International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B7. Istanbul 2004
Figure 5 - Example of the As cosimulated map
30000 199 3
25000
20000 .
T pre J
1000 /
{ Variable Cu:
$0001 } Struct 1: Exponential
j Range: 450m; Sill: 16552 ppm2
0e 500 1000 1500 2000 2500 3000
h (m)
y (h)
250000
200000 . +
150000| ie
| / :
100000 | /
/ Variable Pb:
50000 / Struct 1: Nugget effect. Sill: 50000 ppm’
| Struct 2: Exponential
| Range: 300m; Sill: 111309 pom’
0 500 1000 1500 2000
h (m)
y (h)
450000
400000 :
350000 . °
3000001" A 0$ mid Lii» eA
250000 wr fs
200000 . /
150000| /
190000). / Variable Zn:
50000| / Struct 1: Exponential
à / Range: 750m; Sill: 307762 ppm*
0 500 1000 1500 2000 2500 3000
h (m)
el (h)
5 .
Ames PE em
3 d * .
A64.
/ Variable Cd:
17 Struct 1: Exponential
/ Range: 340m; Sill: 4.20 ppm’
0 T
0 200 400 600 800 1000
h (m)
y (h)
60000 :
50000 : : . :
40000 uU T. 7
SL LJ
A
30000| /
p^
20000 Variable As:
Struct 1: Nugget effect. Sill: 20000 ppm’
10000 Struct 2: Exponential
Range: 500m; Sill: 23740 ppm’
0 7 ;
0 500 1000 1500 2000
h (m)
Figure 6. Variograms of the simulated data
5.2 Hazard Maps
One of the principal aims of this study was to delineate the
areas that need future remediation based on intervention values.
The Consejeria de Medio Ambiente de la Junta de Andalucía
(Environmental Agency of the regional government of the
South of Spain) C.M.A, (C.M.A., 2000) defined for each
contaminant four different remediation levels: maximum level
allowed, recommended investigation, compulsory investigation,
compulsory treatment. Hence joint probabilities of different
metals to be simulated simultaneously, above or under the
remediation levels, can originate hazard maps of the region. The
study area mainly consists of agriculture soils with pH values
lower than 7.
Considering the thresholds: z, (maximum level allowed), z,
(recommended investigation), z; (compulsory investigation) and
Z4 (compulsory treatment), the following joint probabilities, at a
given location xo, can be identified with different hazard levels:
a) Prob (zca(Xo)Czice ZeulX0)<ZiCu> Zzn(X0)<Zızm
Zp(Xo)€Zipo, Zas(Xo)<Zias} corresponds to the most clean
hazard scenario;
b) Prob {zca(Xo) Zacas ZeulXo) Zacw Zzn(X0) Zoz»
ZpXo) Zap» Zas(Xo) Zaas), corresponds to the
intermediate clean hazard scenario, meaning that all metals
at Xo Zp;
c) Prob {ZcalXo) Zscas Zcu(X0) Zscw Zzn(Xo) Z3zm
Zp(Xo) Zspp — Zas(Xo) Zsas}, corresponds to the
intermediate contaminated hazard scenario, meaning that
all metals at x, are greater or equal to zs;
d) Prob {zca(Xo) Zacas Zcu(X0) Zacw Zzn(Xo) Zazm
Zp(Xo) Zapp Zas(Xo) Zaas}, corresponds to the most
contaminated hazard scenario.
We can define a joint indicator using the corresponding
indicator for the different metals: Iz,(Xo) = Iz cq (xo) . 1Z1cu(X0) -
Izip(Xo) . Iziz&(Xo) - Izias(xo). The joint probability at xo —
corresponding to scenario i) — can be estimated with the 10
simulated images:
10
prob, (x,)= n (x,,i) L;(xoi) corresponds to L,;(x)) of
i=l
simulated image 7.
Equivalent joint probabilities can be computed for the other
scenarios: prob,2(Xo), probz3(Xo) and prob,4(xo)-
Finally, a global hazard map was obtained by classifying each
pixel in four defined scenarios (Figure 7). The results show that
approximately 44% of the study area need compulsory
treatment and 40% of the study area need compulsory
investigation.
Since some European legislation impose treatment whenever
one metal exceeds the highest threshold (compulsory treatment),
an alternative for scenario iv was conducted: if at least one
heavy metal exceeds the compulsory treatment threshold the
pixel is considered to belong to scenario iv, i.e., treatment is
imposed to that soil, with Prob {zca(Xo)=Zaca OT Zcu(Xo)7Zacu OT
Zzn(Xo)=Zazn OT Zpp(Xo)=Zapt OT Zas(Xo)=Zaas} -
In this alternative, scenario iv has higher probabilities of
occurring in comparison to the other remediation levels. The
obtained probabilities for this scenario show that approximately
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