Controlling a waste combustion process

Information

  • Patent Application
  • 20080053348
  • Publication Number
    20080053348
  • Date Filed
    March 06, 2007
    17 years ago
  • Date Published
    March 06, 2008
    16 years ago
Abstract
The present invention is concerned with a method of controlling on-line the steam output of a waste incineration plant that is fed with waste of varying composition. Process or system quantities (u2, u3, xGC, xLL, w0) are measured repeatedly, at different times during operation of the plant, and a relation with linear parameters (θi) as coefficients of non-linear expressions (φi) of the process quantities is established by evaluating said measurements. From this relation, an optimal waste feed rate to obtain a desired steam output ({dot over (M)}steam) is determined and applied to a waste feed actuator of the waste incineration plant.
Description

BRIEF DESCRIPTION OF THE DRAWINGS

The subject matter of the invention will be explained in more detail in the following text with reference to preferred exemplary embodiments which are illustrated in the attached drawings, in which:



FIG. 1 schematically shows a waste incineration plant;



FIG. 2 depicts a flow chart of a method of determining a waste feed rate, and



FIG. 3 is a graph showing a controlled steam flow against the steam flow set point.





The reference symbols used in the drawings, and their meanings, are listed in summary form in the list of reference symbols. In principle, identical parts are provided with the same reference symbols in the figures.


DETAILED DESCRIPTION OF PREFERRED EMBODIMENTS


FIG. 1 schematically shows a waste incineration plant with a number of basic components. An input feed mechanism or actuator 10 introduces the municipal or industrial waste, garbage or other debris into a furnace 11 and places the former on a supported movable grate 12 at a particular waste feed rate w0, thereby forming a waste bed. The grate 12 generally comprises some oppositely moving grate plates to spread and mix the waste and forward it along the grate 12. Auxiliary burners 13 may be provided in order to start or support the combustion processes. The combusted flue gases are collected in a flue gas tract or flue gas channel 14 upstream of the furnace 11 and guided to a boiler or steam generator 15.


Without loss of generality, the incineration process is divided into four zones to be serially traversed by the waste: Drying zone 20, first combustion zone for pyrolysis and gasification/volatilization 21, residual zone for char oxidation or solid combustion 22, and ash treatment/sintering zone 23. These zones are actually not very well separated in the furnace and can overlap to a certain extent. A second combustion zone or flame zone 24, where the homogeneous gas phase combustion of the pyrolysis gases takes place, is identified above the waste bed. Primary air 30 is fed from below the grate in generally different amounts to the four abovementioned zones 20, 21, 22, 23. Secondary air 31 is fed above the grate to ensure complete combustion of the gasification and pyrolysis products in the second combustion zone 24.


In order to assess the steam flow in a somewhat systematic way, different kinds of energy balances are considered. First, assuming complete combustion of the fuel, no losses and unitary boiler efficiency, the total energy contained in the steam is equal to the sum of the energy in the waste and that of the combustion air. Accordingly, the energy balance can be written as






{dot over (m)}
steam
H
steam(Tsteam, Psteam)=[w0·ηLHV+u2(1)H(u2(2))+u3(1)H(u3(2))]  (eq. 1)


wherein

    • {dot over (m)}steam steam flow, [kg/s]
    • Hsteam steam enthalpy, [kJ/(kg K)]
    • w0 waste feed rate or fuel flow, [kg/s]
    • η; 0≦η≦1 waste conversion efficiency
    • LHV Lower Heating Value of the waste [kJ/kg]
    • u2=[u2 (1), u2 (2)] primary air (mass flow, temperature), [kg/s]
    • u3=[u3 (1), u3 (2)] secondary air (mass flow, temperature), [kg/s]
    • H air enthalpy at the respective air temperature, [kJ/(kg K)]


      Accordingly, if the product η·LHV were known, it would be possible to determine the waste feed rate w0 for a given, or a required, steam flow {dot over (m)}steam However, as the auxiliary quantity η is only indirectly accessible, said product cannot be determined with sufficient precision.


Second, the steam production can likewise be expressed in terms of an energy balance over the boiler as






{dot over (m)}
steam
H
steam(Tsteam, Psteam)={tilde over (η)}{dot over (m)}gas(u2, u3, d1,gas(xLL, u2), Gcm(XGC, u2))Hgas(xGC)  (eq. 2)


wherein, in addition to eq. 1,

    • {tilde over (η)}; 0≦{tilde over (η)}≦1 boiler efficiency
    • {dot over (m)}gas gas flow
    • xGC flame (Gas Cloud) temperature [K]
    • xLL waste (Lower Layer, combustion zone) temperature, [K]


Eq. 2 is strongly nonlinear and the influence of the incoming waste feed rate w0 is not clearly identifiable.


In order to avoid the respective drawbacks of the first and second approach above, an attempt is made to derive an expression for the steam flow rate {dot over (m)}steam in a semi-heuristic way. To this end, eq. 1 and eq. 2 are replaced by a polynomial having the general form












m
.

steam

=



i

N







ϕ
i



(


u
2

,

u
3

,

x
LL

,

x
GC

,

w
0


)


·

θ
i




,




(

eq
.




3

)







where θi are regression coefficients and φi are individual steam contributions. In other words, the steam flow rate is approximated as a linear combination of distinct steam contributions, each of which depends on operational parameters in distinct way inspired by the physical origin of the respective steam contribution or its corresponding heat source as detailed below.


According to the invention, any uncertainty based on the unknown quantities from eq. 1 and eq. 2 are incorporated in the regression coefficients θi. Eq. 3 is nonlinear in the operational parameters, i.e. the process inputs u2, u3, w0 and the process states xLL, xGC, but it is linear in the regression coefficients θi. This particular form of eq. 3 allows estimating the regression coefficients θi on-line without excessive computational power using e.g. a Recursive Least Square (RLS) method as detailed in the following.



FIG. 2 depicts the steps of controlling a waste incineration process according to the invention. In step 40, during operation of the waste incineration plant, operational values of the operational parameters u2, u3, xGC, xLL, w0 (or the respective control signals and sensor output signals) as well as a value of a corresponding steam flow rate {dot over (m)}steam are measured repeatedly, thus forming a total of N data sets. Subsequently, in step 41, these data sets are evaluated to identify N′≦N regression coefficients θi of a regression relation relating the steam flow rate to the operational parameters. In step 42, a set-point or target {dot over (M)}steam of the steam output flow is provided. In step 43, a control value of the waste feed rate w0 is calculated by solving the regression relation with said set-point and present values of all operational parameters except w0. The control value is finally applied to a waste feed actuator 10 of the waste incineration plant. Step 44 designates the possibility that new data sets may be available regularly or occasionally, necessitating an update of the regression coefficients, or that a new set point or a changing present value of an operational parameter requires a recalculation of the waste feed rate. Regarding the former possibility, the greater the diversity or variability of the data sets to be evaluated, the more trustful will be the regression coefficients θi resulting there from when it comes to dynamic fuel variations.


A somewhat refined version according to an exemplary embodiment of the present invention has the form






{dot over (m)}
steam=(θ1φ12φ23cp·xGC4  (eq. 3′)


where steam contributions take the form








ϕ
1

=


(



u
2



(
1
)


+


u
3



(
2
)



)

n


,

n

1.8

,
and







ϕ
2

=



w
o

·

A
1







-


E
2


R




x
_

LL



(
2
)






·

A
2







-


E
2


Rx
GC




.






The first steam contribution, denoted by φ1, represents the influence of the primary and secondary air, whereas the second steam contribution, denoted by φ2, represents the influence of the combustion gases originating from the solid and gaseous combustion. The latter contribution comprises a first exponential term giving the combustion rate of the solid phase as a function of the waste temperature xLL, and a second term giving the combustion rate of the gaseous phase as a function of the flame temperature xGC.


Furthermore,





    • cp is a flue gas specific heat [kJ/kg K], and

    • A1, A2, R, E1, E2 are constants known from literature, such as the article “Heterogeneous kinetics of coal gasification and combustion” by M. Laurendau, Progress in Energy Combustion Science Vol. 4, pp. 221-270, Pergamon Press 1978.





In this approach, the steam flow {dot over (m)}steam depends linearly on the waste feed rate w0, i.e. {dot over (m)}steam=M(θ)+w0N(θ). This relation can thus be solved analytically for the waste feed rate, which for a given steam set point {dot over (m)}steam determined by steam delivery or energy output contracts can be calculated in a straightforward way. On the other hand, it is to be noted that any approach involving less operational parameters (e.g. θ1+w0θ2 involving no process inputs or states at all other than w0), and in particular an approach that neglects the temperatures xGC and xLL, has proven to be less successful. Hence, the semi-heuristic model of eq. 3 must not be oversimplified.



FIG. 3 shows the result of a simulation that has been run using MATLAB Simulink in order to test the feasibility of the proposed control scheme. A constant waste composition and a steam flow set point {dot over (M)}steam (top graph, curve A) changing occasionally from a first value to a second value and back were assumed. The method according to the present invention was then applied to a waste combustion process that was itself modeled using a waste combustion model [JM1] reasonable complexity. The waste feed rate w0 (bottom graph, curve B) controlled as detailed in the foregoing and the actual steam flow (top graph, curve C) resulting there from are likewise depicted and demonstrate that after a few initial oscillations, the steam flow set point is followed quite accurately.


As there is a delay between the feeding of the waste onto the grate and its effect on the steam production, a corresponding delay time A is introduced into the relations above. This time delay can be in the order of up to one hour, and physically relates to the waste residence time in the initial grate zone. The aforementioned linear relation then reads






{dot over (m)}
steam
=M(θ)+w0(t−Δ)N(θ)  (eq. 4)


Hence, in a preferred variant, the time delay Δ is estimated, and a correspondingly earlier value of the waste feed rate w0 is associated to the measured values of the operational parameters for the purpose of estimating the coefficients θi.
LIST OF DESIGNATIONS




  • 10 actuator


  • 11 furnace


  • 12 grate


  • 13 auxiliary burner


  • 14 flue gas tract


  • 15 boiler


  • 20 drying zone


  • 21 first combustion zone


  • 22 residual zone


  • 23 ash treatment zone


  • 24 second combustion zone


  • 30 primary air


  • 31 secondary air


Claims
  • 1. A method of controlling a waste combustion process, comprising a) providing a plurality of data sets each consisting of operational values of a number of operational parameters (u2, u3, xGC, xLL, w0) of the combustion process and of a corresponding value of a steam flow ({dot over (m)}steam) generated by the combustion process,b) evaluating said plurality of data sets and deriving a relation between the steam flow ({dot over (m)}steam) and the operational parameters (u1, u2, xGC, xLL, w0), andc) solving, given a desired steam flow set point ({dot over (M)}steam) said relation for a control value of a waste feed rate (w0), and applying said control value to a waste feed actuator (10) of the combustion process,wherein step b) comprisesb′) deriving the values of a number of regression coefficients (θi) that multiply, in a polynomial relation (eq. 3) of the form
  • 2. The method according to claim 1, comprising measuring operational values of a temperature (xGC, xLL) of the combustion process and providing data sets comprising the latter.
  • 3. The method according to claim 1, comprising estimating a delay time (Δ) characteristic of a time delay between an application of said control value to a waste feed actuator (10) and an effect on the steam production, and providing data sets each comprising operational values of a number of operational parameters (u2, u3, xGC, xLL) measured at a time t and a value of the waste feed rate (w0) measured at a time t−Δ preceding the time t by the delay time (Δ).
  • 4. The method according to claim 1, comprising providing data sets and deriving updated values of the regression coefficients (θi) on-line during operation of a waste incineration plant.
  • 5. A computer program for executing the method according to claim 1.
  • 6. A system for controlling a waste combustion process, comprising means for deriving, from a plurality of data sets each consisting of operational values of a number of operational parameters (u2, u3, xGC, xLL, w0) of the combustion process and of a corresponding value of a steam flow ({dot over (m)}steam) generated by the combustion process, the values of a number of regression coefficients (θi) that multiply, in a polynomial relation (eq. 3) of the form
  • 7. The system according to claim 6, comprising means for measuring operational values of a temperature (xGC, xLL) of the combustion process.
Priority Claims (1)
Number Date Country Kind
06405102.2 Sep 2006 EP regional