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STATISTICAL ANALYSIS OF WINTER SULPHUR DIOXIDE CONCENTRATION DATA I N VIENNA

P. B o l z e r n G. F r o n z a E. yunca C. b b e r h u b e r S e p t e m b e r 1981 CP-81-25

R e s e a r c h s u p p o r t e d by MA 2 2 , U m w e l t s c h u t z d e s M a g i s t r a t e s d e r S t a d t Wien, V i e n n a , A u s t r i a a n d by IIASA, L a x e n b u r g , A u s t r i a

C o Z Z a b o r a t i v e P a p e r s r e p o r t work w h i c h h a s n o t b e e n p e r f o r m e d s o l e l y a t t h e I n t e r n a t i o n a l I n s t i t u t e f o r A p p l i e d S y s t e m s A n a l y s i s a n d w h i c h h a s r e c e i v e d o n l y l i m i t e d r e v i e w . V i e w s o r o p i n i o n s e x p r e s s e d h e r e i n d o n o t n e c e s s a r i l y r e p r e s e n t t h o s e o f t h e I n s t i t u t e , i t s N a t i o n a l Member O r g a n i z a t i o n s , o r o t h e r o r g a n i - z a t i o n s s u p p o r t i n g t h e work.

INTERNATIONAL INSTITUTE FOR APPLIED SYSTEMS ANALYSIS A - 2 3 6 1 L a x e n b u r g , A u s t r i a

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THE AUTHORS

P. BOLZERN and G. FRONZA are from the Centro Teoria Sistemi, Instituto Elettrotecnica ed Elettronica, Politecnico, Milan, Italy.

E. RUNCA is a research scholar in charge of air pollution re- search at the International Institute for Applied Systems Analysis, Schloss Laxenburg, A-2361 Laxenburg, Austria. For- merly, he was project leader at IBM Italy Scientific Center in Rome.

C. UEBERHUBER is with the Institut fflr Numerische Mathematik, Technische Universitat, Vienna, Austria.

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PREFACE

The m o d e l l i n g o f t h e t i m e e v o l u t i o n o f a i r p o l l u t a n t s con- c e n t r a t i o n i n u r b a n i n d u s t r i a l a r e a s a l l o w s a d m i n i s t r a t i v e b o d i e s r e s p o n s i b l e f o r t h e p r o t e c t i o n o f t h e a t m o s p h e r i c e n v i r o n m e n t t o i d e n t i f y t h o s e s i t u a t i o n s which may l e a d t o a s e r i o u s i n c r e a s e i n a t m o s p h e r i c p o l l u t i o n ,

T h i s p a p e r d i s c u s s e s t h e m o d e l l i n g . o f t h e d a i l y a v e r a g e w i n t e r s u l p h u r d i o x i d e c o n c e n t r a t i o n i n t h e c i t y o f Vienna, A u s t r i a . A s t a t i s t i c a l a p p r o a c h was a d o p t e d , t h a t i s , t h e

m o d e l l i n g was n o t a c h i e v e d t h r o u g h t h e s o l u t i o n o f t h e p h y s i c a l l a w s g o v e r n i n g t h e dynamics o f a t m o s p h e r i c d i f f u s i o n , b u t t h r o u g h r e g r e s s i o n e q u a t i o n s whose p a r a m e t e r s w e r e e s t i m a t e d from t h e a v a i l a b l e measurements o f s u l p h u r d i o x i d e c o n c e n t r a t i o n s and m e t e o r o l o g i c a l p a r a m e t e r s ,

T h i s s t u d y i s p a r t o f t h e a c t i v i t y o f t h e R e s o u r c e s and Environment Area (Task 2 Environment Q u a l i t y C o n t r o l and Manage- ment) on development and a p p l i c a t i o n o f a i r p o l l u t i o n models t o r e a l s i t u a t i o n s . The s t u d y was c o n d u c t e d j o i n t l y w i t h t h e I n s t i t u t f a r Numerische Mathematik, T e c h n i s c h e U n i v e r s i t a t o f Vienna and C e h t r o T e o r i a S i s t e m i , P o l i t e c n i c o o f Milano.

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T h i s p a p e r was o r i g i n a l l y p r e p a r e d u n d e r t h e t i t l e " M o d e l l i n g f o r Management" f o r p r e s e n t a t i o n a t a N a t e r R e s e a r c h C e n t r e

(U.K. ) Conference on " R i v e r P o l l u t i o n C o n t r o l " , Oxford, 9 - 1 1 A s r i l , 1979.

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ABSTRACT

The p a p e r d e s c r i b e s two n o n l i n e a r r e g r e s s i o n m o d e l s , a p p l i e d t o w i n t e r d a i l y SO2 c o n c e n t r a t i o n d a t a a n d t o t h e c o r r e s p o n d i n g m e t e o r o l o g i c a l d a t a from t h e m e t r o p o l i t a n a r e a o f V i e n n a . The f i r s t model a c c o u n t s f o r t h e r o l e o f w i n d s p e e d a n d t e m p e r a t u r e

( a p r o x y f o r e m i s s i o n s d u e t o r e s i d e n t i a l h e a t i n g ) o n a v e r a g e SO c o n c e n t r a t i o n i n t h e a r e a . The s e c o n d r e g r e s s i o n h a s a n a d

2

i t i o n a l wind d i r e c t i o n i n p u t a n d t r i e s t o p o i n t o u t t h e con- t r i b u t i o n b y t h e i n d u s t r i a l e m i s s i o n s ( l o c a t e d p r i m a r i l y n e a r t h e s o u t h - e a s t e r n b o r d e r o f t h e a r e a ) t o c o n c e n t r a t i o n i n t h e m o s t p o l l u t e d s u b a r e a .

Both m o d e l s o f f e r a s a t i s f a c t o r y f i t t i n g p e r f o r m a n c e ( e . g . , c o r r e l a t i o n s a r o u n d 0 . 8 5 S e t w e e n o b s e r v e d a n d r e g r e s s i o n v a l u e s ) . However, s i n c e model v a l i d a t i o n i s a c r i t i c a l p o i n t f o r r e g r e s -

s i o n s , s e n s i t i v i t y t e s t s o f m o d e l f i t t i n g p e r f o r m a n c e a r e c a r r i e d o u t by u s i n g v a r i o u s d a t a s e t s f o r t h e e s t i m a t i o n o f r e g r e s s i o n c o e f f i c i e n t s . One o f s u c h t e s t s p o i n t s o u t t h a t t h e r e i s a n

" o p t i m a l l e n g t h " o f t h e d a t a s e t t o b e u s e d , namely n e i t h e r a t o o s h c r t s e t n o r a s e t i n c l u d i n g " t o o p a s t " d a t a o f f e r a s a t i s - f a c t o r y f i t t i n g q u a l i t y .

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CONTENTS

1 . INTRODUCTION

2 . M A I N CHARACTERISTICS OF SULPHUR DIOXIDE POLLUTION I N VIENNA

3 . THE MODEL ARXI 4 . THE MODEL ARX2

5 . DESCRIPTION OF MODEL SIMULATION RESULTS

F i t t i n g P e r f o r m a n c e of ARXl a n d ARX2 on Winter 1 9 7 8 / 7 9 D a t a

S e n s i t i v i t y of Model P e r f o r m a n c e t o t h e E s t i m a t i o n D a t a S e t

REFERENCES

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STATISTICAL ANALYSIS OF WINTER SULPHUR DIOXIDE CONCENTRATION DATA IN VIENNA

P. Bolzern, G. Fronza, E. Runca, and C. Uberhuber

1. INTRODUCTION

In general terms, mathematical representations of pollntznt dispersion in an airshed belong to one of the following two clas

-

ses (see also Seinfeld (1 975) )

a) Representations ("deterministic models") derived from the pollutant continuity equation

.,

usually under suitable sim- plifying assumptions. The coefficients of such mathematical relations have a physical meaning and are determined on the basis of experimentai evidence.

b) Representations ("stochastic models"), which consist of sta- tistical regressions of one or more "ambient pollution va- riables" on their past values (see for instance Merz et al.

(1972), Chock et al. (1975), McCollister and Wilson (1975), Tiao et al. (1975)) and on factors, like emissions and meteo- rological variables, which affect the dispersion phenomenon

(see for instance Finzi et al. (1 980) )

.

The mathematical form of the regressions is usually derived not on physical grounds but from a statistical point of view. Namely, provided that regression fitting is satisfactory, the model is considered acceptable, at least if its relations somehow "resemble" the

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true cause-effect mechanism of the phenonenon (see also aena- rie (1 981 )

,

Smith and Jeffrey (1 972) !

.

In particular, although stochastic models are often gross simplifications of the phy- sical mechanis~, their structure turns out relatively complex in some cases (see for instance Bacci et al. (1981)). As for the coefficients of the regression, they are estimated by sta- tistical data fitting techniques (usually according to the least squares principle or its modifications) and have gene- rally no direct physical meaning.

By their very nature, precisely by the way their coeffi- cients are evaluated, stochastic models sometimes give a fit- ting of concentration records better than deterministic ones, at least when only an aggregate description of the pollution phenomenon is required. However, the relevant lack -of physical interpretation makes the reliability of the fitting performance by stochastic models a critical point. In other words it may happen that a model shows a satisfactory fitting performance on a particular data set but does not turn out to be a success for a different data set at the same site. Moreover, statistical confidence theory is not very helpful, since it is generally ba- sed on assumptionsr (e.g. normality), which are unrealistic in many applications or, most of all, can hardly be checked (e-a.

stationarity). Therefore, a systematic analysis of model fitting performance on different data sets must be carried out.

The present paper illustrates two stochastic xaodels of win- ter sulphur dioxide pollution in the metropolitan area of Vien- na. The w o r k has been committed by the municipality authorities

for screening purposes, namely for preliminary understanding of relevant aspects like the dilution by moderate-to-strong winds, the transport from outside industrial sources to the city ten-

ter in particular wind conditions, the dependence of residential heating emissions upon temperature variations.

Specifically,two regressions are described in the third and fourth section respectively:

i) A regression accounting for the role of meteorological factors on daily average SO2 concentration in the area. The two fac- tors considered are wind speed and temperature, which is a proxy for emission due to residential heating (a datum not available at daily time scaling).

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i i ) A r e g r e s s i o n s u p p l y i n g a rough measure o f t h e c o n t r i b u t i o n by t h e i n d u s t r i a l s o u r c e s l o c a t e d i n t h e s o u t h - e a s t e r n part of t h e a r e a t o t h e c o n c e n t r a t i o n i n t h e most p o l l u t e d sub- a r e a ( t h e c i t y c e n t e r ) .

The r e s u l t s a r e d e s c r i b e d i n t h e l a s t s e c t i o n . S p e c i f i c a i i y , b o t h models have been f i r s t s e t up by u s i n g w i n t e r 1 9 7 7 / 7 8 da- t a f o r e s t i m a t i n g r e g r e s s i o n c o e f f i c i e n t s (by an ad-hoc i e a s t s q u a r e s a l g o r i t h m ) , w h i l e w i n t e r 1978/79 d a t a have -been used f o r checking t h e model f i t t i n g performance, which h a s t u r n e d o u t r a t h e r s a t i s f a c t o r y ( e . g . c o r r e l a t i o n s between r e g r e s s i o n

v a l u e s and o b s e r v a t i o n s around .85, a l s o i n " e p i s o d e " s i t u a t i o n s ) . Moreover, t h e f o l l o w i n g s y s t e m a t i c t e s t of t h e s e n s i t i v i t y of model performance t o t h e d a t a s e t , used f o r e s t i m a t i n g model coef

-

f i c i e n t s , h a s been c a r r i e d o u t . The c o e f f i c i e n t s have been r e e s t i m a - t e d a f c e r e v e r y f i v e d a y s , by u s i n g t h e c o n c e n t r a t i o n and meteo- r o l o g i c a l d a t a o f t h e l a s t M days. The o v e r a l l f i t t i n g performan- c e h a s t u r n e d o u t poor f o r low v a l u e s of M ( t w e n t y , s a y ) , c o r r e - sponding t o low s t a t i s t i c a l c o n f i d e n c e ( t o o few p a s t d a t a a r e used f o r model c o e f f i c i e n t e s t i m a t i o n , t h u s f i t t i n g i n t h e n e x t f i v e days i s u n s a t i s f a c t o r y ) . Then, t h e performance i n c r e a s e s w i t h M up t o M ,- 4 0 and s u b s e q u e n t l y d e c r e a s e s . Hence, f o r i n s t a n c e , u s i n g t h e l a s t e i g h t y d a y s of d a t a f o r c o e f f i c i e n t e s t i m a t i o n g i v e s a worse f i t t i n g of t h e n e x t f i v e days t h a n u s i n g t h e l a s t s i x t y d a y s of d a t a . I n o t h e r t e r m s , i t i s b e t t e r t o f o r g e t " t o o p a s t "

d a t a , a c l e a r s i g n of t h e n o n - s t a t i o n a r i t y o f t h e p r o c e s s .

F i n a l l y , a s f o r t h e r o l e of i n d u s t r i a l e m i s s i o c s i n t h e p o l l u - t i o n of t h e c i t y c e n t e r it t u r n s o u t modest a s a whole, a l t h o u g h s i g n i f i c a n t i c p a r t i c u l a r s i t u a t i o n s c h a r a c t e r i z e d by moderate-to- scrong winds.

2 . M A I N C H A R k C T E R I S T I C S OF SULPHUR 9 I O X I D E POLLUTION I N V I E N N A

The c o n t o u r of Vienna m e t r o p o l i t a n a r e a i s shown i n F i g . ? , t o g e t h e r w i t h t h e ne:work of s i x t e e n SO2 s e n s o r s , t h e meteoro- l o g i c a l s t a t i o n ( 2 0 m above t h e ground) and t h e t h r e e main i n - d u s t r i a l s o u r c e s S 1 , S 2 and S3. I n p a r t i c u l a r S, i s a power p l a n t w i t h two 150 m s t a c k s , Si i s a power p l a n t w i t h f o u r

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F i g u r e 1 . Vienna m e t r o p o l i t a n a r e a , SO2 m o n i t o r i n g network, m e t e o r o l o g i c a l s t a t i o n MS ( c o i n c i d e n t w i t h s e n s o r 6 ) and i n d u s t r i a l s o u r c e s S , , S2 and S3.

s t a c k s ( 8 0 m , 1 2 0 m, 1 2 0 m , 200 m ) w h i l e s o u r c e S3 c o r r s s p o n d s t o a r e f i n e r y , where s t a c k s do n o t e x c e e d 80 m.

Each s u l p h u r d i o x i d e s e n s o r r e c o r d s 30-min. c o n c e n t r a t i o n , w h i l e t h e m e t e o r o l o g i c a l s t a t i o n s u p p l i e s h o u r l y wind s p e e d , wind' d i r e c t i o n and 3-hour t e m p e r a t u r e d a t a ( s e e f o r i n s t a n c e L o f f l e r (1980) f o r a d e s c r i p t i o n o f t h e m o n i t o r i n g and d a t a r e c o r d i n g s y s t e m ) .

Vienna i s l o c a t e d i n a r e l a t i v e l y f l a t a r e a o f t h e Danube V a l l e y , a l t h o u g h t h e h i l l s o f Wienerwald on t h e w e s t e r n b o r d e r c r e a t e a l o c a l o r o g r a p h i c e f f e c t on a i r c i r c u l a t i o n . A p i c t u r e o f wind s p e e d and d i r e c t i o n d i s t r i b u t i o n s i s g i v e n by F i g . 2 , showing t h e h o u r l y wind r o s e i n w i n t e r 1977/78. S t a g n a t i o n pheno- mena a r e p r a c t i c a l l y a b s e n t . Moreover, wind s p e e d i s s c a r c e l y p e r s i s t e n t a t d a i l y t i m e s c a l i n g , a s p o i n t e d o u t by F i g . 3 , which i l l u s t r a t e s t h e t i m e p a t t e r n o f d a i l y s p e e d i n w i n t e r 1977/78

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I I I I I I

32 63 94 125 156 187

D A Y S

Figure 3. Time pattern of daily wind speed in winter : 9 7 7 / 7 8 .

andgives an idea of the conspicuous weather variability in the region.

Sulphur dioxide pollution in winter is mainly due to residen- tial heating, which is approximately uniformly distributed in the dashed area of Fig. 1. SO2 concentration reaches its highest le- vels in the city center, the area inside the Ringstrasse (see

-

1

Fig. 1 ) . When mo2erate-to-strong winds (in the range 3 rns

-

6 rns-A

,

say) blow from the easternjsouth-eastern sectors, a con- tribution by the industrial sources to pollution in the central area can reasonably be assumed. As a matter cf fact, such contri- bution is partially revealed by the comparison between the wind

speed rose of Fig. 2b and the SO2 concentration rose of Fig. 4.

Precisely, Fig. 4 points out the dilution effect by the moderate- to-strong winds blowing from the western sectors but does not indi- cate a similar ef'ect by winds blowing from the eastern/south-

eastern sectors, characterized by an average wind speed only slightly lower. Hence, a reasonable explanation (validated in

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Figure 4. Winter 1 9 7 7 / 7 8 hourly SO2 concentration rose in station 1, in the city center.

the paper under the limitations and approximations of the statisti- cal approach) is that the smaller contribution by residentiai heat- ing emissions in such moderate-to-strong wind conditions is ba- lanced by the transport of pollutant from industrial sources.

3. THE MODEL ARXl

The t w o regression models described in this section and in the next one are classified as ARX (AutoRegressive with exogenous inputs) in the stochastic modelling literature, therefore they will respectively be labeled as ARXl and ARX2.

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The objective of A m 1 is to fit observed average daily concen- tration in the area only by using concentration and avail~ble me- teoroiogical data. Let xi(k) (k=1,2,. ..) denote the average SO2

concentration (pg.m-3) measured by the i-th sensor (i=1,2,.

.

.16)

in the k-th winter day. Moreover, let x(k)

+A6

x. (k)/16 be the

1

average of concentration measures in the area~lin the k-th day.

Then, ARXl consists of the following nonlinear regression:

where :

T(k) = average temperature ( 0 C) in the k-th day;

v(k) i average wind speed (ms-l) in the k-th day;

5

{aj) j=l

+

regression coefficients, determined by an ad-hoc esti- mation procedure (see below) ;

a,B = other (positive) coefficients, assigned by trial (see also below).

A gross "physical" justification of ARX1, namely of the form of the right-hand side of eq. (1) is the following. By eq. (I), concentration in the (k+l)- ,st day is made to depend upon con- centration in the previous day ( x (k) )

,

temperature (T (k+l ) ) and

wind speed (v(k+l)), Concentration in the k-th day is somehow corre- lated to the pollutant mass existing in the area at the end of the k-th day. Thus, the term a l x (k) in eq. ( I ) can somehow be regarded as the contribution to x(k+l) by the pollutant mass existing in the area at the beginning of the (k+l)- St day. As for the other two

addenda of the regression, the first one aims at taking into ac- count the increase of residential heating emissions when tempera- ture decreases (a concept similar to that of degree-days), while the other one aims at representing pollutant dilution by wind speed on emissions from the residential heating sources.

In conclusion, eq. ( 1 ) attempts to account for three

"phenomena" affecting x(k+l), namely the existence of previous pollutant, the temperature-dependent emissions by residential hea- tin5, the wind dilution effect.

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The s p e c i a l ' n o n l i n e a r form of t h e l a s t two t e r m s o f t h e r i q h c - hand s i d e o f e q . ( 1 ) d i f f e r s from p r e v i o u s l y used ARX modeis. I n p a r t i c u l a r , t h e " i n v e r s e l y p r o p o r t i o n a l " wind s p e e d term i n e q . ( 1 ) r e p l a c e s t h e c o r r e s p o n d i n g n e g a t i v e l i n e a r term used by F i n z i e t a l ,

(1980) i n t h e Milan c a s e . I n f a c t , a n addendum l i n e a r l y d e c r e a s i n g w i t h wind s p e e d h a s p r o v e d i n s u f f i c i . e n t i n t h e Vienna a r e a , cha- r a c t e r i z e d by a r a n g e and d i s t r i b u t i o n o f wind s p e e d c o m p l e t e i y d i f f e r e n t from t h e Milan r e g i o n . -

of e q . ( 1 ) have I n d e t a i l , t h e c o e f f i c i e n t s a , B and { a j I j s l

been d e t e r m i n e d a s f o l l o w s .

Assume t o have s e l e c t e d a c e r t a i n d a t a s e t from t h e a v a i l a b l e c o n c e n t r a t i o n and m e t e o r o l o g i c a l r e c o r d s (which d a t a have a c t u a l l y been used f o r e s t i m a t i n g t h e c o e f f i c i e n t s o f e q . ( 1 ) i n t h e Vien- n a a p p l i c a t i o n i s e x p l a i n e d i n t h e l a s t s e c t i o n ) .

A ) Try a c s r t a i n p a i r ( a

,

6 )

.

3) For s u c h v a l u e s o f a and 6 , t h e c o e f f i c i e n t s a l , a z , . . . , a - a r e

5

e s t i m a t e d from t h e d a t a s e t by a computer a l g o r i t h m . S p e c i f i c a l l y , e a c h s t e p o f s u c h a l g o r i t h m c o n s i s t s o f t h e f o l l o w i n g o p e r a t i o n s . B l ) V a l u e s o f a 3 and a 5 a r e t a k e n from t h e p r e v i o u s s t e p .

I n t r o d u c i n g t h e s e v a l u e s i n t o e q . ( 1 ) makes ARXl f o r m a l l y a l i n e a r r e g r e s s i o n x (kc1 ) = a l x ( k ) +a2T1 (kc1 ) +a4V1 ( k + l )

,

where

T' ( k + l )

+

( k + l ) +aJ-aand v 1 ( k + l ) + [v(k+l ) + a d ' - ' . Hence, c o e f - f i c i e n t s a l , a * , a 4 c a n be e s t i m a t e d from t h e d a t a s e t by izhe o r d i n a r y l e a s t s q u a r e s f o r m u l a .

B 2 ) F i t t i n g o f r e g r e s s i o n ( 1 ) o v e r t h e d a t a s e t i s im2roved . ( = t h e o v e r a l l sum o f t h e e r r o r s q u a r e s i s r e d u c e d ) by d e t e r m i n i n g new a and a , v a l u e s a c c o r d i n g t o o p t i m a l s e a r c h i n t h e p l a n e

3 3

( a j t a s ) ( e . g . Hooke-Jeeves s e a r c h , s e e f o r i n s t a n c e Himmelblau (1972) )

.

C ) When t h e i t e r a t i v e p r o c e d u r e B ) c o n v e r g e s t o some e s t i m a -

3 P

t e s o f { a j

i

j=l

,

a new p a i r ( a , B ) i s t r i e d , t h e i t e r a t i v e e- s t i m a t i o n B ) of { a j ) j = l i s r e p e a t e d and s o o n . 5

O b v i o u s l y , t h a t p a i r (

3 , s )

and t h e c o r r e s p o n d i n g s e t o f e s t i m a t e s o f {a.) 5 . - i s s e l e c t e d , which g i v e s t h e b e s t a b s o l u t e

7 1-1

f i t t i n g o f t h e d a t a s e t . N a t u r a l l y , t r i a l s on ( a , B ) c o u l d be r e - p l a c e d by o p t i m a l s e a r c h a l s o i n t h e ( a , 0 ) p l a n e . I n p r a c t i c e ,

(18)

i t h a s t u r n e d o u t r e a s o n a b l e and s u f f i c i e n t t o t e s t a few p a i r s ( c r , B ) i n t h e r a n g e s 1 c a . & 3 , 1 c 0 L 3.

A f i n a l r e m a r k c o n c e r n s t h e convergence of t h e i t e r a t i v e p r o - c e d u r e B) f o r e s t i m a t i n g a l l a 2 ,

...

a s . Convergence i s n o t gua- r a n t e e d a p r i o r i , however it h a s always been o b t a i n e d i n a r e a - s o n a b l e number o f s t e p s i n t h e Vienna a p p l i c a t i o n . Moreover, t h e e s t i m a t e s r e s u l t i n g from a l g o r i t h m B) have been v a l i d a t e d by a s - suming d i f f e r e n t s t a r t i n g v a l u e s f o r t h e p r o c e d u r e .

4 . THE MODEL A R X 2

Model ARX2, which i s d e s c r i b e d i n t h i s s e c t i o n , a t t e m p t s t o g i v e some i n f o r m a t i o n a b o u t t h e c o n t r i b u t i o n of i n d u s t r i a l e m i s s i o n s t o SO2 c o n c e n t r a t i o n i n t h e c i t y c e n t e r .

F i r s t , t h e wind s p e e d r a n g e h a s been s u b d i v i d e d i n t o a c e r t a i n number of i n t e r v a l s , from now onwards c a l l e d wind s p e e d c l a s s e s . A p o s t e r i o r i , t h e most s u i t a b l e s u b d i v i s i o n i n t h e Vien- na a r e a has t u r n e d o u t t o bg: I =

[o,

1.3 ms-'1

,

I1 = [I . 3 m s -1

,

-1

-

1

-

1

3 1 n s - ~ ) , I I I = [ 3 m s

,

4 m s 1 , I V = [ 4 m s , v m a x

1

(maximum

wind speed v

max r e c o r d e d i n w i n t e r s 1977/78 and 1978/79 h a s been 8 . 7 rns-').

For e a c h wind s p e e d c l a s s w = I, 11, 111, IV, ARX2 c o n s i s t s of t h e f o l l o w i n g r e g r e s s i o n : w

where

y ( k ) = a v e r a g e d a i l y c o n c e n t r a t i o n i n t h e c e n t r a l s u b a r e a i n t h e k - t h day ( p r e c i s e l y , a v e r a g e o f d a i l y concen- t r a t i o n s r e c o r d e d i n s t a t i o n s 1 , 2 , 3 and - 4 ) ;

N(k)

+

number o f h o u r s i n t h e k - t h day c h a r a c t e r i z e d by winds blowing from t h e e a s t e r n / s o u t h - e a s t e r n s e c t o r ? (1 12°30'

,

135") ;

{by.) ;=l ' r e g r e s s i o n c o e f f i c i e n t s ;

Y" = ( p o s i t i v e ) c o e f f i c i e n t found by t r i a l ;

w = i n d e x of wind speed c l a s s w = I 1 1 o r I in t h e (k+l ) - s t day.

(19)

The j u s t i f i c a t i o n of model ( 2 ) a n d , i n p a r t i c u i a r , t h e r e a - son why wind s p e e d h a s b e e n i n t r o d u c e d i n a way d i f f e r e n t from ARXl a r e now g i v e n .

The f i r s t addendum o f t h e r i g h t - h a n d s i d e o f e q . ( 2 ) a c c o u n t s f o r t h e c o n t r i b u t i o n t o y ( k + l ) by t h e " i n i t i a l l y e x i s t i n g " p o l l u - t a n t i n t h e a r e a ( s e e t h e comment i n t h e p r e v i o u s s e c t i o n ) . The second and t h i r d addendum c a n r e s p e c t i v e l y be c o n s i d e r e d as r e - p r e s e n t a t i v e s o f t h e c o n t r i b u t i o n s t o y ( k + l ) by temperature-ciepen

-

d e n t r e s i d e n t i a l h e a t i n g and i n d u s t r i a l e m i s s i o n s , A s i n ARXi, e m i s s i o n s a r e i n t r o d u c e d i n t h e model t h r o u g h t h e r e l a t e d i n p u t s , t e m p e r a t u r e and wind d i r e c t i o n . Moreover, t h e i m p a c t o f t h e s e i n p u t s on y ( k + l ) i s made t o depend upon wind s p e e d , t h r o u g h assum- i n g dependence or' t h e b and

2

r e g r e s s i o n c o e f f i c i e n t s upon t h e s p e e d c l a s s w.

I n c o n c l u s i o n , from e q . ( 2 )

,

c o n c e n t r a t i o n y ( k + l ) i s t h e sum o f c o n t r i b u t i o n s by i n i t i a l l y e x i s t i n g p o l l u t a n t , by t e m p e r a t u r e - d e p e n d e n t r e s i d e n t i a l h e a t i n g s o u r c e s and by i n d u s t r i a l s o u r c e s , e a c h c o n t r i b u t i o n d e p e n d i n g upon t h e wind s p e e d c l a s s i n t h e

( k + l ) - S t d a y .

So, w h i l e i n e q . (1 ) t h e wind s p e e d t e r m a 4 r v ( k + l )

+

as]

-'

c o u l d noc be i n t e r p r e t e d a s t h e c o n t r i b u t i o n o f e x i s t i n g o r new- l y e m i t t e d p o l l u t a n t , h e r e t h e above i n t e r p r e t a t i o n o f e q . ( 2 ) a l l o w s t o draw a g r o s s comparison o f t h e r e l a t i v e i m p a c t of r e - s i d e n t i a l h e a t i n g and i n d u s t r i a l e m i s s i o n s on t h e most p o l - l u t e d s u b a r e a . P r e c i s e l y , s u c h comparison c a n be o b t a i n e d by

t a k i n g day-by-day t h e r a t i o between t h e t h i r d an2 t h e second addendum i n t h e r i g h t - h a n d s i d e of e q . ( 2 )

.

N a t u r a l l y , s i n c e t h e above " p h y s i c a l " i n t e r p r e t a t i o n o f A R X 2 i s g r o s s , t h i s r a t i o can be r e g a r d e d a s a t o o rough mea- s u r e , i f one i s r e l u c t a n t t o a c c e p t t h e s t a t i s t i c a l v i e w p c i n t . However, i t is' t h e o n l y r a t i o computable t h r o u g h t h e p r e s e n t l y a v a i l a b l e m e a s u r e s and c a n , a t l e a s t , be c o n s i d e r e d as a n i n - d i c a t i v e v a l u e .

F i n a l l y , a s f o r t h e e s t i m a t i o n o f ARX2 c o e f f i c i e n t s , a p r o - c e d u r e q u i t e similar t o t h e a n e d e s c r i b e d f o r ARXl h a s been u- s e d ( i n c o r r e s p o n d e n c e w i t h e a c h wind s p e e d c l a s s ) . O b v i o u s l y , s i n c e there i s o n l y o n e n o n l i n e a r t e r m i n e q . ( 2 ) , i n t h i s c a s e o n l y a o n e - d i m e n s i o n a l o p t i m a l s e a r c h on t h e b j - a x i s i s r e q u i r e d W

(20)

by a l g o r i t L k B ) ( e . g . F i b o n a c c i s e a r c h , see for i n s t a n c e W i l d e a n d B e i g h t l e r ( l 9 6 7 ) 1 .

5 . DESCRIPTION OF MODEL SIMULATION RESULTS

F i t t i n g performance o f ARXI and ARX2 on w i n t e r 1978,/79 d a t a F i r s t , the r e p r e s e n t a t i v i t y o f t h e two models ARX1 and ARX2 h a s been checked as f o l l o w s .

-

Model c o e f f i c i e n t s have been a s s i g n e d t h r o u g h t h e A )

-

C)

e s t i m a t i o n a l g o r i t h m (see sect. 3) by u s i n g t h e w i n t e r 1977/78 c o n c e n t r a t i o n and m e t e o r o l o g i c a l d a t a set ( h e r e " w i n t e r " means t h e h e a t i n g s e a s o n 0 c t . l s t

-

March 3 1 s t ) . I n p a r t i c u l a r , t h e b T - c o e f f i c i e n t o f ARX2 ( t h e one m u l t i p l y i n g t h e wind d i r e c t i o n i n p u t N ( k + l ) i n eq. ( 2 ) ) h a s t u r n e d o u t t o b e v e r y n e a r t o z e r o

( i n f a c t s l i g h t l y n e g a t i v e , due t o t h e u n c o n s t r a i n e d o p t i m i z a - t i o n p r o c e d u r e B)) f o r w = I and w = 11. T h i s i s n o t s u r p r i s i n g , b e c a u s e i t i s r e a s o n a b l e t o assume t h a t t h e r e a r e no c o n t r i b u - t i o n s by i n d u s t r i a l s o u r c e s t o p o l l u t i o n i n t h e c i t y c e n t e r f o r

- 1

wind s p e e d l o w e r t h a n 3 m s

.

F u r t h e r m o r e , s e t t i n g a p r i o r i b4 I = b i l = 0 h a s g i v e n a s l i g h t performance improvement, t h u s t h e z e r o v a l u e h a s been d e f i n i t e l y a c c e p t e d f o r t h o s e two

c o e f f i c i e n t s . With t h i s s p e c i f i c a t i o n , t h e o v e r a l r s e t o f ARXI and ARX2 c o e f f i c i e n t e s t i m a t e s i s g i v e n i n T a b l e 1 . .

A s f o r t h e r e s i d u a l s o f t h e r e g r e s s i o n s ( = t i m e s e r i e s o f r e g r e s s i o n e r r o r s ) , t h e i r means have come o u t n e g l i g i b l e .

Moreover, t h e r e s i d u a l s have t u r n e d o u t u n c o r r e l a t e d ( i . e . w h i t e n o i s e ) under t h e c u m u l a t i v e periodogram t e s t ( s e e f o r i n s t a n c e Box and J e n k i n s (1 9 7 0 ) 1

.

-

Then, b o t h models ARXI and ARX2 have been t e s t e d on w i n t e r 1978/79 d a t a . The p e r f o r m a n c e h a s been s a t i s f a c t o r y , a s shown by t h e d i r e c t comparison ( F i g s . 5 and 6 ) between day-by-day ob- s e r v a t i o n s and r e g r e s s i o n v a l u e s . I n p a r t i c u l a r , b o t h models f i t t h e c o n s p i c u o u s measure f l u c t u a t i o n s w i t h a c c e p t a b l e accu- r a c y .

(21)

Table 1 . ( a ) ARX1 a n d ( b ) ARX2 coef f i c i e r l t e s t i m a t e s from w i n t e r 1 9 7 7 / 7 8 d a t a .

1 -

Coefficients

1 I

W i n d speed c l a s s w

1

1w by

(22)

-

OBSERVED

---

COMPUTED

ol I I

OCTOBER

'n

NOVEMBER '70 DECEMBER '78 I

I I I

JANUARY '79 FEBRUARY '79 MARCH '79

F i g u r e 5. Winter 3978/79 observed v e r s u s r e g r e s s i o n concen- t r a t i o n v a l u e s (model AEZX1).

(23)

-

OESERVEO

---

COMPUTED

oL

I I k

OCTOBER '78 NOVLWBER '78 DECEMBER '78

F i g u r e 6 . Winter 1978/79 observed v e r s u s r e g r e s s i o n concen- t r a t i o n v a l u e s (model A R X 2 ) .

0 I I I

JAMUARY ' 7 9 FEBRUARY '79 MAR CH ' 7 9

(24)

The o v e r a l l w i n t e r 1978/79 model p e r f o r m a n c e h a s been eva- l u a t e d by t h e f o l l o w i n g i n d e x e s , r e p o r t e d i n T a b l e -2 :

p

+

c o r r e l a t i o n between o b s e r v a t i o n s and r e g r e s s i o n v a l u e s ;

p E. 7 c o r r e l a t i o n between o b s e r v a t i o n s and r e g r e s s i o n v a l u e s i n

" e p i s o d e " s i t u a t i o n s ; h e r e a n e p i s o d e i s d e f i n e d as a s i t u a t i o n where t h e measured c o n c e n t r a t i o n x ( k ) ( o r y (k) f o r ARX2) e x c e e d s i t s mean p l u s s t a n d a r d d e v i a t i o n ;

a / p $ r a t i o between t h e s t a n d a r d d e v i a t i o n o f t h e r e g r e s - e r r

s i o n e r r o r and t h e c o n c e n t r a t i o n mean;

E

'err same as a e r r / p f b u t i n e p i s o d e s i t u a t i o n s .

-

The day-by-day r a t i o R (k+l) = !b N ( k + l )

by[^

(k+l ) + b T W

,

w = 111, I V , between t h e t h i r d and s e c o n d addendum i n A m 2 h a s been e v a l u a t e d and r e p o r t e d i n F i g . 7. Such r a t i o , u n d e r t h e l i m i

-

t a t i o n s p o i n t e d o u t i n t h e p r e v i o u s s e c t i o n , i s a n i n d i c a t i o n o f t h e w e i g h t o f t h e c o n t r i b u t i o n by i n d u s t r i a l s o u r c e s t o p o l l u t i o n i n t h e c i t y c e n t e r . The o v e r a l l a v e r a g e o f R (&tl)in w i n t e r 1 978/79(i. e

.

by i n c l u d i n g a l s o s i t u a t i o n s u n d e r wind s p e e d c l a s s e s I and 11, when a z e r o c o n t r i b u t i o n by t h e i n d u s t r i a l s t a c k s i s a s s u - med) i s modest ( - 3 % ) . However, as p o i n t e d o u t by F i g . 7 , t h e

T a b l e 2 . P i t t i n g p e r f o r m a n c e o f ARX3 a n d ARX2 on w i n t e r 1978/79 d a t a .

ARX 2 .81 .83 .35

.17

I

I

ARXl

I

P P E

0 err /LI

a E e r r

/uE

.84 .80 .31

. 2 0

(25)

D A Y S

F i g u r e 7 . T i m e p a t t e r n o f r a t i o R i n wind s p e e d classes I11 and I V ( n o n - c o n s e c u t i v e d a y s i n t h e a b s c i s s a ) .

r a t i o R ( k + l ) r e a c h e s n e a r l y 4 0 % i n c e r t a i n d a y s , c h a r a c t e r i z e d by wind* s p e e d i n c l a s s I11 o r I V and by wind blowing from t h e e a s t e r n / s o u t h - e a s t e r n s e c t o r s d u r i n g a r e l e v a n t p a r t of t h e day.

S e n s i t i v i t y o f model p e r f o r m a n c e t o t h e e s t i m a t i o n d a t a s e t S e n s i t i v i t y of model f i t t i n g q u a l i t y t o t h e d a t a s e t u s e d f o r a p p l y i n g t h e c o e f f i c i e n t e s t i m a t i o n p r o c e d u r e A )

-

C)

h a s a l s o been a n a l y z e d . The s e n s i t i v i t y t e s t s h a v e been performed o n l y on ARX1. I n f a c t , ARX2 h a s .a h i g h e r number

of c o e f f i c i e n t s and t h e s t a t i s t i c a l s i g n i f i c a n c e o f their e s t i - mates would become p o o r n e a r t h e l o w e r bound o f t h e s i z e o f t h e e s t i m a t i o n d a t a s e t c o n s i d e r e d by t h e s e n s i t i v i t y t e s t s .

-

F i r s t , i t h a s been a s c e r t a i n e d w h e t h e r i t i s u s e f u l o r n o t t o d i s t i n g u i s h w i t h i n t h e h e a t i n g s e a s o n between t h e months o f O c t o b e r and March and t h e " w i n t e r c o r e " (November-February)

I n p a r t i c u l a r , t h e b e h a v i o u r o f r e s i d e n t i a l h e a t i n g p o l l u t e r s i s l i k e l y t o b e p a r t i a l l y d i f f e r e n t i n O c t o b e r and March, when

some o f t h e o i l b u r n e r s a r e s w i t c h e d o f f o r work f o r a s m a l l e r

(26)

number of h o u r s . Thus, two e s t i m a t e s of ARXl c o e f f i c i e n t s have been c a r r i e d o u t on 1977/78 Z a t a : one by t h e O c t o b e r and M u c h d a t a and one by t h e d a t z of t h e " w i n t e r c o r e " . T h e r e h a s a c t u a l - l y t u r n e d o u t a s l i g h t improvement when f i t t i n g t h e c o n c e n t r a - t i o n of t h e f o l l o w i n g h e a t i n g s e a s o n 1978/79, a s p o i n t e d

o u t by T a b l e 3 .

T a b l e 3 . Performance o f m o d i f i e d A R X l ( d i f f e r e n t c o e f f i c i e n t s between October/Mareh and " w i n t e r c o r e " ) .

Performance Index

Modified ARX 1

1

oE /PE e r r

-

A more s y s t e m a t i c s e n s i t i d * t e s t h a s a l s o been p e r f o r m e d , based on a d a p t i v e c o e f f i c i e n t e s t i m a t i o n . S p e c i f i c a l l y , ARXl c o e f f i c i e n t s have been r e e s t i m a t e d a f t e r e v e r y f i v e d a y s , by u s i n g t h e d a t a of t h e l a s t M d a y s . I n e x p l i c i t words, ARXl c o e f f i c i e n t s a r e f i r s t e s t i m a t e d a c t h e b e g i n n i n g of t h e se- cond w i n t e r , namely on 0 c t . l s t 1978 (by u s i n g t h e d a t a o f t h e l a s t M d a y s o f March 1 9 7 8 ) . Such c o e f f i c i e n t estimates are used f o r f i t t i n g by ARX1 t h e c o n c e n t r a t i o n r e c o r d 0 c t . l s t - O c t .

S t h , 1978. On Oct. 6 t h , t h e c o e f f i c i e n t s are r e e s t i m a t e d ( b y u s i n g t h e d a t a s e t Oct. 1 s t - O c t . S t h , 1978 and t h e l a s t (M-5) d a y s o f March 1 9 7 8 ) . Such new e s t i m a t e s a r e used f o r f i t t i n g t h e concen-

t r a t i o n r e c o r d O c t . 6 t h

-

Oct. l o t h , on O c t . 1 1 t h t h e c o e f f i - c i e n t s a r e r e e s t i m a t e d and s o on,up t o March 3 1 s t 1979.

The o v e r a l l performance i n d e x e s mentioned i n T a b l e 2 have been e v a l u a t e d f o r d i f f e r e n t v a l u e s of M. For i n s t a n c e , t h e p l o t of

p

and

y E

v e r s u s M i s shown i n F i g . 8 . The main c o n c l u s i o n s

(27)

Figure 8 . Performance i n d e x e s

r

and p E v e r s u s "memory" M.

which c a n be drawn from F i g . 8 a r e t h e f o l l o w i n g ( q u i t e

s i m i l a r c o n s i d e r a t i o n s would be s u g g e s t e d by t h e a n a l y s i s of t h e o t h e r two o v e r a l l i n d e x e s o f T a b l e 2 ) .

For low v a l u e s of M t h e r e l i a b i l i t y o f c o e f f i c i e n t e s t i m a t e s i s poor and t h u s model f i t t i n g p e r f o r m a n c e i s low. The q u a l i t y i n c r e a s e s up t o M = 4 0 , which i s t h e r e f o r e a p p r o x i m a t e l y t h e

" o p t i m a l " l e n g t h of t h e d a t a s e t f o r t h e a d a p t i v e c o e f f i c i e n t e s t i m a t i o n ( a c t u a l l y :d h a s Seen v a r i e d w i t h ' B t e n s of 10)

.

For h i g h e r M v a l u e s , t h e r e i s an e v e n c o n s p i c u o u s d e c r e a s e of p e r f o r m a n c e . H e n c e , k e e p i n g memory o f " t o o p a s t " d a t a w o r s e n s

t h e q u a l i t y of t h e f i t t i n g by a d a p t i v e r e g r e s s i o n . T h i s i s

c l e a r l y due t o t h e n o n - s t a t i o n a r i t y of t h e w i n t e r c o n c e n t r a t i o n p r o c e s s , o t h e r w i s e i n c r e a s i n g t h e l e n g t h o f t h e d a t a set s h o u l d g i v e b e t t e r c o e f f i c i e n t e s t i m a t e s and c o n s e q u e n t l y a b e t t e r

p e r f o r m a n c e . Note t h a t h e r e n o n - s t a t i o n a r i t y t u r n s o u t more c o n s - p i c u o u s t h a n i n t h e p r e v i o u s s e n s i t i v i t y t e s t .

I n c o r r e s p o n d e n c e w i t h t h e o p t i m a l M , t h e ARXl f i t t i n g p e r - formances f and

?'

r e a c h . 8 7 and . 9 0 r e s p e c t i v e l y , which a r e s i g n i f i c a n t l y h i g h e r t h a n t h e v a l u e s r e p o r t e d i n T a b l e 2 . There- f o r e , f o r s u i t a b l e "mernory" M , a d a p t i v e r e g r e s s i o n ; namely f r e - q u e n t c o e f f i c i e n t r e e s t i m a t i o n , g i v e s a n improvement w i t h r e - s p e c t t o t h e " b a t c h " r e g r e s s i o n d e s c r i b e d above.

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B e n a r i e , M.M. 1981. A i r p o l l u t i o n m o d e l i n g o p e r a t i o n s a n d t h e i r l i m i t s . I n : M a t h e m a t i c a l M o d e l s f o r P l a n n i n g a n d C o n t r o l o f A i r Q u a l i t y , e d i t e d by G . F r o n z a a n d P. M e l l i . O x f o r d / New York: Pergamon P r e s s ( i n p r e s s ) .

Box, G.E.P., a n d G.M. J e n k i n s . 1970. T i m e - s e r i e s A n a l y s i s , F o r e c a s t i n g a n d C o n t r o l . S a n F r a n c i s c o : Holden-Day.

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s t o c h a s t i c m o d e l s o f s u l p h u r d i o x i d e p o l l u t i o n i n a n u r b a n area. J. A i r P o l l u t . C o n t r o l A s s . 30:1212-1215.

H i m m e l b l a u , D.L. 1 9 7 2 . A p p l i e d N o n l i n e a r Programming. N e w York:

M c G r a w - H i l l .

L b f f l e r , H . 1 9 8 0 . U m w e l t s c h u t z a n d L u f t r e i n h a l t u n g . D e r A u f b a u 34:314-320 ( i n G e r m a n ) .

M c C o l l i s t e r , G . M . , a n d K . R . W i l s o n . 1975. L i n e a r s t o c h a s t i c

m o d e l s f o r f o r e c a s t i n g d a i l y maxima a n d h o u r l y c o n c e n t r a t i o n s o f a i r p o l l u t a n t s . A t m o s p h e r i c E n v i r o n m e n t 9:417-423.

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s p h e r i c smog d i a g r a m . A t m o s p h e r i c E n v i r o m n e n t 6:319-342.

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