13.080.30 土壤的生物特性 标准查询与下载



共找到 527 条与 土壤的生物特性 相关的标准,共 36

本标准规定了土壤脲酶的测定方法,其中包括原理、试剂和溶液、仪器设备、分析步骤、 结 果计算及精密度。 本标准适用于各类土壤脲酶的测定。

Determination of Soil Urease Activity Sodium Phenate-Sodium Hypochlorite Colorimetric Method

ICS
13.080.30
CCS
N772
发布
2020-07-15
实施
2020-10-27

本标准规定了土壤过氧化氢酶的测定方法,其中包括原理、试剂和溶液、仪器设备、分 析 步骤、结果计算及精密度。 本标准适用于各类土壤过氧化氢酶的测定。

Determination of Soil Catalase Activity by Potassium Permanganate Titration

ICS
13.080.30
CCS
N772
发布
2020-07-15
实施
2020-10-27

本标准规定了土壤蔗糖酶的测定方法,其中包括原理、试剂和溶液、仪器设备、分析步 骤、 结果计算及精密度。 本标准适用于各类土壤蔗糖酶的测定。

Determination of Soil Sucrase Activity by 3,5-Dinitrosalicylic Acid Colorimetric Method

ICS
13.080.30
CCS
N772
发布
2020-07-15
实施
2020-10-27

本标准规定了土壤微生物量氮的测定方法。 本标准适用于各类土壤微生物量氮的测定。

Determination of soil microbial biomass nitrogen

ICS
13.080.30
CCS
N772
发布
2020-07-15
实施
2021-09-01

What is ISO 16751 about?    ISO 16751 discusses soil quality. ISO 16751 specifies an extraction method to determine the bioavailable (potential and environmental available) fraction and the non-bioavailable fraction of a contaminant in soil using a “receiver phase” for an organic contaminant with strong sorbing or complexing properties.   The method is applicable for non-polar organic contaminants with an aqueous solubility of <100 mg/l. The method is applicable for soil and soil-like material including (dredged) sediments.   Who is ISO 16751 for?

Soil quality. Environmental availability of non-polar organic compounds. Determination of the potentially bioavailable fraction and the non-bioavailable fraction using a strong adsorbent or complexing agent

ICS
13.080.30
CCS
发布
2020-06-30
实施
2020-06-30

1   Scope The purpose of this International Standard is to describe a method for assessing genotoxic effects (chromosome breakage or dysfunction of the mitotic spindle) of soils or soil materials on the secondary roots of a higher plant: Vicia faba (broad bean). This method allows the assessment of genotoxicity (toxicity for genetic material) of soils and soil materials like compost, sludge, waste, fertilizing matters, etc. Two ways of exposure can be considered: a direct exposure of plants to the soil (or soil material) which is relevant for the real genotoxic potential and an exposure of plants to the water extract of the soil (or soil material). This last way of exposure to a leachate or an eluate allows the detection of the mutagens which are not adsorbed to soils and which may be transferred to aquatic compartments. Moreover, this test may be used to evaluate genotoxic effects of chemical substances and to waters, effluents, etc.

Soil quality. Assessment of genotoxic effects on higher plants. Vicia faba micronucleus test

ICS
13.080.30
CCS
发布
2020-06-30
实施
2020-06-30

1   Scope This part of ISO 17512 specifies a rapid screening method for evaluating the habitat function of soils based on the avoidance behaviour of springtails. The test is a rapid method that reflects the bioavailability of contaminants in natural soils and substances spiked into soils to Folsomia candida . In both cases, it is possible to establish a dose-response-relationship. The avoidance behaviour of the springtails is the measurement endpoint of the test. This test is not intended to replace the Collembola reproduction test.

Soil quality. Avoidance test for determining the quality of soils and effects of chemicals on behaviour - Test with collembolans (Folsomia candida)

ICS
13.080.30
CCS
发布
2020-06-30
实施
2020-06-30

1   Scope This document describes a method to compare the quality of soils by determining the fatty acid composition of the leaves of plant species grown in these soils. This method does not make it possible to determine an optimal value of the Omega-3 index and, therefore, cannot be used to determine the intrinsic quality of a soil from a specific area (regarded as homogeneous). The method can only be used to compare the quality of soils between various areas. This method is applicable to: — soils from contaminated sites; — amended soils; — soils after remediation; — soil with waste products (e.g .  slurry, manure, sludge or composts). Alternatively, the quality of soils can be assessed by determining the Omega-3 index of Lactuca sativa seedlings grown in these soils under controlled conditions (i.e. phytotronic chamber) and by comparing these values to those obtained from control soils (see Annex B).

Soil quality. Determination of the effects of pollutants on soil flora. Leaf fatty acid composition of plants to assess soil quality

ICS
13.080.30
CCS
发布
2020-06-30
实施
2020-06-30

This document specifies an extraction method to determine the bioavailable (potential and environmental available) fraction and the non-bioavailable fraction of a contaminant in soil using a “receiver phase” for an organic contaminant with strong sorbing or complexing properties, for example, Tenax®1) or cyclodextrin, respectively. NOTE 1 The bioavailable fraction is defined in ISO 17402 as environmental bioavailability. The method is applicable for non-polar organic contaminants with an aqueous solubility of 3) and less for compounds with a higher solubility. The applicability is therefore defined for compounds with an aqueous solubility of

Soil quality — Environmental availability of non-polar organic compounds — Determination of the potentially bioavailable fraction and the non-bioavailable fraction using a strong adsorbent or complexi

ICS
13.080.30
CCS
发布
2020-06-26
实施

This document specifies one of the methods for evaluating the habitat function of soils and determining effects of soil contaminants and individual chemical substances on the reproduction of the oribatid mite Oppia nitens by dermal and alimentary uptake. This chronic (28-day) test is applicable to soils and soil materials of unknown quality (e.g., contaminated sites, amended soils, soils after remediation, agricultural or other sites under concern and waste materials). This method is not intended to replace the earthworm or Collembola tests since it represents another taxonomic group (= mites; i.e., arachnids), nor the predatory mite test since this species represents a different trophic level and ecological niche. Effects of substances are assessed using standard soil, preferably a defined artificial soil substrate. For contaminated soils, the effects are determined in the test soil and in a control soil. According to the objective of the study, the control and dilution substrate (dilution series of contaminated soil) should be either an uncontaminated soil with similar properties to the soil sample to be tested (reference soil) or a standard soil (e.g., artificial soil). Information is provided on how to use this method for testing substances under temperate conditions. This document is not applicable to substances for which the air/soil partition coefficient is greater than 1, or to substances with vapour pressure exceeding 300 Pa at 25 °C. NOTE The stability of the test substance cannot be assured over the test period. No provision is made in the test method for monitoring the persistence of the substance under test.

Soil quality — Test for measuring the inhibition of reproduction in oribatid mites (Oppia nitens) exposed to contaminants in soil

ICS
13.080.30
CCS
发布
2020-06-08
实施

1   Scope This document specifies a chronic test method for evaluating the habitat function of soils and determining effects of soil contaminants and substances on the reproduction of Hypoaspis aculeifer by – mainly – alimentary uptake. This method is applicable to soils and soil materials of unknown quality, e.g. from contaminated sites, amended soils, soils after remediation, industrial, agricultural or other sites under concern and waste materials (e.g. dredged material, municipal sludge from a wastewater treatment plant, composed material, or manure, especially those for possible land disposal). The reproduction (= number of juveniles) is the measured parameter of the test. The test reflects the bioavailability of a mixture of contaminants in natural soils (contaminated site soils) to a species which represents a trophic level which is not covered by other ISO standards. This test is not intended to replace the earthworm (see ISO 11268‑2) or Collembola (see ISO 11267) reproduction tests since this species belongs not only to a different trophic group but also a different taxonomic group (= mites; i.e. arachnids) than those used usually. Effects of substances are assessed using a standard soil , preferably a defined artificial soil substrate. For contaminated soils, the effects are determined in the soil to be tested and in a control soil . Depending on the objective of the study, the control and dilution substrate (dilution series of contaminated soil) are either an uncontaminated soil comparable to the soil to be tested ( reference soil ) or a standard soil (e.g. artificial soil). This document provides information on how...

Soil quality. Inhibition of reproduction of the soil mite (Hypoaspis aculeifer) by soil contaminants

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

1   Scope This document specifies a protocol to identify ecotoxicological test specimens (mainly invertebrates and plants) to the species level, based on the DNA barcoding technique. This protocol can be used by laboratories performing DNA barcoding in order to standardize both the wet-lab and data analysis workflows as much as possible, and make them compliant with community standards and guidelines. This document does not intend to specify one particular strain for each test method, but to accurately document the species/strain which was used. NOTE 1 This does not imply that DNA barcoding is performed in parallel to each test run, but rather regularly (e.g. once a year, such as reference substance testing) and each time a new culture is started or new individuals are added to an ongoing culture. This document does not aim at duplicating or replacing morphological-based species identifications. On the contrary, DNA barcoding is proposed as a complementary identification tool where morphology is inconclusive, or to diagnose cryptic species, in order to ensure that the results obtained from different ecotoxicological laboratories are referring to the same species or strain. This document is applicable to identifications of immature forms which lack morphological diagnostic characters (eggs, larvae, juveniles), as well as the streamline identification of specimens collected in field monitoring studies, where large numbers of organisms from diverse taxa are classified. NOTE 2 In principle, all species regularly used in ecotoxicological testing can ...

Soil quality. Identification of ecotoxicological test species by DNA barcoding

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

1   Scope This International Standard provides guidance on the selection and conduct of appropriate test methods for the determination of biodegradation of organic chemicals in aerobic soils. It does not describe any specific test method.

Soil quality. Guidance on laboratory testing for biodegradation of organic chemicals in soil under aerobic conditions

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

1   Scope This document specifies six suitable incubation systems for measuring the rates and extent of mineralization of organic compounds in soil by measurement of carbon dioxide (CO 2 ) evolution. All incubation systems are applicable to soluble or insoluble compounds but choice of system depends on the overall purposes of the study. This document does not apply to the use of such systems for material balance studies, which are often test-substance specific.

Soil quality. Laboratory incubation systems for measuring the mineralization of organic chemicals in soil under aerobic conditions

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

1   Scope This International Standard gives guidance on the selection and method of appropriate tests for the determination of biodegradation of organic chemicals in soil samples under anaerobic conditions. NOTE If the method is intended for tests in the framework of the registration of chemicals, an OECD Guideline on soil degradation [20] gives useful guidance on additional test requirements.

Soil quality. Guidance on laboratory testing for biodegradation of organic chemicals in soil under anaerobic conditions

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

1   Scope This document specifies a method for the measurement of several hydrolase activities (arylamidase, arylsulfatase, β -galactosidase, α -glucosidase, β -glucosidase, N-acetyl-glucosaminidase, acid, alkaline and global phosphatases, urease) simultaneously (or not) in soil samples, using colorimetric substrates. Enzyme activities of soil vary seasonally and depend on soil chemical, physical and biological characteristics. This method can be applied either to detect harmful effects on soil enzyme activities derived from toxic substances or other anthropogenic agents in contaminated soils against a control soil, or to test chemicals.

Soil quality. Measurement of enzyme activity patterns in soil samples using colorimetric substrates in micro-well plates

ICS
13.080.30
CCS
发布
2020-05-31
实施
2020-05-31

This document specifies a method for the measurement of several hydrolase activities (arylamidase, arylsulfatase, β-galactosidase, α-glucosidase, β-glucosidase, N-acetyl-glucosaminidase, acid, alkaline and global phosphatases, urease) simultaneously (or not) in soil samples, using colorimetric substrates. Enzyme activities of soil vary seasonally and depend on soil chemical, physical and biological characteristics. This method can be applied either to detect harmful effects on soil enzyme activities derived from toxic substances or other anthropogenic agents in contaminated soils against a control soil, or to test chemicals.

Soil quality - Measurement of enzyme activity patterns in soil samples using colorimetric substrates in micro-well plates (ISO 20130:2018)

ICS
13.080.30
CCS
发布
2020-05-06
实施
2020-08-31

The purpose of ISO 29200:2013 is to describe a method for assessing genotoxic effects (chromosome breakage or dysfunction of the mitotic spindle) of soils or soil materials on the secondary roots of a higher plant: Vicia faba (broad bean). This method allows the assessment of genotoxicity (toxicity for genetic material) of soils and soil materials like compost, sludge, waste, fertilizing matters, etc. Two ways of exposure can be considered: a direct exposure of plants to the soil (or soil material) which is relevant for the real genotoxic potential and an exposure of plants to the water extract of the soil (or soil material). This last way of exposure to a leachate or an eluate allows the detection of the mutagens which are not adsorbed to soils and which may be transferred to aquatic compartments. Moreover, this test may be used to evaluate genotoxic effects of chemical substances and to waters, effluents, etc.

Soil quality - Assessment of genotoxic effects on higher plants - Vicia faba micronucleus test (ISO 29200:2013)

ICS
13.080.30
CCS
发布
2020-05-06
实施
2020-08-31

Provides guidance on the selection and conduct of appropriate test methods for the determination of biodegradation of organic chemicals in aerobic soils. Does not describe any specific test method.

Soil quality - Guidance on laboratory testing for biodegradation of organic chemicals in soil under aerobic conditions (ISO 11266:1994)

ICS
13.080.30
CCS
发布
2020-05-06
实施
2020-08-31

ISO 15685:2012 specifies a rapid method for the determination of the potential rate of ammonium oxidation and inhibition of nitrification in soils. This method is suitable for all soils containing a population of nitrifying microorganisms. It can be used as a rapid screening test for monitoring soil quality and quality of wastes, and is suitable for testing the effects of cultivation methods, chemical substances [except volatiles i.e. H > 1 (Henry's constant)], extracts of biosolids and pollution in soils.

Soil quality - Determination of potential nitrification and inhibition of nitrification - Rapid test by ammonium oxidation (ISO 15685:2012)

ICS
13.080.30
CCS
发布
2020-05-06
实施
2020-08-31



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