71
views
0
recommends
+1 Recommend
1 collections
    0
    shares
      • Record: found
      • Abstract: found
      • Article: not found

      Practical considerations for conducting ecotoxicity test methods with manufactured nanomaterials: what have we learnt so far?

      review-article

      Read this article at

      ScienceOpenPublisherPMC
      Bookmark
          There is no author summary for this article yet. Authors can add summaries to their articles on ScienceOpen to make them more accessible to a non-specialist audience.

          Abstract

          This review paper reports the consensus of a technical workshop hosted by the European network, NanoImpactNet (NIN). The workshop aimed to review the collective experience of working at the bench with manufactured nanomaterials (MNMs), and to recommend modifications to existing experimental methods and OECD protocols. Current procedures for cleaning glassware are appropriate for most MNMs, although interference with electrodes may occur. Maintaining exposure is more difficult with MNMs compared to conventional chemicals. A metal salt control is recommended for experiments with metallic MNMs that may release free metal ions. Dispersing agents should be avoided, but if they must be used, then natural or synthetic dispersing agents are possible, and dispersion controls essential. Time constraints and technology gaps indicate that full characterisation of test media during ecotoxicity tests is currently not practical. Details of electron microscopy, dark-field microscopy, a range of spectroscopic methods (EDX, XRD, XANES, EXAFS), light scattering techniques (DLS, SLS) and chromatography are discussed. The development of user-friendly software to predict particle behaviour in test media according to DLVO theory is in progress, and simple optical methods are available to estimate the settling behaviour of suspensions during experiments. However, for soil matrices such simple approaches may not be applicable. Alternatively, a Critical Body Residue approach may be taken in which body concentrations in organisms are related to effects, and toxicity thresholds derived. For microbial assays, the cell wall is a formidable barrier to MNMs and end points that rely on the test substance penetrating the cell may be insensitive. Instead assays based on the cell envelope should be developed for MNMs. In algal growth tests, the abiotic factors that promote particle aggregation in the media (e.g. ionic strength) are also important in providing nutrients, and manipulation of the media to control the dispersion may also inhibit growth. Controls to quantify shading effects, and precise details of lighting regimes, shaking or mixing should be reported in algal tests. Photosynthesis may be more sensitive than traditional growth end points for algae and plants. Tests with invertebrates should consider non-chemical toxicity from particle adherence to the organisms. The use of semi-static exposure methods with fish can reduce the logistical issues of waste water disposal and facilitate aspects of animal husbandry relevant to MMNs. There are concerns that the existing bioaccumulation tests are conceptually flawed for MNMs and that new test(s) are required. In vitro testing strategies, as exemplified by genotoxicity assays, can be modified for MNMs, but the risk of false negatives in some assays is highlighted. In conclusion, most protocols will require some modifications and recommendations are made to aid the researcher at the bench.

          Related collections

          Most cited references119

          • Record: found
          • Abstract: found
          • Article: not found

          The diversity and biogeography of soil bacterial communities.

          For centuries, biologists have studied patterns of plant and animal diversity at continental scales. Until recently, similar studies were impossible for microorganisms, arguably the most diverse and abundant group of organisms on Earth. Here, we present a continental-scale description of soil bacterial communities and the environmental factors influencing their biodiversity. We collected 98 soil samples from across North and South America and used a ribosomal DNA-fingerprinting method to compare bacterial community composition and diversity quantitatively across sites. Bacterial diversity was unrelated to site temperature, latitude, and other variables that typically predict plant and animal diversity, and community composition was largely independent of geographic distance. The diversity and richness of soil bacterial communities differed by ecosystem type, and these differences could largely be explained by soil pH (r(2) = 0.70 and r(2) = 0.58, respectively; P < 0.0001 in both cases). Bacterial diversity was highest in neutral soils and lower in acidic soils, with soils from the Peruvian Amazon the most acidic and least diverse in our study. Our results suggest that microbial biogeography is controlled primarily by edaphic variables and differs fundamentally from the biogeography of "macro" organisms.
            Bookmark
            • Record: found
            • Abstract: found
            • Article: not found

            Phytotoxicity of nanoparticles: inhibition of seed germination and root growth.

            Plants need to be included to develop a comprehensive toxicity profile for nanoparticles. Effects of five types of nanoparticles (multi-walled carbon nanotube, aluminum, alumina, zinc, and zinc oxide) on seed germination and root growth of six higher plant species (radish, rape, ryegrass, lettuce, corn, and cucumber) were investigated. Seed germination was not affected except for the inhibition of nanoscale zinc (nano-Zn) on ryegrass and zinc oxide (nano-ZnO) on corn at 2000 mg/L. Inhibition on root growth varied greatly among nanoparticles and plants. Suspensions of 2000 mg/L nano-Zn or nano-ZnO practically terminated root elongation of the tested plant species. Fifty percent inhibitory concentrations (IC50) of nano-Zn and nano-ZnO were estimated to be near 50mg/L for radish, and about 20mg/L for rape and ryegrass. The inhibition occurred during the seed incubation process rather than seed soaking stage. These results are significant in terms of use and disposal of engineered nanoparticles.
              Bookmark
              • Record: found
              • Abstract: found
              • Article: not found

              Environmental behavior and ecotoxicity of engineered nanoparticles to algae, plants, and fungi.

              Developments in nanotechnology are leading to a rapid proliferation of new materials that are likely to become a source of engineered nanoparticles (ENPs) to the environment, where their possible ecotoxicological impacts remain unknown. The surface properties of ENPs are of essential importance for their aggregation behavior, and thus for their mobility in aquatic and terrestrial systems and for their interactions with algae, plants and, fungi. Interactions of ENPs with natural organic matter have to be considered as well, as those will alter the ENPs aggregation behavior in surface waters or in soils. Cells of plants, algae, and fungi possess cell walls that constitute a primary site for interaction and a barrier for the entrance of ENPs. Mechanisms allowing ENPs to pass through cell walls and membranes are as yet poorly understood. Inside cells, ENPs might directly provoke alterations of membranes and other cell structures and molecules, as well as protective mechanisms. Indirect effects of ENPs depend on their chemical and physical properties and may include physical restraints (clogging effects), solubilization of toxic ENP compounds, or production of reactive oxygen species. Many questions regarding the bioavailability of ENPs, their uptake by algae, plants, and fungi and the toxicity mechanisms remain to be elucidated.
                Bookmark

                Author and article information

                Contributors
                +44-1752-584600 , rhandy@plymouth.ac.uk
                Journal
                Ecotoxicology
                Ecotoxicology
                Ecotoxicology (London, England)
                Springer US (Boston )
                0963-9292
                1573-3017
                16 March 2012
                16 March 2012
                May 2012
                : 21
                : 4
                : 933-972
                Affiliations
                [1 ]Ecotoxicology Research and Innovation Centre, School of Biomedical & Biological Sciences, University of Plymouth, Drake Circus, Plymouth, PL4 8AA UK
                [2 ]Alterra, Wageningen UR, Box 47, Wageningen, NL6700AA The Netherlands
                [3 ]U.S. Army Engineer Research & Development Center, Vicksburg, MS USA
                [4 ]Institute of Biological Sciences, TU Bergakademie Freiberg, Leipziger Str. 29, 09599 Freiberg, Germany
                [5 ]Eawag, Swiss Federal Institute of Aquatic Science and Technology, Dübendorf, Switzerland
                [6 ]Health Effects Laboratory, CEE, NILU (Norwegian Institute for Air Research), P.O. Box 100, 2027 Kjeller, Norway
                [7 ]The Slovak Medical University, Limbova 12, 83302 Bratislava, Slovakia
                [8 ]WCA Environment, Brunel House, Volunteer Way, Faringdon, SN7 7YR UK
                [9 ]Finnish Safety and Chemicals Agency, P.O. Box 66, 00521 Helsinki, Finland
                [10 ]School of Life Sciences, Heriot-Watt University, Edinburgh, EH14 4AS Scotland, UK
                [11 ]Institute for Work and Health, IST, Bugnon 21, 1011 Lausanne, Switzerland
                Article
                862
                10.1007/s10646-012-0862-y
                3325413
                22422174
                62d020ac-4524-4e40-89b5-0063201f3adb
                © Springer Science+Business Media, LLC 2012
                History
                : 28 January 2012
                Categories
                Article
                Custom metadata
                © Springer Science+Business Media, LLC 2012

                Toxicology
                bioaccumulation factor tests,aquatic tests,nanoparticle characterisation,oecd test method,gram positive bacteria,earthworm

                Comments

                Comment on this article

                scite_

                Similar content5

                Cited by43

                Most referenced authors1,600