294/2005 Sb.
DECREE
of 11 December 1997. July 2005
on the conditions of storing the waste at landfills and their use on the surface
the terrain and the change of Decree No. 383/2001 Coll., on details of the management of
waste
341/2008: Sb.
61/2010: Sb.
Change: 61/2010 Coll. (part)
Change: 61/2010 Coll. (part)
93/2013: Sb.
Ministry of the environment shall determine according to § 14 para. 5, § 19 para.
3, § 21, art. 5, § 22 para. 2, § 35 para. 3, § 45 para. 3 and § 51 para.
5 of law No. 185/2001 Coll., on waste and amending certain other
laws, as amended by Act No. 477/2001 Coll., Act No. 76/2002 Coll., Act
No. 275/2002 Coll., Act No. 320/2002 Coll., Act No. 167/2002 Coll., Act
No. 188/2004 Coll., Act No. 317/2004 Coll. and Act No. 7/2005 Coll. (hereinafter referred to
"the Act"):
PART THE FIRST
THE DECREE ON THE CONDITIONS FOR STORING THE WASTE AT LANDFILLS AND THEIR USE OF THE
THE GROUND SURFACE
Title I Of The
The subject of editing, and basic concepts
§ 1
The subject of the edit
This Decree incorporates the relevant provisions of the European Union ^ 1) and in
accordance with them modifies the
and) technical requirements for the landfill of waste (hereinafter referred to as "dumps") and
the conditions of their operation,
(b)), which is a list of wastes prohibited to landfill, or that
can be stored in landfills only under certain conditions,
(c)) method of evaluation of waste according to leaching ability and mísitelnosti and
the mode of proof of the acceptability of waste at the facility to use and
disposal of waste,
(d)) the technical requirements for the management of waste generated during combustion
hazardous waste,
e) storage requirements of asbestos waste at landfills,
(f) temporary storage requirements) of metallic mercury,
g) waste storage requirements as technological material
secure landfill
h) method of creating and drawing down cash reserves,
the contents of the plan I) landfills and lays down
j) technical requirements and conditions for the use of waste on the surface
terrain.
§ 2
Basic concepts
For the purposes of this Decree:
and inert waste-waste) that does not have hazardous properties and for which
under normal climatic conditions, there are no significant
the physical, chemical or biological transformations. Inert waste does not burn or
otherwise chemically or physically is not responding, is not subject to biological degradation
or cause the decomposition of other substances with which it comes in contact, and it
manner as to endanger human health, and threatening or affecting the
or the environment leading to pollution limits being exceeded
established by the legislation of the ^ 2). Mixed waste
not considered to be an inert waste,
b) biodegradable waste aerobically or anaerobically-any
biodegradable waste
c) liquid waste-waste in physical state liquid according to ČSN EN 12457-4
(83 8005) in Annex B,
(d)) with an aqueous extract-the solution that has been prepared from the sample in
ČSN EN 12 457-4 (83 8005)
(e) waste-stabilization technology) treatment of waste consisting of
the use of physical, chemical or biological processes, leading to
permanently restricted the release of pollutants from the waste into individual folders
of the environment in accordance with the requirements of (i) specific legal
regulations ^ 2)
f) by modifying the mixed municipal waste ^ 3) before saving them to the dump
-Sift hazardous components of municipal waste, commodities intended for
back under § 38 paragraph 1(a). 1 of law and usable folders according to §
Article 16(1). 1 (b). (b)), § 17 para. 4 of the law, or the separation, other
folders,
g) výluhovou class-set maximum allowable concentration values
selected indicators of pollutants in the first alcoholism waste prepared
According to ČSN EN 12457-4 (83 8005)
h) landfill gas-gas, which develops from the waste stored on the
biological and chemical dump marches,
I) waste disposal in landfills-waste disposal methods
listed in annex No 4 of law under the codes of the D1 and D5,
j) recovery on the ground surface, set out in annex No 3 of the Act
under the code, except on application to the R10 agricultural land-reclamation of surface
field balancing, bumps and other landscaping,
create a closing landfill reclamation layers of closed landfills,
the delivery of extracted surface mines, quarries, sand pits,
the reclamation-putting space) as a general rule of human activities to the
accordance with the surroundings and restore functionality of the surface of the ground in relation to its
the original use or intended use of the new,
l) critical indicators-the limit values of concentration of pollutants and
biological agents are selected on the basis of knowledge of the technology of developing
waste, whose determination is necessary and sufficient for regular
verification of the quality of the waste when it is repeated deliveries into the device without
regardless of whether or not they are for the device, this
the Decree required
m) rated acceptability of waste to facilities-a process whose first
step is processing the basic description of the waste producer or by an authorized
person, the second regular verification of the quality of a continuous or repeated
emerging waste producer or by an authorized person, that waste
took over the property, and the third review of the waste reception in
the device,
n) device-landfills, surface mines, quarries, tailings ponds and other places
on the surface of the ground, where waste is used for backfilling, recultivation of land
and other finishes,
o) nereaktivním hazardous waste-waste according to § 4, paragraph 4. and) of the Act,
that under normal climatic conditions does not burn easily in the water
not dissolve or otherwise physically or chemically does not respond in the environment
where is stored, with other waste or things with which it comes into
contact in a way that could lead to damage to the environment or
the risks to human health,
p) sector a landfill-locally defined part of the landfill, which is used to
storing waste comparable to their origin, composition, and
that will ensure your technical performing separate storage of such
waste within one landfills and prevents the contact, or mixed
waste stored in each sector of the landfill throughout their
Save,
q) the basic description of the waste-waste of the accompanying documents prepared by the
the originator of the waste or by an authorized person to the extent provided for in point 2
Annex No 1 on the basis of all available information about the waste for whose
completeness and veracity of corresponds to the originator or the beneficiary, that
basic description of the waste passes with each one or the first of a series of
repeated supply of waste to the device,
r) supply of waste-waste received in each load of the device at the same time
from one supplier,
with repeated supply of waste)-regularly and irregularly
recurring supply of one type of waste, with the same characteristics of the emerging
manufacturing technological process one author
t) waste asbestos-hazardous waste catalogue numbers ^ 3) 06 13
04, 10 13 09, 16 01 11, 16 02 12, 16 02 15, 16 11 01, 16 11 03, 16 11
05, 17 06 01, 17 09 03 17 06 05, if a hazardous substance,
they contain asbestos,
u) mechanical-biological editing-edit mixed municipal waste
or other similar wastes other wastes of categories
a combination of physical and biological processes,
in the RA of the) construction and demolition waste-material output
from the device to use and modify the construction and demolition waste
category other wastes and wastes of similar construction and demolition
waste, consisting of changing grain size and its sorting on size
fraction in facilities intended for that purpose,
w) temporary storage of metallic mercury-removal of metallic mercury that
is waste, in accordance with the directly applicable European Union law ^ 24)
in the manner specified in annex 4 of the law under the code so that the metal of the D15
Mercury is temporarily stored for more than one year.
Title II
Disposal of waste disposal at landfills
(Article 14, paragraph 5, and article 21, paragraph 5, of the Act)
§ 3
Technical requirements for landfills and the conditions of their operation
(1) the technical requirements on the landfill of waste, including the conditions for their
the location, the operation of landfill sites, technical security seals, monitoring
and the conditions of their closure and reclamation shall be deemed to be fulfilled,
If the technical standards ČSN 83 8030 landfill of waste-
The basic conditions for the design and construction of landfills, CSN 83 8032
The landfill of waste-landfills, CSN 83 8033 landfill of waste-
The management of průsakovými water from landfills, CSN 83 8034 Landfill
waste-degassing of landfills, CSN 83 8035 landfill-Closing
and reclamation of landfills and landfill of waste 83 8036-Monitoring
landfill sites.
(2) the landfill are classified according to the technical group: security
and S-) a group of inert waste-designed for inert waste according to § 2 (b).
and). For the purposes of record keeping and the reporting of waste and landfills of this device
groups indicate S-IO,
(b)) the Group S-other waste-waste category, intended for other wastes.
For the purposes of record keeping and the reporting of waste and the landfill equipment
indicate with-OO. This group is further divided into subgroups:
1.-OO1-landfill or landfill sectors intended for storing waste
category other wastes with low content of organic biologically
degradable substances set out in point 6(a). (c) the annex No. 4), and
wastes from asbestos, on the conditions laid down in section 7,
2.-a landfill or sectors OO3-landfills designated for storing waste
category other wastes including waste with substantial contents of organic
biodegradable substances, waste that cannot be assessed on the
based on their aqueous extract, and wastes from asbestos under the conditions
set out in section 7. These landfills or sectors may not be saved
wastes on the basis of plaster,
(c)) the Group S-hazardous waste-designed for hazardous waste. For the purposes of
record-keeping and the reporting of waste and landfill sites of this group
indicate with-WELL.
(3) Waste from landfills each group can receive only by
the species and categories of waste ^ 3), according to their actual characteristics of ^ 4),
waste water leaching ability by class in accordance with Annex 2,
the basis of their mutual mísitelnosti according to annex No 3, based on the content
pollutants in the dry and in compliance with further details given in the
Annexes 4 and 5.
(4) the total leachability of inert after saving
waste to landfill and the pollutant content of the waste in these as well
the ecotoxicity of the leachate must be insignificant and not
endanger the quality of surface water and/or groundwater ^ 20). The concentration of
pollutants in the dry and in the extract of this waste must not exceed any of the
the parameters set out for the landfill with Group-inert waste in the annexes
# 2, and 4 to this notice.
(5) on the landfill of waste, the waste is stored, so that it cannot be
adverse drug react to form harmful substances, the disruption
tightness, to undesirable distortions, or to disrupt the stability and
the construction of the landfill.
(6) a record of the location of each type of hazardous waste in the landfill is
part of the ongoing registration of waste. Method of recording and scaling raster
maps, according to which the record is carried out, are laid down in the operating system. ".
(7) each from landfills may have established sectors designated for separate
waste storage facility, comparable in its composition and properties, inside
one of the facility, if the technical performance of individual sectors prevents
mixing and merging of waste to them going throughout their
saving.
(8) details of waste necessary for its assessment for the purposes of the adoption of the waste on the
landfill or to other devices under section 2 (b). n) are given in
the basic characterisation of the waste, the content of which is set out in point 2 of annex 1.
§ 4
Method of evaluation of waste by leaching ability and mísitelnosti, list of
the waste, which is prohibited from landfill, and other conditions for
storing waste at landfills
(1) Analytical analyses, ecotoxicological and microbiological tests of waste
for the purposes of processing of the basic description of the waste and the assessment of its
the acceptability of the device can only be performed in laboratories and other
Professional, accredited by the technical standards ČSN EN
ISO/IEC 17025. Fitness professional workplaces shall apply only to
namely, the method contained in annex certificate of accreditation of the workplace.
This condition shall not apply to the methods of determining the critical indicators
other than those referred to in annexes 2, 4 and 10.
(2) sampling of waste for the purposes of processing of the basic description of the waste and
monitor critical indicators may only be performed by a qualified person,
that is not the owner of the waste. In the course of sampling must be consistently
guarantee the quality and quality control of sampling. Model collection
samples is given in a separate legal regulation ^ 5).
(3) Waste dumps for each group according to § 3 (2). 2 store
According to the criteria laid down for these groups in Appendix 4.
(4) the list of waste, which is forbidden to dump all of the groups
or at the landfill are stored only under certain conditions, is listed in the
Annex No 5.
(5) to the landfill is able to save only modified wastes. This condition is
does not apply to inert waste for which the adjustment is technically
impracticable, and wastes which cannot be achieved by adjusting the reduction
their volume or the reduction or elimination of their hazardous
the properties. Edit the patterns and practices of waste, which are considered
waste treatment facility before it saves them to a landfill, are listed in annex
6.
(6) low-Waste biodegradable substances of category
other wastes with lower class leaching ability may be accepted on
the class of the landfill leaching ability. Wastes listed in
higher class of leaching ability may not be accepted at the landfill
corresponding to the lower class of leaching ability.
(7) to the landfill with group-other wastes can be hazardous waste store
only when the
and stabilisation are modified) that will prevent the possibility of their responses with
other stored wastes and landfill environment and their aqueous extract
do not exceed the maximum permissible values of výluhové of class II, or
(b)) are placed in sealed containers or containers whose
technical design must complement the engineering barriers at the level of
the requirements of the landfill with Group-hazardous waste, or
(c)) meet the conditions set out in section 7, in the event that it is a waste of
asbestos.
(8) in accordance with the waste management plan and operational regulations,
It is possible to dump wastes listed in annex No. 8, unfit for their
material use, under the conditions referred to in annex 8, stored on the
dumps all of the groups without testing.
§ 5
The content of the landfill plan
(1) the adjustment of the landfill Plan contains the following details:
and the company, legal form) and registered office, if the operator of the site, which it
submit (the "submitter") is a legal person; the name and
last name, place of business, if the petitioner is a natural person
authorized to do business,
(b) the petitioner, identification number) where it has been allocated, the
(c) the identity and address of the landfill),
(d) the name or names), surname and place of residence of the physical
persons or individuals authorized to act on behalf of the petitioner,
(e) a copy of the business license) or a copy of the extract from the commercial
register or a copy of the incorporation of the Charter of the petitioner,
(f)) name, surname, the waste Manager, and evidence of his professional
eligibility under § 15 para. 6 of the Act, if the offeror has pursuant to section
15 law to determine the waste Manager,
g) past a group of landfill in accordance with § 3 (1). 2,
h) a list of species of waste according to waste catalogue, which are on the site
It is saved.
(2) the assessment of the conformity of the technical status of the landfill with security requirements
laid down in section 3 of the submitter makes filling in annex No. 9, which is
an integral part of this plan.
Title III
Special requirements for storing waste at landfills
(Article 21, paragraph 5, section 22, paragraph 2, § 35, paragraph 3, section 45 (3))
§ 6
The technical requirements for waste disposal as a technological material
to secure landfill
(1) as a technological material to ensure the landfill may not be
used waste laid down in part A of annex # 5. Wastes set out in
part B of annex # 5 can be used for this purpose only under the conditions in this
part of the annex set out and in accordance with the operating regulations of the landfill.
(2) the waste stored in a landfill as a technological material to ensure the
landfill of waste, including used when closing and recultivation of landfills to
creating buffer layers below the closing of the landfill, as sealing layer
are defined by the technical standard CSN 83 8035 landfill of waste-
Closure and reclamation, it must meet all of the conditions
laid down in annex 4 to the appropriate group of the landfill and match
the requirements of project documentation of the landfill.
(3) the amount of technological material to ensure the landfill for the purpose of
its technical security pursuant to § 45 para. 3 of the Act may be
not more than 25% of the volume of all wastes stored at the landfill for each
calendar year.
§ 7
The technical requirements for waste disposal of asbestos in landfills
(1) waste from asbestos can be imposed only on the landfill category
With-O and S-WELL, when you meet the following requirements:
and General requirements are met), § 4, paragraph 4. 3 and the requirements of the Special
^ 6) legislation,
(b)) the waste to landfills, the Group received S-OO to reserved sectors shall not
contain other hazardous substances than the asbestos fibers are bound
Binder, or asbestos waste packed in sealed packaging ^ 7),
(c) waste storage area) must be a day before the hutněním
covered with suitable material and, if the waste is not packed, it must be
zkrápěna on a regular basis,
(d)) on the site may not perform any drilling, excavation and other work,
that could lead to the release of asbestos fibres,
e) appropriate measures must be taken to avoid any
contact people with waste containing asbestos after a period of operation and after
closure of the landfill.
(2) The operator of a landfill that waste from asbestos is stored, with
subject to the further conditions laid down specific legislation ^ 8).
(3) documentation with a map of the location of the asbestos waste in the landfill is
part of the evidence of waste disposed, archived in accordance with § 21 para.
1 (b). (d)) of the Act.
§ 8
Technical requirements for the management of waste generated during combustion
hazardous waste
Fly ash from the incineration of hazardous waste can only be stored in a separate
the landfill sector after their previous edit by stabilizing some of the
procedures listed in annex 6.
§ 9
The technical requirements for waste storage facility modified by stabilising the
landfill
(1) hazardous waste, prepared pursuant to section 4 (4) stabilization. 7 (b). (b)),
may be stored in landfills with group-other waste after the end
technological process stabilization and the achievement of a maximum allowable
the values of the extract of waste laid down by výluhové class.
(2) the method of evaluation of modified waste stabilisation before saving
the landfill is set out in annex 7.
§ 9a
Technical requirements for the temporary storage of metallic mercury
Device for temporary storage of metallic mercury is a landfill group
S-hazardous waste. For the temporary storage of metallic mercury shall be subject
specific requirements in accordance with annex 13 to this Decree.
Title IV
How to create and use cash reserves
(Section 51, paragraph 5, of the Act)
§ 10
How to create financial reserves
(1) the details relating to the creation of financial reserves, its conclusiveness and
cancellation shall be governed by special legislation ^ 9).
(2) for the newly-established landfills arises the obligation to make a financial
reserve the date of the initiation of the navážení waste to landfill.
§ 11
The method of drawing the financial reserves
(1) the request of the operator of a landfill on the consent of the competent regional authority
with drawing from the resources of financial reserves pursuant to § 51 para. 1 law must
contain
and building permits) construction work for the purposes of reclamation
landfill ^ 10),
(b)) project documentation reclamation work, budgetary costs and
schedule of the reclamation work,
c) dump funds stored on the wire-bound
account not older than 3 months.
(2) the Financial Resources of the reserve is gradually drawing in accordance with the
the landfill project documentation up to 90% of the budgetary resources
on the conclusion and implementation of the reclamation work, up to the amount of 90%
financial reserves that are created on the date of application for the release of resources
from it, and the remaining 10% will be freed up after the acquisition of legal power
the final building approval ^ 10) as to the proper construction and building
the work needed to the reclamation and rehabilitation of the landfill.
(3) the provisions of paragraph 2 shall apply mutatis mutandis to the withdrawal of funds
the financial provisions for the gradual closure of parts of the landfill for
the conditions laid down in paragraph 1.
(4) withdrawal of funds is carried out and controlled in terms of
laid down by the regional authority in the decision to consent to the
financial reserve funds pursuant to § 51 para. 1 of the law.
Title V Of The
Technical requirements and conditions for the use of wastes on the ground surface
(For section 19, paragraph 3, of the Act)
§ 12
General technical requirements and conditions for the use of waste on the surface
terrain
(1) on the surface of the terrain cannot make use of waste hazardous, mixed
municipal wastes and wastes listed in annex 5, unless the waste
laid down in points B2 and B4, in accordance with the order of the devices.
Waste used on the ground surface, with the exception of waste used for
reclamation of landfills pursuant to § 13 para. 1, must not contain more
the concentration of pollutants than indicated in table 10.1 of annex 10 to the
This Decree and their aqueous extract must comply with the requirements laid down in
table 6.3 of annex 10 to this Decree. On the surface of the terrain can be of
building waste only excavated soils and tailings and the modified
waste in the form of recycled materials from construction and demolition waste or
construction and demolition wastes, from which they were removed the dangerous
folder, and you can remove the pattern specified for the tests.
(2) the content of harmful substances in the dry waste and the results of the ecotoxicological
tests of waste that are used on the surface of the ground shall not exceed a further
the limit values of the parameters set out in annex 10. In relation to the
the anticipated future use of space, in which the device is to use the
the waste is located, and in accordance with the provisions of section 75 (c). (b)) of the Act may
be established and other parameters not included in annex No 10, if it is
monitoring, including the determination of the limit values necessary for
for the protection of human health and environmental protection.
(3) the provisions of paragraph 2 shall not apply to the outputs of the device to the
the use of biodegradable waste, for which the method and
criteria for the evaluation and classification into groups according to the ways of their use
established Ordinances ^ 10a).
(4) data on waste, necessary for the assessment of its acceptability to the device
to use on the surface of the ground, shall be set out in the basic characterisation of the waste,
the content of which is set out in point 2 of annex 1.
(5) the use of waste on the ground surface must be in accordance with the requirements of
special legislation ^ 2) on health and the environment
and with the provisions of section 75 (c). (b)) of the Act in relation to the intended place
utilization of waste on the ground surface.
section 13 of the
Additional technical requirements and conditions for the use of waste for the conclusion and
recultivation of land for landfills
(1) Waste involved in the closing of the landfill to create the closing
Sealing layers of landfills must meet all the conditions laid down for
the Group of landfill sites in the annex No. 4 and their aqueous extract for
the rest of the hazardous waste landfill sites or in any of the indicators
exceed the exposure limit value výluhové class number (II) (b) listed in the table
Annex No. 2.
(2) Waste involved in the closing of the landfill to create the closing
the protective layer covering the shut-off sealing layer of landfill and waste
used in the upper layers of the landfill reclamation must comply with the conditions
laid down in point 1 of the annex No 11.
§ 14
Additional technical requirements and conditions for the use of waste on the surface
the terrain in addition to closure and reclamation
(Section 19 (3))
(1) Waste used to fill the depleted surface mines, quarries and
of gravel, with a view to their rehabilitation, must also meet the conditions
laid down in point 2 of the annex No 11.
(2) Waste used for terrain, recultivation of land and other adjustments
the surface of the human activities affected by the reclamation of land, with the exception of
landfills must meet the conditions laid down in point 3 of the annex No 11.
Title VI Of The
The mode of proof of the acceptability of waste at the facility
[To section 21, paragraph 5 (b), (c))]
§ 15
(1) the method of proving compliance with the criteria for acceptance of waste into the device
pursuant to section 2 (a). n) and how operators of the waste reception
the equipment is provided in annex 1.
(2) the waste may be accepted from the nepodnikajících of individuals
to the landfill without exams if their list of approved
regulations of equipment, are listed in annex 8.
(3) analytical methods, ecotoxicological and microbiological tests for
the determination of indicators of acceptability of waste into the devices are listed in the
Annex 12, with the exception of methods for the determination of critical indicators,
that are not set out in annexes 2 and 4.
(4) the acceptability of waste at landfills shall be demonstrated by complying with the conditions and
the criteria established for each class of landfill sites in § 3 (1). 2 and in
Annex No. 4.
PART TWO
Amendment to Decree No. 383/2001 Coll., on details of the management of waste, in
amended by Decree No. 41/2005 Coll.
section 16 of the
Decree 383/2001 Coll., on details of the management of waste, as amended by
Decree No. 41/2005 Coll., is amended as follows:
1. In section 4, paragraph 4. 3, after the words "operator", the words "and
supplier (owner) of the waste ".
2. In section 8 paragraph 2 reads as follows:
"(8) the operator of a waste to collect or purchase is required at the
accordance with § 18 para. 3 of the law to keep a record of persons from which the redeemed
things like waste the following types of waste according to the waste catalogue:
The code name of the species type of waste waste
17 04 01 copper, bronze, brass
17 04 02 aluminium
17 04 03 lead
17 04 04 zinc
17 04 06 Tin
17 04 07 mixtures of metals (17 04 01-06)
17 04 11 cables
16 01 17 ferrous metals
16 01 18 non-ferrous metals
17 04 05 iron and steel
17 04 07 mixed metals
20 01 40 metals ".
3. in article 9, paragraph 2 and paragraph 1 shall be deleted.
4. Part three, including title and footnote No 6 to 8 repealed.
5. in section 17(2). 4, the words "Municipal Office municipality with extended
application "shall be replaced by" regional authority ".
6. section 17a shall include footnotes # 10e-10 h shall be deleted.
7. in section 21 para. 1 (b). (c)), the words "(business name or the name, legal
form and registered office, if the person is a legal person, "are replaced by
the words "(ID, name, address, code, ORP (SOP) and IČZÚJ
the establishment, if the authorised person means a legal person ".
8. in section 22 para. 2 the word "establishments" shall be replaced by the word "device".
9. in paragraph 22 of the following shall be added at the end of paragraph 2 the sentence "for devices for mobile
waste collection with the reporting done by the municipal authority of the municipality with extended
operating within the company that operate a mobile
the device provides. In the event that the company has an establishment and operation
the mobile device is provided by this establishment, shall be sent by the annual
reports on waste that the establishment of the municipality with the extended Municipal Council
powers of the local establishment. The construction company
sends one annual reports for all constructions realized on the territory of
one local authority municipalities with extended competence this authority
collectively. "
10. Part eight, including title and footnotes 12 to 14
repealed.
11. In annex 2, point f) of point 1 and point 3, 3.1, 3.2 and 3.3.
shall be deleted.
12. In annex 2, point 2, the words "information and documents about the quality
waste, which "shall be replaced by the words" basic description of waste ^ 14a) ".
Footnote 14a is inserted:
"14a) Decree No. 294/2005 Coll., on conditions for storing waste at landfills
and their use on the ground surface and change of Decree No. 383/2001 Coll.
about the details of the waste facility. ".
13. Appendix No. 4 to 12 and annex No. 28 are deleted.
14. in annex 5, in the explanatory notes is replaced by the word "Region"
words "the region".
15. in annex # 19 and annex No. 19A in the form under the heading ' Registration
fill in "after the word" Fax "following the word" e-mail ".
16. in annex No. 20 worksheet # 3 after the heading of a table "Data the annual values
the composition of the sludge "in parentheses following the text" (to be completed only for sludges
used on agricultural land) ".
17. in annex No. 20 worksheet # 1 how to fill out the form at
the item "establishment" are replaced by the words "pursuant to § 5 para. 1
Act No. 455/1991 Coll., on trades, as amended
regulations "with the words" in accordance with special legislation (e.g.. According to § 5
paragraph. 1 of the law No. 455/1991 Coll., on trades (trade licensing
Act), as subsequently amended). ' and the following sentence "for mobile
treatment, recovery and disposal of waste in the whole of this
to the right of the form, filling out the details of the place of waste management in
device. ".
18. in annex No. 20 worksheet # 2 method of the form yplňování, in the second
line 8, column in annex No. 20A worksheet # 3 How to fill in
form in a column no 8 and in annex b of the worksheet # 3 Way
filling out a form in a column no 8, the words "the business name of each
authorized person (beneficiary) "shall be replaced by the words" the name of the establishment
or the point of waste management ".
19. in annex No. 20A worksheet # 3 How to fill out a form, the words
"in a column no 10" shall be replaced by "in column no. 9".
20. In the annexes, No 20, 20A and 20B in the manner of filling in tables 1
in the line, "the imports of waste" adds the text "EU Member State" on
text: "the importation of waste from a Member State of the EU" and the "export of waste"
the following text "EU Member State" by the wording: "the export of waste from
EU Member State ".
21. In the annexes, No 20, 20A and 20B in the manner of filling out at the end of
tables no. 1 lines:
+-------------------------------------------------------+--------+
| Imports of waste into the State that is not a Member State of the EU | XN16 |
+-------------------------------------------------------+--------+
| The export of waste to a State which is not a Member State of the EU | XN17 |
+-------------------------------------------------------+--------+
22. in annex 22 to the end of the table "device codes to modify,
recovery and disposal of waste "the following line:
+-------------------------------------------+--------------------+
| elektroodpadů processing | Z9 |
+-------------------------------------------+--------------------+
23. in annex No. 24, the title "device code table" is replaced by
the heading "places of Assembly code table for hazardous waste,
mobile devices for waste collection, waste collection sites and warehouses "and on the
the end of this table, the following line:
+-------------------------------------------+--------------------+
| elektroodpadů warehouse | S12 |
+-------------------------------------------+--------------------+
24. in annex No. 25 section E) in the text in brackets after the words "§ 78 para.
2 (a). c), (e)), i), (j)) "is inserted after the word") "and the words" § 79 paragraph 2. 1
(a). (b)) "shall be added after the word" c) '.
25. In annex 25 at the end of the table the following line # 50
+------+------------------------------------------------+--------+
| 50 | The number of permits issued to the limit | |
| values for the parameters referred to in annex a | # 4 point 10 | |
| | 294/2005 Decree No. Coll., on conditions for storing | |
| | & waste at landfills of their exploitation on the surface | |
| terrain and change | Decree No. 383/2001 Coll. | |
| | about details of waste management | |
+------+------------------------------------------------+--------+
26. in annex No. 26 in item No. 6. Carrier 1, and in item # 7.
The carrier **), the words "LICENSE PLATE semi-trailer" shall be replaced by "registration number
trailer ".
27. in annex No. 26 in the way of filling out the registration sheet under
6. Carrier 1, on the Street, place, postal code, the words "authorized persons"
shall be replaced by the word "carrier".
28. in Annex # 27 in the last row of the column "a separate establishment
the carrier "with the words" total vehicle establishment
transporting wastes ".
PART THREE
The EFFECTIVENESS of the
section 18
This Decree shall enter into force on the fifteenth day after its publication, with the
the exception of § 16 points no. 11 and 12 and annex No. 1, which will become effective
on 1 January 2004. January 1, 2006.
Minister:
RNDr. Ambrozek in r.
Č. 1
Acceptance of waste into the device and the substantiation of the quality of inbound waste
1. the operator shall ensure the reception of waste following
activities:
1.1. to all types of devices under section 2 (b). n)
and completeness check) the basic description of the waste referred to in point 2 and in the case of
landfills and described in section 3 when the first of a series of one-time or recurring
the supply of waste, while other repeated supply of waste control
test results validation of critical parameters or a statutory declaration,
that this is the same waste,
(b) a Visual inspection of each delivery) waste,
c) random checks to verify the conformity of the waste of the waste with the basic
a description of the waste submitted by the supplier (owner)
d) a record of each received a shipment of waste to a facility in accordance with the
requirements for the management of ongoing registration according to a special legal
prescription, ^ 11)
e) issue a written confirmation of each shipment of waste received in the
the device,
f) solemn declaration acceptance the supplier waste (owner-originator
or authorised persons, i.e.. the person responsible for the waste until it is
pass additional authorised person), that all the information referred to in
the basic characterisation of the waste are true, the affidavit may be
part of the basic description of the waste.
1.2. the acceptance of waste at landfills, it is necessary to perform an addition
compliance with the conditions laid down for the reception of waste on the appropriate group
dumps in the annex No. 4.
1.3. the documents about the quality of the waste to a facility with
be kept for 5 years, for the landfill after the period provided for in § 21 para. 1
(a). e) of the Act.
2. the elements of the basic description of the waste (information and documentation about the quality
waste) that the supplier shall waste (the owner) to pass to the person
authorized to operate relevant equipment for waste management in
the case of the first of a series of one-time or recurring shipments of waste to
the following are the devices
and) identification of suppliers of waste (name, registered office, address, ID,
If it has been allocated),
(b) the name, address of the establishment) where waste is generated,
(c)) the name type of waste, catalogue number, category, enumeration of hazardous
properties, if the waste is the category of "hazardous waste",
(d) a description of the generation of waste),
e) physical properties of the waste (smell, colour, consistency, etc.),
(f)) name, surname, place of residence, telephone, fax, e-mail and signature of the person
responsible for the completeness, accuracy and veracity of the information referred to in
the basic characterisation of the waste,
g) Protocol on the sampling of waste whose particulars are set out
special legislation, ^ 5) If you are in acceptance of waste
required test results, and if it is not a waste referred to in point
5.2.,
h) Protocol on the results of the tests (the properties of waste), aimed
in particular, the conditions of treatment of the waste in the negative
the device, not older than 3 months from the date of the drafting
the basic description of the waste, where the results of tests at acceptance
waste required
I) the forecast quantity of waste in the delivery,
j) estimated weight and frequency of the supply of waste the same properties
and the anticipated quantity of waste delivered to the device for the year,
to determine the critical indicators) that will be tracked in the course
recurring shipments of waste:
-the originator of the waste shipped at least once a year,
-operator-supplied devices to collect and purchase of waste in the case of
regularly and irregularly recurring each shipment of one kind
waste the same characteristics produced by the device to collect and purchase
waste control the same types of waste from a variety of designers
at least twice a year.
3. for the receipt of the waste to a landfill of waste waste must also base description
include:
and) data on the composition of the waste and the leaching ability needed to specify the
the Group of the landfill under the conditions set out in annex 4,
b) waste miscibility other kinds of waste,
(c)) to specify a group of the landfill based on the data referred to at point a),
d) a statement that the waste cannot be used or otherwise delete on the basis of
assessment in accordance with § 11 para. 3 of the Act,
e) statement that it is not a waste, which cannot be stored at landfills
all groups (in accordance with Annex No.5),
f) measures that need to be in the landfill after receiving some
types of waste (e.g. overlay for waste containing asbestos, a ban on
the mixing of the waste according to the evaluated Annex No. 3).
4. the basic description of the waste is updated when any change to the raw materials and
technology process in which waste is produced and other changes that
qualitative indicators will affect the waste.
5. Simplified acceptance of waste to landfill
5.1. When shipments of waste can be a basic description of the waste
replaced by a declaration of the owner of the waste, that waste is equivalent to
the basic description, delivered at the first of a series of deliveries and verifying
critical indicators according to the conditions laid down in paragraph 2 (a). k).
5.2. Waste, whose basic description need not be compiled on the basis of
results of the tests are:
a) wastes listed in annex No. 8, imposed under the conditions set out therein,
b) waste, whose evaluation for the purpose of admission to a device
professional judgment based on knowledge of the input raw materials, technology
creation, editing, and other information; judgement must be in the basic characterisation
documented in detail in relation to each indicator for admission to
the equipment laid down in annexes 2 and 4 to this Decree,
c) waste, of which a representative sample and cannot be removed
the basic description of the processes on the basis of judgment.
Č. 2
Vyluhovatelnost of waste and the leaching ability class
1. treatment of the sample and the preparation of an aqueous extract
When you modify the sample and subsequent preparation of an aqueous extract, follow the
EN 12457-4 (83 8005). Pretreatment of the sample of waste prepared
stabilisation is listed in annex 7. For filtration of extract specified to
ecotoxicological tests shall apply filter medium
pore size 5 mikrom.
2. analytical methods
The reference methods of analysis are listed in annex 12. On the analysis of
You can also use other comparable methods for purpose validated.
3. Class leaching ability
Maximum permissible values of indicators-pollutant in water
the extract of the waste (in mg/l) for each class of leaching ability are
listed in table 2.1.
Table 2.1.
Maximum permissible values of the indicators for each class
leaching ability
------------------------------------------------------------------
Class leaching ability
-------------------------------------------
pointer and IIa IIb III
-------------------------------------------
mg/l mg/l mg/l mg/l
------------------------------------------------------------------
Doc (dissolved
organic carbon) 50 80 80 100
------------------------------------------------------------------
Phenol index 0.1
------------------------------------------------------------------
Chlorides 80 1500 1500 2500
------------------------------------------------------------------
Fluoride 1 30 15 50
------------------------------------------------------------------
sulfate 100 3000 2000 5000
------------------------------------------------------------------
As 0.05 2.5 0.2 2.5
------------------------------------------------------------------
BA 2 30 10 30
------------------------------------------------------------------
CD 0.004 0.5 0.1 0.5
------------------------------------------------------------------
CR total 0.05 7 1 7
------------------------------------------------------------------
CU 0.2 10 5 10
------------------------------------------------------------------
Hg 0.001 0.2 0.02 0.2
------------------------------------------------------------------
NI 0.04 4 1 4
------------------------------------------------------------------
Pb 0.05 5 1 5
------------------------------------------------------------------
SB 0.006 0.5 0.07 0.5
------------------------------------------------------------------
Is 0.01 0.7 0.05 0.7
------------------------------------------------------------------
0.4 20 5 20 Zn
------------------------------------------------------------------
Mo 0.05 3 1 3
------------------------------------------------------------------
RL (dissolved
substances) 1) 400 8000 6000 10 000
------------------------------------------------------------------
pH >= 6 >= 6
------------------------------------------------------------------
Note for table 2.1.:
1) if the value of the pointer is fixed RL (the solute) is not
necessary to establish the values of concentration of sulphates and chlorides and vice versa.
4. the procedure for the assessment of leaching ability of waste
Procedure for the assessment of leaching ability of waste are set out in the relevant methodological
instruction of the Ministry of the environment for the evaluation of leaching ability
published in the journal of the MINISTRY of the ENVIRONMENT of the waste, the amount of grade XII, 12, December
2002.
Č. 3
Miscibility waste going to landfill
When storing the waste at landfills must be minimized option
chemical reactions between the different kinds of waste to be deposited.
Miscibility is a criterion for the assessment of common storage options
two or more types of waste to landfill. Wastes are miscible with each other,
If you save their common to dump there reactions with
adverse symptoms. For the adverse symptoms of chemical reactions between waste
placed on landfill is considered especially manysorted heat generation with
burn, development options for combustible or toxic gases, creating a
conditions to allow a significant increase in harmful leaching ability
substances from waste landfill in internal waters.
1. the procedure for evaluation of mísitelnosti waste
Producer of the waste or the authorized person in the basic characterisation of the waste
evaluates whether the chemical substances and preparations contained in waste cannot
cause when mixed with other waste adverse reactions. If such
the risk exists, shall be specified in the basic characterisation of waste, chemical
substances, preparations and/or waste waste cannot be mixed, or what
waste storage to be taken to the adverse
reactions avoid. Whenever the taking over of waste to landfill must
operator of the site to assess whether chemical substances and preparations that are contained
in the přejímaném of the waste will not be in the State and the amount in which they are present
in this waste, responding with waste placed in the active layer of landfill
for the adverse symptoms, including an evaluation of neutralization
capacity.
2. compatibility of the waste
In one sector of the dump body (section 3 (5)) shall not be
stored in particular:
2.1 waste covered-stabilized with inorganic binding agents and waste
high sulphur content (e.g. gypsum) management subject
biological degradation (e.g. municipal waste),
2.2 waste with increased content of metals (eg. inorganic wastes containing
metals from metal processing, surface treatment of metals, from hydrometallurgical processes
non-ferrous metals) of waste subject to biological degradation (e.g..
municipal waste),
2.3 waste containing nitrates (such as containers with the remains of artificial fertilizers)
wastes containing oil substances,
2.4 wastes containing cyanides of waste subject to biological
degradation (e.g. municipal waste) or with waste acid reactions.
Č. 4
The conditions that must meet the waste stored at the landfill
1. In landfills all groups must not be stored wastes listed in section
And annex No. 5.
2. for all waste going to landfills must comply with the conditions
mísitelnosti referred to in annex 3.
3. the waste covered by one of the methods referred to in the annex to the stabilization
# 6 under code D9, must not be stored in landfills with Group-IO and
S-OO3. Landfill-OO1 groups or with-WELL are stored according to the class
leaching ability.
4. Fly ash from hazardous waste incinerators may be imposed only after
modify the stabilisation in a separate sector of the waste dump.
5. the conditions and criteria for acceptance at a landfill for inert waste group
S-inert waste:
and) without tests may be accepted only waste listed in annex No. 8
under the conditions set out therein,
(b) prepared from aqueous extract) of waste procedure according to ČSN EN 12 457-4 (83
8005) must not exceed, in any of the indicators not exceeding permissible values
listed in annex No. 2 for výluhovou class number I,
(c)) the waste cannot contain a higher concentration of organic pollutants, than
is shown in the following table 4.1.
Table 4.1.
Maximum permissible concentrations of pollutants for wastes
that may not be stored in landfills with Group-inert waste
------------------------------------------------------------------
A pointer to the limit value Unit
------------------------------------------------------------------
BTEX mg/kg dry weight 6
------------------------------------------------------------------
Hydrocarbons C10-C40 mg/kg dry weight 500
------------------------------------------------------------------
PAU mg/kg of dry matter 80
------------------------------------------------------------------
PCB mg/kg dry weight 1
------------------------------------------------------------------
TOC mg/kg of dry matter 30 0001) (3%)
------------------------------------------------------------------
Note to table 4.1:
1) in the case of soil can be the maximum permitted value of the TOC indicator 3
% is exceeded, provided that the value is DOC = < 50 mg/l
Abbreviations used
-A sum of BTEX benzene, toluene, Ethylbenzene and the XYLENES
C10-C40-hydrocarbons containing 10 to 40 carbon atoms in the molecule
Pau-polycyclic aromatic hydrocarbons (sum of antracenu,
benzo (a) antracenu, benzo (a) pyrene, benzo (b) fluoranthenu,
benzo (ghi) perylene and, benzo (a) phenanthrene, fluoranthenu, fluoranthenu,
chrysenu, indeno (1, 2, 3-cd) pyrene, naphthalene and pyrene)
PCBS-polychlorinated biphenyls (sum congeners # 28, 52, 101, 118, 138,
153, 180)
TOC-total organic carbon
Doc-dissolved organic carbon
6. the conditions and criteria for acceptance of waste to landfill with the Group-
other wastes (S-OO1):
and) without tests may be accepted only waste listed in annex No. 8
under the conditions set out therein,
(b) prepared from aqueous extract) of waste procedure according to ČSN EN 12 457-4 (83
8005) must not exceed, in any of the indicators not exceeding permissible values
listed in annex No. 2 for výluhovou class number of the IIa,
(c)) in the dry matter content of TOC waste must not exceed 5%. When exceeding this
maximum permissible value for the waste to be regarded as complying with the criteria
to receive in the case that the value is DOC < = 80 mg/l TOC Content in the dry matter.
waste stabilized (code D9 in annex No. 6) it shall not be;
d) wastes with asbestos are stored in accordance with section 7.
7. the conditions and criteria for acceptance of waste to landfill with the Group-
other wastes (S-OO3):
and this group of landfills) may not be stored wastes on the basis of plaster,
(b)) free trials may be accepted only waste listed in annex No. 8
under the conditions specified therein and waste which cannot be assessed on the basis of the
the aqueous extract in accordance with § 3 (1). 2 (a). (b)) (2),
c) aqueous extract prepared from waste procedure according to ČSN EN 12 457-4 (83
8005) must not exceed, in any of the indicators not exceeding permissible values
listed in annex No. 2 for výluhovou class number of the IIa, the exception is only
compost bin (output from the stabilized equipment for biological treatment
Bio waste 3. the group referred to in annex No 6 to Decree No 341/2008 Sb.)
the DOC does not check pointer
(d)) the proportion of biodegradable municipal waste stored at landfills
must be progressively restricted in accordance with the timetable laid down in the plan
waste management of the CZECH REPUBLIC and regions [i.e. to reduce this share to 2010
at 75%, by 2013 to 50% and by 2020 to 35% of the total amount
(weight) of biodegradable municipal waste produced in the
1995],
e) asbestos waste are stored in accordance with section 7,
f) output from the device for the mechanical-biological waste treatment facility, which
is stabilized, the compost bin can be accepted without tests according to annex
# 2 only if it is produced by modifying the mixed municipal waste, and waste
similar, and subject to the fulfilment of the stability parameter AT4
listed in table 4.2, and if its calorific value does not exceed 8
000 kJ/kg.
8. the conditions and criteria for acceptance of waste to landfill with the Group-
hazardous waste (with-NO):
and) without tests may be accepted only waste listed in annex No. 8
under the conditions set out therein,
(b) prepared from aqueous extract) of waste procedure according to ČSN EN 12 457-4 (83
8005) must not exceed, in any of the indicators not exceeding permissible values
listed in annex No. 2 for výluhovou class number III,
(c)) shall not be received by the wastes that exhibit the loss on ignition of the higher
than 10% of the dry matter, or a pointer to a TOC in the dry matter of more than 6%. When
exceeding this maximum permissible values of the TOC for the waste indicators
considered to be the criteria for income in the event that the value of
DOC = < 100 mg/l TOC Content in the dry matter. emulsion stabilised waste (D9 in code
Annex No 6 to this Ordinance) shall not be necessary.
d) wastes with asbestos are stored in accordance with section 7,
e) metallic mercury that is waste, is accepted for temporary storage
under the conditions of section 9a. The other conditions laid down in this annex,
for the temporary storage of metallic mercury shall not apply.
9. A maximum of three a maximum allowable values of indicators
except pH set out in table no. 2.1 of Annex No. 2 to the competent
a group of landfill sites, is only possible under the following conditions:
and all the other requirements) laid down in annex 4 are met,
(b) it does not present an increased risk of being exceeded) the environment
under special legislation ^ 2)
(c)) it is a concrete wastes by specific pathogens, referred to in
the operational procedure of the landfill,
d) in the case of inert waste may not be increased no more than the permitted
the parametric values DOC, BTEX, PCBS, TOC and hydrocarbon series C10-C40,
e) in the case of the common store other waste and hazardous waste
in landfills with-OO DOC pointer must not be increased and adjusted pH value,
(f)) in landfills for hazardous waste with-NO you cannot increment the pointer to a DOC,
g) will be reported in accordance with Annex No. 25 of Decree No. 383/2001 Coll.
the details of the waste facility, as amended.
10. Wastes from the mechanical-biological waste stored at the landfill site editing
must meet the parameter stability AT4 listed in table 4.2.
Table 4.2.
----------------------------------------------------------------------------------------------
The parameter limit value Unit
----------------------------------------------------------------------------------------------
oxygen consumption after 4 days (AT4) *) 10 mg O2/gsušiny
----------------------------------------------------------------------------------------------
*) AT4-test respiratory activity, test method for evaluating the stability of organic waste on the basis of the measurement of consumption
O2 in 4 days in accordance with Decree No. 341/2008 Coll.
Č. 5
The list of waste, which is forbidden to dump all of the groups and the
use as a technology or to use the material on the surface of the ground and
wastes that can be to the landfill to store only under certain conditions
A. the list of waste, which is forbidden to dump all of the groups and the
use as a technology or to use the material on the surface of the ground
1. wastes arising from the products subject to the obligation to take back
(section 38 of the Act).
2. Liquid wastes and waste which releases the liquid phase sedimentation, with
the exception of the metal mercury, which is taken as waste to a temporary
storage under the conditions under section 9a.
3. Hazardous wastes that have any of the following dangerous
properties: explosivity, flammability, oxidizing high ability, the ability to
give off very toxic or toxic gases in contact with water, air
or acids, or infectivity, with the exception of the metal mercury, which is like
waste accepted for temporary storage under the conditions under section 9a.
4. wastes which react violently upon contact with water.
5. Waste of chemical and biological substances arising from the research,
development or learning activities, whose identity has not been established or
are new and whose effects on man and/or the environment are not
known.
6. all drugs ^ 13), addictive substances and preparations ^ 21), the same ^ 21) and
drug precursors ^ 22).
7. the Biocides (pesticides). ^ 2)
8. strongly odorous Waste. ^ 15)
9. Waste (containers and equipment) containing gas under pressure differing from
atmospheric pressure.
10. Waste, for which the rate of content of radionuclides or contaminated by them
does not allow their entry into the environment. ^ 16)
11. Acid hydrolysis and subject to wastes from titanium dioxide production.
B. Waste that can be stored in a landfill just under certain conditions
1. Usable waste only in accordance with the plan of waste management
region and the screened usable folders municipal waste (waste paper, glass,
plastic, metal, and beverage cartons) only if, in accordance with § 11 para. 2
the law is not their use of technically and economically possible.
2. Untreated waste only if it is about waste inert, for which
the adjustment is technically impracticable, and waste, which cannot be, or by editing the
a reduction in their volume or the reduction or elimination of their
the hazardous properties.
3. only the Tires, if used as a technological material for
technical security and the closure of the landfill in accordance with the operating regulations
the landfill.
4. the biodegradable waste only, if it is a biologically
biodegradable ingredients contained in municipal waste (groups of 20 Catalog
waste), for which a timetable for gradual limitation of their store on
landfill set out in point 7 of annex 4 to this notice.
5. the Management of persistent organic pollutants only for
conditions laid down by the directly applicable European Union law ^ 23).
Č. 6
The patterns and practices that are considered waste treatment facility before their
saving on landfill
The patterns and practices that are considered waste treatment facility, as defined in section 4 (b).
to act before deleting them) are listed in annex 4 of the law No.
under the codes, D8, D9, D13, D14. The most common presentations of waste to be carried out
before deleting them ways listed in annex 4 of the Act under the
codes D1, D5 and D12 are as follows:
D8-biological treatment
-is controlled by the action of biologically active components of the waste in order to change
properties of waste consisting, for example. a reduction in content or release
harmful substances contained in the waste into the solution, reduce the volume or
the weight of the waste or the significant reduction of pathogenic biological
officials in order to remove the dangerous properties of H9-infectivity.
Technology belonging to this group using the Edit to modify the waste
waste both natural and selected microbial cultures. The effectiveness of the modification,
in particular, if it is a selective biodegradation of contaminants in
waste (such as oil), must be monitored in relation to the total
the weight of the waste being edited so as to eliminate the effects of dilution of this
waste other substances (products, materials, waste), added to it
in the context of the treatment technology. The effectiveness of the technology in order to reduce or
removal of pathogenic biological agents must be tracked by the
physical, chemical, and biological indicators.
D9 physico-chemical treatment-
-eg. evaporation, drying, calcination, change reaction (pH-
neutralization), changing the chemical composition, drainage, coagulation, filtration,
reinforcement (solidification), encapsulation (encapsulation), manner
(vitrification), sealed in glass (vitrification), sealing the asphalt
(bitumenace), sealing the sulfur, a combination of the above methods, etc.
The concept includes not only strengthening the solidification of liquid waste, but it is
used for the description of the adjustment of solid wastes, which consists in their
mixing with binders and then changing their physical and often, in
following the type of the used binders, as well as chemical properties. As
binders are used all sorts of materials (and waste), which sometimes
chemically react with waste, other times only wrap the particles without
progress of chemical reactions. As the active Binder are most often
used maltotvorná, hydraulic binders-cement, lime, and mixtures thereof
-supplemented by other ingredients, e.g.. silicates, ash, bentonite.
As a passive binders are most often used sulfur, asphalt, plastics
etc. When solidifikaci using maltotvorných binders are solid wastes
often rozplavovány or dissolved in water and then into the solution
added binders or a suspension, and with them the excipients (additives)
that adjusts to the shape of solid waste things. Solidification technology
are applied in dozens of variants based on the ratio of used
additives and binders, which are normally characteristic of the facility,
the adjustment are used. Solidification of, respectively, the maturation of the product,
which solidified waste in the course of editing the reshaping, is considered
as part of the waste treatment technology.
Referred to ways of adjusting the waste, the use of which is not possible or
It is economically and technologically very demanding and whose removal would
editing an unreasonably increase the risk to the health of the people, for the individual
elements of the environment or would not be possible due to limitations of
resulting from the generally binding regulations.
D13-to adjust the composition of the waste.
Modifying the composition of the waste includes waste sorting. Department
the individual components of the waste, carried out primarily for the purpose of their
use, which is generally also treated differently,
While at least one graded component is being deleted by saving on
landfill. When mixed wastes must be followed by a ban on "diluting and mixing"
hazardous waste in accordance with § 12 para. 5 of the Act and other restrictions
arising out of this Ordinance and of the Act.
D14-other presentations of waste
It includes presentations of waste whose assignment to the above codes
It is not possible (e.g. packaging waste including their placement in special
containers), or a combination of the procedures covered by the above
procedures.
Č. 7
Evaluation of modified waste stabilisation before storing it in a landfill
Waste covered by stabilizing some of the methods provided in annex No.
4 of law under code D9 (freezing, vitrification, bitumenace, sealing
to sulfur, etc.) before saving to landfills, only on the basis of
the extract in annex No. 2. Analysis of dry matter in table 4.1. Annex No.
4 do not. Edit the sample waste for the purpose of preparing its aqueous
the extract is carried out:
1. for the modified waste solids with a fixed character of friable consistency
Earth in accordance with point 1 of Annex No. 2,
2. for the modified facility, having the consistency of firm, nature of the
building materials (such as concrete, asphalt) or glass, the sample
conditioned waste for extracting formed in the shape of cylinder diameter
4 cm and weighing 100 g +/-10 g.
Č. 8
List of waste and the conditions for their acceptance on the landfill of waste without
tests
1) wastes listed in table 8.1. It is possible to receive at a landfill without
the tests only under the following conditions:
1. supplier of waste is the nonentrepreneurial natural person
2. the waste cannot be recycled or otherwise use,
3. wastes are listed in production order of the landfill,
4. shipments of waste are from one particular building (location)
5. waste is not contaminated by wastes, which is prohibited on
dumps all of the groups referred to in annex No. 5
6. when taking delivery of waste to landfill is passed to the affidavit
nonentrepreneurial natural persons, that the waste is not polluted by any substances
causing their gravity and does not contain metals, plastics, asbestos,
chemicals, and possibly other types of waste not listed in the table.
2) when you suspect that the waste is contaminated (e.g. on the basis of Visual
control or knowledge of the origin of the waste), waste shall not be without testing on
landfill accepted.
Table 8.1.
An overview of waste acceptable at landfills of waste without testing
------------------------------------------------------------------------------------------------------------------
Waste code name description of waste waste must not contain
------------------------------------------------------------------------------------------------------------------
10 11 03 waste material of mineral cotton wool with the content
on the basis of glass fibres of asbestos, organic binders
------------------------------------------------------------------------------------------------------------------
15 01 07 Glass packaging used glass containers
the remnants of the filling
------------------------------------------------------------------------------------------------------------------
17 01 01 Beton1) pieces of concrete and reinforced concrete coatings and coatings (e.g..
demolition and reconstruction of buildings, insulation, decorative,
which may contain minor penetration), pollution
particles of metals (e.g. screws) and wood oil hydrocarbons
(e.g., the remnants of the lost formwork)
less than significant
------------------------------------------------------------------------------------------------------------------
17 01 02 Cihly1) Bricks, chunks of brick, brick blocks of coatings and coatings (e.g..
(brick United Malta) from demolition waste insulation, decorative,
construction and reconstruction of penetration) pollution
petroleum hydrocarbons)
------------------------------------------------------------------------------------------------------------------
17 01 03 Bags and ceramic roof tiles of clay, Concrete Roofing
výrobky1) facing and floor ceramic and roofing with the content
Tile demolition and reconstruction of the asbestos
buildings
------------------------------------------------------------------------------------------------------------------
17 01 07 mixtures of, or separate fractions of waste construction products Wastes containing asbestos
concrete, bricks, tiles based on natural materials and protective coatings containing
and ceramic products 1) organic compounds and petroleum
than those mentioned in substance
17 01 06
------------------------------------------------------------------------------------------------------------------
17 02 02 Glass glass from the fill hole buildings contaminated
------------------------------------------------------------------------------------------------------------------
17 05 04 soil and stones Ornici, peat, soil
not listed under the number of contaminated sites
17 05 03 *
------------------------------------------------------------------------------------------------------------------
20 01 02 Glass shards of itself Only beverage packaging residues
collected cartridges, broken glass beverage containers packaging
and in the case of sheet glass and packaging for chemicals
that in that time and place is not
the municipalities included in the grading system
and the use of such waste
------------------------------------------------------------------------------------------------------------------
soil and stones 20 02 02 waste from gardens and parks maintenance, wastes from the excavations
and reconstruction engineering
networks, ornici and peat
------------------------------------------------------------------------------------------------------------------
Note to table 8.1:
1) construction and demolition wastes containing metals, plastics, přimíšených
Earth rubber, wood and other plant materials up to 5% of the total
the weight of the waste, which does not alter the basic physical properties of the species
waste and sorting is not economically advantageous and in terms of the protection
the environment required.
Č. 9
cancelled
Č. 10
Requirements for the content of harmful substances in the waste that are used on the surface of the ground
Table 10.1
Maximum permissible concentrations of pollutants in the dry waste
------------------------------------------------------------------
A pointer to the limit value Unit
------------------------------------------------------------------
Metals
------------------------------------------------------------------
As mg/kg dry weight 10
------------------------------------------------------------------
CD mg/kg dry weight 1
------------------------------------------------------------------
CR total 200 mg/kg dry weight
------------------------------------------------------------------
Hg mg/kg dry weight 0.8
------------------------------------------------------------------
Her mg/kg of dry matter 80
------------------------------------------------------------------
PB mg/kg dry weight 100
------------------------------------------------------------------
In mg/kg dry weight 180
------------------------------------------------------------------
Monocyklické aromatic
hydrocarbons (non-halogenated)
------------------------------------------------------------------
BTEX 0.4 mg/kg dry weight
------------------------------------------------------------------
Polycyclic aromatic
hydrocarbons
------------------------------------------------------------------
PAU mg/kg dry weight 6
------------------------------------------------------------------
Chlorinated aliphatic
hydrocarbons
------------------------------------------------------------------
EOX mg/kg dry weight 1
------------------------------------------------------------------
Other hydrocarbons
(mixed, non-halogenated)
------------------------------------------------------------------
Hydrocarbons C10-C40 mg/kg dry weight 300
------------------------------------------------------------------
Other aromatic
hydrocarbons (halogenated)
------------------------------------------------------------------
PCB 0.2 mg/kg dry weight
------------------------------------------------------------------
Note to table 10.1:
Reference methods of analysis for the determination of individual indicators are
set out in annex 12.
Abbreviations used
-A sum of BTEX benzene, toluene, Ethylbenzene and the XYLENES
Pau-polycyclic aromatic hydrocarbons (sum of antracenu,
benzo (a) antracenu, benzo (a) pyrene, benzo (b) fluoranthenu,
benzo (ghi) perylene and, benzo (a) phenanthrene, fluoranthenu, fluoranthenu,
chrysenu, indeno (1, 2, 3-cd) pyrene, naphthalene and pyrene)
EOX-extractable organically bound halogens
PCBS-polychlorinated biphenyls (sum congeners # 28, 52, 101, 118, 138,
153, 180)
Table 6.3 requirements for the results of the ecotoxicological tests
----------------------------------------------------------------------------------------------
The test organism and Time. II.
the action of the
[hour]
----------------------------------------------------------------------------------------------
Poecilia reticulata 96 fish should not show fish should not show
or Brachydani rerio in the validation test, significant in the validation test, significant
behavior changes compared to changes in behaviour in comparison
with the control samples and control samples may not and must not
not a single fish die die not a single fish
----------------------------------------------------------------------------------------------
Daphnia magna Straus 48 percentage immobilisation percentage immobilisation
perlooček not perlooček not in the verification in the verification
the test shall not exceed 30% of the test shall not exceed 30%
in comparison with the control in comparison with the control
samples samples
----------------------------------------------------------------------------------------------
Proven in 72 Raphidocelis verification proves the vověřovacím
subcapitata algae growth inhibition test inhibicenebo stimulation test
(Selenastrum greater than 30% growth of eyelashes more than 30%
capricornutum) with the control samples in comparison with the control
or Scenedesmus samples
buspicatus
----------------------------------------------------------------------------------------------
the seeds of Sinapis alba 72 proven in validation does not prove the vověřovacím
root growth inhibition test inhibicenebo stimulation test
the seed of greater than 30% growth of the root of the seed of greater
in comparison with the control than 30% compared
samples with control samples
----------------------------------------------------------------------------------------------
Note to table 6.3
Acute toxicity tests shall be carried out with the undiluted aqueous extract waste.
Ecotoxicological tests are listed in annex 12. In the case of waste
containing inorganic binders (lime, hydraulic lime, cement
, etc.) can be adjusted to the pH value of the extract solution in the interval 7.8
+/-0.2.
Č. 11
The conditions for the recovery of the waste on the ground surface
1. wastes can be used when closing the landfill to create a protection
layer covering a layer of sealing of the landfill and the upper layer reclamation
landfills, if:
and acute toxicity tests) carried out tests in ekotoxikologickými
accordance with the specific legislation, ^ 17) requirements are met
laid down in annex No 10, table 10.2, column I,
(b) a dry matter content of harmful substances) that are used by the waste does not exceed the maximum
the permissible values of inorganic and organic pollutants referred to in
Annex No 10, table 10.1,
(c)) for the use of the upper layers of the landfill reclamation designated for
greening (reclamation layers capable of fertilization-biology
reclamation of landfills) meet the conditions set out in (a). a) and b) and, if
biodegradable wastes are used as bearers of the nutrients shall
be proven to be adjusted in terms of the removal of the dangerous properties of
infectivity of technologies whose efficacy shall be demonstrated in accordance with Annex No.5
Decree No 341/2008 Sb.
2. the Waste may be used for the reclamation of extracted surface
mine workings (surface mines, quarries, sand pits), if:
and acute toxicity tests) carried out tests in ekotoxikologickými
accordance with the specific legislation, ^ 17) requirements are met
laid down in annex No 10, table 10.2, column II, and in the late
reclamation layer in the powers of at least 1 m from the ground surface meet
the requirements set out in column I of the table 6.3 of annex 10 to this
the Decree (stimulation of the growth of algae and seed is not the limiting factor),
(b) the content of harmful substances in the dry) the waste does not exceed the maximum permissible
the value of inorganic and organic pollutants listed in table 10.1.
of annex 10 to this Decree,
(c) waste used to top) reclamation layers designed for landscaping
(reclamation layers capable of fertilization-biological reclamation)
meet the conditions laid down in point (a). a) and b) and if they are being used
biodegradable waste as bearers of nutrients (e.g. sludge from
wastewater treatment plants) must be shown to be adjusted within the meaning of
the removal of the dangerous properties of the infectivity of technologies whose
the effectiveness of the jse demonstrated by Annex No. 5 to the Decree No 341/2008 Sb.
3. wastes can be used on the surface of the terrain to terrain or
land recultivation of land affected by human activity (with the exception of
reclamation), if:
and acute toxicity tests) carried out tests in ekotoxikologickými
accordance with the specific legislation, ^ 17) requirements are met
laid down in annex No 10, table 10.2, column II, and in the late
Layer (landscaping, landscaping, etc.) in power at least 1 m from the
the ground surface meets the requirements set out in column I of the table 10.2
of annex 10 to this Decree (stimulation of the growth of algae and seed is not
the limiting factor),
(b) the content of harmful substances in the dry) the waste does not exceed the maximum permissible
the value of inorganic and organic pollutants listed in table 10.1.
of annex 10 to this Decree,
(c) to the top layer reclamation) intended for landscaping (landscaping
layer capable of fertilization-biological reclamation) are used only
waste meeting the conditions laid down in point (a). a) and b) and biologically
biodegradable waste used as bearers of the nutrients must be
proven to be adjusted in terms of the removal of the dangerous properties of
infectivity of technologies whose efficacy shall be demonstrated in accordance with Annex No.5
Decree No 341/2008 Sb.
4. In the case of waste referred to in points 2 and 3 at a given point in the amount of
more than 1 000 t this place must be processed for risk assessment
in the site in accordance with the specific legislation ^ 19).
5. Exceeding of maximum allowable values of the individual indicators
referred to in paragraphs 1 to 3 shall be tolerated if their increase
matches the conditions of the characteristic, for a given location and geological and
the hydrogeological characteristics of the place and its surroundings, if used
waste under normal climatic conditions are not subject to any
significant physical, chemical or biological transformation, which leads to the
the release of harmful substances into the environment, and if they are prepared
the exposure limit values, including the critical indicators other than those listed in points 1 to
3, set out in the operational procedure of the device. In the case of the use of
the waste referred to in points 2 and 3 shall in addition be always met the requirements laid down
in section 4 and section 12 paragraph 1. 4.
Č. 12
The technical standards for analytical determination
Determination Of The Standard
----------------------------------------------------------------------------------------------
determination of dry matter dry matter Calculation 14 346 prEN based on determination of the residue after evaporation
or water content
ČSN ISO 11 465 (83 6635) soil quality-determination of the percentage by weight of
dry matter and the mass of soil moisture-Gravimetric method
----------------------------------------------------------------------------------------------
preparation of the extract to ČSN EN 12 457/1-4 Leaching test criteria provyluhování
granular sludge and waste materials
----------------------------------------------------------------------------------------------
The decomposition of ČSN EN 13 657 (83 8015) characterization of waste-Decomposition for subsequent
determination of soluble elements in the dissolved Royal
----------------------------------------------------------------------------------------------
The decomposition of ČSN EN 13 656 (83 8014) Decomposition using microwave radiation
with a mixture of hydrofluoric acid (HF), nitric (HNO3)
and hydrochloric (HCl) for subsequent determination of elements (the full decomposition
solid waste before hair elements analysis)
----------------------------------------------------------------------------------------------
Analysis of the extract to ČSN EN 12 506 (83 8013) characterization of waste-leaching-Analysis
Determination of pH, As, Ba, Cd, Cl, Co, Cr, CR(vi), Cu, Mo, Ni, NO2-,
Pb, total with SO42-, and Zn, in
----------------------------------------------------------------------------------------------
analysis of the extract to ČSN EN 13 370 (83 8012) characterization of waste-leaching-Analysis
Determination of ammoniacal nitrogen, to absorb organic
bound halogen (AOX), conductivity, Hg, jednosytných phenols,
total organic carbon (TOC), easily-and F-uvolnitelnýchCN
----------------------------------------------------------------------------------------------
the pH of the ČSN ISO 10 523 (75 7365) water quality. Determination of pH
----------------------------------------------------------------------------------------------
As to ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN EN ISO 11 969 (75 7403) water quality. Determination of arsenic. Method
atomic absorption spectrometry (hydride technique)
EN 26 595 (75 7404) water quality. The determination of all arsenic.
The Spectrophotometric method with silver diethyldithiokarbamanem
----------------------------------------------------------------------------------------------
Indeed, ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
TNV 75 7408 water quality-determination of barium by methods of Atomic
absorption spectrometry
----------------------------------------------------------------------------------------------
CD EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN ISO 8288 (75 7382) water quality. Determination of cobalt, nickel, copper,
of zinc, cadmium and lead. Flame atomic absorption method
spectrometry
ČSN EN ISO 5961 (75 7418) water quality. Determination of cadmium by Atomic
absorption spectrometry (ISO 5961:1994)
ISO 17294-2, Water quality-Application of inductively coupled
plasma mass spectrometry (ICP-MS)-Part 2: Determination of 62
elements
----------------------------------------------------------------------------------------------
CR total ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
EN 1233 (75 7425) water quality-determination of chromium-Atomic Methods
absorption spectrometry
----------------------------------------------------------------------------------------------
CU ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN ISO 8288 (75 7382) water quality. Determination of cobalt, nickel, copper,
of zinc, cadmium and lead. Flame atomic absorption method
spectrometry
TNV 75 7426 water quality-determination of copper by flameless technology AAS
----------------------------------------------------------------------------------------------
Hg EN 1483 (75 7539) water quality. Determination of mercury
TNV 75 7440 water quality. The determination of all mercury by single-purpose
Atomic Absorption Spectrometer
----------------------------------------------------------------------------------------------
MO ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ISO 15 586 water quality-determination of trace elements by atomic absorption
spectrometry with a graphite cells having a
----------------------------------------------------------------------------------------------
NI EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN ISO 8288 (75 7382) water quality. Determination of cobalt, nickel, copper,
of zinc, cadmium and lead. Flame atomic absorption method
spectrometry
TNV 75 7461 water quality. Determination of nickel by flameless technology AAS
----------------------------------------------------------------------------------------------
PB ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN ISO 8288 (75 7382) water quality. Determination of cobalt, nickel, copper,
of zinc, cadmium and lead. Flame atomic absorption method
spectrometry
TNV 75 7467 water quality. Determination of lead by flameless technology AAS
----------------------------------------------------------------------------------------------
SB ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ISO 15 586 water quality-determination of trace elements by Atomic
absorption spectrometry with a graphite cells having a
ISO 17 294-2, Water quality-Application of inductivelycoupled
plasma mass spectrometry (ICP-MS)-Part 2: Determination of 62
elements
----------------------------------------------------------------------------------------------
With the ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ČSN ISO 9965 (75 7480) water quality. The determination of selenium. Method of Atomic
absorption spectrometry (hydride technique)
ISO 17 294-2, Water quality-Application of inductivelycoupled
plasma mass spectrometry (ICP-MS)-Part 2: Determination of 62
elements
----------------------------------------------------------------------------------------------
In EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
ISO 17 294-2, Water quality-Application of inductivelycoupled
plasma mass spectrometry (ICP-MS)-Part 2: Determination of 62
elements
----------------------------------------------------------------------------------------------
Zn ČSN ISO 8288 (75 7382) water quality. Determination of cobalt, nickel, copper,
of zinc, cadmium and lead. Flame atomic absorption method
spectrometry
ČSN EN ISO 11 885 (75 7387) water quality. Determination of 33 elements by Atomic
emission spectrometry with inductively bound plasma (ICP-AES)
TNV 75 7497 water quality. Determination of zinc by flameless technology AAS
----------------------------------------------------------------------------------------------
BTEX (benzene, toluene, ISO 15009:2002 quality-Soil-Gas chromatographic determination
Ethylbenzene and Xylenes) of the contet of volatile aromatic hydrocarbons, naphthalene
and volatile halogenated hydrocarbons--Purge-and-trap method
with thermal desorption
(Draft standard) DIN ISO 15009-Bodenbeschaffenheit
Gaschromatographische Bestimmung des Anteils an flüchtigen
aromatischen Kohlenwasserstoffen, Naphthalin
und Halogenkohlenwasserstoffen-Thermisches Desorptionsverfahren
MIT Reinigungs-und Auffangschritt (ISO/DIS 15009:2001)
----------------------------------------------------------------------------------------------
chlorides ČSN ISO 9297 (75 7420) water quality. Determination of chlorides.
Argentometric determination with chromanovým (indicator method
According to the Mohr)
----------------------------------------------------------------------------------------------
ČSN EN ISO 10 304-1 (75 7391) water quality. Determination of dissolved
fluorides, chlorides, bromides, phosphates, nitrites, nitrates
liquid chromatography method and sulphate ions. Part 1: Method
for the low-polluted water
----------------------------------------------------------------------------------------------
ČSN EN ISO 10 304-2 (75 7391) water quality. Determination of dissolved
anions by liquid chromatography of ions. Part 2:
bromides, chlorides, nitrates, orthofosforečnanů, and síranův waste
the waters of the
----------------------------------------------------------------------------------------------
ČSN EN ISO 15 682 (75 7421) water quality. Determination of chlorides
flow analysis (FIA and CFA), spectrophotometric or
potentiometric detection
----------------------------------------------------------------------------------------------
Doc (dissolved EN 1484 (75 7515) water quality-determination of total organic
organic carbon) carbon (TOC) and dissolved organic carbon (DOC)
----------------------------------------------------------------------------------------------
EOX (Cl) (Draft standard) DIN 38414-17 Deutsche Einheitsverfahren zur Wasser-,
Abwasser-und Schlammuntersuchung; Schlamm und Sedimente (Gruppe);
Bestimmung von ausblasbaren und extrahierbaren, organisch gebundenen
Halogenen (17)
----------------------------------------------------------------------------------------------
phenol index ČSN ISO 6439 (75 7528) water quality. Determination of jednosytných phenols.
The Spectrophotometric method with 4-aminoantipyrinem after distillation
ČSN EN ISO 14 402 (75 7567) water quality-determination of phenol flow
analysis (FIA and CFA)
----------------------------------------------------------------------------------------------
fluoride ČSN EN ISO 10 304-1 (75 7391) water quality. Determination of dissolved
fluorides, chlorides, bromides, phosphates, nitrites, nitrates
liquid chromatography method and sulphate ions. Part 1: Method
for the low-polluted water
ČSN ISO 10 359-2 (75 7430) water quality. Determination of fluoride. Part 2:
Determination of total fluoride inorganically bound after decomposition
and distillation
----------------------------------------------------------------------------------------------
-standard is not released
the neutralizer
the capacity of the
----------------------------------------------------------------------------------------------
hydrocarbons C10-C40 ČSN EN 14 039 characterization of waste-determination of hydrocarbon waste
C40-C40 by gas chromatography
----------------------------------------------------------------------------------------------
PAHS (polycyclic DIN 38 414-23 Deutsche Einheitsverfahren zur Wasser-Abwasser,-
aromatic hydrocarbons) und Schlammuntersuchung-und Schlamm Sedimente (Group S)-Teil 11:
Bestimmung von 15 polycyclischen aromatischen Kohlenwasserstoffen
(THEN) durch Hochleistungs-Flüssigkeitschromatographie (HPLC)
und Fluoreszenzdetektion (23)
(Draft standard) DIN ISO Bodenbeschaffenheit-Bestimmung 18 287
der polycyclischen aromatischen Kohlenwasserstoffe (THEN)-
Gaschromatographisches mit Verfaren Nachweis durch Massenspektrometrie
(GC-MS) (ISO/DIS 18 287:2003)
ISO 13 877 Soil quality-Determination of polynuclear aromatic
hydrocarbons-Method using high-performance liquid chromatography
DIN ISO 13 877 Bodenbeschaffenheit-Bestimmung von polycyclischen
Hochleistungs-Kohlenwasserstoffen-aromatischen
Flüssigkeitschromatographie-(HPLC)-Verfahren (ISO 13877:1998)
TNV 75 8055 characterization of sludge-determination of selected
polycyclic aromatic hydrocarbons (PAHs) by HPLC
with fluorescence detection
----------------------------------------------------------------------------------------------
PCB (polychlorinated DIN 38 414-with 20 Deutsche Einheitsverfahren zur Wasser-Abwasser,-
biphenyls) und Schlamuntersuchung-und Schlamm Sedimente (Group S)-Teil 20:
Bestimmung von 6 polychlorierten Biphenylen (PCB) (20)
DIN ISO 10 382-Bestimmung von Bodenbeschaffenheit
Organochlorpestiziden und Biphenylen-polychlorierten
Gaschromatographisches Verfahren mit Elektroneneinfang-detector
(ISO 10 382:2002)
----------------------------------------------------------------------------------------------
the solute to CSN 75 7346 (75 7346) water quality-determination of dissolved substances
----------------------------------------------------------------------------------------------
ČSN EN ISO 10 304-1 sulphate (75 7391) water quality. Determination of dissolved
fluorides, chlorides, bromides, phosphates, nitrites, nitrates
liquid chromatography method and sulphate ions. Part 1: Method
for the low-polluted water.
ČSN EN ISO 10 304-2 (75 7391) water quality. Determination of dissolved
anions by liquid chromatogrfie ion. Part 2:
bromides, chlorides, nitrates, and sulfates of orthofosforečnanů
in waste water
----------------------------------------------------------------------------------------------
TOC (total ČSN EN 13 137 determination of TOC in waste, sludge and sediments
organic carbon)
----------------------------------------------------------------------------------------------
the loss on ignition of the ČSN EN 12 879 characterization of sludge-determination of loss on ignition
----------------------------------------------------------------------------------------------
Ecotoxicity guideline of the Department to determine the ecotoxicity of waste waste
(Journal of the MINISTRY of the ENVIRONMENT 6/2003)
Ecotoxicological tests ČSN EN ISO 7346-2 water quality-determination of the acute lethal toxicity
for the freshwater fish Brachydanio rerio Hamilton-[Buchanan
(Teleostei, Cyprinidae)] -Part 2: the Refresh method
ČSN EN ISO 6341 water quality-test of inhibition of mobility of Daphnia
Magna Straus (Cladocera, Crustacea)-acute toxicity test
EN 28 692 water quality-fresh water algal growth inhibition test
Scenedesmus subspicatus and Selenastrum capricornutum (ISO8692:1989)
Root growth inhibition test white mustard (Sinapsis alba).
Guidance note of the Ministry of the environment to determine the
ecotoxicity of waste
----------------------------------------------------------------------------------------------
Microbiological tests to ČSN ISO 10381-6 soil quality-sampling-part 6: guidelines for
the collection, handling and conservation of soil samples for prostudium
aerobic microbial processes in the laboratory
ACTA hygienica, epidemiologica et mikrobiologica (AHEM) No 1/2008
----------------------------------------------------------------------------------------------
Notes:
*) standard only in the English language
**) German national standard
Annex 13
Specific requirements for the temporary storage of metallic mercury
A. the criteria and procedure for temporary storage of metallic mercury
1. The composition of the metallic mercury
Metallic mercury shall meet the following specifications:
and mercury content) greater than 99.9% by weight,
(b) the absence of impurities) capable of cause corrosion of carbon or stainless steel
steel, for example, nitric acid solution or solutions of chloride
salt.
2. requirements for Assembly resources
Containers used for the storage of metallic mercury shall be resistant to
corrosion and impact. Must not be welds. Containers must satisfy the following
specifications:
and) material: carbon steel container (a minimum of ASTM A36) or
stainless steel (AISI 304, 316 l),
(b) the containers must not shed) gases and liquids,
c) external wall of the container must be resistant to storage conditions,
(d) the design of the container) must pass the test of free fall and
leak test in accordance with annex and Chapter 6.1.5.3 and 6.1.5.4 European
the agreement on the international carriage of dangerous goods by road (ADR) ^ 25).
The maximum filling ratio is 80% by volume, in order to ensure
sufficient expansion space as a result of expansion of the liquid and as a result
the high temperature could cause leakage or permanent violations of the container.
3. recruitment for temporary storage of metallic mercury
You can only receive a certificate showing compliance with containers
the requirements referred to in part A of this annex. Certificates are issued by the supplier
the waste, which means the originator or the beneficiary, i.e.. the person behind the waste
responsible until its delivery to the other authorized person. Certificate
does not replace the basic description of waste according to annex No 1.
Procedures for the adoption must meet the following requirements:
a) accepted only metallic mercury that meets the minimum criteria for
the adoption referred to in paragraph 1,
b) containers must be visually inspected before storing;
damaged or corroded containers, or containers, showing escape
are taken,
(c)) the containers must be stamped a permanent mark indicating the
the container identification number, production materials, empty weight,
link to the manufacturer and date of manufacture,
(d)) on the containers must be permanently attached table
identification number certificate.
4. the content of the certificate
The certificate referred to in paragraph 3 shall contain the following information:
and) identification of suppliers of waste (name, registered office, address, ID,
If it has been allocated),
(b)) identification of the person responsible for filling containers (name,
registered office, address, identification number, if assigned)
(c) place and date of the performance) of containers,
(d)), the amount of mercury
e) purity mercury and, where appropriate, a description of the impurities, including an analytical report
f) affidavit that the containers were used exclusively for the carriage of
and storage of mercury,
(g)) the identifying numbers of containers,
h) any special notes.
B. requirements for the temporary storage of metallic mercury
For the temporary storage of metallic mercury, the following requirements must be met:
1. metallic mercury shall be stored separately from other waste,
2. the containers shall be stored in collection tanks with a suitable surface without a
cracks and crevices and impermeable to metallic mercury, the detention
the volume of the corresponding quantities of mercury,
3. as the repository can serve only the devices that comply with the technical
the requirements laid down by law and by a special legislation on the protection of
the environment and people's health ^ 2), which was set up by this
purpose in accordance with the specific legislation in the field of spatial
planning and building law ^ 10).
4. storage to your design and traffic organisations must ensure that
There will be a threat to human health and damage to any of the elements of the
in accordance with the specific legislation on the protection of the
environment and human health ^ 2)
5. storage must meet the same technical and security requirements
as the warehouses of substances, preparations and products of the same dangerous
the properties of the metallic mercury that is waste,
6. storage must be fitted with the artificial or natural barriers that
sufficiently guarantee the protection of the environment from emissions of mercury, and
You must have retention volume corresponding to the total amount of stored
Mercury,
7. the floor of the store must be covered with sealing materials resistant to
Mercury, vyspádované and equipped with a ditch,
8. the repository meets the requirements of a specific legislation in the field of
fire protection ^ 26),
9. the stored material shall be so arranged that all containers be
can be easily removed.
C. requirements for monitoring, control and procedures in case of accident and
record-keeping for the temporary storage of metallic mercury
1. requirements for the monitoring, control and procedures in the event of a disaster
In the store to install permanent monitoring of mercury vapour system with
a sensitivity not less than 0.02 mg of mercury per cubic metre. Sensors are placed on a level
floors and when piece measures 160-180 cm above floor level. Included is a Visual
and audible warning system. System maintenance is performed each year.
The operator of storage and containers at least once a month, visually
checks. When you detect the leak immediately, the operator shall take the necessary
measures to prevent the emission of mercury into the environment and restore the
the security of the storage of mercury. In doing so, it shall proceed in accordance with the measures for the
in case of a disaster, that are part of the approved operational procedure, and with the
the approved emergency plan according to the Water Act ^ 27). These documents,
as well as the necessary equipment for the safe handling of metallic mercury,
must be all the time on-premises storage traffic. For all releases
It is considered to have adverse effects on human health or the
the environment within the meaning of section 20 (b). I) of the Act.
2. record keeping
All documents containing the information specified in parts A and C of this
the annex, including the certificate accompanying the container and records
relating to the picking and dispatch of metallic mercury after their temporary
storage, destination and intended process, shall be kept
at least three years after their storage, unless otherwise specified in § 21 para. 1
(a). e) of the Act to retain these documents for a longer period.
Selected provisions of the novel
Article. (II) Decree No. 61/2010 Coll.
Transitional provision
The landfill with subgroups-OO2. April 2012 are considered landfills
the subgroup of S-OO1.
1) Council Directive 1999/31/EC of 26 July 2000. April 1999 on the landfill of waste.
Council directive 2011/97/EU of 5. 31 December 2011 and amending
Council Directive 1999/31/EC, as regards the specific criteria for storage
metallic mercury considered as waste.
2) for example, Act No. 254/2001 Coll. on waters and on amendments to certain laws
(the Water Act), as subsequently amended, Act No. 258/2000 Coll.
the protection of public health and amending certain related laws, in
as amended, law No. 86/2002 Coll., on the protection of the atmosphere and of the
amendments to certain other laws (law on the protection of the atmosphere), as amended by
amended.
3) Annex No. 1 of the Decree No. 381/2001 Coll. laying down a catalogue of
waste, hazardous waste and a list of lists of wastes and the States for the purpose of
exports, imports and transit of waste and the procedure for granting consent to
exports, imports and transit of waste (waste catalogue), as amended by Decree No.
503/2004 Sb.
4) for example, Decree No. 376/2001 Coll., on evaluation of dangerous
the properties of the waste, as amended by Decree No. 502/2004 Coll.
5) Appendix 5 of Decree No. 376/2001 Coll., as amended by Decree No. 502/2004
SB.
6) section 40 and 41 of the Act No. 258/2000 Coll., as amended. § 19
and 21 of regulation of the Government No. 178/2001 Coll., laying down the conditions of protection
health of workers at work, as amended. § 5
Decree No. 432/2003 Coll., laying down the conditions for the classification
work in categories, limit values for biological exposure indicators
tests, the conditions of collection of biological material for the implementation of
biological exposure tests and requirements for the reporting of work with asbestos and
biological agents.
7) § 21 para. 6 (a). c) Government Regulation No. 178/2001 Coll.
8) section 41 of Act No. 258/2000 Coll.
9) Act 593/1992 Coll., on reserves to ensure the tax base of the
income, as amended.
10) Act 50/1976 Coll., on zoning and the building code
(the building Act), as amended.
10A) Decree No. 341/2008 Coll., on details of the handling of the biological
degradable waste and amending Decree No. 294/2005 Coll., on conditions for
storing waste at landfills and their use on the surface of the ground and change
Decree No. 383/2001 Coll., on details of the waste management (Decree
about the details of the management of biodegradable waste).
11) paragraph 21 of Decree No. 383/2001 Coll., on details of the management of waste,
as amended by Decree No. 41/2005 Coll.
12) Decree No. 383/2001 Coll., on details of the management of waste, in
amended by Decree No. 41/2005 Coll.
13) Act 378/2007 Coll., on pharmaceuticals and on changes of some
related laws (law on medicinal products), as amended.
14) Annex No 5 of Regulation No 850/2004 on persistent organic
pollutants and amending Directive 79/117/EEC.
15) for example, Decree No. 356/2002 Coll. laying down the list of
pollutants, General emission limits, a message-passing and
information, determining the quantity of discharged pollutants
darkness of smoke, the permissible degree of harassment and the intensity of odors
the conditions of the authorization of the persons operating the register keeping requirements resources
air pollution, the conditions for their application.
16) 3 § 57 para. 1 (b). e) Decree of the State Office for nuclear
Security No. 07/2002 Coll., on radiation protection.
17) Act 246/1992 Coll., on the protection of animals against cruelty, as amended by
amended.
Decree 207/2004 Coll., on the protection, breeding and use of experimental animals.
19) Decree No. 99/1992 Coll., on the establishment, operation, safeguarding and
disposal facilities for waste disposal in underground areas in
amended by Decree No. 300/2005 Coll.
20) Act 254/2001 Coll.
21) Act 167/1998 Coll., on addictive substances and amending certain
other acts, as amended.
22) European Parliament and Council Regulation (EC) No 273/2004 of 11 March.
February 2004 on drug precursors.
Council Regulation (EC) No 111/2005 of 22 March. December 2004
laying down rules for the monitoring of trade in drug precursors between the
community and third countries.
Commission Regulation (EC) No 1277/2005 of 27 June. July 2005
detailed rules for the regulation of the European Parliament and of the Council (EC)
No 273/2004 on drug precursors.
23) Article. 7 European Parliament and Council Regulation (EC) No 850/2004 on
persistent organic pollutants and amending Directive
79/117/EEC.
24) European Parliament and Council Regulation (EC) no 1102/2008 of 22 March.
October 2008 on the banning of exports of metallic mercury and certain compounds and mixtures
Mercury and the safe storage of metallic mercury.
25) Decree No. 64/1987 Coll. on European Agreement concerning the international carriage of
carriage of dangerous goods by road (ADR) and the Ministry of foreign communication No.
13/2009 Sb. m. s., supplementing communication No. 159/1997 Coll. No.
186/1998 SB., no. 54/1999 Coll., no 93/2000 Sb. m. s., no. 6/2002 Coll. m.
s., no. 65/2003 Coll. m. s., no. 77/2004 Coll. m. s., no. 33/2005 Coll. m. s.,
No 14/2007 Sb. m. s., and no 21/2008 Sb. m. s. as regards the adoption of the amendments and
Add-ins "Annex A-general provisions and provisions concerning the
dangerous substances and articles "and" Annex B-provision of transport
resources and on the carriage of "European Agreement concerning the international carriage of
transport of dangerous goods (ADR).
26) Act 133/1985 Coll., on fire protection, as amended
regulations.
27) § 39 para. 2 of the Act 254/2001 Coll. No.
