Principal tools employed by the city authorities against air
pollution are the drafting and approval of city decrees and city
budgets, approval of land-use and strategic plans. Offices are
instrumental in performing other functions of state administration
and local governments, such as granting building licences,
conducting Environmental
Impact Assessments for new capital investment and development
projects, keeping track of and levying charges upon air pollution
sources, running fuel conversion programmes etc. As to crisis
management functions, the city operates and maintains the Smog
Regulation System (SRS).
The
city has additional professional institutions which participate in
its management processes from the viewpoint of environmental issues.
The City Development Authority of Prague prepares supporting
information and documents for the land-use plan and formulates
conceptual programmes for future development of the city, and is one
of the parties involved in the assessment of capital investment
projects and building licence proceedings. There is a specialised
environmental unit within the Authority the main responsibility of
which is the preparation of supporting data for the land-use plan of
the city.
Another department specialising in environmental information
issues, collection and collation of data from different sources,
management of databases and GIS layers, preparation of outputs for
the city management, experts and general public exists at the
Institute of Municipal Informatics of the City of Prague.
City-sponsored projects include, for example, the Environmental
Information System of Prague (IOZIP) and other related projects –
ATEM (air quality modelling), REZZO (updating and management of data
on air pollution sources), SCOL (a pilot project monitoring organic
compounds), and PREMIS (a project providing access to operational
data from the Automatic Immission Monitoring System and other
information by means of Intranet/Internet).
Comparing the
number of days on which a warning by Smog Control System (SCS) of a
possible smog situation was issued with previous years, there was an
overall decrease in the whole territory of the Czech Republic (1995
- 62 days, 1996 - 42 days, 1997 - 40 days). Owing to very poor dispersion conditions especially in January
the number of days on which restrictions were imposed was slightly
higher (1995 - 14 days, 1996 - 6 days, 1997 - 11 days). The month of
January accounted for 36 out of the total of 40 warning days and for
all of the restriction days. Compared to 1996 the number of warning
days in Prague increased by one but there were no automotive traffic
restrictions imposed in 1997.
Distribution of days with SCS signals for all smog
areas of the Czech Republic
|
Year
|
North
Bohemia |
Prague
|
Region
Ostrava |
Region
Melník |
|
warning
|
restriction |
warning
|
restriction |
warning
|
restriction |
warning
|
restriction |
|
1993
|
36
|
27
|
26
|
11
|
32
|
3
|
13
|
6
|
|
1994
|
8
|
5
|
35
|
-
|
8
|
2
|
-
|
-
|
|
1995
|
10
|
8
|
31
|
-
|
15
|
4
|
-
|
-
|
|
1996
|
22
|
4
|
10
|
1
|
10
|
1
|
-
|
-
|
|
1997
|
9
|
8
|
11
|
-
|
14
|
3
|
6
|
-
|
Source:
CHMÚ
Because of
unfavourable dispersion conditions a warning was issued for the
period from January 14 till January 20, 1997. However, the
concentrations were not high enough to justify traffic restriction
measures. While concentrations of nitrogen oxides reached high
values (up to 600 µg.m-3) for short periods of time, they
invariably dropped around noon and in nighttime hours. Another
warning signal was issued between November 7 and 10, 1997. In this
case too, the concentration of pollutants was not high enough to
justify imposing regulatory measures.
The operation of
Smog Control Systems in the Czech Republic has been extended to the
warm season as well, when near-ground concentrations of ozone become
a major concern. As a rule, the highest concentrations occurring for
a longer period of time were previously confined to April and May.
During 1997 conditions favouring the formation of high
concentrations of ozone did not materialize. The special ozone
concentration imission limit of 180 µg.m-3 was recorded
by a few monitoring stations in the Czech Republic during the year.
In Prague, the limit was exceeded only for two hours at the Libuš
station (191 µg.m-3) and for one hour in Kobylisy (183
µg.m-3).
Smog
Contingency Measures, Air Pollution Charges
Crucial activities of
the Department of Environment of the Prague City Hall include
contingency measures instituted in cooperation with other
authorities during a smog situation, as well as keeping track of,
levying and collecting charges payable by medium-sized air pollution
sources under Act No. 389/1991.
Medium-sized air pollution sources paying
appropriate charges to the Department of Environment of the Prague
City Hall as of September 1, 1997
|
|
Number of sources |
Charges [CZK 1000] |
Emissions [t] |
|
solids
|
SO2 |
NOx |
CO
|
CxHy |
|
Boiler
rooms |
2 466
|
5 098
|
577.225
|
973.621
|
603.281
|
2
306.9538 |
533.952
|
|
Technology
|
324
|
1 794
|
88.872
|
0.966
|
9.618
|
31.476
|
272.575
|
|
TOTAL
|
2 790
|
6 893
|
666.097
|
974.587
|
612.899
|
2 338.429
|
806.527
|
Source: OZP
MHMP
Review of
measures instituted under the Smog Ordinance since 1992
|
Year
|
Warning
|
Regulatory measures applied to stationary sources
|
Road
traffic restrictions |
|
number/days |
number/days |
number/days |
|
92 - 93
|
5/26
|
3/12
|
1/4
|
|
93 - 94
|
6/31
|
2/7
|
|
|
94 - 95
|
3/15
|
|
|
|
95 - 96
|
5/34
|
|
|
|
96 - 97
|
2/11
|
|
1/2*
|
|
97 - 98
|
3/9
|
|
|
* New Smog Ordinance
No. 58/1996 of the City Council of the Prague City Hall -
regulations of stationary sources and traffic restrictions are
declared and instituted simultaneously.
number/days = number
of instances/duration
Source: OZP
MHMP
Smog alarms declared and called off in 1997/1998
|
WARNING
|
REGULATION |
|
declared
|
called
off |
declared
|
called
off |
|
November
7, 1997, 1 p.m. |
November
10, 1997, 10 a.m. |
|
|
|
January
11, 1998, 8 p.m. |
January
13, 1998, 2 p.m. |
|
|
|
January
27, 1998, 4 p.m. |
January
28, 1998, 3 p.m. |
|
|
Source: OZP
MHMP
Issues of a photochemical smog warning signal in
1998
|
INFORMATION |
WARNING
|
|
declared
- called off |
declared
- called off |
|
August
12, 1998 1 p.m. - 7 p.m. |
|
|
August
17, 1998 4 p.m. - 6 p.m. |
|
|
August
18, 1998 3 p.m. - 7 p.m. |
|
Source: OZP
MHMP
Stationary air pollution sources affected by
regulatory measures (as of October 1, 1998)
|
Source
name and address |
Category
|
|
Czech
Railways Engine Shed, Masaryk Station, Praha 1, Hybernská 13
|
large
|
|
Škoda -
ÚJP Praha a.s., Nad Kamínkou 1345 |
large
|
|
Ministry
of Interior of the Czech Republic, Pelléova |
large
|
|
Prazská
teplárenská, Division Malešice, Praha 10 |
large
|
Source: OZP
MHMP
Medium-sized air pollution sources affected by
regulatory measures (as of October 1, 1998)
|
|
Number of sources |
Consump- tion of fuel |
Emissions [t] |
|
[103 t.m3] |
solids
|
SO2 |
NOx |
CO
|
CxHy |
|
Boiler
rooms |
2 466
|
|
577.25
|
973.6
|
603.3
|
2 306.953
|
534.0
|
|
- coke |
465
|
47 264.62
|
423.1
|
478.8
|
73.4
|
2 114.9
|
467.7
|
|
- brown coal |
25
|
7 865.76
|
107.1
|
142.6
|
27.0
|
88.1
|
20.8
|
|
- wood |
8
|
1 503.48
|
21.1
|
4.0
|
4.9
|
11.8
|
3.8
|
|
- LFO |
103
|
9 894.36
|
20.8
|
322.7
|
95.1
|
6.1
|
4.7
|
|
- petroleum |
16
|
11.27
|
0.012
|
0.114
|
0.058
|
0.008
|
0.003
|
|
- NG |
1 746
|
218 218.8
|
4.291
|
2.0
|
384.1
|
67.1
|
27.4
|
|
- others |
85
|
|
0.776
|
23.4
|
18.7
|
19.0
|
10.3
|
|
Technology
|
324
|
|
88.9
|
1.0
|
10.1
|
31.5
|
272.6
|
|
- filling-stations |
108
|
|
|
|
|
|
136.5
|
|
- painting enterprises |
59
|
|
0.2
|
|
|
|
55.2
|
|
- joineries |
11
|
|
6.3
|
|
|
|
|
|
- printing industry |
85
|
|
0.24
|
|
|
|
66.4
|
|
- dry-cleaners |
23
|
|
|
|
|
|
0.4
|
|
- crematories |
4
|
|
1.3
|
0.96
|
5.6
|
1.4
|
0.04
|
|
- others |
34
|
|
80.9
|
0.1
|
|
30.090
|
14.0
|
|
TOTAL
|
2 790
|
|
666.1
|
974.6
|
612.9
|
2 338.4
|
806.6
|
Source: OZP
MHMP
Analysis
of air quality measurement network
In 1998, the
National Institute of Public Health (SZÚ) undertook an analysis the
purpose of which was to optimize the network of monitoring stations
operated by the Public Health Office in the territory of Prague. The
project made use of data acquired between 1991 and 1997 by a total
of 24 stations operated by the Public Health Office and the Czech
Hydrometeorological Institute (13 AIM stations and manual and
semi-automatic stations of the Public Health Office). A list of the
stations, including their locations, is presented in Chapter 1B.1.
The analysis was
based on an evaluation of imission data and an assessment of the
exposure of population in accordance with recommendations of the
World Health Organization (WHO).
Model-based evaluation of air quality (ATEM
project)
Between 1997 and
1998, the ATEM project was focusing on the following four principal
areas:
• an evaluation
of the new emission and imission situation in the territory of
Prague in the framework of the Updating 1998 project (the completion
date of which was later than the closing date of the 1998 Yearbook)
• an assessment
of plans and intentions laid down in the draft Land-Use Plan of the
City of Prague from the viewpoint of the air quality anticipated in
the year 2010
• an evaluation
of capital investment/development plans by means of alternative
model calculations (supporting data for Environmental Impact
Assessments, land-use planning, land-use rulings)
• consulting
services provided to public servants working for city authorities.
The purpose of
the exercise was to assess plans and intentions laid down in the
Land-Use Plan from the viewpoint of the air quality
in the territory of Prague as of the year 2010. The changes were
compared against the 1996 benchmark (the latest completely updated
set of data for Prague). The results show that the implementation of
the intentions set forth in the Land-Use Plan will have a positive
impact on the air quality in Prague. More specifically, there should
be, in particular, a significant decrease in concentrations of
suspended particulate matter, sulphur dioxide, and carbon monoxide.
Similarly, there will be slight improvement of the overall average
imission load of nitrogen oxides. The situation will get worse along
new roads, but the city as a whole (including its centre) will show
an improvement. The changes are a logical consequence of the trend
the beginnings of which date back to the early 1990s. Positive changes cannot be expected
especially insofar as concentrations of nitrogen oxides in the close
vicinity of major roads. Results of the model calculations confirm
that, in spite of the fast renovation of the rolling stock, there
will be a slight local deterioration of the present imission load
due to a dramatic growth of automotive traffic.
Alternative calculation -
draft Land-Use Plan, outlook in the year 2010
a) model
array b) differential
map
Alternative model calculations permit to
evaluate the impact of every capital investment project, plan, or
concept on the quality of air in Prague, and to seek solutions
minimizing the impact of every new or refurbished source on the
quality of the air in its close vicinity. The studies undertaken
since 1996 include, for example, the gas-steam heat generation plant
in the seventh district of Prague (Holešovice); conversion of the
heating system of Narex company in the tenth district to gas; the
New Smíchov commercial and cultural center in the fifth district and
so on.
Insofar as stationary sources are concerned, the most
comprehensive assessment based on alternative modeling was done for
the area of the Prague Historical District (PHD). After an
evaluation of the contribution of each source to the overall
atmospheric pollution, different energy supply scenarios, i.e.
gasification (Alternative A) and electrification (Alternative B),
and their effects on the imission situation of the Historical
District were assessed. Later on, an alternative based on a proposal
submitted by the City Development Authority of Prague was added
(Alternative C), which took into account specific possibilities of
supplying various parts of the area under study with different types
of energies.