section 1 of this Regulation shall apply to operations with the combustion of
solid or liquid waste in an incineration plant and
activities with the treatment of waste waters from the cleaning of
exhaust gases from an incinerator. Regulation
contains provisions on the
– the application of (2 – 20 sections),
– waste and residues (21-26 sections),
– certain preventive measures (paragraphs 27 to 30),
-chimney, temperature, support burners, absolute
limit values and heat recovery (paragraphs 31 to 37),
-measurements and measurement results (§§ 38-53),
-calculations of dioxins and furans (54),
-calculations in the percentage of oxygen (55),
– emissions to air from waste incineration plants
(paragraphs 56 to 66),
– emissions to air from co-incineration in cement kilns
(paragraphs 67 to 70),
– mixing calculation for co-incineration (paragraphs 71 to 79),
– air emissions from energy plants (80-96 section),
– air emissions from industrial facilities (paragraphs 97 to 99),
– emissions, waste water (100 – 103 §§)
– change of an activity (paragraph 104),
– dispenser (105),
-information in the environmental report (106), and
– information to the environmental protection agency and the European
the Commission (paragraphs 107-109).
The regulation is notified pursuant to Chapter 9. section 5 of the environmental code in
question about 17 to 47 and 49 to 103 sections, with the backing of the chapter 9. 6 §
the environmental code in terms of section 104 and otherwise under Chapter 8.
section 7 of the Constitution.
Definitions
section 2 of the waste and domestic waste for the purposes of this regulation,
the same as in chapter 15. the environmental code.
section 3 of the hazardous waste and waste oils as referred to in this regulation
the same as in the waste regulation (2011:927).
4 section With incineration of waste referred to in this regulation
thermal treatment of waste by oxidation or other
heat treatment processes such as pyrolysis, gasification or
plasma process, insofar as the topics from the treatment then
burnt.
paragraph 5 of the combustion plant as referred to in this regulation a
stationary or mobile technical plant where waste
burnt. In an incineration plant within the meaning of this
regulation included
1. the entire facility and the area belonging to the facility
with all incineration lines, areas, equipment and
system linked to the waste treatment, and
2. everything in the plant related to thermal treatment
of waste by oxidation or any subsequent
combustion process.
section 6 of the waste incineration plant referred to in this
Regulation a combustion plant
1. intended for incineration, with or without
recycling of produced energy,
2. where the incineration of waste is done in such a way that it
main purpose of the plant is not considered
the production of energy or materials,
3. where more than 40% of the resulting heat release comes from
incineration of hazardous waste, or
4. where it is incinerated household waste than waste
According to annex 4 to the waste regulations (2011:927)
of any of the waste types in Chapter 20 01 and is
sorted or is covered by any of the waste types in
under Chapter 20 02.
7 § With co-incineration plant in accordance with this regulation a
combustion plant
1. is mainly intended for the production of energy or
material but where waste is used as a regular or
additional fuel or heat treated in order to be able to
disposed of, and
2. is not a waste incineration plant.
section 8 of this regulation, '
energy plant: co-incineration plant that mainly
produce energy, and
industrial plant: co-incineration plant that is not a
energy plant or cement furnace.
section 9 With stack referred to in this regulation cover a design
contains one or more exhaust gas channels through which
the flue gas is discharged in the air.
section 10 of the supervisory authority referred to in this regulation, the
According to the environmental protection Decree (2011:13) exercises
operational oversight of a combustion plant.
section 11 of this regulation, '
State: such a condition referred to in Chapter 9.
Environment Act or the equivalent older provisions,
licensing conditions: a condition of a permit that is valid for
a combustion plant, and
injunction constraint: a constraint in an order from
the supervisory authority addressed to the operator of the activity
on a combustion plant.
section 12 Of 2002-facility referred to in this regulation cover a
combustion plant
1. by 28 december 2002 was operational and was covered by
a condition,
2. by 28 december 2002 were subject to a condition
or of a notification under regulations issued by
support of Chapter 9. section 6 of the environmental code, and was operational by 28
December 2003,
3. before 28 december 2002, was subject to a complete and
complete application for a permit and was operational by the
december 28, 2004, or
4. is one co-incineration plant incineration of waste
began before on 28 december 2004, on the complex was then
in operation as a stationary or mobile plant intended for
the production of energy or material and subject to the
permit required for the plant before the burning of
waste was started.
section 13, 2013-plant referred to in this regulation cover a
combustion plant has been in operation before 7
January 2014, if the facility before 7 January 2013
covered by a State or by a complete and
complete application for a permit.
section 14 With normal dry gas referred to in this regulation cover dry flue gas
normalized to 273.15 kelvin temperature and pressure
101.3 kilopascals.
section 15 for the purposes of this regulation,
antimony: antimony and its compounds, expressed as
antimony,
arsenic: arsenic and its compounds, expressed as
arsenic,
lead: lead and its compounds, expressed as lead,
cadmium: cadmium and its compounds, expressed as
cadmium,
Cobalt: cobalt and koboltföreningar expressed as
cobalt,
copper: copper and its compounds, expressed as copper,
chromium: chromium and chromium compounds, expressed as chromium,
Mercury: Mercury and its compounds, expressed
like mercury,
NOx: nitrogen dioxide and nitrogen monoxide expressed as
nitrogen dioxide,
manganese: manganese and manganese compounds expressed as manganese,
Nickel: nickel and its compounds, expressed as nickel,
suspended solids: organic or inorganic particles
who can settle, and
Vanadium: vanadium and its compounds, expressed as
vanadium.
16 § With residual product referred to in this regulation
liquid or solid waste that occurs in a
waste incineration plant, or
co-incineration plant.
Exemptions from the application of
section 17 of this Regulation shall not apply to establishments where
the waste is treated only
1. waste vegetable matter from agriculture or
forest management and can be used as fuel for recycling
energy content,
2. vegetable waste from agriculture and forestry,
3. vegetable waste from the food processing industry, if the
heat generated by the incineration is recovered,
4. fibrous vegetable waste incurred by
production of paper from pulp or paper production
from pulp, if it is co-incinerated at the place of production
and the heat generated by the incineration is recovered,
5. the Cork waste,
6. wood waste, wood waste is a waste of
because it is construction or demolition waste or of any
Another reason is likely to contain organic
halogenated organic compounds or heavy metals as a result of treatment
with wood preservatives or coating,
7. radioactive waste,
8. animal bodies, subject to the other provisions of
animal carcasses, or
9. waste from prospecting or mining of an oil-
or gas discovery from an offshore platform, if the waste
burnt on the platform.
section 18 of this Regulation shall not apply to
1. experimental facilities for research, development and
testing in order to improve the incineration process, if the
treat less than 50 tonnes of waste per year,
2. gasification or pyrolysis plants, if gases from
gasification or pyrolysbehandlingen is purified in such
extent that they, when they in turn are burned, do not entail
higher emissions than burning natural gas, or
3. waste explosives that for security reasons, can not
incinerated in a facility that meets the requirements of this
Regulation or the provisions adopted pursuant to
the regulation.
Conditions in permits and orders
section 19 of this Regulation shall apply in addition to the licence conditions and
order conditions.
Operation, maintenance and control of combustion plants
section 20 of The doing business with the incineration of waste at
an incineration plant shall ensure that
1. the operation and control of the plant is carried out by at least
a natural person who is competent to manage the plant,
and
2. the measures taken otherwise necessary to comply with this
Regulation.
Acceptance of waste
section 21 of the operator of an incineration plant shall, for the
waste is received or intended to be received for the combustion
1. understanding of what waste is a waste type
attributable to according to annex 4 to the waste regulations
(2011:927),
2. check that the waste should be incinerated in
the facility and must be incinerated in the,
3. record the amount received in each waste type
or, to the extent that it is not possible to attribute the waste
to a certain type of waste, in the notes describe the
physical, physical and chemical properties and any
hazardous properties,
4. save your notes in three years, and
5. leave notes to the supervisory authority if
authority requests it.
section 22 of the operator of an incineration plant shall, before
hazardous waste is received for incineration
1. obtain information about waste and its emergence
contained in the documents required under the
a) European Parliament and Council Regulation (EC) No 1013/2006
of 14 June 2006 on shipments of waste,
b) Act (2006:263) on the transport of dangerous goods or
regulations issued under the Act, or
c) waste regulations (2011:927),
2. obtain the additional information in the case of
its physical and chemical composition, in terms of
the hazardous properties of the waste, in the case of substances which are waste
cannot be mixed with, in the case of precautionary measures required
in the handling of the waste or otherwise needed to
assess its suitability for the intended incineration,
3. ensure that the waste is in compliance with
the information referred to in 1 and 2, take representative
samples and analyze them,
4. save the samples until a month has passed from the
the waste is burned, and
5. submit the samples to the supervisory authority, if the authority
request it.
Samples as referred to in the first subparagraph 3 should be taken before the waste unloaded
at the facility, if this is not inappropriate. The samples must
be taken and analyzed in a way that makes it possible for
the operator and the supervisory authority to determine
in the nature.
section 23 of The permit conditions or conditions that
means that the requirements of sections 21 and 22 in whole or in part
need to be met may be used, if the condition relating to such
incineration of waste
1. takes place in an activity covered by Chapter 2. section 1, Chapter 4. 12
or section 16, Chapter 5. 1, 4, 10, 18, 19, 34, 35, 37 or 39 §,
Chapter 6. section 1, Chapter 7. section 1, Chapter 8. 1 or section 6, Chapter 9. 1 or 2
§, Chapter 11. 2 or 4 section, Chapter 12. 1, 2, 3, 5 or section 14,
Chapter 14. 1, 5, 8, 10 or section 14, chapter 15. 1, 3, 6, 9, 10 or
section 14, Chapter 16. section 1, chapter 17. section 4, chapter 19. section 1, chapter 21. 1, 5
or section 6, Chapter 28. paragraph 3, or 29. 3, 18, 19, 22, 23, 24,
25, 30, 35, 36, 38, 39, 49, 50, 54 or 58 §
Environmental Assessment Regulation (2013:251), and
2. only covers waste generated in the
licensed activities and in the place where the
combustion takes place.
Management of waste
section 24 the operator of an incineration plant shall, in the case of
to receive waste and leave waste take the measures
needed to, as far as possible, prevent or restrict
pollution of air, soil, surface water and groundwater, other
negative effects on the environment, as well as odors, noise, and other
inconvenience to people's health.
section 25 of the Waste from the healthcare system as referred to in
regulations announced by the National Board of health and welfare is infectious
refuse must not be confused or kept in other
types of waste. It should be placed straight in the furnace without direct
handling.
section 26 of the operator of an incineration plant shall, in the case of
residues shall take the necessary measures to
1. minimize restprodukternas amount and harmfulness,
2. transport the dry dust in such a way that it does not
spread in the environment,
3. analyze residues in order to determine their
physical and chemical characteristics and the polluting potential,
and
4. recycle the residues in or outside the plant, if
This is possible.
The analyses referred to in the first subparagraph 3 should refer to restprodukternas
total soluble fraction and the soluble fraction of
heavy metals. Analyses should be made before deciding on
which way the residues to be recovered or
disposed of.
Measures to prevent unauthorized or accidental discharges
section 27 of an incinerator and the landfill and
other areas belonging to the facility to have the design
and operations on them, will be carried out as
1. that the facility, areas and operation are appropriate
to prevent unauthorized or accidental discharges of
polluting substances into soil, surface water and groundwater,
2. that there is the capacity to store polluted storm water from
the plant and the areas that belong to it and store
such water in areas that have been contaminated in connection with
spillage or fire-fighting operations, and
3. that the capacity referred to in 2 is sufficient to
water, when necessary, to be analyzed and treated before the
are placed.
section 28 of an incineration plant shall be equipped with a
operation of the automatic system that prevents administration of
waste during periods when
1. the plant starts until the temperature is reached in the
the flue gases as required by this regulation,
2. the temperature of the flue gases required under this
Regulation is not maintained, and
3. the continuous measurements required by this
regulation shows that a limit value
is exceeded and the overrun is due to disturbances or failures of the
flue gas cleaning equipment.
If a permit conditions or conditions in terms of
a given waste category or a specific thermal process involves
requirements for different temperature than the one referred to in the first subparagraph 1
and 2, to the temperature specified in condition apply when
the first subparagraph of paragraph 1 and 2 shall be applied to the waste category
or process. The condition, however, should not be applied so as to
causes more waste products or higher levels of polluting
organic compounds in sewage sludge.
section 29 of an incineration plant shall be of a design and
operations on the conducted so that
1. If a limit value according to §§ 56-100
is exceeded
a) incineration of waste never incessantly continues with
exceeded the limit value for longer than four hours in
facility or in a single oven that is connected to the
equipment for flue gas treatment that the overrun is attributable
to, and
(b)) the duration of the burning continues with exceeded
the restriction value exceeds 60 hours per
years, and
2. in the event of a breakdown, the operation is being restricted or stopped as soon as
practicable and until normal operations can
resume.
A provision on the absolute limit values during periods
referred to in the first subparagraph are found in section 34.
Measures to reduce slag, bottom ash and
loss of ignition
section 30 when burned in an incineration plant shall
the measures taken in respect of the pre-treatment of waste and
the operation of the facility is needed to
1. the total amount of organic carbon in the slag and bottom ashes
should be less than three percent of the dry weight of the material, or
2. their loss on ignition must be less than five per cent of
dry weight.
Chimney
section 31 of the Emissions of exhaust gases from an incinerator shall
be done in a controlled manner through a chimney that has the
height needed to protect human health and the environment
as well as taking into account the environmental quality standards for air quality.
The furnace gas temperature
32 § an incineration plant shall be designed, equipped
and built and operated in such a way that, even in the
most unfavourable conditions, the temperature of the combustion gases in the
the combustion process is raised in a controlled and homogeneous
way to
1. at least 850 degrees Celsius and keeps at least that level during
at least two seconds, or
2. at least 1 100 degrees Celsius and keep at least the level
for at least two seconds, if the loss relating to dangerous
waste containing more than 1% organic
halogen compounds expressed as chlorine.
In a waste incineration plant to temperatures measured
near the inner wall of the combustion chamber. The measurement may be
be made at another representative point of the combustion chamber,
If such a measurement point is specified in a licence conditions or
order conditions. In a waste incineration plant shall
requirement referred to in the first subparagraph if the two-second residence time for
the flue gas after the last administration of the
combustion air.
A permit conditions or conditions in question
If a given waste category or a specific thermal process
different from what is stated in the first and second subparagraphs,
applied. In the case of waste incineration plants, a
such application however does not cause more residues or
higher concentrations of polluting organic substances in
the residues.
Support burner
33 § in a waste incineration plant, each line be
equipped with at least one support burner
1. start automatically when the temperature of the combustion gases after the
the last supply of combustion air
a) is less than 850 degrees Celsius, or
b) is less than 1 100 degrees Celsius, if loss concerns
hazardous waste containing more than one percent organic
halogen compounds, expressed as chlorine, and
2. use during periods when the plant is put into operation or
be taken out of service so that the temperature required by 1
are maintained when there is unburned waste in
the combustion chamber.
During the periods referred to in the first subparagraph 2 shall support burner
not be fired with a fuel that can cause higher emissions than
what the resulting from the combustion of diesel fuels referred
in 4 and 5 §§ sulfur Regulation (2014:509).
A permit conditions or conditions in question
If a given waste category or a specific thermal process
different from what is stated in the first and second subparagraphs,
applies, if it does not cause more residues or higher
levels of polluting organic compounds in sewage sludge.
Regulation (2014:512).
Absolute constraint values
34 section During a period referred to in section 29 as a
exceeding of a limit value is in progress or when a
accident emissions into air from a
waste incineration plant shall not under any circumstances
on average during each half-hour in terms of
1. dust contain more than 150 milligrams per cubic meter of normal
dry gas,
2. total organic carbon contain more than what is said in paragraph 59,
and
3. carbon monoxide include more than what is stated in paragraph 66
subparagraph 2 (a).
35 section where for one co-incineration plant shall apply
any such permit conditions or conditions that
referred to in section 28, 32 or 33, emissions into the air from the
the plant does not contain
1. more total organic carbon than that which corresponds to the requirements of a
waste incineration plant in 57 § 2 and § 59, or
2. more carbon monoxide than the corresponding to the requirements of a
waste incineration plant in section 66.
36 § From one co-incineration plant which is a bark-fired boiler
in the pulp and paper industry emissions into air
contain more total organic carbon than that which corresponds to
the requirements for a waste incineration plant in 57 § 2 and § 59,
If
1. boiler was in operation and was subject to a condition
before 28 december 2002 and
2. such permit conditions or conditions that
referred to in section 28, 32 or 33 is applied to the bark boiler.
Recovery of heat
37 § any heat generated in the combustion plant shall
be recycled as much as possible.
Measurements
38 section At an incinerator, the measurement equipment and
technology can be used as needed to monitor and control
compliance with this regulation.
section 39 the measurements made for pursuant to this regulation
check the pollutants in the emissions to air and water,
be made in such a way that the measurement results are
representative of the actual concentration of
pollution.
Emission controls under this Regulation shall be in a manner
consistent with relevant and current standards
has been developed by the European Committee for standardisation
CEN in the field of
1. sampling and analysis of pollutants,
2. quality assurance of automated measuring systems, and
3. reference methods to calibrate automated measurement
measuring systems.
If there is no relevant and current CEN standard,
should the control be done in a way that has an equivalent
scientific quality and conform to a standard that
has been produced by the International
Organization for Standardization (ISO) or any other
international or national standard.
section 40 of the automated measuring systems used for emission control
at least once annually checked for
installation and function by means of parallel measurements with the
reference methods of measurement.
41 § automated measuring systems shall be so designed that in case
a constraint value under this regulation relating to the
average for one day's measurement uncertainty expressed as
95% confidence interval for individual measurement values, in
question about
1. carbon monoxide not more than 10% of the limit value,
2. sulfur dioxide up to 20 per cent of the limit value,
3. nitrogen dioxide up to 20 per cent of the limit value,
4. dust up to 30% of the limit value,
5. total organic carbon less than 30% of
limit value,
6. hydrogen chloride up to 40 per cent of the limit value, and
7. hydrogen fluoride not more than 40 per cent of the limit value.
Measurement of flue gas
42 § measurements of flue gases in a combustion plant shall
1. in the case of temperature, pressure, oxygen content and content of
water vapor is made continuously, and
2. in the case of residence time, minimum temperature and the oxygen content of
be done in an appropriate manner at least once when the
the property is placed in service and under the most unfavourable
conditions of overload.
Notwithstanding the first subparagraph 1 does not need the water vapour content
be measured continuously, if the sampled exhaust gas is dried before the emissions
analyzed.
Measurement of pollutants in emissions to air
43 § measurements of emissions to the air from a
incineration plant shall
1. in the case of dust, TOC, HCL,
hydrogen fluoride, sulphur dioxide, nitrogen oxides and carbon monoxide be made
continuously, and
2. in the case of mercury, cadmium, thallium, arsenic, lead,
chromium, copper, nickel, zinc, dioxins and furans shall be made at least
once every three months during the first 12
operation months and then at least twice a year.
Despite the first paragraph 1 need measurements of HF won't
be done continuously, if such processing steps is used as
ensure that the limit value of the emissions of hydrogen chloride
compliance and emissions of HF instead measured periodically
According to that of the polluting substances referred to in the first
subparagraph 2.
section 44 authorisation conditions or conditions that
means that there is no need for continuous measurement of
hydrogen chloride, hydrogen fluoride, or sulphur dioxide may be applied, if
emissions of the pollutant can under no circumstances be
exceed the throttling values in this regulation.
Measurement of pollutants in waste water
45 § wastewater from an incineration plant shall
be checked at the point where the waste waters are discharged and
by
1. continuously measure the water's acidity (pH), temperature
and flow,
2. at least once a day, take the sampling for total
suspended matter or take representative
flow-proportional dygnsprover,
3. at least once a month to a representative
monthly daily tests for mercury, cadmium,
thallium, arsenic, lead, chromium, copper, nickel and zinc, and
4. at least once every three months during the first
twelve months of operation and thereafter at least once every six months to measure
dioxins and furans.
Measurements as referred to in the first subparagraph 2 to 4 shall be made with unfiltered
sample. In the case of suspended solids, the measurements
be made as required by regulations that have
issued under Chapter 9. section 5 of the environmental code on the control of
urban waste water discharges.
section 46 Of the waste water from the purification of exhaust gases is treated on the
a combustion plant together with urban waste water
other sources at the facility, the measurements according to § 45
be done
1. on the waste water stream from the exhaust gases prior to its input
to the common facility for the treatment of
waste water,
2. on the other waste water stream or streams prior to its or their input into the
common plant for the treatment of waste water,
and
3. at the point where the waste waters are discharged after
complete purification.
Sampling and measuring points
47 § If the location of the sampling or measurement points are not
determined in a permit for an incineration plant, the
the operator of the facility to propose a location and submit
the proposal to the supervisory authority.
48 section in a case referred to in section 47, the supervisory authority shall
decide where the sampling or measurement points shall be placed
and submit to the operator to comply with the decision.
Measurement results
49 § all measurement results from the monitoring of emissions as needed
to comply with this regulation, or to comply with the
condition that the property is subject to registration,
processed and presented in a way that makes it possible for
the supervisory authority to check that the regulation and
authorization are followed.
section 50 of the results of the measurements referred to in sections 43 and 44 shall be counted
If taking into account the oxygen levels under this regulation
apply to the current limitation value and according to the
the calculation rule in section 55.
For a facility where hazardous waste is incinerated and emissions
of pollutants are reduced by exhaust gas treatment, recount
referred to in the first subparagraph shall be done only if the oxygen content measured
in connection with the measurement of the pollutant
exceed the oxygen content referred to in the first subparagraph.
A permit conditions or conditions which means
the recalculation shall be made to another certain oxygen level than the
referred to in the first subparagraph may be applied, if the waste
incinerated in a syreanrikad atmosphere and the oxygen content
specified in the condition reflects the particular circumstances
added to because of it.
51 § average values for days, half hour periods and
ten minute periods laid down in this Regulation shall relate to the periods
When the plant is in operation. Periods when the plant is put into
operation or is taken out of service to be covered only if the waste
burned during such a period.
Average values for half hour periods and
ten minute periods should be validated for the uncertainty of measurement,
multiply the average of days in case of
1. carbon monoxide with 0.90,
2. sulfur dioxide by 0.80;
3. nitrogen oxides by 0.80;
4. dust with 0.70,
5. total organic carbon with 0.70,
6. hydrogen chloride with 0.60,
7. hydrogen fluoride with 0.60.
These validated values are the values that should be compared to
throttle values.
52 § an average value for the day is invalid if more than five
of the half-hourly average values over a day have been rejected on
because of a malfunction in the automatic measuring system or
maintenance of the system.
section 53 for one year, a maximum of ten average values for days
discarded due to malfunction in the automatic
the measuring system or the maintenance of the system.
Calculation of dioxins and furans
§ 54 the provisions of this regulation concerning dioxins and
furans refers to polychlorinated dibenzo-p-dioxins and
dibenzofurans. For the purposes of the regulation, the
total concentration of dioxins and furans calculated using
account of the dioxinernas and furanernas toxicity
so that the total concentration is specified as the sum of
1. the concentration of 2, 3, 7, 8-tetraklordibensodioxin
(TCDD) multiplied by the toxic ekvivalensfaktorn 1,
2. the concentration of 1, 2, 3, 7, 8-pentaklordibensodioxin
(PeCDD) multiplied by the toxic ekvivalensfaktorn
0.5,
3. the concentration of 1, 2, 3, 4, 7,
8-hexaklordibensodioxin (HxCDD) multiplied by the toxic
ekvivalensfaktorn 0.1,
4. concentration of 1, 2, 3, 6, 7, 8-hexaklordibensodioxin
(HxCDD) multiplied by the toxic ekvivalensfaktorn
0.1,
5. the concentration of 1, 2, 3, 7, 8,
9-hexaklordibensodioxin (HxCDD) multiplied by the toxic
ekvivalensfaktorn 0.1,
6. the concentration of 1, 2, 3, 4, 6, 7,
8-heptaklordibensodioxin (HpCDD) multiplied by the
toxic 0.01 ekvivalensfaktorn,
7. the concentration of oktaklordibensodioxin (OCDD)
multiplied by the toxic 0.001 ekvivalensfaktorn;
8. concentration of 2, 3, 7, 8-tetraklordibensofuran (TCDF)
multiplied by the toxic ekvivalensfaktorn 0.1,
9. the concentration of 2, 3, 4, 7, 8-pentaklordibensofuran
(PeCDF) multiplied by the toxic ekvivalensfaktorn
0.5,
10. the concentration of 1, 2, 3, 7,
8-pentaklordibensofuran (PeCDF) multiplied by the toxic
ekvivalensfaktorn 0.05,
11. the concentration of 1, 2, 3, 4, 7, 8-hexaklordibensofuran
(HxCDF) multiplied by the toxic ekvivalensfaktorn
0.1,
12. the concentration of 1, 2, 3, 6, 7,
8-hexaklordibensofuran (HxCDF) multiplied by the toxic
ekvivalensfaktorn 0.1,
13. the concentration of 1, 2, 3, 7, 8, 9-hexaklordibensofuran
(HxCDF) multiplied by the toxic ekvivalensfaktorn
0.1,
14. the concentration of 2, 3, 4, 6, 7,
8-hexaklordibensofuran (HxCDF) multiplied by the toxic
ekvivalensfaktorn 0.1,
15. the concentration of 1, 2, 3, 4, 6, 7,
8-heptaklordibensofuran (HpCDF) multiplied by the toxic
ekvivalensfaktorn 0.01;
16. the concentration of 1, 2, 3, 4, 7, 8,
9-heptaklordibensofuran (HpCDF) multiplied by the toxic
ekvivalensfaktorn 0.01, and
17. the concentration of oktaklordibensofuran (OCDF)
multiplied by the toxic ekvivalensfaktorn 0.001.
Calculation of emissions by percentage of oxygen
section 55 Of the emissions for the purposes of this regulation,
is determined by calculating the emission concentration at the
percentage of oxygen, the emission concentration shall be deemed to have
the value corresponding to the result of that
1. reduce the number 21 with the number that indicates the percentage
oxygen content,
2. reduce the number 21 with the number indicating the measured
percentage of oxygen
3. divide the result by calculation according to 1 with the result
by calculation according to the 2, and
4. multiply the result of the calculation according to 3 with the
number that indicates the percentage emission concentration that have
measured at the measured oxygen levels.
Emissions to air from waste incineration plants
56 § throttling values in sections 57 to 66 refers to normal dry gas with
11% oxygen. The incineration of waste oil concerns
However, the throttling values 3% oxygen.
In paragraph, there is a provision that conversion to oxygen
should not be done at the incineration of hazardous waste in some
case.
57 § From a waste incineration plant emissions into
air, on average, during each day do not contain
1. dust with more than 10 milligrams per cubic meter of normal dry
gas,
2. total organic carbon with more than the equivalent to 10
milligram per cubic meter of normal dry gas,
3. HCL with more than 10 milligrams per cubic meter of normal
dry gas,
4. hydrogen fluoride with more than 1 milligram per cubic meter of normal
dry gas,
5. sulphur dioxide by more than 50 milligrams per cubic meter of normal
dry gas, and
6. nitrogen oxides by more than
a) 400 milligrams per cubic meter of dry flue gas, if the facility
is a 2002-plant whose combustion capacity is a maximum of 6
ton per hour, or
b) 200 milligram per cubic meter of dry flue gas, if the facility
not covered by (a).
section 58 From a waste incineration plant emissions into
air in the case of dust
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 10
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than
30 milligrams per cubic meter of normal dry gas.
59 section From a waste incineration plant emissions into
air in terms of total organic carbon
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 10
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than
20 milligrams per cubic meter of normal dry gas.
60 section From a waste incineration plant emissions into
air in the case of hydrogen chloride
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 10
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than
60 milligrams per cubic meter of normal dry gas.
61 section From a waste incineration plant emissions into
air in the case of hydrogen fluoride
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 2
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than 4
milligram per cubic meter of normal dry gas.
62 section From a waste incineration plant emissions into
air in terms of sulphur dioxide
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 50
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than
200 milligrams per cubic meter of normal dry gas.
63 section From a waste incineration plant emissions into
air in the case of nitrogen oxides
1. during every half hour in 97 percent of all
half hour periods in a year do not contain more than 200
milligram per cubic meter of normal dry gas, or
2. during each half-hour doesn't contain more than
400 milligrams per cubic meter of normal dry gas.
The first subparagraph shall not apply if the facility is a
2002-plant whose combustion capacity does not exceed 6 tonnes per
hour.
64 section From a waste incineration plant emissions into
air on average during any period that is at least 30 minutes
and not more than 8 hours long, not contain, whether in solid form,
liquid or gaseous form;
1. more cadmium or thallium than total 0.05 milligrams per
cubic meter of normal dry gas,
2. more than a total of mercury 0.05 milligrams per
cubic meter of normal dry gas, or
3. more antimony, arsenic, lead, chromium, cobalt, copper, manganese,
nickel or vanadium than total 0.5 milligrams per
cubic meter of normal dry gas.
65 section From a waste incineration plant emissions into
air on average during any period that is at least 6 hours
and not more than 8 hours long doesn't contain more dioxins or
furans, whether in solid, liquid or gaseous form;
than a total of 0.1 nanograms per cubic meter of normal dry gas.
66 section From a waste incineration plant emissions into
air in the case of carbon monoxide
1. during each day in 97% of all days
in one year do not contain more than 50 milligrams per
cubic meters of dry gas, and
2. on average during
a) every half an hour in a twenty-four hour period does not contain
more than 100 milligrams per cubic meter of normal dry gas, or
b) each ten minute period in 95% of all
ten-minute periods in a twenty-four hour period does not
contain more than 150 milligrams per cubic meters of dry gas.
Notwithstanding the first subparagraph 2 (b) emissions on average during each
ten minute period in 95 percent of all the ten minute periods
over a period of seven daily contain 150 milligrams of carbon monoxide
per cubic metre of dry gas, if the combustion process means that
the gas that arises is heated to at least 1 100 degrees Celsius
for at least two seconds.
A permit conditions or conditions in question
If a waste incineration plant with fluidized bed
bed technology means higher limit values for emissions of
carbon monoxide than what is stated in the first paragraph may be applied, if
the condition means that emissions during each
hour shall not contain more than 100 milligrams of carbon monoxide per
cubic meter of normal dry gas.
Emissions to air from co-incineration in cement kilns
67 § throttling values in sections 68 to 70 pertain to normal dry gas with
10 percent oxygen content.
68 section From a cement kiln that is one co-incineration plant
emissions into the air during each day not
contain more
1. dust than that which corresponds to 30 milligrams per cubic meter
normal dry gas,
2. total organic carbon than that which corresponds to 10 milligrams
organic carbon per cubic meter of normal dry gas,
3. hydrogen chloride than the corresponding to 10 milligrams per
cubic meter of normal dry gas,
4. hydrogen fluoride than the equivalent to 1 milligram per
cubic meter of normal dry gas,
5. sulphur dioxide than that which corresponds to 50 milligrams per
cubic meter of normal dry gas, and
6. nitrogen oxides than that which corresponds to 500 milligrams per
cubic meter of normal dry gas.
Despite the first paragraph 2 and 5, total organic carbon and
sulphur dioxide discharged with the larger amounts specified in a
permit conditions or conditions, if the total
organic carbon and sulphur dioxide are not derived from
the incineration of waste.
69 section From a cement kiln that is one co-incineration plant
emissions into the air during each period
at least 30 minutes and up to 8 hours in length, not contain, either
in solid, liquid or gaseous form, more
1. cadmium or thallium than that which in total equal to 0.05
milligram per cubic meter of normal dry gas,
2. total mercury than that corresponding to 0.05 milligrams
per cubic meter of normal dry gas, or
3. antimony, arsenic, lead, chromium, cobalt, copper, manganese,
nickel or vanadium than that in total is equivalent to 0.5
milligram per cubic meter of normal dry gas.
70 section From a cement kiln that is one co-incineration plant
emissions into the air during each period
a minimum of 6 hours and a maximum of 8 hours in length, contain not more
dioxins or furans, whether in solid, liquid,
or gas form, than that which in total equal to 0.1 nanograms
per cubic meter of normal dry gas.
Mixing calculation for co-incineration
71 § discharges to air from
co-incineration plants referred to in 80 to 93 and 97 sections should
the number that specifies the maximum allowable pollutant load can be determined
through a mixing calculation to include
1. the waste flow values referred to in section 72,
2. the maximum levels of the pollutant that
specified in 81 to 93 and 97 sections,
3. a standard oxygen waste value for waste oil, waste oil
incinerated in the plant, which is calculated by
waste flow value of waste oil is multiplied by
waste oil waste emission limit value,
4. a standard oxygen waste value of waste other than
waste oil, if such waste is incinerated in the plant, which
is calculated through the waste stream value of waste
multiplied by the limit value for waste the waste;
5. waste value, which is the sum of all
standard oxygen waste values calculated according to 4,
6. the process flow values referred to in section 73,
7. the process limits resulting from 74 to 76 and 79 sections,
8. a fuel process value for each fuel, calculated
through that process flow value of fuel is multiplied by
process limit value of the fuel,
9. the process value, which is the sum of all fuel process values
calculated according to 8,
10. waste co-incineration flow value, which is the sum of all
waste flow process flow values and all values, and
11. co-incineration value, which is the sum of the loss value and the
the process value.
Mixing calculation should be done by dividing
co-incineration co-incineration value flow value after
all values are normalized to the same oxygen content in
accordance with section 55.
For the purposes of this paragraph and paragraphs 72 to 79, waste
referred to in section 17 are considered different fuel than waste.
section 72 By mixing calculation according to section 71, a
waste flow value be determined for waste oil, waste oil,
incinerated in the plant, and a waste flow value
be determined for other waste may be incinerated in the plant.
Waste stream value should be the number that specifies the maximum flow
by flue gas combustion of waste gives rise to the
cubic meter of normal dry gas per day.
If hazardous waste is incinerated in the plant and the
-burning giving rise to less than ten percent of the
total heat released, the part of the exhaust gas flow
comes from hazardous waste in the calculations should be determined as
It represents the gas flow from the amount of the
hazardous waste that is needed to give rise to ten
percent of the total heat released from combustion of
plant.
73 section At mixing calculation according to section 71 shall be determined
a process-flow value for solid fuel and a
process flow value of the liquid fuel,
incinerated in the plant. Process flow value should be the
number that specifies the minimum flow of flue gas combustion of other
fuels than waste raises in cubic metres of normal dry
gas per day and calculated from the oxygen content in gas as a
the limit value of this regulation relates or, if no
oxygen is not specified for the limit value, the oxygen content
as the gas is without dilution by addition of air that does not
needed for the process.
74 § Process limit specified in 81 to 93 and 97 § § or
determined in accordance with this Regulation shall concern the milligrams per
cubic meter of normal dry gas with six percent oxygen content, if
the fuel is fixed, and three percent oxygen content, if the fuel is
liquid.
Waste limits in 81 to 93 and 97 sections or determined according to
This Regulation shall relate to milligrams per cubic meter of normal
dry gas with eleven percent oxygen content. When burning
waste oil to promote waste limits, however, normal dry gas with
three percent oxygen content.
75 section At mixing calculation according to section 71 shall, as
process limit used the speech given in 81 to 93 and 97
§§. If a permit conditions or conditions set
a more stringent process limit value, shall be the value
be used.
If the process limit is not apparent from 81 to 93 and 97 sections,
1. the process limit has been determined in a
permit conditions or terms be used, or
2. the limit value set out in a permit terms and conditions
or terms used as process limit value, if
the plant is not covered by any licence conditions or
injunctive relief terms that specify a process limit value, and
limit value is expressed as a daily average value of
emissions of the pollution from the combustion of fuels other than
waste.
The process limit referred to in the second subparagraph of paragraph 1 shall not
bring a mitigation that are unreasonable compared to what
that would have applied if the burning was intended only to other
fuels than waste.
76 section if no process limit value can be determined in the manner
as indicated in paragraph 75, the actual concentrations may be used
When mixing calculation.
paragraph 77 of chapter 19. paragraph 5, second subparagraph, and 22. 25 (b) §
Environment Act provides for a decision or a judgment
that means that the permission given to a business
contain provisions on restriction values should
calculated in accordance with the provisions adopted by virtue of Chapter 9. paragraph 5 of the
the environmental code. If such a condition if the constraint value set
a process limit for mixture calculation that has
determined in accordance with section 75, the condition
process limit value applied. If the permit condition specifies the
the limit value as a mixing calculation under section 71 gives
and this appears from the permit condition,
the operator apply the criteria limit value in
rather than that which follows from 71 to 76, 79 to 93 and 97 sections.
section 78 in relation to emissions not covered by a
permit conditions referred to in paragraph 77, the supervisory authority of the
an order and conditions, decide on a process limit
or constraint value, if the operator request.
order condition indicates a process limit for
mixing calculation and the condition meets the requirements of section 75,
should the condition process limit value applied. If
order conditions indicate the limit value as a
mixing calculation under section 71 provides and this is evidenced by
order condition, the operator shall apply
condition limit value rather than that resulting from
71-76, 79-93 and 97 sections.
section 79 of the process set out in sections 81 to 92 shall not
apply to gas turbines or engines.
Total emissions from energy plants
80 section in the application of the provisions of §§ 81-92, two
or more separate waste co-incineration plants shall be considered to be
one co-incineration plant, if
1. waste gases from co-incineration plants are placed
through a common stack, or
2. co-incineration plants have received their first
condition on 30 June 1987 or later is installed
so that, having regard to the technical and economic
the conditions would be possible to let out fumes
from combustion plants through a common stack.
If more than one co-incineration plants referred to in the first subparagraph
should be considered as a single combustion plant, to the sum of
co-incineration plant abilities form the basis
for the calculation of the rated power.
Dust from power plants
81 section From an energy plant with a rated thermal input
effect of less than 50 megawatts of emissions into air in
average for each day not contain dust with more than
the number of milligrams per cubic meter of normal dry gas
is determined by a mixing calculation under section 71 with
waste and process limit value limit value 10 50.
section 82 From an energy plant with a rated thermal input
effect that is 50 megawatts or higher, but not exceeding 100
megawatt, emissions into the air during each day
not contain more dust than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with
1. waste limit 10,
2. process limit value 30, if the facility is a
2013-facility, and
3. process limit 20, if the plant is not covered by
2.
83 section From an energy plant with a rated thermal input
power greater than 100 megawatts, up to a maximum of 300 megawatts,
emissions into the air during each day not
contain more dust than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 with
1. waste limit 10,
2. process limit value 25, if the facility is a
2013-plant and the fuel is either peat or biomass,
and
3. process limit 20, if the plant is not covered by
2.
84 section From an energy plant with a rated thermal input
effect of more than 300 megawatts of emissions into air in
during every day contain no more dust than it
number of milligrams per cubic meter of normal dry gas as determined
through a mixing calculation under section 71 with
1. waste limit 10,
2. process limit 20, if the facility is a
2013-plant or if the fuel is biomass, peat or
and
3. process the limit 10, if the plant is not covered by
2.
Sulfur dioxide from power plants
85 section From an energy plant with a rated thermal input
effect of less than 50 megawatts of emissions into air in
average for each day not contain more sulphur dioxide
than the number of milligrams per cubic meter of normal dry gas
is determined by a mixing calculation under section 71 with
limit waste 50 and the process limit value resulting from the
75 – 78 sections.
86 section From an energy plant with a rated thermal input
effect that is 50 megawatts or higher, but not exceeding 100
megawatt, emissions into the air during each day
not contain more sulfur dioxide than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with
1. waste limit 50;
2. process limit 400, if the fuel is solid but not turf
or biomass,
3. process limit 350, if the fuel is liquid,
4. process limit 300, if the fuel is peat, and
5. process limit value 200, if the fuel is biomass.
87 section From an energy plant with a rated thermal input
power greater than 100 megawatts, up to a maximum of 300 megawatts,
emissions into the air during each day not
contain more sulfur dioxide than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with
1. waste limit 50;
2. process limit 300, if the plant is not a
2013-facility, if the fuel is burning peat and on
in Fluidised bed,
3. process limit 250, if
a) plant is a 2013-plant and the fuel is
liquid, or
(b)) the facility is not a 2013-facility, if the fuel is
peat and if combustion takes place in a Fluidised bed, and
4. process limit value 200, if the facility is not subject to 2
or 3.
88 section From an energy plant with a rated thermal input
effect of more than 300 megawatts of emissions into air in
average for each day not contain more sulphur dioxide
than the number of milligrams per cubic meter of normal dry gas
is determined by a mixing calculation under section 71 with
1. waste limit 50;
2. process limit value 200, if
a) fuel peat and combustion takes place in Fluidised
bed,
b) the fuel is another solid fuel than peat and
combustion takes place in circulating or pressurized bed,
or
c) facility is 2013, and
3. process the limit 150, if the plant is not covered by
2.
Nitrogen oxides from power plants
89 section From an energy plant with a rated thermal input
effect of less than 50 megawatts of emissions into air in
average for each day not contain more nitrogen oxides than
the number of milligrams per cubic meter of normal dry gas
is determined by a mixing calculation under section 71 with
1. waste limit 400, if the facility is a
2002-plant whose combustion capacity does not exceed 6 tonnes per
hour,
2. waste emission limit value 200, if the plant is not covered by
1, and
3. the process limit imposed by paragraphs 75 to 78.
90 section From an energy plant with a rated thermal input
effect that is 50 megawatts or higher, but not exceeding 100
megawatt, emissions into the air during each day
not contain more nitrogen oxides than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with
1. waste limit 400, if the facility is a
2002-plant whose combustion capacity does not exceed 6 tonnes per
hour,
2. waste emission limit value 200, if the plant is not covered by
1,
3. process the limit 400, if
a) the fuel is liquid, or
b) plant is a 2013-plant and the fuel is
coal powder,
4. process limit 250, if the plant is not a
2013-plant and the fuel is peat or biomass, and
5. process limit 300, if the plant is not covered by 3
or 4.
91 section From an energy plant with a rated thermal input
power greater than 100 megawatts, up to a maximum of 300 megawatts,
emissions into the air during each day not
contain more nitrogen oxides than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with
1. waste limit 400, if the facility is a
2002-plant whose combustion capacity does not exceed 6 tonnes per
hour,
2. waste emission limit value 200, if the plant is not covered by
1,
3. process limit 250, if the facility is a
2013-plant and the fuel is biomass,
4. process limit 150, if the facility is not
2013-plant and the fuel is liquid, and
5. process limit value 200, if the plant is not covered by 3
or 4.
92 section From an energy plant with a rated thermal input
effect of more than 300 megawatts of emissions into air in
average for each day not contain more nitrogen oxides than
the number of milligrams per cubic meter of normal dry gas
is determined by a mixing calculation under section 71 with
1. waste limit 400, if the facility is a
2002-plant whose combustion capacity does not exceed 6 tonnes per
hour,
2. waste emission limit value 200, if the plant is not covered by
1,
3. process limit value 200, if
a) plant is a 2013-plant and the fuel is not
liquid, or
(b)) the plant not covered by (a) and the fuel is
coal powder,
4. process limit value 100, if the plant is not a
2013-plant and the fuel is liquid, and
5. process limit 150, if the plant is not covered by 3
or 4.
Carbon monoxide, total organic carbon, hydrogen chloride and hydrogen fluoride
from energy plants
93 section From an energy plant emissions into air in
during each day do not contain
1. more carbon monoxide than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limit value of 50 and it
process limit imposed by paragraphs 75 to 78,
2. more total organic carbon than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 of the limit value of 10 and
the process limit imposed by paragraphs 75 to 78,
3. more hydrogen chloride than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limiting value 10 and it
process limit imposed by paragraphs 75 to 78, and
4. more fluoride than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limit value 1 and the
process limit imposed by paragraphs 75 to 78.
Heavy metals, dioxins and furans from energy plants
94 section Limit values given in paragraphs 95 and 96 shall relate to
normal dry gas with six percent oxygen content, if the fuel is
fixed, and three percent oxygen content, if the fuel is liquid.
95 section From an energy plant emissions into air in
average for each period that is at least 30 minutes and
up to 8 hours in length, not contain, whether in solid form,
liquid or gaseous form;
1. more cadmium or thallium than total 0.05 milligrams per
cubic meter of normal dry gas,
2. more than a total of mercury 0.05 milligrams per
cubic meter of normal dry gas, or
3. more antimony, arsenic, lead, chromium, cobalt, copper, manganese,
nickel or vanadium than total 0.5 milligrams per
cubic meter of normal dry gas.
96 § From an energy plant emissions into air in
average for each period that is at least 6 hours and a maximum of
8 hours long doesn't contain more dioxins or furans,
in solid, liquid or gaseous, than the total
0.1 nanograms per cubic meter of normal dry gas.
Air emissions from industrial facilities
§ 97 From an industrial plant emissions into air in
during each day do not contain
1. more dust than the number of milligrams per cubic meter of normal
dry gas as determined by a mixing calculation under section 71
with waste limit 10 and the process limit
follows from paragraphs 75 to 78,
2. more nitrogen oxides than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 with
(a) the limit value 400) and waste process limit
follows from paragraphs 75 to 78, if the plant is a 2002-facility
whose combustion capacity is a maximum of 6 tonnes per hour, or
b limit value 200) waste and the process limit
follows from paragraphs 75 to 78, if the plant is not covered by (a),
3. more sulfur dioxide than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limit value of 50 and it
process limit imposed by paragraphs 75 to 78,
4. more total organic carbon than the number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 of the limit value of 10 and
the process limit imposed by paragraphs 75 to 78,
5. more hydrogen chloride than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limiting value 10 and it
process limit imposed by paragraphs 75 to 78,
6. more fluoride than the number of milligrams per cubic meter
normal dry gas as determined by a mixing calculation
According to section 71 of the limit value 1 and the
process limit imposed by paragraphs 75 to 78, or
7. more antimony, arsenic, lead, chromium, cobalt, copper, manganese,
nickel or vanadium than the total number of milligrams per
cubic meter of normal dry gas as determined by a
mixing calculation under section 71 with waste limit 0.5
and the process limit imposed by paragraphs 75 to 78.
98 section From an industrial plant emissions into air in
average for each period that is at least 30 minutes and
up to 8 hours in length, not contain, whether in solid form
or gas form,
1. more cadmium or thallium than total 0.05 milligrams per
cubic meter of normal dry gas, or
2. more than a total of mercury 0.05 milligrams per
cubic meter of normal dry gas.
99 section From an industrial plant emissions into air in
average for each period that is at least 6 hours and a maximum of
8 hours long doesn't contain more dioxins or furans,
in solid, liquid or gaseous, than the total
0.1 nanograms per cubic meter of normal dry gas.
Waste water from the cleaning of exhaust gases
100 § From the cleaning of exhaust gases in a combustion plant shall
waste water discharges to the aquatic environment is limited so far
as it is possible. The wastewater discharged must not
contain
1. more than 0.3 nanograms of dioxins and furans per litre,
2. more than 0.03 milligrams of mercury per litre,
3. more than 0.05 milligrams of cadmium per litre,
4. more than 0.05 milligrams of thallium per litre,
5. more than 0.15 milligrams of arsenic per liter,
6. more than 0.2 milligrams of lead per liter,
7. more than 0.5 milligrams of chrome per litre,
8. more than 0.5 milligrams of copper per litre,
9. more than 0.5 milligrams of nickel per litre,
10. more than 1.5 milligrams of zinc per litre, or
11. more organic or inorganic particles that can
to settle (suspended matter) than 45 milligrams per litre
at each measurement is being done to make sure
the pollutant content and 30 milligrams per litre at 95%
of all such measurements.
§ 101 A limit value of 100 § 2 – 10 may be exceeded at
not more than
1. a sample per year, or
2. five per cent of the samples taken in the course of a year, if it is in
a permit conditions or conditions have been determined
more than twenty sampling shall be made per year.
102 § throttling values in 100 § refers to unfiltered samples
at the point where the waste waters discharged from
incineration plant or from an establishment
treats wastewater from the cleaning of exhaust gases.
In the case of waste water from a plant where waste waters
from the cleaning of exhaust gases is treated along with other
wastewater, it is estimated the emissions of the
final effluent from the treatment facility that
attributable to the portion of the wastewater coming from
purification of waste gases. The calculation shall be made using the
mass balance calculations and based on the results of the
measurements of emissions to air are made according to 42 to 44 and 50
§§.
§ 103 sewage must not be diluted to meet
throttling values in section 100.
Modification of an activity
section 104 If an activity of a combustion plant is
subject to licensing requirements under the environmental assessment regulation
(2013:251) is amended by adding from the incineration of only
non-hazardous waste released into the incineration of hazardous
waste, required the authorization of the change, no matter what
stated in Chapter 1. section 4 of the environmental assessment regulation. Permits for
change is required unless it is expressly indicated by the
regarding the authorization to include the intended
incineration of hazardous waste.
Dispenser
section 105 the supervisory authority may waive the provisions
If
1. acceptance of waste in 21 and 22 sections, if the exemption is combined
with the injunction conditions equivalent to that provided for in section 23 of the
required to apply the criteria,
2. the temperature of the flue gases in paragraph 28, concerning the
the exemption is combined with the imposition of conditions that correspond to the
as referred to in paragraph 28 is required to apply
the condition,
3. the furnace gas temperature and residence time in paragraph 32 and
other paragraphs, if the exemption is combined with the imposition of conditions
equivalent to that required under paragraph 32 of
to apply the criteria,
4. aid burners in the first and second paragraphs of section 33, if
the exemption is combined with the imposition of conditions that correspond to the
which, according to paragraph 33, is required to apply
the condition,
5. measurements of emissions to air in section 43, if the exemption is not possible
beyond that, according to paragraph 44, is required to apply a
order conditions and exemptions be reconciled with such
conditions,
6. conversion of measurement results in paragraph 50, on
the exemption is combined with the imposition of conditions that correspond to the
which, according to paragraph 50 is required to apply
the condition,
7. carbon monoxide in paragraph 66, concerning the exemption
combined with the imposition conditions conforming to that referred to in
paragraph 66 is required to apply the criteria,
and
8. discharge of total organic carbon and sulphur dioxide in 68
paragraph 2 and 5, if the exemption is combined with
procedure conditions conforming to that referred to in section 68
the paragraph is required to apply the condition.
Information in the environmental report
106 § The operator to provide information on emissions
in the environmental report as referred to in chapter 26. section 20 of the environmental code,
refer to average values prior to validation in accordance with section 51.
Information to the environmental protection agency and the European
the Commission
107 § When a judgment or a decision of a State objective or
tillståndsärende sent to the environmental protection agency under section 11
Ordinance (1998:899) concerning environmentally hazardous activities and
the health protection agency to review pay particular attention to
the work on the decision or judgment contains such
permit conditions referred to in section 28, 32 or 33.
When the regulatory authority provides an exemption under § 105 2, 3
or 4 or decides on such an order conditions
referred to in section 28, 32 or 33, the supervisory authority shall inform
The environmental protection agency about this.
108 section environmental protection agency shall inform the Commission of the European communities
If all permit conditions and order conditions
applied under section 32 or 33 28, as well as on the results of the
checks are being made regarding the conditions meet the
the requirements of this regulation.
109 § the supervisory authority shall communicate the
combustion plants which fall within the scope of this regulation
environmental protection agency, if the Agency so requests.
Transitional provisions
2013:253
1. This Regulation shall enter into force on 18 June 2011.
2. The Ordinance (2002:1060) on waste incineration shall cease
with effect from 17 June 2013.
3. in the case of a combustion plant is in operation at
entry into force, a proposal for the placement of
sampling and measurement points according to § 47 left to
the supervisory authority by 30 June 2014.
4. In the case referred to in (3) the supervisory authority shall decide
an order to the sampling or measurement points shall
take effect no later than 31 March 2015.
5. For the period prior to 1 January 2016 emissions from a
Lepolugn or long rotary kilns despite 68 § 6 contain more than 800
milligrams of nitrogen oxides per cubic meter of normal dry gas, if so
much nitrogen oxides total may be placed from the oven according to the
a permit conditions or conditions.
6. For the period before January 1, 2016, in terms of
2013-facilities
a) process limit value 50 apply instead of the provisions of
82 section 2,
b) process limit value 30 apply instead of the provisions of
83 84 § 2 and 3 and § 2,
c) process limit 850 apply instead of the provisions of
86 § 2-4,
d) process limit 400 with 200 linear reduction to apply
instead of what is said in the 87 § 3 (a) and the linear
the reduction to be applied to process 400 limit applies
for plants with a rated thermal input
300 megawatts and process limit value 200 applies for
plants with a rated thermal input of which is not
more than insignificantly higher than 100 megawatts,
e) process limit 350 apply instead of the provisions of
90 section 5, if the fuel is biomass,
f) process the limit 400 apply instead of the provisions of
90 section 5, if the fuel is a fuel that is not
biomass,
g) process limit 300 apply instead of the provisions of
91 § 3, and
h) process limit value 200 apply instead of the provisions of
92 § 5.
7. facilities that are licensed pursuant to chapter 29. 18,
19, 22, 23, 24 or section 25 of the environmental assessment regulation
(2013:251) and that upon entry into force is 2013-facilities
need not meet the requirements of this regulation until the 7
January 2014.
