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FERIODICA POLYTECHNICA SER. CIVIL ENG. VOL. 38, NO. 2, PP. 243-250 (J994)

A COMPLEX MODEL FOR ENVIRONMENTAL QUALIFYING AND FORECAST: CMEQ

Kalman RORIS Department of "YVater Management

Technical University of Budapest H-1521 Budapest, Hungary

Received: March 31, 1994

Abstract

A quantitative characterization of the environmental situation provides important infor- mation whenever a judgement of the environment's quality is formed or investments are planned or decisions are to be supported. Such a quantitative qualification of the environ- ment may play an important role even on a regional scale when forming an opinion on the quality of the given region's environment or preparing regional strategies for environment protection or signing pacts for regional protection of the environment. The model and numerical examples to be shown in this paper describe the environment of a minor region by a parameter system of vlater, air, and soil quality. It is a task of the future to include ecological (biological) and social (economic) components into the model. In such a way, the model is an appro:Limative measure of the environment's state, comparing the latter with computed quality categories, i. e., classifying the given state. If any of the quality parameters changes (e. g., the NOx emission of a country is reduced), the environment's quality changes as well and the numerical value of this change can be expressed by the model.

Keywo7'ds: environmental modelling. matrix equations. environmental subsystems and qualifying.

The CMEQ Model

The environment is broken into subsystems the CMEQ model

(Complex Model for Environmental Qualifying). The three most important groups of the subsystems are:

1. Geosphere Subsystems:

1.l. Soil quality (lithosphere, pedosphere),

1.2. Water quality (surface and subsurface water), 1.3. Air quality.

2. Biological (Ecological) Subsystems:

2.1. Microbiota, 2.2. Flora, 2.3. Fauna,

2.4. Public health (human sanitation).

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244 n. KORIS

3. Social (Economic) Subsystems:

3.1. Social environment, 3.2. Urban environment,

3.3. Noise, stink, vibration, waste, radiation, etc.

3.4. Economic parameters, 3.5. Environmental aesthetics.

The measurement of the state of the environment and its qualification may be carried out by taking these subsystem groups into account.

The Model for Environmental Qualifying

In the CMEQ model, subsystems and within it parameters are used for qualifying the environment. The relative quality values derived from the probability distribution of the parameters are:

All parameters are included in a B matrix in which any row represents the parameter series of one of the subsystems (e. g. of the water quality subsystem). The parameters are weighted by Si weight numbers, or the B matrix is '.veighted by a S weighting matrix:

I

011 012

0:21 0::2

x

=

(u: is the nUI11ber of environrnental indices considered and

n: is the nU111ber of paranleters defining a given index.

\\"c:lgiltmg is carried as a i1rst in the forn1 of . S

'"';"HCH'_", TI1atrix containing different """a-nT vec'Sors in

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A COMPLEX MODEL FOR ENVIRONMEHTAL qUALiFYING 245

The matrix product will be the following:

I:

b1j Slj Cl2 Cl3 Clj

j

d21

I:

b2jS2j e23 C2j

j

d 31 d32

I:

b3jS3j C3j C3m

j

L

Cim

where: Clj

= I:

b1j S1j , d mj

= I:

bmjsij, etc.

j j

As a next step, the matrices C and D are defined without being described here in detail. By using the latter matrices, the F matrix of results can be obtained as

:L

b1j Sl j 0

j

0

:L

b2j S2j

j

0 0

0 0

0

:L

OijSij

j

o

o

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246

Fkl 0 0 Fk2

0 0

K. KORIS

0 0

Fki

0

o o

Fkm

In can be seen that by means of matrix operations a matrix of results has been obtained whose main diagonal contains the Fki values of the environmental indices.

These Fki values are we'ighted characteristics of the environment, i. e., quality measures of the various environmental subsystems. The last step is the weighting of these Fki numbers. By using the Fki elements included in the main diagonal of the F matrix, the following vector f can be generated, called vector of environmental qualification:

... , ... ,

By weighting the subsystems with the v vector (i. e., by carrying out the second weighting), the weighted number for environmental qualification Q is obtained:

Q

=

f(m) v(m)

=

[FJd, • • • 1 F'.1ci , .l'km Tl

1 V~ J

m

=

LFkiVi.

i=l

The value of the index can be also -written in the following form of double summarization:

m m

Q= Vi Lbij8ij , i=l j=l

where bij are the relative parameters of environmental qualification, 8ij are their weighting numbers and Vi are the weighting numbers of the various subsystems.

The index Q for environmental qualification can be also computed directly, by original matrix equation, since

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A COMPLEX MODEL FOR ENViRONMENTAL qUALfFYI1VG

0 0

Fki

o

0 0 Fl~m

Let us now define the vector e(m):

VI V2

Vi

vm

L) 2.) i. )

m.) The environmental qualification index Q will be:

and can be also written in the form:

- is the matrix of parameters,

=

where B

S - the matrix of weight numbers,

v1Fkl V2 F k2

ViFki

VmFt:m

- are matrices (not defined in this paper),

=

q(m) .

C and D

v - is the weight vector of the subsystems and e - is the column vector defined above.

247

In the following practical computations the formula of double sum- marization will be adopted.

Computations Carried Out with the Model

In order to realize the calculations, a computer program has been devel- oped for an IBM PC, in the program language Turbo Pascal, by using the translator program Borland V5.5 Turbo Pascal. The program can treat 10 types of graphical cards. It is a 'user friendly' type program, steered by

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248

--,

K. KORIS

- - - / - ' - - - ----.--.---~ s;

. - - . - - - - -

'"

"-

:::r...

';.,."::

- - - -

~ -&---~----~---~---~----_r

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A COl,fPLEX A1C"DEL POR ENVI.FiO.VAfENTAL CjUALIPYlilG

Table 1

Quality class Description of environment 1.

n.

m.

IV.

V.

Very good quality of environment withcut poilution

Good quality of environment, slight pollution

Average quality of enyircnment

Poor quality of enyirollmenL strong pollution

poor quality of environment ~

very !)ollution

Limit values of index Q 0.0-2.7 2.7 - 5.5 5.5 8.2 8.2 - 11.0

11.0 <

249

2. Indices Q

or

the environnwntal quality of the counties of Hungary in 1980

a menu system, enabling quick data input, modifications, the determina- tion of the index Q qualifying the environment's quality and displaying the results obtained.

First, the environmental quality classes were computed to which the numerical values of Q can be associated.

These classes are listed in Table 1.

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250 K. KORIS

The limit values of Q given in the above table could have been deter- mined on the basis of the principle of class intervals of equal probabilities.

As a next step, computer runs were carried out aiming at the determi- nation of the mean environmental quality of Hungary. The average indices were calculated for each year on the basis of the county indices. The time series of the Q values are shown in Fig. 1 for the period from 1968 to 1993.

The deteriorating quality of the environment can be seen from the graph of the time series. In the figure, the long-term forecast based on the linear trend has also been plotted, indicating that the environment's quality in- dex Q is likely to reach (or at least to approximate) the upper limit value of the middle (IH.) category by 2000. The regional distribution of the en- vironmental quality index is shown in Fig. 2 for the so far most polluted year of 1980. In the figure, a very clear distinction between polluted and less polluted counties can be seen.

Conclusions

Since the results of the model investigations carried out so far are based exclusively on factors of the geosphere (water, air and soil quality), the inclusion of other environmental factors into the study is highly recom- mended. The indices obtained until now provide only an approximaiive characterization of the environmentai quality. Further development of the model including both an increase of the number of submodels and param- eters as well as an improvement of computation techniques is under way.

After these improvements the model, due to its basically dynamic charac- ter, will be very handy for making forecasts.

References

K01U.o. t\. (lU89): :\ ~10del for Environmental Quaiifying. Conference on Cl-i-

("ail, and Water. WaleT 2. The publications of the Academy of Finland. Helsinki.

Bl;Z':", 1\. KOfUS, K. (1990): Characterization and Prediction of the State of the

1~!i\·jr()1tment. (Research report, manuscript, ill lIung:arian.) Technical University of BiICL'[l"st, Faculty of Civil Engineering. Buda.pest.

K(Ji(J-. f\ (Jr.) (1990): A Computerized Procedure for Hegional Qua.lification ()f the

l.l!\' rollmellt. (Scielltific study, manllscript, in I1ung;,rian) Technical rllivcrsily of

Bli( ,q)(st, Faculty of Civil EngiIleering. Budape;;1.

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