Federal Soil Protection and Altlastenverordnung (BBodSchV)Non-official table of contents
Date of issue: 12.07.1999
" Federal Soil Protection and Waste Ordinance of 12. July 1999 (BGBl. 1554), as last amended by Article 5 (31) of the Law of 24 February 2012 (BGBl. 212) "
|:||Last modified by Art. 5 para. 31 G v. 24.2.2012 I 212|
For details, see Notes
(+ + + Text evidence: 17.7.1999 + + +) Non-Official Table of Contents
On the basis of § § 6, 8 (1) and (2) and § 13 (1) sentence 2 of the Federal Soil Protection Act of 17. March 1998 (BGBl. 502), after consulting the interested parties, the Federal Government decrees: Non-official table of contents
| § 1||Scope|
|§ 2|| Definitions|
|Requirements for the Investigation and evaluation of suspected areas and areas suspected of old-load suspicion|
| § 4||Rating|
| Requirements for the refurbishment of harmful soil changes and legacy loads|
|§ 5|| Sanation measures, protection and restrictions measures |
| Supplementary provisions for legacy loads|
|§ 6||Sanation investigation and remediation planning|
| Fifth Part|
| Supplementary provisions for the security of harmful soil changes due to soil erosion by water|
|§ 8|| Hazardous Soil Degradation due to soil erosion by water|
| Presume against the emergence of harmful soil changes|
|§ 9||Worse pest Soil changes|
|§ 10||precautionary requirements|
|§ 11|| Allowed added load|
|§ 12||Requirements for the application and placement of materials on or in the Bottom|
| § 13||Accessibility of technical rules and standards sheets|
|§ 14|| Entry into force|
|Sample sampling requirements Analysis and quality assurance in the investigation|
|1.||Scope of investigation and required knowledge level|
| 1.1||Orientation Inquiry|
|1.2|| Detail Inquiry|
|2.1|| Sample sampling planning for soil investigations-determination of sampling points and testing depths |
|2.1.1|| Reaction path soil-person|
|2.1.2||Reaction path ground-crop path|
| 2.1.3||Reaction path ground-ground water|
|2.2||sampling planning Ground air|
|2.3||Sample planning when the floor material is removed and out|
| 2.4||Sample recovery|
|2.4.1||Soils, soil materials and other Materials|
|2.5|| Sample Conserve, Transport and Storage|
| 3.1||Investigation process for floors, soil materials and other materials|
|3.1.1|| Sample selection and pre-treatment|
| 3.1.3||Analytical method|
|3.2||Ground air investigation|
| 3.3||Method of estimating the fabric entry from suspected or old-load suspicious areas into the groundwater|
| 4.||Quality Assurance|
|4.1||Sample Accepting and Sample storage|
|4.2||Sample pretreatment and analytics|
|5.|| Abbreviation Directory|
|5.1||Units of Measure|
| 5.2||Instrumental analytics|
| 6.||Standards, Technical Rules, and other methods, sources of reference|
|6.1|| Standards, Technical Rules and Other Methods|
|6.2||Sources of Reference|
| Appendix 2|
|Actions, check and benefit values|
| 1.||Floor-to-person action path (direct contact)|
|1.1||delimitation the usages|
|1.3|| Application of policy values|
|2.|| Reaction path ground-to-use plant|
| 2.2||Test and policy values-arable crops and farm gardens with respect to plant quality |
| 2.3||Policy values-green spaces with regard to plant quality|
|2.4|| Test values-arable crops with respect to growth impairments in crop plants|
|2.5||Application of the test and test values Policy values|
|3.||Reaction path ground-ground water|
|3.1|| Test values for assessing the ground groundwater action path|
|3.2||Application of the Audit values|
|4.||Soil precautionary values|
|4.1|| precautionary values for metals|
|4.2||precautionary values for organic substances|
| 4.3||Application of precautionary values|
|5.||Permitted additional annual Shipments of pollutants across all action paths|
| Requirements for remediation investigations and the recovery plan|
| 2.||remediation plan|
| Requirements for the investigation and evaluation of areas where there is a suspicion of soil erosion due to water soil erosion|
|2.||Investigation and |
First partNon-official Table of Contents
§ 1 Scope
This regulation applies to
unofficial table of contents
- the investigation and Assessment of suspected areas, areas suspected of long-load conditions, harmful soil changes and contaminated sites, as well as for the requirements for sampling, analysis and quality assurance in accordance with § 8 (3) and § 9 of the Federal Soil Protection Act,
- Security requirements due to decontamination and security measures as well as other protection and restriction measures in accordance with Section 4 (2) to (5), Section 8 (1), second sentence, No. 3 of the Federal Soil Protection Act,
- Supplementary requirements for remediation investigations and remediation plans for certain Altlasts according to § 13 paragraph 1 of the Federal Soil Protection Act,
- Requirements for the prevention of the emergence of harmful soil changes in accordance with § 7 of the Federal Act on Soil Protection Federal Soil Protection Act, including the requirements for the installation and introduction of materials according to § 6 of the Federal Soil Protection Act,
- the determination of test and measures of measures as well as of precautionary values, including the permissible additional burden in accordance with § 8 (1) sentence 2 no. 1 and 2 and para. 2 no. 1 and 2 of the Federal Soil Protection Act.
§ 2 definitions
For the purposes of this regulation,
- soil material: material from soils within the meaning of § 2 (1) of the Federal Soil Protection Act and its source substrates, including motherland, which are related to construction measures or other changes in the surface of the earth, being removed or treated;
- Area of impact: area in which a property within the meaning of section 2 (3) bis (3) bis (3) bis (3) bis (3) bis (3) bis 6 of the Federal Soil Protection Act (Federal Soil Protection Act) are expected to have an impact on protective goods or in which the cause of damage caused by the emergence of harmful soil changes is caused by effects on the ground;
- Orientation investigation: Local investigations, in particular measurements, based on the results of the capture for the purpose of determining whether the suspicion of a harmful Land change or old load is dispelled or there is a sufficient suspicion within the meaning of § 9 (2) sentence 1 of the Federal Soil Protection Act;
- Detailed investigation: deepened further investigation into the final risk assessment, in particular the determination of quantity and spatial distribution of pollutants, their mobile or mobilisable units, their capacity to spread in soil, water and air, and the possibility of their being taken up by humans, animals and plants;
- Sicker Water Forecast: Estimate of a suspected area, an old-load-suspicious area, harmful soil change or contaminated land, or in a manageable future expected pollutant entries via leachate into groundwater, taking into account concentrations and cargo, and related to the transition range from unsaturated to the water-saturated zone;
- pollutants: substances and preparations which are based on their health hazards, their longevity or bioavailability in the soil, or because of other properties and their concentration is likely to damage the soil in its functions or cause other hazards;
- Conditions of exposure: local conditions and conditions; the use of land in an individual case, in which protective goods can be exposed to the effects of pollutants;
- Reaction path: route of a pollutant from the source of pollutants to the site of a potential impact on a protective material;
- Background content: pollutant content of a soil from the geogenic soil (natural) base content of a soil and ubiquitous fabric distribution as a result of diffuse entries in the soil;
- Erosion surface: surface area, from which: Soil material with surface discharge is rinsed off;
- Groundable soil layer: soil layer, which is derived from the plant roots as a function of the natural Site conditions can be penetrated.
Second Part Non-official table of contents
Requirements for the investigation and evaluation of suspected areas and areas suspected of old load
§ 3 Investigation
(1) There is evidence of the existence of an old load at an old location, in particular if land has been dealt with over a prolonged period of time or in a significant quantity of pollutants, and the operation, management or method of operation or disturbances of the intended operation are not insignificant entries of such land Substances in the soil suggest. In the case of deposits, these indications are given, in particular, where the nature of the holding or the date of closure suggests that waste has not been handled, stored or deposited in a proper manner.(2) Paragraph 1, first sentence, shall apply mutatily to harmful soil changes. In addition to paragraph 1, there are indications of the existence of a harmful soil change, in particular by means of general or concrete references to
- the entry of pollutants over a longer period of time and in a significant amount over the air or water or by applying considerable amounts of waste to waste or waste water on soils,
- a significant release of natural elevated levels of harmful substances in soils,
- increased pollutant contents in food or fodder plants at the site,
- the escape of water with Significant amounts of pollutants from soils or deposits,
- substantial soil deposits and deposits by water or wind.
To be included in this Also findings based on general studies or empirical values from comparative situations, in particular for the spread of pollutants.If there are indications as referred to in paragraph 1 or 2, the suspected area shall be subject to an orientation examination after the recording has been recorded.(4) Concrete indications that justify the reasonable suspicion of a harmful soil change or legacy load (Section 9 (2) sentence 1 of the Federal Soil Protection Act) are generally available if investigations result in exceeding of test values or if an assessment in accordance with Section 4 (3) is to be expected to exceed test values. If there is sufficient suspicion within the meaning of sentence 1 or on the basis of other findings, a detailed examination shall be carried out.(5) In the case of detailed investigations, it should also be established whether there are dangers arising from spatially limited enrichment of pollutants within a suspected area or suspected area of old load, and whether and how a delineation of non-polluting substances is Areas are offered. A detailed examination may be carried out if the hazards arising from harmful soil changes or contaminated sites, major disadvantages or significant nuisances, after the competent authority has been established by simple means can be removed or removed.(6) In so far as there is evidence of the spread of volatile pollutants from a suspected area or an area suspected to be of old-load in buildings, as a result of the local conditions or the results of ground-air investigations, a inspection of indoor air; the tasks and powers of other authorities shall remain unaffected.(7) In accordance with § 9 (2) sentence 1 of the Federal Soil Protection Act (Federal Soil Protection Act), recurrent investigations of the propagation of harmful substances and of the relevant circumstances shall also be considered.(8) The requirements for the investigation of soils, soil materials and other materials, as well as soil air, landfill gas and leachate, are also determined in accordance with Annex 1. Non-official table of contents
§ 4 Evaluation
(1) The results of the orienting studies are subject to compliance with this Regulation To assess the circumstances of the individual case, in particular on the basis of test values.(2) The content or concentration of a pollutant below the relevant test value in Annex 2 shall be cleared in so far as the suspicion of a harmful soil change or contaminated load has been eliminated. If a test value in accordance with Annex 2, point 3, is exceeded at the site of the sampling, it shall be determined on a case-by-case basis whether the pollutant concentration in the leachate at the site of the assessment exceeds the test value. Measures within the meaning of Section 2 (7) or (8) of the Federal Soil Protection Act may already be necessary if, in individual cases, all unfavourable circumstances adopted in connection with the derivation of a test value in accordance with Annex 2 meet and the salary or the concentration of a pollutant is slightly above the relevant test value in Annex 2.(3) A Sickerwater forecast shall be drawn up for the assessment of the risks to groundwater from suspected areas or areas suspected of having old-load suspicion. Where a Sickerwater forecast is based on studies in accordance with Annex 1, point 3.3, it shall in particular be estimated and assessed in particular cases to what extent it is to be expected that the concentration of pollutants in the seepage water shall be subject to the test value at the site of the assessment. exceeds. The site of the assessment is the area of transition from the unsaturated to the saturated zone.(4) The results of the detailed investigation shall be assessed in accordance with this Regulation in accordance with the circumstances of the individual case, in particular on the basis of measures of measures, in order to assess the extent to which measures pursuant to § 2 (7) or (8) of the Federal soil protection law is required.(5) Where no test or measure value is fixed for a pollutant in this Regulation, the methods and standards used to derive the corresponding values in Annex 2 shall be taken into account for the evaluation. These are published in the Federal Gazette No. 161a of the 28th Published in August 1999.(6) If a more sensitive use differs from the predominant use within a suspected area or an old-load suspicious area, these sub-areas shall be determined according to the scales laid down for their use. assess.(7) In individual cases, findings from groundwater investigations shall be taken into account in the assessment with regard to pollutant entries in groundwater. If increased concentrations of pollutants in leachate or other polluting substances can only be expected to have low pollutant concentrations and only locally limited concentrations of pollutants in water, this is the case when it comes to the test to take account of the proportionality of investigative and remedial measures. Water legislation remains unaffected.(8) A harmful soil change does not exist in soils with naturally elevated levels of pollutants solely on the basis of these contents, in so far as these substances have not been released to a significant extent by effects on the soil; or . A comparison of these contents with the pollutant contents determined in individual cases can be included in the hazard assessment in the case of soils with increased pollutant contents.
Third Partunofficial table of contents
Requirements for remediation of harmful soil changes and legacy loads
§ 5 Remediation measures, protection and restriction measures
(1) Decontamination measures are suitable for refurbishment if they are based on technically and economically feasible methods which are suitable for the environment-friendly environment. To ensure the elimination or reduction of the pollutants. Account must also be taken of the consequences of the intervention, in particular for soils and waters. Once a decontamination measure has been completed, it is necessary to confirm that the restoration target has been reached with the competent authority.(2) If pollutants are to be eliminated in accordance with Section 4 (5) of the Federal Soil Protection Act and there is a preload, the person who is subject to the charge shall, in principle, demand the services which he would have to provide without any preloading. The previously existing uses of the land should be restored.(3) Safety measures shall be appropriate for remediation if they ensure that the remaining pollutants in the soil or contaminated sites do not permanently pose any risks, significant disadvantages or significant nuisances to the individual or to the Generality arise. In this case, the danger potential of the pollutants remaining in the soil and their transformation products must be taken into account. A subsequent restoration of the securing effect in the sense of the sentence 1 must be possible. The effectiveness of security measures must be documented and permanently monitored in relation to the competent authority.(4) As a precautionary measure, a suitable covering of harmful modified soils or contaminated sites with a soil layer or a sealing is also possible.(5) Areas used for agricultural and forestry purposes are subject to protection and restriction measures, in particular by adapting the use and management of soils, and changes in the land used in the case of harmful soil changes or contaminated sites. Soil quality is possible. Records shall be kept of the protection and restriction measures taken. Agreement shall be reached with the competent agricultural authority. § 17 (3) of the Federal Soil Protection Act remains unaffected.(6) If the material is to be expelled, ejected or treated in the course of the restoration in the area of the same harmful soil change or contaminated land or within the area of a recaptised plan of remediation, reinstated or introduced or migrated, the requirements of § 4 (3) of the Federal Soil Protection Act are to be fulfilled.
Fourth part Non-official table of contents
Supplementary provisions for legacy loads
§ 6 Sanation investigation and refurbishment planning
(1) In the case of remediation investigations, it is also necessary to examine in particular what measures can be taken in order to ensure that changes in the soil remain after the refurbishment and what legal, organisational and financial conditions are required for the renovation of the soil in accordance with Section 4 (3) of the German Federal Soil Protection Act (BfN) the implementation of the measures is important.(2) In the preparation of a restructuring plan, the measures pursuant to Section 13 (1) sentence 1 No. 3 of the Federal Soil Protection Act are to be presented in full text and drawings. The recovery plan shall state that the measures envisaged are likely to avoid any permanent risks, significant disadvantages or significant nuisance to the general public or to the general public. In particular, the impact of the measures on the environment and the estimated costs as well as the necessary authorisations are also to be presented, even if a binding restructuring plan according to § 13 (6) of the German Federal Soil Protection Act (Federal Soil Protection Act) is to be presented. cannot be included.(3) The requirements for a refurbishment investigation and a refurbishment plan are, moreover, determined in accordance with Annex 3.
Fifth Part unofficial table of contents
§ 7 exceptions
harmful soil changes and contaminated sites where, after the competent authority has been identified, hazards, significant disadvantages or significant § 6 does not apply.
Part SixNon-tampering table of contents
Supplementary provisions for the security of harmful soil changes due to soil erosion by water
§ 8 Security of harmful soil changes on the ground Soil Erosion by Water
(1) The presence of a harmful soil change due to soil erosion by water must be considered in particular when
- considerable amounts of soil material have been swamped from an erosion surface by surface discharge and
- additional soil yields as set out in point 1.
(2) Indications of the presence of a deleterious soil change due to soil erosion In particular, water can be obtained if the areas situated outside the supposed erosion surface have been frayed by abraded soil material.(3) If there is evidence as referred to in paragraph 2, it is necessary to determine whether there is a harmful soil change due to soil erosion by water. Where it is possible to determine which erosion surface may be attributed to soil precoat and that considerable quantities of soil material have been washed off, it shall be examined whether the conditions laid down in paragraph 1 (2) have been met.(4) The evaluation of the results of the investigations is carried out on a case-by-case basis, taking into account the specificities of the site. Additional land yields can be expected if
- already has significant multiple times in the past years. Quantities of soil material from the same erosion surface have been swamped or
- from the location data and the data on the long-term rainfall conditions of the It follows that, over a period of ten years, there is a sufficient likelihood of the re-entry of land in accordance with paragraph 1 (1).
(5) The further requirements for the investigation and evaluation of Areas where there is a suspicion of harmful soil erosion due to soil erosion by water, are set out in Annex 4.(6) If the erosion surface is used for agricultural purposes, the competent advisory body shall be given the opportunity, in accordance with Section 17 of the Federal Soil Protection Act, to take appropriate erosion-reducing measures for the use of the erosion surface in the context of the consultation to be recommended. In the case of orders, it is necessary to reach agreement with the responsible agricultural authority.
Seventh part Unofficial Table of Contents
Preventable against the emergence of harmful soil changes
§ 9 Discharge of Harmful Soil Changes
(1) The Emergence of Harmful Soil Changes according to § 7 of the Federal Soil Protection Act is usually to be obtained if
- Pollutant contents measured in the soil , which exceed the precautionary values referred to in Annex 2, point 4, or
- a significant enrichment of other pollutants, which is due to their Carcinogenic, mutagenic, toxic to reproduction or toxic properties are particularly suitable for causing harmful soil changes.
§ 17 (1) of the Federal Soil Protection Act remains unaffected.(2) In the case of soils with naturally increased levels of pollution, there is concern at the emergence of harmful soil changes if the precautionary values are exceeded in accordance with Annex 2, point 4, only if a significant release of pollutants or pollutants is found to be harmful to the soil. Additional entries can be expected from the adverse effects on the soil functions provided by § 7 sentence 1 of the Federal Soil Protection Act (Federal Soil Protection Act).(3) Paragraph 2 applies correspondingly in the case of soils with increased pollutant contents due to the large area of settlement. Non-official table of contents
§ 10 precautionary requirements
(1) If the requirements of § 9 (1), first sentence, no. 1, para. 2 or 3 are fulfilled, the following conditions are fulfilled. 7 of the Federal Soil Protection Act (Federal Soil Protection Act) to take precautions to prevent or effectively reduce further pollutant entries caused by it on the property and its area of impact, insofar as this is also done with regard to the The purpose of the use of the land is proportionate. This also includes technical arrangements for installations or procedures and measures for the investigation and monitoring of soils. Annex 1 shall apply mutatily to the investigation.(2) Entries of harmful substances within the meaning of § 9 (1) sentence 1 (2), for which no precautionary values are fixed, shall, in accordance with paragraph 1, be limited as far as technically possible and economically justifiable. This applies in particular to substances classified as carcinogenic, mutagenic or toxic to reproduction in accordance with the Hazardous Substances Ordinance. Unofficial Table Of Contents
§ 11 Permitted Additional Load
(1) The precautionary values set out in Annex 2, point 4.1, in the case of a pollutant, shall be: , an additional burden shall be allowed to the extent of the annual cargo of the pollutant set out in Annex 2, point 5. The effects on the ground via air and water as well as direct entries must be taken into account.(2) Insofar as the permissible additional load on a pollutant specified in Annex 2, point 5 is exceeded, the geogenic or large-scale settlement-related pre-loads must be taken into account in individual cases.(3) The rates laid down in Annex 2, point 5, do not determine, within the meaning of Section 3 (3) sentence 2 of the Federal Soil Protection Act, which additional charges by the operation of a plant are not considered to be a causal contribution to the development of harmful substances. Changes in the soil are to be considered. Non-official table of contents
§ 12 Requirements for the application and placement of materials on or off the ground
(1) For the manufacture of a Soil layer can be obtained in and on soils only soil material as well as dredgergut according to DIN 19731 (edition 5/98) and mixtures of soil material with such wastes, which meet the material quality requirements of the Circulatory economic law and § 8 of the bis zum 1. Regulations and the Sewage Sludge Ordinance, which are in force in June 2012, are to be fulfilled, brought up and brought into force.(2) Materials on or in an entrentable soil layer or for the production of an entrentable soil layer in the context of recultivation projects, including re-use, shall be permitted if
- in particular according to the type, quantity, pollutant contents and physical properties of the materials, as well as According to the pollutant contents of the soils at the place of entry or introduction, the concern of the emergence of harmful soil changes in accordance with § 7 sentence 2 of the Federal Soil Protection Act and § 9 of this Regulation is not evoked and
- At least one of the ground functions mentioned in § 2 (2) (1) and (3) (b) and (c) of the Federal Soil Protection Act is sustainably secured or restored.
The Intermediate storage and the transfer of land material on land in the context of the construction or conversion of construction and plant installations are not subject to the regulations of this paragraph, if the soil material at the place of origin is reused.(3) In accordance with § 7 of the Federal Soil Protection Act (BundesBodenschutzgesetz), the persons who are subject to the obligation to apply and introduce the materials must carry out or arrange for the necessary examinations of the materials in accordance with the specifications in Annex 1. The competent authority in accordance with § 10 (1) of the German Federal soil protection law may order further investigations concerning the location and soil properties if the emergence of a harmful soil change is to be obtained; in this case the Requirements in accordance with DIN 19731 (issue 5/98).(4) With regard to future unavoidable pollutant entries by means of management measures or atmospheric pollutant entries, the pollutant contents in the resulting solid soil layer 70 shall be used for the use of agricultural use. Percentage of the precautionary values referred to in Annex 2 (4) shall not exceed(5) In the application of soil material to agricultural soils, including garden-building, their profitability is to be sustainably secured or restored and must not be permanently reduced.(6) In the production of a suitable soil layer for agricultural use in the context of recultivation projects, including re-use, soil material suitable for the type, quantity and pollutant content shall be:-or be introduced.(7) The supply of nutrients by the introduction and introduction of materials in and on the soil is to be adapted according to quantity and availability to the plant requirements of the subsequent vegetation, in order to avoid, in particular, nutrient entries in water bodies to the greatest extent possible. DIN 18919 (issue 09/90) must be observed.(8) Soils, which fulfil the soil functions according to § 2 para. 2 no. 1 and 2 of the Federal Soil Protection Act to a particular extent, shall be excluded from the application and introduction of materials. This also applies to soil in the forest, in water protection areas in accordance with § 51 paragraph 1 of the Water Resources Act, in nature reserves, national parks, national natural monuments, biosphere reserves, natural monuments, protected landscape elements, Natura 2000 sites and biotopes protected by law within the meaning of § 30 of the Federal Nature Protection Act as well as for the soils of the core zones of large-scale nature conservation projects of the federal state of national importance. The competent authorities may allow deviations from this if they are necessary for the protection of the groundwater or the protection of the groundwater, if they are to be put on and put into place.(9) In the establishment and introduction of materials on or into the soil compaction, wetting and other adverse changes in soil shall be carried out by appropriate technical measures and by taking account of the quantity and time of the This is to be avoided. After the application of materials with a thickness of more than 20 centimetres, the securing or the construction of a stable floor structure must be added. DIN 19731 (issue 5/98) is to be observed.(10) In areas with increased levels of pollution in soils, a displacement of soil material within the area is permissible if the soil functions mentioned in § 2 para. 2 No. 1 and 3 (b) and (c) of the Federal Soil Protection Act do not additionally and, in particular, the pollutant situation at the location of the application is not adversely affected. The areas of increased pollutant content may be determined by the competent authority. In doing so, the competent authority may also allow derogations from paragraphs 3 and 4.(11) § 5 (6) remains unaffected.(12) Paragraph 3 does not apply to the establishment and dumping of soil material on the agricultural land after locally limited erosion events or for the recycling of soil material from the purification of agricultural harvesting products. name="BJNR155400999BJNG000800305 " />
Achter PartNon-official table of contents
§ 13 Accessibility of technical rules and
(1) Technical rules and standards referred to in this Regulation are stored in the German Patent Office in an archive-protected way. The sources of supply are listed in Annex 1, point 6.2.(2) references to draft technical standards in the Annexes shall relate in each case to the text published at the date stated in the referral. Non-official table of contents
§ 14 Entry into force
This Regulation will enter into force on the day after the announcement. Non-official table of contents
The Federal Council has agreed. unofficial table of contents
(Fundstelle: BGBl. I 1999, 1561-1574)
- Requirements for sampling, analytics, and quality assurance at the
This appendix applies to the investigation of soils, soil materials and other materials in the soil or on the soils of suspected or old-load suspects. In
case of old-load suspected old deposits, the scope of the investigation and the sampling, in particular with regard to the investigations on landfill gas, are to be determined. Volatile pollutants, deposited waste and the transfer of pollutants into groundwater, according to the requirements of the individual case.
For the purposes of this Annex, the state of development of methods and methods of development advanced methods and methods which make it possible to ensure their practical suitability for the above-mentioned studies. Findings on such methods and methods and on their application will be compiled by a selected group of experts from the federal and state governments as well as those affected in consultation with the Länder, the Federal Ministry for the Environment, conservation and reactor safety.
- Scope of investigation and required State of knowledge
The investigations in accordance with § 3 of this Regulation relate to the paths of action for which, on the basis of the information available on a case-by-case basis, there is a suspicion of danger. When determining the scope of the investigation, the results of the collection, in particular the knowledge or reasonable suspicions about the occurrence of certain pollutants and their distribution, the current use and the use according to § 4 para. 4 of the Federal Soil Protection Act and the resulting protection needs as well as the other local circumstances which are subject to appraisal of the assessment. The E DIN ISO 10381-3: 02.96 is to be observed. For occupational health and safety, reference is made to the ZH 1/183: 04.97.
In the investigation into the ground-human action path, use
and in the investigation into Real-life path ground-Utility plant the uses
- Children's playgrounds
- residential areas
- Park and leisure facilities
- industrial and commercial plots
to be distinguished.
- Farmhouse, utility garden
For investigations into the soil-groundwater path of action, do not differ according to the type of land use.
Orientation studies of suspected sites and old-load suspects should also be based on the findings and the Assessment of the scope of partial areas with different levels of pollutant contents.
In the case of old-load suspected old deposits, investigations of landfill gas and volatile pollutants as well as of volatile pollutants are generally considered. to carry out investigations, in particular with regard to the transfer of pollutants into groundwater.
In the case of suspected areas or areas suspected of being contaminated with old load, investigations of the reason or of the ground at the request of the competent authority shall be carried out. Surface water must be taken into account when determining the extent and the flow of the orienting examination for soil or seepage water studies.
In the case of suspicions, it cannot rely on existing soil maps. , or if there is no suitable soil-related information, an indicative mapping or ground address at the site of the sampling on the basis of the ground information shall be carried out within the framework of the indicative investigation. Cartieranleitung, 4. The
requirements for soils and soil materials shall apply mutagenically to § § 9, 10 and 12.
- detail investigation
the detailed investigation, the actions referred to in § 3 (5) and (6) of this Regulation should also be the same as those for the action paths clarify the relevant exposure conditions, in particular the mobile or mobilizable components of the pollutant content that are important for the different pathways. It is also intended to determine whether risks arise from spatially limited enrichment of pollutants within a suspected area or an area suspected of old-load suspicion, and whether and how a delineation of non-polluted areas is required.
The sampling procedure depends in particular on the individual case the area size, the expected vertical and horizontal distribution of pollutants due to the results of the detection, as well as the current, the permissible and the earlier use. The requirements referred to in points 2.1 to 2.3 shall be taken into account. The procedure for sampling shall be justified and documented. The requirements of occupational health and safety are to be observed.
Investigation areas are to be divided into suitable faces for sampling. The division shall be based on a different hazard suspicion, different land use, terrain or soil characteristics as well as abnormalities, such as a different vegetation development, or on the basis of Insights from the capture are done.
- Sample sampling planning for soil investigations-definition of sampling points and Probation Depth
the spatial distribution of the pollutants is to be determined, the area or sub-area to be examined is to be sampled in principle with the aid of a raster. To the extent that a hypothesis on the spatial distribution of pollutants can be derived from prior knowledge, in the case of old-load suspected old sites, in particular according to the results of the detection, it shall be used in the determination of the sampling points and of the grid. For the determination of sampling points, results from an appropriate on-site analysis can also be used.
Contaminated pollutant accumulations are to be tested in a targeted manner. The test shall be carried out, in particular with regard to the number and spatial arrangement of the sampling points, in such a way that the suspicion of danger is clarified, a possible danger is assessed and a spatial delimitation of pollutant enrichment takes place.
the determination of the depth of sampling for the soil-human and soil-useful plants, the probation depths referred to in Table 1 shall be used for the study of inorganic and low-volatility organic pollutants.
| Table 1|
Usage-based testing depth for investigations
on the ground-human and soil-crop action paths
| Reaction path|| Usage|| Beprobing Depth|
| Floor-Man|| Children's play area, residential area|| 0-10 cm 1)|
10-35 cm 2)
| Park and leisure location|| 0-10 cm 1)|
| Industrial and commercial plots|| 0-10 cm 1)|
| Floor-to-use plant|| Ackerbau, Nutzgarten|| 0-30 cm 3)|
| Grünland|| 0-10 cm 4)|
- Contact area for oral and dermal pollutant intake, additionally 0-2 cm with relevance of the inhaled recording path.
- 0-35 cm: average thickness of applied soil strata; at the same time max. depth to children.
- machining horizon.
- main root area.
are as to be sampled in a horizontal way. The basis for the determination of the horizontal sequence is the ground-based caring instructions of the Geological Landesämter (AG Bodenkunde, 4. Edition, 1994). Soils that have been destroyed in the subsoil are to be sampled in layers (see Table 1). The plies or horizons, which can be represented by taking a sample, is usually 30 cm. More powerful horizons or layers are to be divided if necessary. In addition to Table 1, the depth of sampling must be taken into account, for which special precautions must be taken in the use to be taken into account in accordance with Section 4 (4) of the Federal Soil Protection Act. The reasons for different sampling depths are to be documented.
When taking the sample, the following should be noted with respect to the mode of action:
- Reaction Path Floor- Human
the framework of the determination of the sampling points and the sampling depth, investigations into the conditions of exposure present in the individual case shall also be carried out, in particular about
- the actual use of the area (type, frequency, duration),
- the accessibility of the surface,
- the sealing of the surface and over the growth,
- the possibility of inhalation of soil particles,
- the relevance of further Action paths.
To assess the hazards of inhalation of soil particles, the topmost two centimetres of the soil are decisive. Such pollutants, for which the inhalative path according to the diversion standards in accordance with Article 4 (5) of this Regulation has proven to be decisive for the determination of the test value, are significant in terms of inhalation. By rehearsals, it must be ensured that the pollutant content in the fine grain fraction of up to 63 mym relevant for the formation of dust can be analyzed separately, if necessary.
Pollutants in the assessment-relevant soil layer are distributed approximately uniformly over a surface area, can be taken from areas up to 10,000 square meters for 1,000 square meters each, but at least 3 partial faces, a mixed sample. The mixing sample is to be obtained from 15 to 25 individual samples of a test depth. In the case of areas under 500 square metres, as well as in house gardens or other gardens of corresponding use, a division can be dispensed with. For surfaces over 10,000 square meters, at least 10 faces are to be tested.
- Reaction Path Floor-
agriculturally gartenstructurally used soils with approximately uniform soil characteristics and pollutant distribution on areas of up to 10 hectares as a rule for 1 hectare each, but at least 3 partial areas a mixed sample according to the testing depths from the table. In the case of areas of less than 5,000 square metres, a division can be dispensed with. For areas larger than 10 hectares, however, at least 10 faces shall be tested. Sampling is carried out according to the rules of sampling on agricultural soils (E DIN ISO 10381-1: 02.96, E DIN ISO 10381-4: 02.96) by 15 to 25 single stitches per face, which are combined to form a mixed sample in each case.
In The use of the sample is usually carried out by taking a mixed sample for each sample depth and in accordance with the rules of sampling on arable land.
For the suitability of equipment for sampling, the sample is usually taken from the sample. E DIN ISO 10381-2: 02.96 authoritative.
- Reaction path ground-
bottom-ground water path is the Determination of the vertical pollutant distribution to test the unsaturated soil zone up to below a presumed pollutant enrichment or a conspicuous soil body. The test is carried out in a horizontal or layer-specific manner. Samples from deep intervals up to a maximum of 1 m may be taken in the subsoil. In well-founded cases, the summary is of a grainy soil horizons or -layers up to a maximum of 1 m depth interval allowed. Conspicuity shall be assessed and, where appropriate, tested separately. The depth of sampling should be reduced if it becomes apparent that in the case of a through-bore of water-damp layers in the subsoil, a contamination of the ground water resulting from this is to be obtained. If the drilling of water-damp layers is necessary, special precautionary measures must be taken. For the suitability of devices for sampling, DIN 4021: 10.90 is authoritative.
- Sample sampling ground
sampling is done according to VDI guideline 3865, sheet 1 and 2.
- Sample collection planning for sheared and excavated soil
The sampling is based on DIN 52101: 03.88 or according to DIN EN 932-1: 11.96.
- Sample recovery
- Soils, soil materials, and other materials
necessary The sample quantity is determined according to DIN 18123: 11.96 according to the size grain and must be sufficient to ensure the laboratory examination and, if necessary, the provision of recovery samples after appropriate sample pretreatment. A coordination with the investigative body should be carried out.
coarse materials (materials > 2 mm) and foreign materials which may contain pollutants or which they can adhere to, can be taken from the entire sample quantity and shall be supplied separately to the laboratory examination. Their mass fraction of the tried-and-tested soil horizon, The coating unit must be identified and documented.
For the removal of soil, soil material and other materials, methods are to be used which are in DIN 4021: 10.90 and E DIN ISO 10381-2: 02.96. In the course of the selection process, the required sample quantity and the structure of the substrate must be taken into account in addition to the data contained in the standard.
- ground air
soil air sampling, VDI guideline 3865, sheet 2 applies.
- Sample Conserve, Transport
the selection of sample vessels as well as for sample conservation, transport and storage of samples, the relevant provisions in the examination regulations according to point 3.1.3, Tables 3 to 7, shall be complied with. If such regulations are missing, E DIN ISO 10381-1: 02.96 and DIN EN ISO 5667-3: 04.96 must be observed.
The transport of the soil samples for the investigation of organic pollutants and their storage is carried out according to E DIN ISO 14507: 02.96.
- Investigations for soils, soil materials and other Materials
- Sample selection and pre-
case of step-by-case studies, it is necessary to decide on a case-by-case basis in the sequence in the field shall be analysed, and, if necessary, A summary of several samples is also expedient. The decision and its reasons are to be documented.
The sample pre-treatment, including the drying of the sample material, is carried out for the determination of physico-chemical properties (point 3.1.3, Table 3) and the determination of the sample material. Inorganic pollutants (point 3.1.3, Table 4) according to DIN ISO 11464: 12.96. For organic pollutants, E DIN ISO 14507: 02.96 is to be applied.
If soil, soil material and other materials (in particular slag and construction rubble) require separation into coarse and fine particles, this has to be carried out via a sieve with a Mesh size of 2 mm into the fractions < = 2 mm (fine fraction) and > 2 mm (coarse fraction) grain diameter to be carried out. Clumps are to be crushed, but low-stable aggregates (e.g. carbonate, iron concretions, and Bims) should not be broken up. Both fractions shall be weighed, described and documented, and their dry matter content shall be determined. The fine fraction shall be homogenized and examined. If there is evidence of an increased pollutant content of the fraction > 2 mm, this fraction must be obtained and, after pre-comminution and homogenization, also to be examined. Foreign materials contained in the sample material must, if necessary, be examined separately and should be taken into account in the evaluation.
Representative parts of the samples taken in the field shall be retained as rehearsals. The nature and extent of the provision shall be agreed upon in accordance with the requirements of the individual case.
- Extraction, Elution
The determination of the content of Inorganic pollutants for the comparison of the pollutant absorption on the soil-human activity path with the values set out in Annex 2, point 1, with the exception of the cyanides, for the effective path of the soil-crop plant on arable land and in farm gardens with regard to Arsenic and mercury referred to in point 2.2 of Annex 2 and for the route of action of the soil-useful plant on grassland in accordance with point 2.3 of Annex 2, and with regard to the precautionary values referred to in Annex 2, point 4.1, shall be made from the Royal Water Extract according to DIN ISO 11466: 06.97 made from ground samples (grain size < 150 mym).
ammonium nitrate extraction
The ammonium nitrate extract according to DIN 19730: 06.97 is used to determine the contents of inorganic pollutants for the assessment of pollutants in the ground-of-action path. Crop plant and in farm gardens with respect to plant quality with regard to cadmium, lead and thallium as defined in point 2.2 of Annex 2, and to arable land with a view to reducing growth in crop plants referred to in Annex 2 Point 2.4 and may be used for the estimation of inorganic pollutant concentrations in leachate in accordance with point 3.3 of this Annex.
Extraction of organic pollutants
The determination of the content of organic pollutants in organic pollutants. Pollutants for the comparison of the pollutant intake on the soil-human activity path with the values set out in point 1.2 of Annex 2, and with regard to the precautionary values referred to in Annex 2, point 4.2, shall be taken from those indicated in point 3.1.3, Table 5. Soil extracts. If other methods are to be used, this should be justified and demonstrated that their results are equivalent to or comparable to the results of the above-mentioned procedures.
Elution with water
For the production of eluates with water for the estimation of concentrations of pollutants in the leachate in accordance with point 3.3 of this Annex, the procedures indicated in Table 2 shall apply.
| Table 2|
Method for the production of eluates with water
| Method|| Procedure Notes|| Method|
| inorganic substances|
| Soil saturation extract|| Method see (1)|
| Elution with water|
- Sample mass below Consideration of dry matter according to DIN 38414-2: 11.85 or according to DIN ISO 11465: 12.96
- filtration see (2)
| DIN 38414-4: 10.84|
| Organic fabrics|
| Pillow or Lysimeter Test|| The expected speed with which the equilibrium concentration is established is to be achieved. |
- Extraction of the Soil saturation extract: For preparation, the soil sample is slowly added in a polyethylene vessel so much bidistilled water that it is completely humidified. The required amount of water for pre-humidification is dependent on the soil and should correspond approximately to the field capacity. In the case of sandy rehearsals, the 25%, in the case of loam/slippage samples of approx. 35% and in the case of tonous samples of approx. 40% of the weight of the soil was dry. The amount of water added shall be determined gravimetrically and recorded. The sample is thoroughly mixed and is allowed to stand for 24 hours at 5 ° C. under evaporation protection. For the production of the soil saturation extract, the pre-moistened soil material is transferred into centrifuge cups. Bidistilled water is slowly added with continuous stirring until the yield point has been reached (formation of a glossy surface and disintegration of a spatula notch). In the case of clay samples, it is necessary to wait for 15 minutes until the swelling is complete and, if necessary, to give up water. The amount of water added is determined gravimetrically and the soil paste is stirred with a glass rod. The soil paste is to be stored in a refrigerator or room at 5 ° C under evaporation protection in order to adjust the equilibrium for 24 h. The soil/water ratio is calculated from the initial weight of air-dry soil and two-times water addition. In this case, the water content of the air-dry sample must be determined separately at an Aliquot (drying at 105 degrees C to constant weight) and taken into account by calculation. Refrigerated centrifuge for 30 min. The supernatant solution is decanted and membrane filtered by means of a negative pressure in order to separate suspended particles into previously weighed polyethylene bottles. The amount of filtrate shall be determined gravimetrically. The solutions are to be stabilized by adding 10% by volume of nitric acid (c= 5 mol/l), taking into account the addition of acid in the analysis of measurement results and the preparation of calibration solutions.
- filtration step: Use is made of a pressure filtration unit for membrane filters (142 mm diameter, media-carrying parts made of PTFE) with a membrane filter with 0.45 mym pore width. When using deviating devices, the volume to be filtered must be changed in accordance with the filter area; the ratio of the filtration volume and the filter area is to be maintained. After shaking, the suspension is approx. Allow to stand for 15 min to sedimentation of the coarser particles. The supernatant liquid is to be decanted to the greatest possible extent in the centrifuge cup. The centrifugation is carried out for 30 minutes with 2,000 g. Thereafter, the supernatant liquid is decanted to the greatest possible extent in the membrane pressure filtration apparatus. After 5 min of pressureless filtration, a pressure of 1 bar is applied for acceleration of the filtration. If after 15 minutes less than two thirds of the eluate passed through the filter, the pressure is increased to 2 bar. If necessary, the pressure is increased to 3.5 bar after a further 30 minutes. The filtration is continued until the entire supernatal of the centrifugation has passed through the filter. If the filtration is still incomplete after 120 minutes, it will be broken off and further worked on with the incomplete filtrate.
Soils, soil materials and other materials
The analysis of soils, soil material and, where appropriate, other materials, is based on the In
to identify the reasons other than those described in Tables 3 to 5, it must be demonstrated and documented that the results of these procedures are based on the results of the procedures set out in Tables 3 to 5. shall be equivalent to or comparable to those specified. The extent to which individual procedures can be applied, in particular, in particular under the points referred to in point 4.2, shall be considered in individual cases. The pollutant contents shall be based on dry matter (105 degrees C). They must be specified in the same unit as the corresponding test, measure, and precautionary values in Appendix 2.
| Table 3|
Analysis of physico-chemical properties
| investigative parameters|| Procedure Notes|| Method|
| Determination of dry matter|| field-fresh or air-dried soil samples|| DIN ISO 11465: 12.96|
| Organic carbon and total carbon after dry burning|| Air-dried soil samples|| DIN ISO 10694: 08.96|
| pH value (CaCl (deep) 2)|| Suspension of the field fresh or air-dried soil sample in CaCl (deep) 2-solution; c (CaCl (deep) 2): 0.01 mol/l|| DIN ISO 10390: 05.97|
| Grain Size Distribution|| |
- "Fingerprobe" in the terrain *)
|Ground map guide, 4. Edition, 1994; DIN 19682-2: 04.97|
- Siebung, Dispergierung, Pipette-Analyse *)
| E DIN ISO 11277: 06.94 DIN 19683-2: 04.97|
- Siebung, Dispergierung, Aräometer method
| DIN 18123: 11.96 E DIN ISO 11277: 06.94|
| Raw density|| Drying a volume-righteous soil sample at 105 degrees C, back-weighing|| E DIN ISO 11272: 01.94 DIN 19683-12: 04.73|
- Recommended method.
| Table 4|
Analysis of inorganic pollutant contents
| investigative parameters|| Procedure Notes|| Method|
|Cd, Cr, Cu, Ni, Pb, Tl, Zn|| AAS|| E DIN ISO 11047: 06.95|
|As, Cd, Cr, Cu, Ni, Pb, Tl, Zn|| ICP-AES (ICP-MS possible) Consideration of spectral interferences at high matrix concentrations required|| DIN EN ISO 11885: 04.98|
|Arsen (As)|| ET-AAS|| Analogy to E DIN ISO 11047: 06.95|
| hydride-AAS|| DIN EN ISO 11969: 11.96|
|Mercury (Hg)|| AAS cold steam technology During the sample pre-treatment, the drying temperature must not exceed 40 degrees C|| DIN EN 1483: 08.97 reduction with tin (II) chloride or NaBH4|
| Chrome (VI)|
- Extraction with phosphate-buffered aluminium sulphate solution
| spectrophotometrics DIN 19734: 01.99|
- Elution with water, separation of Cr (III), determination of soluble Cr (VI) in soils
| DIN 38405-24: 05.87|
| Cyanide|| E DIN ISO 11262: 06.94|
| Table 5|
Analysis of organic Pollutant contents
| investigative parameters|| Procedure Notices|| Method|
| Polycyclic aromatic hydrocarbons (PAH): 16 PAK (EPA) Benzo (a) pyren|| |
- Soxhlet extraction with toluene, chromatographic Clean-up; Quantification using GC-MS *)
|Merkblatt Nr. 1 des LUA-NRW, 1994 *)|
- Extraction with tetrahydrofuran or acetonitrile; quantification by HPLC-UV/DAD/F *)
|Merkblatt Nr. 1 des LUA-NRW, 1994 *)|
- Extraction with acetone, addition of petroleum ether, removal of the acetone, Chromatographic purification of the petroleum ether extract, intake in acetonitrile; quantification by HPLC-UV/DAD/F
| E DIN ISO 13877: 06.95|
- Extraction with a water/aceton/
petroleum ether mixture in the presence of NaCl; quantification by GC-MS or HPLC-UV/DAD/F
| VDLUFA-Method Book, Volume VII; Manual Altloads Bd. 7, LfU HE|
| Hexachlorobenzene|| Extraction with acetone/cyclohexane mixture or acetone/petroleum ether, if necessary Chromatographic purification after removal of the acetone; quantification by GC-ECD or GC-MS|| E DIN ISO 10382: 02.98|
| Pentachlorophenol|| Soxhlet extraction with heptane or acetone/heptane (50:50); derivatization with acetic anhydride; Quantification by GC-ECD or GC-MS|| E DIN ISO 14154: 10.97|
| Aldrin, DDT, HCH-mixture|| |
- Extraction with petroleum ether or acetone/petroleum ether mixture, chromatographic purification; quantification by GC-ECD or GC-MS *
| E DIN ISO 10382: 02.98 *)|
- Extraction with Water/Aceton/
Petrolether-Gemisch; Quantification by GC-ECD or GC-MS
| VDLUFA-Method Book, Volume VII|
| Polychlorinated biphenyls (PCB): 6 PCB congeners (no. 28, 52, 101, 138, 153, 180 according to Ballschmiter)|| |
- Extraction with heptane or acetone/petroleum ether, chromatographic purification; quantification by means of GC-ECD (GC-MS possible)
| E DIN ISO 10382: 02.98|
- Soxhlet extraction with heptane, hexane or pentane, chromatographic purification AgNO (deep) 3/silica gel; quantification by GC-ECD (GC-MS possible)
| DIN 38414-20: 01.96|
- Extraction with a Water/acetone/
Petrolether mixture in the presence of NaCl; quantification by means of GC-ECD (GC-MS possible)
| VDLUFA-Method Book, Volume VII|
| Polychlorinated dibenzodioxins and dibenzofurans|| Soxhlet extraction of freeze-dried samples with toluene, chromatographic purification; quantification by GC-MS|| according to the Sewage Sludge Ordinance Compliance with DIN 38414-24: 04.98, VDI guideline 3499, sheet 1: 03.90|
|*) recommended method.|
eluates and seepage water
The analytical determination of the inorganic substance concentrations in eluates and leachate is according to the The analytical methods listed in Table 6, the determination of the organic concentrations of substances in the seepage water shall be carried out in accordance with the methods set out in Table 7.
Should the reasons be mentioned other methods should be used: to demonstrate that their results are equivalent to or comparable to the results of the procedures indicated in Tables 6 and 7.
Determination of the concentration of inorganic pollutants in eluates and seepage water
Investigative parameter procedure shinweiseMethod
|As, Cd, Cr, Co, Cu, Mo, Ni, Pb, Sb, Se, Sn, Tl, Zn|| ICP-AES (ICP-MS possible)|| On the basis of DIN EN ISO 11885: 04.98 1 *)|
|Arsen (As), Antimon (Sb)|| hydrid-AAS|| DIN EN ISO 11969: 11.96|
|lead (Pb)|| AAS|| DIN 38406-6: 07.98|
|Cadmium (Cd)|| AAS|| DIN EN ISO 5961: 05.95|
| Chrome (Cr), total|| AAS|| DIN EN 1233: 08.96|
|Chrome (Cr VI)|| Spectrophotometrie ion chromatography|| DIN 38405-24: 05.87|
| DIN EN ISO 10304-3: 11.97|
| Cobalt (co)|| AAS|| DIN 38406-24: 03.93|
|Copper (Cu)|| AAS|| DIN 38406-7: 09.91|
|Nickel (Ni)|| AAS|| DIN 38406-11: 09.91|
|Mercury (Hg)|| AAS Cold Steam Technology|| DIN EN 1483: 08.97|
|Selenium (Se)|| AAS|| DIN 38405-23: 10.94|
|Zinc (Zn)|| AAS|| DIN 38406-8: 10.80|
| Cyanid (CN-), total|| spectrophotometrics|| DIN 38405-13: 02.81|
| E DIN EN ISO 14403: 05.98|
| Cyanid (CN-), easy to release|| spectrophotometrics|| DIN 38405-13: 02.81|
|Fluorid (F-)||Fluoridsensitive||DIN 38405-4: 07.85|
| Electrode Ion Chromatography||DIN EN ISO 10304-1: 04.95|
Determination of the concentration of organic pollutants in the soil sicker water
investigative parameter procedure shinweiseMethod
| benzene|| GC-FID|| DIN 38407-9: 05.91 2 *)|
| BTEX|| GC-FID adhere to matrix load|| DIN 38407-9: 05.91|
| Light Volatile Halogenohydrocarbons (LHKW)|| GC-ECD|| DIN EN ISO 10301: 08.97|
| Aldrin|| GC-ECD (GC-MS possible)|| DIN 38407-2: 02.93|
| DDT|| GC-ECD (GC-MS possible)|| DIN 38407-2: 02.93|
| Phenole|| GC-ECD|| ISO/DIS 8165-2: 01.97|
| Chlorphenole|| GC-ECD or GC-MS|| ISO/DIS 8165-2: 01.97|
| Chlorobenzole|| GC-ECD (GC-MS possible)|| DIN 38407-2: 02.93|
| PCB, total|| GC-ECD||DIN EN ISO 6468: 02.97|
|DIN 51527-1: 05.87|
| GC-ECD or GC-MS|| DIN 38407-3: 07.98|
| PAK, total|| HPLC-F|| DIN 38407-8: 10.95|
| naphthaline|| GC-FID or GC-MS|| DIN 38407-9: 05.91|
|Mineral oil hydrocarbons||extraction with petroleum ether, gas chromatographic quantification|| according to ISO/TR 11046: 06.94|
- By appropriate Measures or a suitable equipment must be adapted to the destination of the investigation.
- Adjustment of the limit of determination required.
- investigating ground air
The investigation of ground air is carried out according to VDI guideline 3865 sheets 2 and 3.
- Method to estimate the substance entry from suspected or old-load suspicious areas to the
The concentrations and loads of substances in the seepage water and the input of pollutants into the groundwater in the transition zone from the unsaturated to the water-saturated ground zone (the site of the assessment) can be estimated, unless favorable circumstances allow for representative testing of seepage water at the site of assessment.
This estimate can approximate
- by means of conclusions or returns from investigations in the groundwater flow, taking into account the concentration of substances in the groundwater flow, the dilution, the Pollutant behaviour in the unsaturated and saturated soil zone as well as pollutant inventories in the soil,
- based on in-situ investigations or
- on the basis of material investigations in the laboratory (elution, extraction), in the case of inorganic substances in particular the elution with water, according to the table 2
can also be done using fabric transport models.
The substance concentrations in the seepage water can be found at the site of sampling
- for inorganic pollutants, equivalent to the results of the Soil saturation extract; estimates based on analytical results according to Table 6 and Other elution processes (e.g. DIN 19730 or DIN 38414-4) are permissible if the equivalence of the results is ensured, in particular by reference to these results on the soil saturation extract; results according to DIN 38414-4: 10.84 shall be used only if the filtration has been carried out in accordance with point 3.1.2 of this Regulation;
- for organic substances from column tests of samples taken under Consideration of the location conditions at the point of removal, in particular with regard to the contact time, with the method according to Table 7.
The analytical results of the investigation of leachate water, groundwater, extracts and eluates as well as of the analysis of the site conditions are determined by the following methods: Soil samples shall be indicated by means of the respective examination procedure. The estimation of the seepage water quality and rates for the transition range from the unsaturated zone to the water-saturated zone based on this assessment must be explained and explained in
. which have been successfully applied to practical questions. For this purpose, the following instructions should be taken into consideration in individual cases.
In addition, the following instructions should be noted:
If in the individual case of a harmful soil change or contaminated soil an access of acidic leachate waters, an entry of Redeeming agents or a change in the redox potential should be expected, appropriate further extraction methods should be used.
In the estimation of the pollutant input in the transition zone from the unsaturated to the saturated zone shall, in particular, take account of the deplete and retention effect of the unsaturated zone. In particular, the following criteria are relevant:
- ground water flurp distance,
- organic matter content (humus content),
- groundwater reformation rate/seepage water rate,
- The mobility and degradability of the substances.
The influence of these factors on the retention of substances in the unsaturated zone is due to the general scientific background Findings and experiences for the respective location are estimated. The use of material transport models can also be expedient.
In the case of direct testing and examination of leachate water, the weather-related dynamics must be taken into account in the evaluation of the measured substance concentrations.
- Quality Assurance
- Sample Accepting and Sample
the Sampling points and sampling depths as well as sampling must be carried out by qualified personnel.
sampling, sample transport and sample storage must be carried out in such a way as to influence the chemical, physical and the biological nature of the sample material by working methods and/or materials, as well as storage conditions, as far as possible.
The sampling must be documented. The documentation shall contain all the information relevant for the laboratory examination and the evaluation of the results of the investigation, in particular information on
- Sample sampling time, sampler,
- the location of the investigation area and the Sampling Points,
- Area Label,
- Sample Depth,
- Ground horizons, according to the ground-based cartier instructions, 4. Edition, Reprint 1996,
- Layer Directory,
- pick procedure,
- former and current space usage, previous knowledge Contamination.
Existing standards, regulations of countries and professional quality assurance rules must be observed.
- Sample pretreatment and
Itappropriate to carry out, monitor and monitor the appropriate internal and external quality assurance measures, in particular with regard to the reproducibility (precision) and accuracy of the test results.
Internal quality assurance measures are in particular:
- the execution of independent multiple specifications,
- the calibration of measurement and test equipment,
- the Use of certified and/or laboratory-internal reference materials for quality control of reproducibility and correctness,
- plausibility control of the Investigation results.
External quality assurance measures are in particular:
- the Successful participation in comparative tests, in particular ring trials,
- Certificate of competence according to DIN EN 45001: 05.90.
Examination procedures shall specify the limits of detection and determination in accordance with DIN 32645: 05.94. The determination procedure shall be selected in such a way as to ensure that, on the basis of the limit of determination, the overwriting of the relevant test, measures and precautionary values in accordance with Annex 2 can be assessed safely. The method of determination is to be documented.
For the analytical result, a measurement uncertainty according to DIN 1319-3: 05.96 and/or DIN 1319-4: 12.85 is to be specified. style="font-weight:normal; font-style:normal; text-decoration:none; ">
- Abbreviation directory
- units of
| 1 ng (nanogram)||= 10 (high) -9 g||= 0,000 000 001 grams|
| 1 myg (microgram)||= 10 (high) -6 g||= 0,000 001 grams|
|1 mg (milligram)|| = 10 (high) -3 g||= 0.001 grams|
|1 kg (kilogram)||= 10 (high) 3 g||= 1,000 grams|
|1 mym (micrometer)||= 10 (high) -6 m|| = 0,000 001 meters|
|1 mm (millimeter)||= 10 (high) -3 m||= 0.001 Meter|
|1 cm (centimeters)||= 10 (high) -2 m||= 0.01 meter|
| 1 ha (hectare)||= 10 (high) 4 qm||= 10,000 square meters|
| Degree C-degree Celsius|
|AAS||-||Atomic Absorption Spectrometry|
|ET AAS||-|| Nuclear absorption spectrometry with electrothermal excitation|
|ICP-AES||-|| Atomic Emission Spectrometry with inductively coupled plasma|
|HPLC||-|| High Performance Liquid Chromatography|
|Detectors (GC, HPLC):|
|DAD||-||diodes array detector|
|ECD||-|| Electron Capture Detector|
| F||-||Fluorescence Detector|
|MS||-|| Mass Spectrometer|
|I-TEq||-|| International Toxicity Equities|
|6 PCB Congoners (PCB (deep) 6) by Ballschmiter:|
|No. 28:|| 2,4,4 '||trichlorobiphenyl|
|no. 52:||2.2 ',5,5'|| Tetrachlorobiphenyl|
|No. 101:||2.2 ', 4,5,5'|| Pentachlorobiphenyl|
|No. 138:||2.2 ', 3,4,4' ,5 '|| Hexachlorobiphenyl|
|No. 153:||2.2 ', 4,4' ,5,5 '|| Hexachlorobiphenyl|
|No. 180:||2.2 ', 3,4,4' ,5,5 '|| Heptachlorobiphenyl|
|16 PAK (EPA):|
|Benz (a) anthracen|
| Benzo (b) fluoranthene|
|Benzo (k) fluoranthene|
|Benzo (a) pyrene|
| Dibenz (a, h) anthracen|
|Indeno (1,2,3-cd) pyrene|
|Benzo (g, h, i) perylene|
- norms, technical rules and other methods, sources of reference
- Standards, Technical Rules and other methods
DIN ISO 10381-1: 02.96
soil sampling-Part 1: Guidance on the preparation of sampling programs (ISO/DIS 10381-1: 1995)
E DIN ISO 10381-2: 02.96
Floor condition- Sampling-Part 2: Instructions for sampling methods (ISO/DIS 10381-2: 1995)
E DIN ISO 10381-3: 02.96
Soil-sampling-Part 3: Guidance on safety (ISO/DIS 10381-3: 1995)
E DIN ISO 10381-4: 02.96
Soil quality-sampling-Part 4: Guidance for the investigation of natural, near-natural and cultivated sites (ISO/DIS 10381-4: 1995)
E DIN ISO 10382: 02.98
soil properties-gas chromatographic Determination of the content of polychlorinated biphenyls (PCBs) and organopesticides (OCP) (ISO/CD 10382: 1995)
DIN ISO 10390: 05.97
soil properties-determination of pH (ISO 10390: 1994)
DIN ISO 10694: 08.96
Soil condition-Determination of organic carbon and total carbon after dry combustion (elemental analysis) (ISO 10694: 1995)
ISO/TR 11046: 06.94
Soil quality-Determination of mineral oil content-Methods by infrared spectrometry and gas chromatographic method
E DIN ISO 11047: 06.95
soil composition-Determination of cadmium, chromium, cobalt, copper, lead, manganese, nickel and zinc-flame and electrothermal atomic absorption spectrometry (ISO/DIS 11047)
E DIN ISO 11262: 06.94
Floor condition-Determination of cyanides
E DIN ISO 11272: 01.94
Floor condition-Determination of dry bulk density (ISO/DIS 11272: 1992)
E DIN ISO 11277: 06.94
Soil properties-Determination of particle size distribution in mineral soils-Process by sieving and sedimentation after removal of soluble salts, organic matter and carbonates (ISO/DIS 11277: 1994)
DIN ISO 11464: 12.96
Soil quality-Sample pre-treatment for physico-chemical investigations (ISO/DIS 11464: 1994)
DIN ISO 11465: 12.96
soil condition-Determination of dry residue and water content on the basis of mass- Gravimetric Procedure (ISO 11465: 1993)
DIN ISO 11466: 06.97
Soil-quality extraction in Königswasser soluble trace elements (ISO 11466: 1995)
E DIN ISO 13877: 06.95
Floor condition-Determination of the soil polycyclic aromatic hydrocarbons (PAHs)-High Performance Liquid Chromatography (HPLC) Process (ISO/DIS 13877)
E DIN ISO 14154: 10.97
Soil composition-Determination of selected chlorophenols in soils- Gas chromatographic procedure (ISO/CD 14154: 1997)
E DIN ISO 14507: 02.96
Soil composition-Sample pretreatment for the determination of organic impurities in soils (ISO/DIS 14507)
DIN 19730: 06.97
Soil quality-extraction of trace elements with ammonium nitrate solution
DIN 19731: 05.98
soil properties-recovery of soil material
DIN 19734: 01.99
soil properties-determination of chromium (VI) in phosphate-buffered solution
DIN 19682-2: 04.97
Soil examination procedure in agricultural water engineering-Field investigations-Part 2: Determination of the type of soil
DIN 19683-2: 04.97
Ground examination procedure in the Agricultural water engineering-Physical laboratory tests, determination of grain size composition after pre-treatment with sodium pyrophosphate
DIN 19683-12: 04.73
Soil examination procedures in agricultural water construction; Physical laboratory tests, determination of the gross density
DIN EN 1233: 08.96
Water quality-Determination of chromium processes by atomic absorption spectrometry; German version EN 1233: 1996
DIN EN ISO 5667-3: 04.96
Water quality-sampling-part 3: instructions for the preservation and handling of samples (ISO 5667-3: 1994); German version EN ISO 5667-3: 1995 (A 21)
DIN EN ISO 5961: 05.95
Water quality-determination of cadmium by Atomic absorption spectrometry (ISO 5961: 1994); German version EN ISO 5961: 1995 (A 19)
DIN EN ISO 6468: 02.97
Water quality-Determination of selected organoinsecticides, polychlorbiphenyls and chlorobenzenes; Gas-chromatographic Process according to liquid-liquid extraction (ISO 6468: 1996); German version EN ISO 6468: 1996
ISO/DIS 8165-2: 01.97
Water quality-Determination of Selected Monohydric Phenol by Derivatisation and Gas Chromatography
DIN EN ISO 10301: 08.97
Water condition-Determination of low-volatility halogenated hydrocarbons-Gas-chromatographic methods (ISO 10301: 1997); German version EN ISO 10301: 1997
DIN EN ISO 10304-1: 04.95
Water quality- Determination of the dissolved anions fluoride, chloride, nitrite, orthophosphate, bromide, nitrate and sulphate by means of ion chromatography-Part 1: Process for low-polluted waters (ISO 10304-1: 1992); German version EN ISO 10304-1: 1995 (D 19)
Water quality-Determination of the dissolved anions by means of ion chromatography-Part 3: Determination of chromate, iodide, sulphite, thiocyanate and thiosulphate (ISO 10304-3: 1997); German version EN ISO 10304-3: 1997 (D 22)
DIN EN ISO 11885: 04.98
Water condition-Determination of 33 elements by inductively coupled plasma-atom emission spectrometry (ISO 11885: 1996); German version EN ISO 11885: 1997
DIN EN ISO 11969: 11.96
Water quality-Determination of arsenic-Atomic absorption spectrometry (hydride process)
E DIN EN ISO 14403: 05.98
Water quality-Determination of the total cyanide and the free cyanide with continuous flow analysis (ISO/DIS 14403: 1998); German version prEN ISO 14403: 1998
DIN 38405-4: 07.85
German unit method for water, sewage and sludge investigation-anions (group D); determination of fluoride (D 4)
DIN 38405-13: 02.81
German unit processes for water, sewage and sludge investigation-anions (group D); determination of cyanides (D 13)
DIN 38405-23: 10.94
German unit method for water, sewage and sludge investigation-anions (group D)-Part 23: Determination of selenium by means of atomic absorption spectrometry (AAS) (D 23)
DIN 38405-24: 05.87
German unit method for water, sewage and sludge investigation-Anions (Group D)-Part 24: Photometric determination of Chromium (VI) by means of 1,5-diphenylcarbazide (D 24)
DIN 38406-6: 07.98
German unit method for water, sewage and sludge investigation-cations (Group E)-Determination of lead by atomic absorption spectrometry (AAS) (E 6)
DIN 38406-7: 09.91
German unit method for water, sewage and sludge investigation; cations (group E); determination of copper by atomic absorption spectrometry (AAS) (E 7)
DIN 38406-8: 10.80
German Unit processes for water, sewage and sludge investigation; cations (group E); determination of zinc (E 8)
DIN 38406-11: 09.91
German unit method for water, sewage and sludge investigation; cations (group E); determination of nickel by means of atomic absorption spectrometry (AAS) (E 11)
DIN 38406-24: 03.93
German unit method for water, sewage and sludge investigation; cations (group E); determination of cobalt by atomic absorption spectrometry (AAS) (E 24)
DIN 38407-2: 02.93
German unit method for water, sewage and sludge investigation; jointly detectable groups of substances (group F); gas chromatographic determination of low-volatility halogenated hydrocarbons (F 2)
DIN 38407-3: 07.98
German Unity Method for Water, Wastewater and Sludge Investigation; Shared groups of substances (Group F); Part 3: Gas chromatographic determination of polychlorinated biphenyls (F 3)
DIN 38407-8: 10.95
German unit method for water, sewage and sludge investigation; Shared groups of substances (group F); Determination of 6 polycyclic aromatic hydrocarbons (PAHs) in water by means of High performance liquid chromatography (HPLC) with fluorescence detection (F 8)
DIN 38407-9: 05.91
German unit method for water, sewage and sludge investigation; Shared groups of substances (group F); determination of benzene and some derivatives by means of gas chromatography (F 9)
DIN 38414-2: 11.85
German unit method for water, sewage and sludge investigation; sludge and sediments (group S); determination of the water content and the dry residue or the dry substance (S 2)
DIN 38414-4: 10.84
German unit method for water, sewage and sludge investigation; sludge and sediments (group S); determination of the elucibility with water (S 4)
DIN 38414-20: 01.96
German unit procedures for water, sewage and sludge investigation-sludge and sediments (Group S)-Part 20: Determination of 6 polychlorinated biphenyls (PCBs) (S 20)
DIN 38414-24: 04.98
Deutsche unitary procedure for water-, Sewage and sludge investigation-sludge and sediments (group S)-Part 24: Determination of polychlorinated dibenzodioxins (PCDD) and polychlorinated dibenzofurans (PCDF) (S 24)
DIN EN 1483: 08.97
Water analysis-determination of Mercury; German version EN 1483: 1997 (E 12)
DIN 32645: 05.94
Chemical analysis-detection, detection and determination limit-Determination under repetition conditions-terms, procedures, evaluation
DIN 1319-3: 05.96
Basics of measurement technology-Part 3: Evaluation of measurements of a measured variable, measurement uncertainty
DIN 1319-4: 12.85
Basic terms of measurement technology; Handling of uncertainties in the evaluation of measurements
DIN EN 45001: 05.90
General criteria for the operation of test laboratories; Identical to EN 45001: 1989
DIN 4021: 10.90
Construction ground breakdown by means of aprons and drillings as well as removal of samples
DIN 18123: 11.96
Building ground study of Soil samples-Determination of grain size distribution
DIN EN 932-1: 11.96
Test procedure for general properties of rock formations-Part 1: Sample methods; German version EN 932-1: 1996
DIN 52101: 03.88
Testing of Natural stone and rock formations-sampling
DIN 51527-1: 05.87
Testing of petroleum products; Determination of polychlorinated biphenyls (PCB)-Liquid chromatographic pre-separation and determination 6 of selected PCBs by means of a Gas chromatographs with Electron Capture Detector (ECD)
ZH 1/183: 04.97
Safety and health rules for work in contaminated areas, Main Association of Industrial Occupational Unions-Technical Committee Deep Construction, Edition April 1997
VDI guideline 3865: Measure organic soil contaminants
- Sheet 1: Measure Low volatile halogenated hydrocarbons, measurement planning for ground-air examination procedures (Oct. 1992);
- Sheet 2: techniques for the active removal of Soil air samples (January 1998);
- Sheet 3: Measurement of organic soil impurities; Gas chromatographic determination of low-boiling organic compounds in Soil air after enrichment of activated carbon or XAD-4 and desorption with organic solvents (draft November 1996);
VDI guideline 3499, sheet 1: Measurement of emissions-measurement of residual materials. Measurement of polychlorinated dibenzodioxins and furans in pure and crude gas from combustion plants with the dilution method, determination in filter dust, boiler ash and in slag. VDI-Handbuch Reinhaltung der Luft, Volume 5 (Draft March 1990)
Working Group of Soil Science of the Geological State Offices and the Federal Institute for Geosciences and Natural Resources (1994): Ground-based Cartiera guidance. -4. Edition, corrected reprint Hannover 1996, E. Schweizerbart 'sche Verlagsbuchhandlung Stuttgart
Landesumweltamt Nordrhein-Westfalen (LUA NRW): Determination of polycyclic aromatic hydrocarbons (PAHs) in soil samples. Leaflet LUA NRW No. 1, Essen 1994
Hessische Landesanstalt für Umwelt (LfU HE): Determination of polycyclic aromatic hydrocarbons in solids from the old-load range. Manual Altweigh, Volume 7, Wiesbaden 1998
Verband Deutscher Landeconomically Inveschungs-und Forschungsanstalten (VDLUFA): Method book, volume VII Environmental analysis, VDLUFA-Verlag Darmstadt 1996
standards, technical rules, and other method rules listed in this regulation are to be taken:
unofficial table of contents
- DIN and ISO standards and draft standards, VDI Guidelines: Beuth-Verlag GmbH, 10772 Berlin
- Bodenkundliche Kartieranleitung: E. Schweizerbart 'sche Verlagsbuchhandlung, 70176 Stuttgart
- VDLUFA-Method Book: VDLUFA-Verlag, 64293 Darmstadt
- Merkblatt LUA NRW: Landesumweltamt NRW, 45023 Food
- Manual Altburdens LfU HE: Hessische Landesanstalt für Umwelt, 65022 Wiesbaden
- ZH 1/183: Hauptverband der FachBerufsgenossenschaften, Fachausschuss Tiefbau, 81241 München
(site: BGBl. I 1999, 1575-1579)
1. Reaction path soil-human (direct contact)1.1usage delineationa) Children's play area recreation areas for children, which are used locally for play, without the playing sand of sand boxes. Officially designated children's playgrounds may be in accordance with public health standards.b)Territories, including residential areas, including In-house gardens or other gardens of corresponding use, even if they are not shown or fixed in accordance with the Baunal Ordinance, except for parks and leisure facilities, children's play areas and fortified areas. c)Park and leisure facilities for social, health and sports purposes, in particular public and private green spaces, and non-fortified areas, which are regularly accessible and are used in a comparable way.d)Industrial and commercial land-unsecured areas of work and Production sites that are only used during working hours.
- Measures, Check and Preemption
1.2 Measures according to § 8 (1) sentence 2 no. 2 of the Federal Soil Protection Act for the direct inclusion of dioxins/furans on children's play areas, in residential areas, park and Leisure facilities and industrial and commercial properties (in ng/kg dry mass, fine soil, analytics according to Appendix 1)
| Measures values (ng l-TEq/kg TM) 1 *)|
| fabric|| Children's play areas|| residential areas|| Park-u. Leisure facilities|| Industrial and commercial plots|
|dioxine/Furane (PCDD/F)|| 100||1,000||1,000||10,000|
- Sum of 2,3,7,8-TCDD toxicity equivalent (by NATO/CCMS).
- Application of policy values
In case of dioxin-containing lye residues from copper shale ("silica red") an application of the measures values due to the low absorption in the human organism does not take place directly for the protection of human health, but rather for the purpose of the sustainable security. 1.4 Test values according to § 8 (1) sentence 2 No. 1 of the Federal Soil Protection Act for the direct inclusion of pollutants on children's play areas, in residential areas, park and leisure facilities and industrial and commercial land (in mg/kg dry matter, Fine-bottomed analysis according to Appendix 1)
| Audit values (mg/kg TM)|
| fabric|| Children's play areas|| Living areas|| Park-u. Leisure facilities|| Industrial and industrial plots|
| Arsen|| 25|| 50|| 125|| 140|
| Lead|| 200|| 400|| 1.000|| 2,000|
| Cadmium|| 10 1)|| 20 1)|| 50|| 60|
| Cyanide|| 50|| 50|| 50|| 100|
| Chrome|| 200|| 400|| 1.000|| 1,000|
| Nickel|| 70|| 140|| 350|| 900|
| Mercury|| 10|| 20|| 50|| 80|
| Aldrin|| 2|| 4|| 10||-|
| Benzo (a) pyren|| 2|| 4|| 10|| 12|
| DDT|| 40|| 80|| 200||-|
| Hexachlorobenzene|| 4|| 8|| 20|| 200|
- In house and allotment gardens, which are used both as recreation areas for children and for the cultivation of food crops, the value of cadmium is 2.0 mg/kg TM as a test value application.
| Test values (mg/kg TM)|
| fabric|| Children's play areas|| Living areas|| Park-u. Leisure facilities|| Industrial and industrial plots|
| Hexachlorocyclohexane (HCH-mixture or Beta-HCH)|| 5|| 10|| 25|| 400|
| Pentachlorophenol|| 50|| 100|| 250|| 250|
| Polychlorinated Biphenyls (PCB (deep) 6) 2)|| 0, 4|| 0, 8|| 2|| 40|
- As far as Total PCB contents are determined by the factor of 5 to divide the measured measured values.
- Reaction Path Floor-Utility
- Payout of Use
- arable land for the cultivation of alternating arable crops including vegetables and field fodder, including working-gardening areas.
- Commercial garden garden-, garden and other garden areas used to grow food crops
- grassland areas under permanent pasture
2.2 Test and measure values according to § 8 (1) sentence 2 no. 1 and 2 of the Federal Soil Protection Act for the Pollutant Transfer Soil crop plant on arable land and in farm gardens with a view to plant quality (in mg/kg dry mass, fine soil, analysis according to Annex 1)
StoffMethod 11) Audit value policy value
| Arsen|| KW|| 200 22)||-|
| Cadmium|| AN||-|| 0.04/0, 1 33)|
| Lead|| AN|| 0, 1||-|
| Mercury|| KW|| 5|
| Thallium|| AN|| 0, 1||-|
|Benzo (a) pyren||-||1||-|
- Areas with bread wheat cultivation or cultivation of highly cadmium-rich vegetables are considered to be a measure of 0.04 mg/kg dry matter; otherwise, the measure shall be 0.1 mg/kg. Dry mass.
- In the case of soils with temporary reducing conditions, a test value of 50 mg/kg is valid. Dry mass.
- Extraction procedure for arsenic and heavy metals: AN = ammonium nitrate, KW = Royal Water.
2.3 Measures according to § 8 (1) sentence 2 no. 2 of the Federal Soil Protection Act for the Harmful Transfer Soil plant on grassland areas with regard to plant quality (in mg/kg dry matter, fine soil, arsenic and heavy metals in the Königswasser-extract, analysis according to Appendix 1)
Fabric Policy Value
| Arsen|| 50|
| Lead|| 1.200|
| Cadmium|| 20|
| Copper|| 1.300 11)|
| Nickel|| 1.900|
| Mercury|| 2|
| Thallium|| 15|
|Polychlorinated Biphenyle (PCB (deep) 6)|| 0, 2|
- In the case of grassland use by sheep, the measure value is 200 mg/kg dry mass.
2.4 Test values according to § 8 (1) sentence 2 No. 1 of the Federal Soil Protection Act for the Harmful Transfer Soil plant on arable land with regard to growth impairments in crop plants (in mg/kg Dry mass, fine soil, in ammonium nitrate extract, analysis according to Annex 1)
Fabric Test Value
| Arsen|| 0, 4|
| Copper|| 1|
| Nickel|| 1, 5|
- Application of test and policy values
The audit and policy values apply to the assessment the pollutant contents in the soil depth of 0 to 30 cm for arable land and in farm gardens and in the soil depth of 0 to 10 cm for grassland in accordance with Annex 1, point 2.1, Table 1. For the greater depth of ground referred to in Annex 1, point 2.1, Table 1, the 1.5-fold values shall apply.
- Reaction path ground-ground water
- Test values for assessing the ground-groundwater action path According to § 8 paragraph 1 sentence 2 no. 1 of the Federal Soil Protection Act (in myg/l, analytics according to appendix 1)
| Inorganic fabrics|| Audit value (myg/l)|
| chrome, total|| 50|
| Copper|| 50|
| Zinc|| 500|
| cyanid, total||50|
| Cyanid, easy to release|| 10|
| Fluorid|| 750|
| Organics|| Checkvalue (myg/l)|
| Mineral Oil Hydrocarbons 1)||200|
| BTEX 2)|| 20|
| LHKW 3)||10|
| Aldrin|| 0, 1|
| PCB, total 4)||0.05|
| PAK, total 5)||0,20|
| naphthaline|| 2|
- n-alkanes (C 10 C39), isoalkanes, cycloalkanes, and aromatic hydrocarbons.
- Light Volatile Aromatic Hydrocarbons (benzene, toluene, xylenes, ethylbenzene, styrene, cumene).
- Light Volatile Halogenated Hydrocarbons (sum of halogenated C1 and C2 hydrocarbons).
- PCB, total: total of polychlorinated biphenyls; as a rule, determination of the 6 congeners according to Ballschmiter according to waste oil-VO (DIN 51527) multiplied by 5; if necessary e.g. in the case of a known Material spectrum simple sum formation of all relevant individual substances (DIN 38407-3-2 or -3-3).
- PAH, total: sum of polycyclic aromatic hydrocarbons without Naphthalene and methylnaphthalenes; as a rule, determination of the sum of 15 individual substances in accordance with the list of the US Environmental Protection Agency (EPA) without naphthalene; if necessary Taking into account other relevant PAHs (e.g. Chinoline).
- Audit values application
- The test values are valid for the transition range from the unsaturated to the water-saturated ground zone (site of assessment). The site of the soil sampling does not necessarily correspond to the site of the groundwater assessment.
- In assessing whether or not it is expected that the Test values for the seepage water at the site of the assessment shall be exceeded, the changes in pollutant concentrations in leachate during passage through the unsaturated soil zone, as well as the groundwater levels and their variations, shall be
- In the case of aldeposits, the estimation of pollutant concentrations in leachate is due to material studies due to inhomogeneities of the waste, as a rule, is not appropriate. The same applies to old sites with particularly non-uniform pollutant distribution. In these cases, an estimation of the concentrations of pollutants in the leachate can be carried out by means of conclusions or recalculation from downstream measurements in groundwater, taking into account, in particular, the concentration of substances in the flow of anelectricity.
- As far as the concentrations of pollutants in the seepage water can be measured directly, sampling should, if possible, at the site of the assessment for the
- As far as harmful soil changes and contaminated sites are located in the water-saturated soil zone, they are likely to be hazardous to the environment. the groundwater is evaluated according to water regulations.
- The geogenic background situation of the respective groundwater region is in the application of the Test values to be taken into account.
- precautionary values for soils according to § 8 paragraph 2 no. 1 of the Federal Soil Protection Act (Analysis according to Appendix 1)
- Precautionary values for metals (in mg/kg dry mass, fine soil, royal water digestion)
| Floors|| Cadmium|| Lead|| Chrome|| Copper|| Mercury|| Nickel|| Zinc|
| Bodenart Ton|| 1, 5|| 100|| 100|| 60|| 1|| 70|| 200|
| Bodenart Lehm/Schluff|| 1|| 70|| 60|| 40|| 0, 5|| 50|| 150|
| Bodenart Sand|| 0, 4|| 40|| 30|| 20|| 0, 1|| 15|| 60|
| Floors with natural and large-scale settlement-related increased background contents|| harmless to the extent that a release of the pollutants or Additional entries in accordance with § 9 (2) and (3) of this Regulation do not expect any adverse effects on the ground functions|
| 4.2 Precautionary values for organic substances|
(in mg/kg dry mass, fine soil)
| Floors|| Polychlorinated Biphenyls (PCB (deep) 6)|| Benzo (a) pyren|| Polycycl. Aromatic hydrocarbons (PAHs (deep) 16)|
| Humus content > 8%|| 0, 1|| 1|| 10|
| Humus content < = 8%|| 0, 05|| 0, 3||3|
d)The precautionary values in Table 4.1 are not used for soils and soil horizons with a humus content of more than 8 percent. For these soils, the competent authorities may, if necessary, 5.Permitted additional annual polls of pollutants over all Acting subject to § 8 para. 2 no. 2 of the Federal Soil Protection Act (in grams per hectare)
- precautionary application application
- The precautionary values will be based on the main soil types according to the ground-based cartier instructions, 4. A distinction made in 1996, a revised edition, which takes account of the preventative protection of soil functions in the case of sensitive uses. § 17 (1) of the Federal Soil Protection Act applies to the agricultural land use.
- Stark slippage sands are to be found according to the soil type clay/silt
- For the precautionary values in Table 4.1, the acid level of the soils should be taken into account as follows:
- On floors of soil type clay with a pH of < 6,0, cadmium, nickel and zinc are the Precautionary values of soil type clay/silt.
- In the soil of the soil type clay/silt with a pH of < 6.0, cadmium, nickel and zinc are subject to the precautionary values of the soil type. Soil type of sand. § 4 (8) sentence 2 of the Sewage Sludge Ordinance of 15. April 1992 (BGBl. 912), as last amended by the Regulation of 6. March 1997 (BGBl. I p. 446), remains unaffected.
- In the case of soils with a pH of < 5.0, the precautionary values for lead are equivalent to the first two paints.
unofficial table of contents
ElementFracht (g/ha x a)
| Lead|| 400|
| Cadmium|| 6|
| Chrome|| 300|
| Copper|| 360|
| Nickel|| 100|
| Mercury|| 1, 5|
Fundstelle: BGBl. I 1999, 1580-1581
- Requirements for remediation investigations and the Refurbishment
- refurbishment investigations
With remediation investigations in the case of legacy loads, are the tasks required to fulfil the obligations of § 4 (3) to determine the appropriate, necessary and appropriate measures to be taken. The measures to be taken for this purpose shall be presented in the light of the combination of measures and the accompanying measures.
test must be -of the quantities to be treated and the transport routes for soil treatment in off-site installations,- the technical design of backup measures and accompanying measures, in particular
- the suitability for harmful substances, soil, material and site the procedure,
- the technical feasibility,
- the required Time,
- the effectiveness with regard to the remediation target,
- Cost estimation as well as the ratio of costs and effectiveness,
- the effects on the persons concerned within the meaning of § 12 sentence 1 of the Federal Soil Protection Act and on the Environment,
- the requirement of authorisations,
- the creation, recovery and disposal of waste,
- the labor protection,
- the duration of the actions and their Monitoring capabilities,
- the requirements of aftercare and
- the Post-improvement
The test is to be carried out using existing data, in particular from investigations in accordance with § 3 of this Regulation, as well as on the basis of other assured findings. Insofar as such information is not sufficient, in particular for the secure demarcation of contaminated areas or for the assessment of the suitability of refurbishment procedures in individual cases, additional investigations shall be carried out in order to verify the suitability of a method on the market.
The results of the audit and the policy concept that is to be presented accordingly are to be presented.
A recovery plan is to provide the information specified in points 1 to 5, as well as contain the information and documents required for a declaration of liability in accordance with Section 13 (6) of the German Federal Soil Protection Act (Bundessoil Protection Act).
- Sanation Plan
- Representation of the starting position, in particular with respect to
- Location ratios (including: geological, hydrogeological situation; existing and planning allowed use),
- of the hazard situation (summary of investigations according to § 3 of these Regulation with regard to the inventory of pollutants by type, quantity and distribution, affected pathways, protection goods and needs),
- Remediation objectives,
- of the decisions taken by the authorities and the public service contracts concluded, in particular with regard to the Concept of measures affecting the performance of the obligations to be fulfilled in accordance with § 4 of the Federal Soil Protection Act, and
- the results of the Remediation investigations
- Text and graphic representation of the measures to be carried out and proof of their suitability, in particular with regard to
- the impact area of the legacy load and the areas that are required for the actions that are provided
- of the territory of the refurbishment plan,
- the elements and the flow of the refurbishment with regard to
- the construction flow,
- the earthworks (in particular excavation, separation, rebuilding, relocations in the area of the refurbishment plan),
- the demolition work,
- the intermediate storage of soil material and other materials. materials,
- waste disposal when operating plants,
- the use of soils and the deposition of waste at landfills and
- the work and immission protection measures
- the subject-specific calculations for
- on-site ground handling systems,
- in-situ measures,
- Appendices and Treatment of Deponiegas or Float Air,
- Groundwater Treatment Plants,
- Systems and measures for the version and treatment of Sickerwasser
-the official Approval requirements for the measures to be taken.3.Presentation of the self-control measures to verify the proper execution and Effectiveness of the measures envisaged, in particular
- Surface, Vertical, and Base Seals,
- Surface Coverings,
- Intermediate or Deployment stores,
- Passive pneumatic, hydraulic, or Other measures (e.g. Baufeldentirrigung, drainage of the excavation material, inhouse, waste air collection and treatment) and
- Examination concept for materials and components in the execution of buildings4.Presentation of the self-control measures in the context of follow-up care including monitoring, in particular with regard to
- the monitoring concept with regard to
- ground management in case of cutterance, separation, and rebuilding,
- ground and ground water treatment, degassing, or bottom air extraction,
- of the work and Immission protection,
- the accompanying sampling and analysis
5.Presentation of schedule and cost. Non-Official Table of Contents
- of the requirement and the design of In the longer term, installations or installations for the version or treatment of groundwater, leachate, surface water, ground air or landfill gas, as well as requirements for monitoring and maintenance thereof,
- the monitoring measures (e.g. measuring points) and
- of the function control with regard to the Compliance with remediation requirements and maintenance of backup structures or facilities
Fundstelle: BGBl. I 1999, 1582
- Requirements for the investigation and evaluation of areas where the suspicion of a harmful Soil erosion due to soil erosion by water
This appendix is applicable in accordance with § 8 Application Investigation of areas where there is a suspicion of harmful soil degradation due to soil erosion by water.
- Investigation and Evaluation
Evidence of the presence of a harmful Soil erosion due to soil erosion by water, so first check,
- whether significant Quantities of soil material from the erosion surface have been washed and
- on which erosion surfaces and on which polluters the soil precoat can be attributed
Information for the identification of the erosion surface is given above all by clearly visible transfer points of soil material from the erosion surface to the outside of the erosion surface and by soil material affected areas. Further information is obtained from the presence of clearly visible erosion forms on the erosion surface. In the case of the test referred to in point (a), it may be necessary for the quantity of the soil to be washed off from a roof area during an erosion event or in the event of erosion events which have occurred at a distance of a maximum of a few weeks from a roof area. , This can be done with the help of the "Kartieranleitung zur Capture Current Erosion Forms" (DVWK 1996).
For the estimation of the probability of re-entry of land in accordance with § 8 (1), especially area-specific statistical evaluations of long-time rainfall records of the German Weather Service are to be used. For this purpose, erosion prognosis models can also be used as aids to the extent that they are demonstrably suitable for the erosion of the soil with sufficient accuracy in the case of concretely occurring erosion events from the erosion surfaces. ,
The conditions for the expectation of further land yields in accordance with § 8 (1) No. 2 are generally fulfilled if, within the last ten years, at least in one further case, significant amounts of soil material from the same erosion surface area are met. have been swamped.