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Myriophyllum sibiricum
Automaticky přeložený název:
Standardní Příručka pro vedení statické, Axenic , 14-denní testy fytotoxicity ve zkumavkách s ponořená vodní makrofyt , Myriophyllum sibiricum Komarov (Withdrawn 2012 )
NORMA vydána dne 1.9.2012
Označení normy: ASTM E1913-04(2012)
Poznámka: NEPLATNÁ
Datum vydání normy: 1.9.2012
Kód zboží: NS-43544
Počet stran: 15
Přibližná hmotnost: 45 g (0.10 liber)
Země: Americká technická norma
Kategorie: Technické normy ASTM
Keywords:
aquatic toxicity testing, Myriophyllum sibiricum, phytotoxicity test, submersed aquatic macrophyte, ICS Number Code 13.060.70 (Examination of water for biological properties)
Significance and Use | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
5.1 Protection of aquatic areas is currently being emphasized by several agencies including the U.S. Environmental Protection Agency and Environment Canada. For pesticide registration, these agencies are beginning to require data regarding the toxicity of test chemicals to aquatic rooted vascular plants 5.2 Toxicological research with terrestrial and aquatic vascular plants has been initiated 5.3 This guide is designed to assess the phytotoxic effects of chemicals upon a selected freshwater species of submersed aquatic macrophyte, Myriophyllum sibiricum Komarov. This species is an ecologically important submersed aquatic dicotyledon with a north temperate distribution. It is readily cultured in test tubes in the laboratory (36). Lower temperatures in autumn initiate the formation of turions on lateral branches that develop into new plants when environmental conditions become favorable 5.4 It is a common practice to use sterile plant culture when testing the direct effects of test materials upon a plant species. Sterile plant culture and toxicity testing have been conducted with algae (Practice D3978, 5.5 There are numerous possible physiological and morphological endpoints that can be utilized to assess the toxicity of chemicals to this aquatic plant species. The test material effect may be assessed as a change in total plant height, growth rate, fresh or dry weight, number and total length of roots, chlorophyll a, chlorophyll 5.6 This toxicity test may be utilized during the pesticide registration process, to provide an early warning of potential ecosystem problems, identify hazardous chemicals before contamination of aquatic systems occurs, and help establish “margins of safety” for specific chemicals within wetlands (see Guide E1023). Plants cultured using this method have also been used to determine the effects of toxicants on plants in microcosms 5.7 This test is not designed to replace field assessments of test material damage or other aquatic testing procedures, but should be used as a screening tool. It should compliment other testing so that a more complete environmental assessment is possible. It is difficult to interpret effects observed in the lab in reference to those that could be found in the environment. Currently, there is a need for additional field data to validate the results obtained in laboratory plant toxicity tests. Since this toxicity test can detect non-lethal physiological endpoints as well as morphological changes, this toxicity test could act as an early warning system for possible environmental effects. If effects are noted in this toxicity test, it could indicate that further lab and field testing may be required. |
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1. Scope | ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
1.1 Submersed rooted aquatic macrophytes are important components of aquatic systems. They contribute to primary productivity, improve water quality, cycle nutrients, generate oxygen, affect flow patterns, provide habitat and food for other organisms, and stabilize the sediment. These plants can be adversely affected when pesticides are sprayed to control aquatic weeds and algal blooms or when phytotoxic chemicals enter the waterway through atmospheric fallout, soil erosion, industrial effluent, sewage discharge, spills or drift from aerial or ground applications. 1.2 This guide is designed to give guidance for assessing the potential phytotoxicity of a test material added to a sterile liquid growth medium on a species of freshwater submersed macrophyte (Myriophyllum sibiricum Komarov) during a 14-day static exposure. A sterile system is recommended to determine the direct effect of the test chemical upon individual parameters of the submersed macrophyte because there is no degradation of the test item by micro-organisms. For similar reasons, other aquatic plant testing, such as those of, Lemna and algae, is commonly conducted in an axenic fashion. Overall environmental impact can not be directly determined. The main other disadvantage of the axenic test system is the difficulty in preventing accidental contamination. These procedures could possibly be useful for conducting toxicity tests with other species of submersed macrophytes, although modifications might be necessary (1-8)2. 1.3 The procedures in this guide are applicable to most chemicals, either individually or in formulations, commercial products, or known mixtures. These procedures might be used to conduct tests for dependency on temperature, light, nutrients and pH. With appropriate modification, these procedures might be used to conduct tests for contaminated surface waters and aqueous effluents (see Guide E1192). This static, axenic toxicity test might not be applicable to materials that contain microorganisms unless the sample can be filter sterilized without removing the toxicant. If the test materials are highly volatile, care should be taken to ensure that the test chambers are isolated. It might be necessary to replace the test material on a regular basis if the test material is rapidly biologically or chemically transformed in aqueous solution, or is removed from the test solutions in substantial quantities by the test chambers or organisms during the test. This toxicity test is not suitable for testing interactions between aquatic plants and other organisms, such as plant pathogens. 1.4 Results from the toxicity test outlined in this guide can be reported in terms of a 14-day IC25, IC50, or NOEC. This parameter may be based on several endpoints including inhibition of plant growth during the 14-day period, inhibition of shoot length, inhibition of root number and length, inhibition of fresh or dry weight (see Guide E1415), inhibition of oxygen production, change in membrane permeability, and change in chlorophyll a, chlorophyll 1.5 This guide is arranged as follows:
1.6 The values stated in SI units are to be regarded as the standard. 1.7 This standard does not
purport to address all of the safety concerns, if any, associated
with its use. It is the responsibility of the user of this standard
to establish appropriate safety and health practices and determine
the applicability of regulatory limitations prior to use.
Standard Terminology Relating to Water
(Includes all amendments and changes 2/14/2024). Standard Guide for Conducting Static
Toxicity Tests With Lemna gibba G3 Standard Practice for Statistical
Analysis of Toxicity Tests Conducted Under ASTM Guidelines Standard Guide for Conducting Renewal
Phytotoxicity Tests With Freshwater Emergent Macrophytes Standard Guide for Conducting Static
Toxicity Tests with Microalgae Standard Guide for Conducting Acute
Toxicity Tests on Aqueous Ambient Samples and Effluents with
Fishes, Macroinvertebrates, and Amphibians Standard Guide for Assessing the Hazard
of a Material to Aquatic Organisms and Their Uses Standard Terminology Relating to
Biological Effects and Environmental Fate Standard Specification for Reagent
Water Standard Practices for Measurement of
Chlorophyll Content of Algae in Surface Waters Standard Practice for Conducting Early
Seedling Growth Tests (Withdrawn 2003) Standard Guide for Conducting Acute
Toxicity Tests on Test Materials with Fishes, Macroinvertebrates,
and Amphibians (Includes all amendments and changes 2/22/2023). Standard Practice for Algal Growth
Potential Testing with Pseudokirchneriella subcapitata (Includes
all amendments and changes 1/20/2022). Standard Guide for Use of Lighting in
Laboratory Testing |
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