Advanced Search

On The Determination Of The Details Of The Protection Of Quality Agricultural Land

Original Language Title: o stanovení podrobností ochrany kvality zemědělské půdy

Subscribe to a Global-Regulation Premium Membership Today!

Key Benefits:

Subscribe Now for only USD$40 per month.
153/2016 Sb.



DECREE



of 9 June. may 2016



on the determination of the details of the protection of the quality of agricultural soils and amending

Decree No. 13/1994 Coll. laying some of the details of the protection

agricultural land resources



Ministry of the environment shall determine, pursuant to section 22(1) of the 1 (b). (b)), and

c) of Act No. 334/1992 Coll., on the protection of agricultural land resources in

amended by Act No. 41/2015 Coll.:



PART THE FIRST



DECREE ON DETERMINATION OF QUALITY OF AGRICULTURAL LAND PROTECTION DETAILS



§ 1



Determination of content of prevention of risk elements and values of risk

substances and display the values of the contents of the risk elements and hazardous substances in the

agricultural land



The preventive value of the contents of the risk elements and hazardous substances in the

agricultural land are set out in annex 1 to this notice.

Indicator of the value of the risk elements and hazardous substances in agricultural soil

are set out in annex 2 to this Decree.



§ 2



The procedures for the assessment and evaluation of the contents of the risk elements and the risk

substances in agricultural soil



(1) the discovery of the contents of the risk elements and hazardous substances in the agricultural

the soil is carried out using the procedures and analyses provided for in annex 3 to the

This Decree. The sampling procedure designed to detect the contents of

risk elements and hazardous substances in agricultural land is set out in

Annex No 4 to this notice.



(2) the assessment of the contents of the risk elements and hazardous substances in the agricultural

the soil is done by comparing the contents of the risk elements identified and

hazardous substances in agricultural land referred to in paragraph 1 to the preventive and

with indicator values.



PART TWO



Amendment to Decree No. 13/1994 Coll., determining some details

protection of agricultural land resources



§ 3



Decree 13/1994 Coll. laying some of the details of the protection

agricultural land holdings, is amended as follows:



1. section 2 is repealed.



2. Annexes 1 and 2 shall be deleted.



PART THREE



FINAL PROVISION



§ 4



This Decree was notified in accordance with the directive of the European Parliament

and of the Council (EU) 2015/1535/EU of 9. September 2015, the procedure for the provision

information in the field of technical regulations and of rules on services,

information companies, as amended.



PART FOUR



The EFFECTIVENESS of the



§ 5



This Decree shall enter into force on 1 January 2000. June 2016.



Minister:



Mgr. Vratislav Brabenec in r.



Č. 1



Preventive values

Table No. 1



The preventive value of the contents of the risk elements identified in agricultural land

extraction by Agua Royal (mg.kg-1)



I---------------I------------------------------------------------------------I

Even the category of soil and preventive value1)

I I----I-----I-----I----I----I----I------I----I----I-----I-----I

And Even As I Be Even Cd And What I And Cu And The Hg2) And Ni And Pb And Zn In And I

I---------------I----I-----I-----I----I----I----I------I----I----I-----I-----I

And the regular půdy3) and 20 (I) 2.0 0.5 30 and 90 and 60 and 0.3 up to 50 even 60 and 130 and 120 and

I---------------I----I-----I-----I----I----I----I------I----I----I-----I-----I

Light půdy4) and 15 as well as 1.5 and 0.4 to 20 and 55 and 45 and 45 and 55 0.3 and even 120 and 105 and

I---------------I----I-----I-----I----I----I----I------I----I----I-----I-----I



Explanatory notes to table:



1) values do not apply to soils anomalous, at geogenně to be used

the sediments under the legislation on the use of sediment on agricultural land.



2) total content.



3) normal soil: Sandy-loamy, Loamy, jílovitohlinité and clay soil

that occupy the bulk of agricultural used soils. This is a land

with the normal variability of the elements, with a normal soil development in the various

geomorphological conditions, including soils on carbonate rocks.



4) Light soil: soil resulting from very light and poor matečních rocks

such as sand. In the definition of these soils is based on the

representation of fine particles (up to 0.01 mm) that make up a maximum of 20%. These

the soil is characterized by a very low absorption capacity.



Table No. 2



The preventive value of the contents of hazardous substances in agricultural soil (mg.kg-1)



I---------------------------------I------------------------------------------I

(I) the substance and preventive value even

I---------------------------------I------------------------------------------I

And polycyclic aromatic hydrocarbons and

I---------------------------------I------------------------------------------I

(I) the SUM of (I) onto an angled Cliff) and 1.0

I---------------------------------I------------------------------------------I

And chlorinated hydrocarbons and

I---------------------------------I------------------------------------------I

(I) the SUM of PCB2) and 0.02 and

I---------------------------------I------------------------------------------I

(I) the SUM of DDT3) and even 0.075

I---------------------------------I------------------------------------------I

I HCB4) and 0.02 and

I---------------------------------I------------------------------------------I

And HCH (sum of alpha + beta + gamma) 4) and 0.01 and

I---------------------------------I------------------------------------------I

And PCDD/F4) and 5.05)

I---------------------------------I------------------------------------------I

Even non-polar hydrocarbons and

I---------------------------------I------------------------------------------I

Even Hydrocarbons C 10-C 404) and 100 (I)

I---------------------------------I------------------------------------------I



Explanatory notes to table:



1) SUM-PAH polycyclic aromatic hydrocarbons (anthracene, benzo (a) anthracene,

benzo (b) fluoranthene, benzo (k) fluoranthene, benzo (a) pyrene, benzo (ghi) perylen,

fenantren, chrysen, fluoranthene, indeno (l, 2.3-cd) pyrene, naphthalene, pyrene)



2 SUM of PCB congeners)-28 + 52 + 101 + 118 + 138 + 153 + 180



3) SUM of DDT, DDE, DDD (of ' p ' and p-, p-isomers)



4) HCB, HCH (sum of alpha + beta + gamma), PCDD/F and hydrocarbons C 10-C 40

track when about suspicions of their occurrence (e.g., previous pollution

land of the production).



5) International toxic equivalent value of I-TEQ PCDD/F (ng.kg-1)



Č. 2



Indicator values

Table No. 1



Indicator values above which health may be at risk

safety of food or feed (mg.kg-1)



I----------------I---------------I---------------I---------------------------I

And Risk control as well as Soil type and pH value and Indicator and/CaCl2

I I I I---------------I-----------I

I I I I I I extraction extraction

I I I I I I by Agua NH4NO3

I I I I I I a King

I----------------I---------------I---------------I---------------I-----------I

Even As I-I-I I I 40.0 1.0

I----------------I---------------I---------------I---------------I-----------I

Even Cd and soil < Common1) = 6.5 and 1.5 I-I

I I I---------------I---------------I-----------I

I I I I I > 6.5 2.0 0.1 and

I I---------------I---------------I---------------I-----------I

Even Light půdy2 > 6.5 and) 2.0 and 0.04 and

I----------------I---------------I---------------I---------------I-----------I

And I-I = 6.5 and 150 < I-I

I I---------------I---------------I---------------I-----------I

I I-I I I 200 > 6.5-I

I I---------------I---------------I---------------I-----------I

I I - I - I - I 1,0 I

I----------------I---------------I---------------I---------------I-----------I

And the Pb I-I-I 300 and 1.5 I

I----------------I---------------I---------------I---------------I-----------I

And I-I) Hg3-and 1.5 I I

I----------------I---------------I---------------I---------------I-----------I



Explanatory notes to table:



1) normal soil: Sandy-loamy, Loamy, jílovitohlinité and clay soil

that occupy the bulk of agricultural used soils. This is a land

with the normal variability of the elements, with a normal soil development in the various

geomorphological conditions, including soils on carbonate rocks.



2) Light soil: soil resulting from very light and poor matečních rocks

such as sand. In the definition of these soils is based on the

representation of fine particles (up to 0.01 mm) that make up a maximum of 20%. These

the soil is characterized by a very low absorption capacity.



3) total content



For exceeding the indicator values for the content of the risk element in agricultural soil

It considers both of the determination being exceeded-if the indicator values for them

fixed, IE. and extraction by Agua) Royal, b) NH4NO3, and extraction

for the evaluation of chemical analyses should be performed first element content

by Agua Royal and exceeding the indicator values then NH4NO3.



Table No. 2



Indicator values above which may be suspected of endangering growth

plant and soil production function (mg.kg-1)



I----------------I-------------------I---------------------------------------I

And Risk control and pH value and Indicator and/CaCl2

I I I-------------------I-------------------I

I I I the extraction by Agua and extraction and


I I I the Royal and NH4NO3 and

I----------------I-------------------I-------------------I-------------------I

And Zn and-I and-I 400

I I-------------------I-------------------I-------------------I

I I - I - I 20 I

I----------------I-------------------I-------------------I-------------------I

Even her and even 150 < = 6.5 I-I

I I-------------------I-------------------I-------------------I

I I I I > 6.5 200-I

I I-------------------I-------------------I-------------------I

I I - I - I 1,0 I

I I-------------------I-------------------I-------------------I

I I < 5,0 I 150 I - I

I----------------I-------------------I-------------------I-------------------I

I Cu I 5,0 - 6,5 I 200 I - I

I I-------------------I-------------------I-------------------I

I I > 6,5 I 300 I - I

I I-------------------I-------------------I-------------------I

I I - I - I 1,0 I

I----------------I-------------------I-------------------I-------------------I



Table 3



Indicator of the value of the risk elements, above which might be at risk

human and animal health (mg kg-1 dry weight)



I-------------------------I--------------------------------------------------I

And Risk control and the indicating value (extraction by Agua Royal)

I-------------------------I--------------------------------------------------I

I As I 40 I

I-------------------------I--------------------------------------------------I

I Cd I 20 I

I-------------------------I--------------------------------------------------I

I Pb I 400 I

I-------------------------I--------------------------------------------------I

I Hg1) I 20 I

I-------------------------I--------------------------------------------------I



Explanatory notes to table:



1) total content



Table 4



Indicator values for hazardous substances, above which might be at risk

human and animal health (mg kg-1 dry weight)



I-------------------------------I--------------------------------------------I

I Risk substance and value of the Indicator and the

I-------------------------------I--------------------------------------------I

(I) Benzo (a) pyrene and 0.5 and

I-------------------------------I--------------------------------------------I

(I) the SUM of (I) onto an angled Cliff) and 30.0

I-------------------------------I--------------------------------------------I

(I) the SUM of PCB2) and 1.5 I

I-------------------------------I--------------------------------------------I

(I) the SUM of DDT3) and 8.0 and

I-------------------------------I--------------------------------------------I

I HCB I 1 I

I-------------------------------I--------------------------------------------I

And HCH (sum of alpha + beta + gamma) and 1 (I)

I-------------------------------I--------------------------------------------I

And PCDD/F4) and 100.05)

I-------------------------------I--------------------------------------------I



Explanatory notes to table:



1) SUM-PAH polycyclic aromatic hydrocarbons (anthracene, benzo (a) anthracene,

benzo (b) fluoranthene, benzo (k) fluoranthene, benzo (a) pyrene, benzo (ghi) perylen,

fenantren, chrysen, fluoranthene, indeno (l, 2.3-cd) pyrene, naphthalene, pyrene)



2 SUM of PCB congeners)-28 + 52 + 101 + 118 + 138 + 153 + 180



3) SUM of DDT, DDE, DDD (of ' p ' and p-, p-isomers)



4) International toxic equivalent (I-TEQ PCDD/F)



5) (ng.kg-1)



Č. 3



Procedures and analyses identify risk elements and hazardous substances

I----------------------------------------------------I-----------------------I

I subject matter, purpose, the Czech standard pointer

I----------------------------------------------------I-----------------------I

And soil quality-pretreatment of samples by freeze-drying for ČSN EN ISO 16720 and

And subsequent analysis, (11/07) I I

I----------------------------------------------------I-----------------------I

And the quality of the soil-treatment of samples for both ISO and 11464

And physico-chemical analyses, (7/11) I I

I----------------------------------------------------I-----------------------I

And MUDs, the modified soil-compost bin and instructions for adjustment and ČSN EN 16179 I

And samples (3/13) I I

I----------------------------------------------------I-----------------------I

(I) characterization of waste-Leaching-Validation and ČSN EN 12457-2 I

The test for leaching ability of granular wastes and sludge-I I

I, part 2: single-stage batch test at a ratio of I I

Both liquid and solid phases of 10 l/kg for materials with even

And the grain size of less than 4 mm (without reducing the size I I

Particulate matter, or even with it), (8/03) I I

I----------------------------------------------------I-----------------------I

Soil quality-determination of pH, (8/2011) and ČSN ISO 10390 I

I----------------------------------------------------I-----------------------I

And sludge, biowaste and soil-adjusted Determination and ČSN EN 16167 I

And polychlorinated biphenyls (PCBs) by gas I I

Chromatography with detection by mass spectrometry and also

I (GC-MS) and gas chromatography detector I I

And electron-capture detection (GC-ECD), (3/13) I I

I----------------------------------------------------I-----------------------I

And sludge, biowaste and soil-adjusted determination of pH and ČSN EN 15933 I

I (4/13) I I

I----------------------------------------------------I-----------------------I

And MUDs, the modified soil-compost bin and the decomposition of the factions as well as to ČSN EN 16174 I

Even elements of the soluble dissolved the Royal, (2/13) I I

I----------------------------------------------------I-----------------------I

And MUDs, the modified soil-compost bin and the determination of dioxins and ČSN P 16190 and CEN/TS

I and furans and PCBs similar I I

And dioxins by gas chromatography with mass I I

And high resolution mass spectrometry (GC-MS), I I

I (9/12) I I

I----------------------------------------------------I-----------------------I

And sludge, biowaste and soil-adjusted determination of elements and ČSN P 16188 and CEN/TS

Even in fertilizer extracts by Agua Royal and acid I I

And nitric-method of flame atomic absorption and even

And spectrometric (FAAS), (9/12) I I

I----------------------------------------------------I-----------------------I

(I) characterization of waste-determination of the content and ČSN EN 14039 I

Even hydrocarbons C10 to C40 by gas chromatography (I)

I----------------------------------------------------I-----------------------I



I----------------------------------------------------I-----------------------I

I subject matter, purpose,, pointer and other standards and procedures as well as

I----------------------------------------------------I-----------------------I

(I) analysis of the soil-ÚKZÚZ1)-NRL2) and JPP3)

I----------------------------------------------------I-----------------------I

And Soil quality-Determination of mercury in aqua and ISO 16772:2004 and

And soil extracts with regia cold-vapour atomic I I

And spectrometry or atomic fluorescence cold-vapour I I

And spectrometers (I)

I----------------------------------------------------I-----------------------I



Explanatory notes to table:



1) CISTA-Central control and testing Institute of agriculture



2) NRL-national reference laboratory



3) workflow-analysis of soils, CISTA Brno (30350.1 procedures;

30400.1; 30410.1; 30450.1; 30460.1; 30500.1; 30600.1; 30620.1; 30630.1;

30660.1; 30670.1; 30680.1; 30690.1; 30720.1).



Č. 4



Sampling procedure



1. The sampling plan



Before sampling plan must be drawn up for the sampling, which

contains



1) the purpose of sampling,



2) sampling scheme,



and the basic sampling scheme (a) number and the distribution of samples of pet

territory) and



(b)) 2. the sampling scheme on sampling site (number and the distribution

the individual samples for a pooled sample),



3) type sampler and the sampling technique,



4) subscription and the reasons the proposed depth depth subscription



5) the weight of a collective specimen,



6) the number of individual subscriptions (5-30 strokes according to the used equipment-

sondýrky) on a pooled sample (5-30 punctures from used equipment

-sondýrky)



7) time, where appropriate, sampling period,



8) adjustment (kvartování collective specimen) and packaging samples (Department

the control sample),



9) description, transport and storage of samples,



10) required analyses,



11) documentation (record of the Protocol), and



12) description during the sampling.



2. determination of the number of samples



Samples shall be taken as the broken, mixed samples. Minimum numbers

pooled samples taken in the area are set out in table 1. The actual number of

sampling procedure is set so as to ensure the representativeness of the results with the

view of the expected level of risk, the level and variability of contamination


and how to evaluate the results.

Table No. 1



Determination of the minimum number of subscribed pooled samples, depending on the

the size of the area under investigation



I-------------------------------------I--------------------------------------I

The size of the investigated area (ha) as well as the number of mixed vzorků1)

I-------------------------------------I--------------------------------------I

I 30.0000 and individual sampling plan and

I-------------------------------------I--------------------------------------I



Explanatory notes to table:



1) including collection of one or more reference samples taken outside the area

the collection of the pooled sample, if necessary to determine the originator of the

pollution or capture the State of the background.



3. the number of subscriptions, subscription and device information required for compound samples



One pooled sample shall consist of at least 5 subscriptions. As the sampler

device may be used probing rods, soil drill or blades.

When sampling is affecting the whole evenly absorbed by soil horizon.

Used sampling equipment must not cause secondary contamination of the sample.



When removed, the sample must be accompanied by the following particulars



and the serial number of the sample) localization (cadastral area,

land-register reference number, the coordinates in the coordinate space of the sampler

system S-JTSK),



b) climate and soil characteristics of the consumption space expressed

bonitovanou soil-ecological unit,



(c) relief of the terrain)



(d) the State of the weather at the time) of sampling,



(e) the area under investigation in the area) hectares,



f) date of collection and the names of people involved in the collection,



g) date of transmission of the sample into the laboratory, the signatures of the transferring and

the accepting person,



h) map plot investigated area and reception sites on the substrate

land maps.



4. Depth of sampling composite sampling



Depth of sampling composite sampling depending on the type of land is

set out in table no. 2

Table No. 2



Depth of sampling of soil, depending on the type of pozemku1)



I-------------------------------------I--------------------------------------I

I kind of land and depth of sampling and

I-------------------------------------I--------------------------------------I

And arable land as well as the depth of topsoil, however, even the deepest

(I) to a depth of 30 cm and

I-------------------------------------I--------------------------------------I

And gardens, orchards and vineyards and 0-30 cm

I-------------------------------------I--------------------------------------I

And permanent grassland and 0-15 cm soil layer (drnová (I)

I I removed) and

I-------------------------------------I--------------------------------------I

I Planted and 0-40 cm (top deseticentimetrová (I)

And even layer of soil will be removed)

I-------------------------------------I--------------------------------------I



Explanatory notes to table:



1) when sampling the soil for the purpose of detecting pollution resulting from the fallout, or

application of surface pollutants caused by extraordinary events

the depth of the subscription shall be fixed so that the soil sample subscribed as faithfully as possible

Despite the condition, which is to be the analysis of the sample.



5. the weight of a collective specimen



One pooled sample must have a weight of at least 0.5 kg.



6. storage of pooled samples



If there are samples only to the risk elements,

they are stored in paper or PE bags. For the determination of hazardous substances

store in a clean glass jar with sealing cap. These samples

shall be transported and stored chilled at 4 ° c.



7. preparation of the pooled samples taken for analysis



After the removal of the skeleton, samples are dried in air, it is done

their grinding, homogenization and sieving, by 2 mm on the network. This procedure

does not apply to the determination of organic substances.