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1.
Three different types of chromosome 12 inversion were seen in 15 individuals out of 44 individuals examined in one 8 generation family. Type 1: a pericentric inversion inv(12) (p112; q131) was found in 7 individuals and twice at prenatal diagnosis. Type 2: a paracentric inversion inv(12) (p123; p131) was seen in two individuals. Two individuals carried both inversion chromosomes, namely type 1 and type 2. The two inversion chromosomes were transmitted from each of the parents. Type 3: a double pericentric and paracentric inversion (type 3) inv(12) (p123; p131) (p112; q131) was observed in the daughter of one of the carriers of type 1 and 2 inversions and again at prenatal diagnosis in her son. The double inversion most likely arose through crossing-over in between the two inversion loops. A balanced translocation t(7; 13) and the inversion type 1 was observed in one individual, who transmitted the translocation only to an offspring. The frequency of inversions in amniotic fluid cells observed in our laboratory was 1·9 per cent. The clinical implications of these findings are discussed. 相似文献
2.
Kerstin Holmgren 《Ambio》2014,43(1):19-29
Since the 1980s, Swedish lakes have in general become less acidified. Assessment of biological recovery is, however, hampered by poor pre-acidification data, confounding effects of climate change, and few lakes with annual sampling of fish and other organisms. Only three critically acidified, but non-limed, lakes had two decades of fish monitoring. The lakes had not yet recovered to pre-industrial chemical targets. Fish had low species richness compared to other organism groups. Roach (Rutilus rutilus) and/or European perch (Perca fluviatilis) were the dominant fish species, and the acid-sensitive roach had been lost from one of the lakes. Calcium decreased, possibly approaching pre-acidification concentrations, but exceeded minimum levels needed to sustain some Daphnia species. High or increasing levels of total organic carbon, likely due to reduced acidification and climate change, might influence the biological communities in unexpected ways, for example, facilitating more frequent occurrence of the invasive algae Gonyostomum semen. 相似文献
3.
Planet Earth has experienced repeated changes of its climate throughout time. Periods warmer than today as well as much colder, during glacial episodes, have alternated. In our time, rapid population growth with increased demand for natural resources and energy, has made society increasingly vulnerable to environmental changes, both natural and those caused by man; human activity is clearly affecting the radiation balance of the Earth. In the session “Climate Change and Mitigation” the speakers offered four different views on coal and CO2: the basis for life, but also a major hazard with impact on Earth’s climate. A common denominator in the presentations was that more than ever science and technology is required. We need not only understand the mechanisms for climate change and climate variability, we also need to identify means to remedy the anthropogenic influence on Earth’s climate. 相似文献
4.
Joke Muys Bettina Blaumeiser Yves Jacquemyn Claude Bandelier Nathalie Brison Saskia Bulk Patrizia Chiarappa Winnie Courtens Anne De Leener Marjan De Rademaeker Julie Désir Anne Destrée Koenraad Devriendt Annelies Dheedene Annelies Fieuw Erik Fransen Jean-Stéphane Gatot Philip Holmgren Mauricette Jamar Sandra Janssens Kathelijn Keymolen Damien Lederer Björn Menten Marije Meuwissen Benoit Parmentier Bruno Pichon Sonia Rombout Yves Sznajer Ann Van Den Bogaert Kris Van Den Bogaert Olivier Vanakker Joris Vermeesch Katrien Janssens 《黑龙江环境通报》2018,38(13):1120-1128
5.
Pienkoß Fabian Abis Marco Bruno Martina Grönholm Raul Hoppe Michel Kuchta Kerstin Fiore Silvia Simon Franz-Georg 《Journal of Material Cycles and Waste Management》2022,24(1):364-377
Journal of Material Cycles and Waste Management - This work is aimed at exploring the recovery of heavy metals from the fine fraction of solid waste incineration bottom ash. For this study,... 相似文献
6.
In the present study, endpoints including in vitro pollen performance (i.e., germination and tube growth) and lethality were used as assessments of nanotoxicity. Pollen was treated with 5-10 nm-sized Pd particles, similar to those released into the environment by catalytic car exhaust converters. Results showed Pd-nanoparticles altered kiwifruit pollen morphology and entered the grains more rapidly and to a greater extent than soluble Pd(II). At particulate Pd concentrations well below those of soluble Pd(II), pollen grains experienced rapid losses in endogenous calcium and pollen plasma membrane damage was induced. This resulted in severe inhibition and subsequent cessation of pollen tube emergence and elongation at particulate Pd concentrations as low as 0.4 mg L−1. Particulate Pd emissions related to automobile traffic have been increasing and are accumulating in the environment. This could seriously jeopardize in vivo pollen function, with impacts at an ecosystem level. 相似文献
7.
Background, Aim and Scope
Due to their large potential for manifold applications, the use of nanoparticles is of increasing importance. As large amounts
of nanoparticles may reach the environment voluntarily or by accident, attention should be paid on the potential impacts on
the environment. First studies on potential environmental effects of photocatalytic TiO2 nanoparticles have been performed
on the basis of widely accepted, standardized test systems which originally had been developed for the characterization of
chemicals. The methods were adapted to the special requirements of testing photocatalytic nanoparticles.
Materials and Methods:
Suspensions of two different nanoparticles were illuminated to induce their photocatalytic activity. For testing, the growth
inhibition test with the green alga Desmodesmus subspicatus and the immobilization test with the daphnid Daphnia magna were
selected and performed following the relevant guidelines (algae: ISO 8692, OECD 201, DIN 38412-33; daphnids: ISO 6341, OECD
202, DIN 38412-30). The guidelines were adapted to meet the special requirements for testing photocatalytic nanoparticles.
Results:
The results indicate that it is principally possible to determine the ecotoxicity of nanoparticles. It was shown that nanoparticles
may have ecotoxicological effects which depend on the nature of the particles. Both products tested differ in their toxicity.
Product 1 shows a clear concentration-effect curve in the test with algae (EC50: 44 mg/L). It could be proven that the observed
toxicity was not caused by accompanying contaminants, since the toxic effect was comparable for the cleaned and the commercially
available product. For product 2, no toxic effects were determined (maximum concentration: 50 mg/L). In the tests with daphnids,
toxicity was observed for both products, although the concentration effect-curves were less pronounced. The two products differed
in their toxicity; moreover, there was a difference in the toxicity of illuminated and non-illuminated products.
Discussion:
Both products differ in size and crystalline form, so that these parameters are assumed to contribute to the different toxicities.
The concentration-effect curves for daphnids, which are less-pronounced than the curves obtained for algae, may be due to
the different test organisms and/or the differing test designs. The increased toxicity of pre-illuminated particles in the
tests with daphnids demonstrates that the photocatalytic activity of nanoparticles lasts for a period of time.
Conclusions:
The following conclusions can be drawn from the test results: (I) It is principally possible to determine the ecotoxicity
of (photocatalytic) nanoparticles. Therefore, they can be assessed using methods comparable to the procedures applied for
assessing soluble chemicals. - (II) Nanoparticles may exert ecotoxicological effects, which depend on the specific nanoparticle.
- (III) Comparable to traditional chemicals, the ecotoxicity depends on the test organisms and their physiology. - (IV) The
photocatalytic activity of nanoparticles lasts for a relevant period of time. Therefore, pre-illumination may be sufficient
to detect a photocatalytic activity even by using test organisms which are not suitable for application in the pre-illumination-phase.
Recommendations and Perspectives:
First results are presented which indicate that the topic 'ecotoxicity and environmental effects of nanoparticles' should
not be neglected. In testing photocatalytic nanoparticles, there are still many topics that need clarification or improvement,
such as the cause for an observed toxicity, the improvement of the test design, the elaboration of a test battery and an assessment
strategy.
On the basis of optimized test systems, it will be possible to test nanoparticles systematically. If a potential risk by specific
photocatalytic particles is known, a risk-benefit analysis can be performed and, if required, risk reducing measures can be
taken. 相似文献
8.
9.