.
The incineration treatment of garbage process flow chart that Fig. 1 is provided for a kind of embodiment of the present invention.
Parameter extraction shows in the higher calorific value determination process for the rubbish that Fig. 2 is provided for a kind of embodiment of the present invention
It is intended to.
Fig. 3 determines flow chart for the draining parameter that a kind of embodiment of the present invention is provided.
Embodiment
Technical scheme is clearly and completely described below in conjunction with the drawings and specific embodiments, but
Be it will be understood to those of skill in the art that following described embodiment is part of the embodiment of the present invention, it is rather than whole
Embodiment, is merely to illustrate the present invention, and is not construed as limiting the scope of the invention.Based on the embodiments of the present invention, ability
Domain those of ordinary skill all other embodiments obtained without making creative work, belong to guarantor of the present invention
The scope of shield.The person that is not specified actual conditions in embodiment, the condition suggested according to normal condition or manufacturer carry out.Agents useful for same
It is the conventional products that can be obtained by commercially available purchase or production firm person is not specified in instrument.
In the description of the present invention, it is necessary to explanation, term " " center ", " on ", " under ", "left", "right", " vertical ",
The orientation or position relationship of the instruction such as " level ", " interior ", " outer " be based on orientation shown in the drawings or position relationship, merely to
Easy to describe the present invention and simplify description, rather than instruction or imply signified device or element must have specific orientation,
With specific azimuth configuration and operation, therefore it is not considered as limiting the invention.In addition, term " first ", " second ",
" the 3rd " is only used for description purpose, and it is not intended that instruction or hint relative importance.
In the description of the present invention, it is necessary to illustrate, unless otherwise clearly defined and limited, term " installation ", " phase
Even ", " connection " should be interpreted broadly, for example, it may be being fixedly connected or being detachably connected, or be integrally connected;Can
To be mechanical connection or be electrically connected;It can be directly connected, can also be indirectly connected by intermediary, Ke Yishi
Connection inside two elements.For the ordinary skill in the art, with concrete condition above-mentioned term can be understood at this
Concrete meaning in invention.
Rubbish in waste incinerator can the major influence factors of normal combustion be calorific value into incineration furnace garbage, state
Family can carry out the minimum Lower heat value (minimum threshold) of incineration treatment of garbage for this provision, and can rubbish enter waste incinerator
The judge index for carrying out burning disposal only has one data of Lower heat value.
The higher calorific value (butt) of rubbish can release after referring to the combustible completely burned of the Unit Weight in rubbish
Heat, higher calorific value only it is related with the physical make-up of rubbish.
The component of usual rubbish can not possibly control, and therefore, control the water content of rubbish, be control rubbish Lower heat value
Unique controllable factor.
In stove in terms of processing, by development for many years, the continuous adjustment to waste incineration furnace structure, either import
The type of furnace, or the domestic type of furnace, the characteristics of all substantially having adapted to domestic rubbish, can normal combustion power generation, it is but right
It is excessive in the fluctuation of moisture, still low in the presence of the thermal efficiency of burning, the adverse conditions such as combustion process is unstable, due to water
Divide too high levels, cause the rubbish that Lower heat value is too low, still can not normal combustion.
Processing is to allow stove to adapt to rubbish in the stove of waste incineration, but since the composition of rubbish is ever-changing, it is desirable to one
Determine that the type of furnace meets different types of rubbish, be totally impossible.Phase shaft striving direction is concentrated in the processing of stokehold, to rubbish
The characteristic of rubbish is transformed, and is made different types of rubbish with optimum state, is burned into stove, will greatly improve rubbish and burn
The hot working effect of burning.
Meanwhile the stokehold processing of rubbish, relative to the improvement of the type of furnace, small with difficulty, flexibility is big, adaptable, is one
Kind takes into account the technique direction with province.
The R&D intensity of refuse furnace pre-treatment is increased, will significantly improve the burning condition of rubbish, reduce and rubbish is burnt
The dependence of the type of furnace is burnt, reduces the control difficulty of Refuse Incineration Process.The emphasis of garbage burning processing method of the present invention is to pass through
Control the water content of rubbish, adjust the Lower heat value of rubbish, make can not the rubbish of normal combustion transform into can be with combustion refuse.
Ensure rubbish Lower heat value, the effect of burning can be improved, improve the thermal efficiency of burning, have to the utilization rate for improving resource real
Really meaning.
A kind of garbage burning processing method proposed by the present invention, passes through specific stokehold treatment process, it is ensured that burn into rubbish
The rubbish for burning stove has stable Lower heat value, its technological process can be found in shown in Fig. 1.
The key link of garbage burning processing method of the present invention is operated by draining, and quantitative control enters waste incineration
The Lower heat value of the rubbish of stove.Need to try to achieve the state parameter of rubbish for this online.Determine that the stokehold relevant parameter of draining amount can
Carried out by the steps.
(a), the higher calorific value of rubbish is definite:
The caloric value of industrial measure fuel usually use thermostatic type calorimeter, can not on-line measurement, it is contemplated that present invention survey
Amount mainly provides support for practical operation, therefore can be by the real background process for burning data, that is, passing through the state of burning
Data, try to achieve the data of the relatively accurate online calorific value of rubbish.The hot-fluid of known spam incinerator has 4 outlets:Hot gas flows out
Mouthful, hot steam outlet, hot slag outlet and furnace body heat dissipation.The sensible heat that hot entrance is brought into for water, air and fuel, that is, the heat filled into
Amount.If the logistics capacity and stream temperature of each outlet are tried to achieve respectively, you can try to achieve the heat total value of waste incinerator output;Such as
Fruit tries to achieve the reset condition parameter of waste incinerator input material (including water, air and fuel) respectively, you can tries to achieve rubbish and burns
The heat total value that stove fills into is burnt, both subtract each other the total amount of heat that i.e. period incineration firing is released for this.
And the wet basis weight of the interior crude waste into waste incinerator is known during this period, if it is possible to survey at the same time
Obtain rubbish initial moisture content, you can push away to obtain rubbish higher calorific value.
The extraction of Fig. 2 figuratively bright parameters, 1. position measures the flow and temperature of the flue gas of discharge, position in figure
2. 3. the temperature and flow of measurement output steam, position measure the temperature and flow of deslagging, 4. position measures the temperature of furnace wall, folding
Radiation loss is calculated, 5. position measures the temperature and flow of the air blasted, 6. position is measured into the total of the rubbish of incinerator
Amount.
This reckoning result necessarily has certain deviation, but as the practical application in engineering, not necessarily gets parms
Actual value, as long as the parameter associated with absolute value can be obtained as control parameter, you can make process in controllable state
Lower progress.
(b), the on-line determination of rubbish initial moisture content:
The measure of rubbish initial moisture content, is usually all heating power method, i.e., by the method for heating, evaporates contained in rubbish
Moisture, try to achieve the content of moisture by weighing, this method, sampling trouble, due to the limited mass of test specimen, measures
Result offset it is also big, it is longer to test the time of cost, can not application on site.Therefore the specific embodiment of the invention proposes
A kind of method measurement water content of limit squeezing, applies rubbish larger pressure, such as 20MPa, makes water contained in rubbish
Point, almost excluded completely, rubbish initial moisture content can be tried to achieve by measuring displacement.
The pressure applied to rubbish can carry out online, when pressure continues to increase, be until almost no longer there is moisture to leach
Only, draining amount at this time is tried to achieve.
The weight for adding crude waste is known, you can obtains rubbish initial moisture content.
Although under the pressure of experiment, discharged without moisture, at this time, certain moisture for also having remaining in rubbish, due to
Absolute magnitude is seldom, can ignore in engineering.
It is of course also possible to tried to achieve in advance by experiment under test pressure, the quantity of Residual water, when being calculated,
It is modified, then result can be more accurate.
(c), Lower heat value needed for stove rubbish is entered:
The standard state that this numerical value is waste incinerator just to be had determined in design, is datum, when entering stove rubbish
During with such a status data, waste incinerator is by with optimal combustion state, and production capacity is big, flameholding, in combustion gas
Nuisance can be effectively controlled, the safety in operation of waste incinerator is good, and the control of combustion process is relatively easy.
(d), required draining amount is definite:
According to the definition of Lower heat value (wet basis):It is aqueous that rubbish Lower heat value refers to that rubbish higher calorific value subtracts institute in rubbish
The heat for dividing gasification to absorb, i.e., utilizable heat after incineration firing.It is aware of rubbish higher calorific value, it is known that enter stove rubbish
Required Lower heat value, the heat that when unit moisture vaporization absorbs is the intrinsic physical characteristic of moisture, can by charging temperature and
The temperature of discharge vapor determines.It is aware of above-mentioned data, you can when obtaining into stove, remaining water content is answered in rubbish.
This is a very simple mathematical problem, it is known that the moisture in crude waste, it is known that can be retained in rubbish
Moisture, required draining amount is known that naturally.
(e), draining operating parameter is definite:
According to the required draining amount tried to achieve, you can be translated into the draining operating parameter of water logging device, such as extruding force, is squeezed
Press residence time etc., commander's water logging device action, completes the draining operation needed.
Necessary state parameter is obtained using sensor, passes through the numerical computations on backstage, you can is online to obtain rubbish original
Beginning water content, rubbish higher calorific value, required draining amount and the draining operating parameter of control water logging device operation, as shown in Figure 3
Flow chart.The draining ability of charging gear can be with on-line tuning, this can also provide soft or hard for the intelligent control of combustion process
Part basis.
Using the internal pressure formed during rubbish is fed into stove, as dewatering means, make charging simple before this
Operation, becomes charging, dehydration, seals three-in-one operating process.
Garbage burning processing method of the present invention, is handled by specific stokehold, and the oven-like state that enters of rubbish is adjusted, can be adopted
With intelligentized mode of operation, it is ensured that enter the stabilization of Lower heat value needed for stove rubbish, be just the stabilization of rubbish from the beginning of burning
Burning creates condition.Compared with waste incineration system before this, garbage burning processing method of the present invention and system at least have
Following advantage:
1), when improving incineration firing state, using garbage burning processing method of the present invention and system, burnt with improving rubbish
Burning furnace body constructs in itself to be compared, and required simple in structure, project investment is few;
2), garbage burning processing method and system suitability of the present invention are strong, can meet the needs of any type grate furnace,
Any one incinerator is set to burn must well, it is ensured that the stabilization of combustion process.
3), the extracting mode of data can be closely coupled with the combustion process of rubbish, and method is simple, with strong points, practicality
By force, it is versatile.
4), the garbage property stablized, reduces the control difficulty of Refuse Incineration Process.
5), the combustion state stablized, is conducive to the control to flue gas, reduces the generation of harmful substance.
In short, the system of waste incineration is adapted to rubbish by the present invention from stove is adjusted to rubbish adaptation stove, it may be said that is
A developing direction to get twice the result with half the effort is indicated for the development of waste incineration industry.
Although being illustrated and the invention has been described with specific embodiment, but it will be appreciated that various embodiments above is only used
To illustrate technical scheme, rather than its limitations;It will be understood by those of ordinary skill in the art that:Without departing substantially from this hair
In the case of bright spirit and scope, it can modify to the technical solution described in foregoing embodiments, or to wherein
Some or all of technical characteristic carries out equivalent substitution;And these are changed or are replaced, the essence of appropriate technical solution is not made
Depart from the scope of various embodiments of the present invention technical solution;It is, therefore, intended that include belonging to the present invention in the following claims
In the range of all these substitutions and modifications.
Claims (10)
1. a kind of garbage burning processing method, it is characterised in that by determining rubbish higher calorific value, rubbish initial moisture content and entering
Lower heat value needed for stove rubbish, is calculated required draining amount.
2. a kind of garbage burning processing method according to claim 1, it is characterised in that by determining that incineration firing is released
Total amount of heat, enter the wet basis total amount and rubbish initial moisture content of stove rubbish, rubbish higher calorific value is calculated.
3. a kind of garbage burning processing method according to claim 1 or 2, it is characterised in that by pressing rubbish
Squeeze, determine rubbish initial moisture content.
4. according to a kind of any garbage burning processing method of claim 2, it is characterised in that by determining waste incineration
The heat total value of device output and the heat total value filled into, are calculated the total amount of heat of incineration firing releasing.
5. a kind of garbage burning processing method according to claim 4, it is characterised in that by determining garbage combustion device
The logistics capacity and stream temperature respectively exported, is calculated the heat total value of garbage combustion device output.
6. a kind of garbage burning processing method according to claim 4, it is characterised in that by determining garbage combustion device
The reset condition parameter of material is inputted, the heat total value that garbage combustion device fills into is calculated.
7. a kind of garbage burning processing method according to claim 2, it is characterised in that by determining the high-order heat of rubbish
Required by value, rubbish initial moisture content and garbage combustion device enter stove rubbish needed for Lower heat value, rubbish is calculated and enters stove
When answer remaining water content;
Remaining water content and rubbish initial moisture content are answered when entering stove according to gained rubbish, required draining amount is calculated.
A kind of 8. garbage burning processing method according to claim 1, it is characterised in that according to required draining amount, with reference to
Water logging device, determines draining operating parameter.
9. a kind of garbage burning processing method according to claim 1, it is characterised in that according to required draining amount to rubbish
Draining operation is carried out, then is burned by garbage combustion device.
10. using a kind of refuse burning system of any garbage burning processing methods of claim 1-9.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109781785A (en) * | 2019-01-31 | 2019-05-21 | 成都市兴蓉再生能源有限公司 | A kind of sludge-rubbish collaboration burning mixed material heating-value determination method |
CN112183883A (en) * | 2020-10-19 | 2021-01-05 | 浦湘生物能源股份有限公司 | Method and system for prejudging incineration calorific value of household garbage and incineration system |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4566461B2 (en) * | 2001-06-11 | 2010-10-20 | 住友重機械エンバイロメント株式会社 | Sludge supply equipment |
CN106090933A (en) * | 2016-06-17 | 2016-11-09 | 北京高能时代环境技术股份有限公司 | The method and device of one way of life waste incineration and generating electricity |
CN106897492A (en) * | 2017-01-19 | 2017-06-27 | 苏州西热节能环保技术有限公司 | A kind of quick calculation method of burning power plant fuel Lower heat value |
-
2017
- 2017-12-01 CN CN201711251838.8A patent/CN107990328A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4566461B2 (en) * | 2001-06-11 | 2010-10-20 | 住友重機械エンバイロメント株式会社 | Sludge supply equipment |
CN106090933A (en) * | 2016-06-17 | 2016-11-09 | 北京高能时代环境技术股份有限公司 | The method and device of one way of life waste incineration and generating electricity |
CN106897492A (en) * | 2017-01-19 | 2017-06-27 | 苏州西热节能环保技术有限公司 | A kind of quick calculation method of burning power plant fuel Lower heat value |
Non-Patent Citations (1)
Title |
---|
李登新: "《固体废物处理与处置》", 31 July 2014 * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109781785A (en) * | 2019-01-31 | 2019-05-21 | 成都市兴蓉再生能源有限公司 | A kind of sludge-rubbish collaboration burning mixed material heating-value determination method |
CN109781785B (en) * | 2019-01-31 | 2021-06-15 | 成都市兴蓉再生能源有限公司 | Method for measuring heat value of sludge-garbage co-incineration mixed material |
CN112183883A (en) * | 2020-10-19 | 2021-01-05 | 浦湘生物能源股份有限公司 | Method and system for prejudging incineration calorific value of household garbage and incineration system |
CN112183883B (en) * | 2020-10-19 | 2023-12-15 | 浦湘生物能源股份有限公司 | Incineration heat value prejudging method and system for household garbage and incineration system |
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