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La catastrophe de Fukushima plus coûteuse que prévu

30 Août 2014,

Publié par Bioécologie

Dans la zone abandonnée de Fukushima (Japon, juin 2012)
Dans la zone abandonnée de Fukushima (Japon, juin 2012)

Un article de Philippe Mesmer (Tokyo, correspondance), Le Monde.fr | 30.08.2014 à 10h57 • Mis à jour le 30.08.2014 à 11h38

Combien aura coûté la catastrophe nucléaire de Fukushima ? Deux fois plus que prévu, selon Kenichi Oshima, de l’université Ritsumeikan (Kyoto) et Masafumi Yokemoto, de l’université d’Osaka. Selon les calculs dévoilés le 27 août par ces spécialistes de l’économie et des politiques environnementales, la facture de ce drame commencé en mars 2011 et dont la résolution doit prendre officiellement quarante ans dépassera les 11 000 milliards de yens (81 milliards d’euros). L’estimation officielle du gouvernement faite en décembre 2011 est de 5 800 milliards de yens (42 milliards d’euros).

Le professeur Oshima – ancien membre du comité consultatif du gouvernement sur les énergies renouvelables et l’énergie – et son collègue ne remettent pas en cause les calculs officiels. Ils les reprennent en ajoutant des coûts indirects, estimés selon des données de différentes administrations et de la Compagnie d’électricité de Tokyo (Tepco, responsable de la centrale endommagée).

DÉCONTAMINATION ET DÉDOMMAGEMENTS

Selon eux, les travaux nécessaires pour adapter les réacteurs aux nouvelles normes de sûreté, fixées en juillet 2013 en s’inspirant de la catastrophe de Fukushima, devraient coûter près de 2 200 milliards de yens (15 milliards d’euros). La décontamination des 2 400 km² – quasiment la taille du Luxembourg – de zones polluées aux substances radioactives reviendrait à 2 480 milliards de yens (18 milliards d’euros). Une somme complétée par 1 060 milliards de yens (7,7 milliards d’euros) pour le stockage temporaire des déchets générés par cette décontamination.

A cela pourraient s’ajouter 2 170 milliards de yens (15,8 milliards d’euros) pour démanteler la centrale sinistrée, ainsi que 4 910 milliards de yens (35,7 milliards d’euros) pour dédommager les victimes et les personnes ayant perdu leur emploi à cause de la catastrophe,.

Le professeur Oshima souligne par ailleurs que son estimation est un minimum car les coûts devraient encore augmenter. La hausse serait due au traitement des éléments radioactifs produits par le démantèlement des réacteurs endommagés et à l’évolution des dédommagements. Sur ce dernier point, aucune limite financière n’a été fixée.

Pour ces compensations, Tepco utilise l’argent d’un fonds spécial créé en septembre 2011, alimenté par le gouvernement et les autres compagnies d’électricité et qui restera en place après la résolution de la catastrophe de Fukushima. Ce fonds a vu son plafond de crédits disponibles relevé en décembre 2013 de 5 000 à 9 000 milliards de yens (36,4 à 65,6 milliards d’euros). Tepco doit rembourser l’argent utilisé, accordé sous forme de prêts sans intérêt.

RELANCE DU NUCLÉAIRE

L’entreprise n’a pas souhaité commenter l’étude du professeur Oshima. Le ministère de l’économie, du commerce et de l’industrie, qui s’occupe notamment de la promotion du nucléaire mais qui a officiellement perdu le contrôle de la sûreté après la catastrophe de Fukushima, n’y voit qu’une « étude parmi d’autres ».

La presse nippone est restée étonnamment silencieuse sur les annonces des deux chercheurs. Leurs travaux sont dévoilés alors que le gouvernement du premier ministre Shinzo Abe, soutenu par la principale fédération patronale, Keidanren, cherche à relancer les réacteurs nucléaires à l’arrêt. En avril, l’administration Abe a fait du nucléaire un « élément de base important de la production d’électricité ». En 2015, les autorités annonceront la part de l’atome dans la politique énergétique du Japon.

Lire la suite ici

Le chant d'espoir des rainettes

29 Août 2014,

Publié par Bioécologie

Un article de Marine Corniou - 04/08/2014

"...Cette petite grenouille, que l’on ne trouve au Canada que dans le sud du Québec et de l’Ontario, est gravement menacée. Ses effectifs sont en chute libre, surtout à cause de l’urbanisation et de l’agriculture intensive qui détruisent son habitat..."

La plateforme expérimentale O3HP

29 Août 2014,

Publié par Bioécologie

L’O3HP (Oak Observatory at OHP) est un observatoire pour étudier la dynamique, le fonctionnement et la biodiversité d’une forêt méditerranéenne face aux changements climatiques.

La nécessité de mieux comprendre le fonctionnement de la forêt méditerranéenne afin d’en prévoir les évolutions futures a conduit à l’élaboration d’un projet ambitieux concernant la forêt de Chêne pubescent, l’une des trois espèces phares de la région méditerranéenne française, couvrant plus de 250000 ha pour la seule région PACA.

Time For Change? Pollution has had an unexpected effect on natural evolution

25 Août 2014,

Publié par Bioécologie

Article by Heather Baldwin in Synapse (The Boston University Undergraduate Science Magazine)

 

Tomcod fish gain hereditary resistance to certain contaminants when exposed to high levels of pollution.   Wikimedia Commons | Credit H.B. Bigelow and W.C. Shroeder

Tomcod fish gain hereditary resistance to certain contaminants when exposed to high levels of pollution. Wikimedia Commons | Credit H.B. Bigelow and W.C. Shroeder

Evolution is a genetic process that shapes the behavior and appearance of species in a beneficial way as a result of long-term exposure to environmental stresses. Normally, the evolutionary process is very slow; the transformation of simple single-celled organisms into today’s complex species, including the human race, took thousands of years. Ironically, humans themselves have introduced an environmental pressure powerful enough to speed up the evolutionary clock: pollution. A recent study by Dr. Zhangpeng Yuan and his team at the New York University School of Medicine found that a population of tomcod fish in the Hudson River had been exposed to such chronically high levels of industrial pollution that they gained a heritable resistance to the damaging effects from the contaminants. Many other examples of drastic evolutionary genotypic and phenotypic changes have been observed over a relatively short period: decades, or even within generations – each in response to pollution. Are these “micro-evolutions” leading to beneficial adaptations, or are they a signal of severe harm to our ecosystem and ourselves?

Environment to Mutation

Illustration by Evan Caughey

Brown Squirrels, for example, have seen their primary habitat change from forests to landfills in the last 35 years.

Every known organism on Earth follows the central dogma of genetics: DNA (deoxyribonucleic acid) is transcribed to RNA, which is then translated into protein. DNA consists of a code of paired nucleotide bases, termed the genome of the organism. Messenger RNA uses this code to determine the sequence of amino acids that make up the protein corresponding to the particular gene being expressed. Proteins then directly affect the appearance and behavior, or phenotype, of the organism. Mutations may occur when DNA is altered by factors such as UV rays, chemicals, X rays, or radioactivity. Small-scale changes include disruption of the DNA double helix shape, incorrect combination (or dimerization) of adjacent nucleotides, and insertions/deletions of bases. Large-scale mutations involve the deletions, insertions, or translocations of entire parts of the chromosomes. Since evolution works at a genetic level, one individual’s mutation has the capability of affecting the entire species.

A major player in pollution-induced mutation is the benzopyrene class of compounds. These chemicals disrupt normal maintenance and expression of genetic information when metabolized by the liver. Their metabolites, benzoyprene epoxides, alter the expression of genes by inserting themselves into DNA and preventing replication and transcription.  Polycyclic Aromatic Hydrocarbons (PAHs) are an especially destructive class of benzopyrenes, formed from the partial combustion of organic compounds, such as wood, coal, plant matter, and animal fat. Therefore, power stations, transportation, and even cigarette smoke are the greatest culprits for the rising levels of these highly mutagenic and carcinogenic compounds.1

Mutation to Evolution

Mutations lead to evolution when an organism’s observable traits, or phenotype, change. For a particular mutation to lead to evolution, it must first cause a change in the organism’s observable traits, or phenotype. This most often occurs through an alteration of the DNA making up a particular gene. If the protein produced still functions normally, the mutation is considered “silent” and does not affect the organism. Not every beneficial trait within a particular organism will necessarily undergo selection. In order for the altered phenotype to be selected by evolution, it must also improve the fitness of the organism to its surroundings. Those with the new mutation must be able to survive to adulthood and reproduce more easily than the individuals without it. If the change is beneficial but does not affect the ability of the organism to have offspring, the amount of offspring with the mutation does not change, and no phenotypical change in the population will occur.

Evolution of a particular trait requires lengthy exposure to a persistent environmental stressor, such as changing climate or resource availability. Micro-evolution can occur over a relatively short time in areas where pollution is persistent or inescapable.  A species can develop resistance to a highly or consistently polluted environment through one of two paths. The first option is physiologic acclimation without a genetic basis. This physiological change cannot be inherited by the offspring, and is lost after the organism is no longer exposed to the particular stressor. The second path is through the genetic adaptation of resistance resulting from long-term exposure, and can be inherited by the offspring.2

Examples of Species Undergoing Evolution Induced by Pollution

Micro-evolution occurs most frequently in marine species. This is most likely due to limited mobility and habitat isolation that prevents the organisms from avoiding the pollution. The tomcod of the Hudson River have high mobility, but cannot escape the contamination spread throughout their habitat. The Hudson River contains historically high levels of PAHs, including polychlorinated biphenyls (PCBs) and 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin (TCCD).  Effects of PAHs include DNA damage, hepatic neoplasms (epithelial carcinoma), birth defects, and increased early mortality.3 The tomcod population has evolved a genetic adaption that prevents the harmful effects of the polluting substances through a single mutation of the CYP1A gene.3 The CYP1A protein is involved in xenobiotic (foreign chemical) and drug metabolism.4 Only benzopyrene metabolites are harmful to DNA, resulting in toxic and carcinogenic effects on the organism. If the organism can slow its metabolism, then the effects of benzopyrene epoxides on the organism’s health slow as well.

Tawny Owls have evolved to carry a dominant brown coloration trait due to climate change. Previously, gray colored plumage was the dominant expression.  Wikimedia Commons | Credit K.M. Hansche

Tawny Owls have evolved to carry a dominant brown coloration trait due to climate change. Previously, gray colored plumage was the dominant expression. Wikimedia Commons | Credit K.M. Hansche

The CYP1A mutation has been positively selected because it leads to reduced inducibility of CYP1A, therefore preventing the harmful consequences described above by slowing the metabolism of chemicals such as benzopyrenes. Z. Yuan and his team proved that this newly developed resistance to PAHs in a high proportion of the tomcod Hudson River population is heritable. He found a reduced induction of CYP1A in offspring of mutated fish that were raised in a pollution-free laboratory setting.3 In a similar study, mummichog killifish also known as “mud minnows” or “mummies,” were collected from several highly polluted sites in Massachusetts, New Jersey, and Virginia. The mummichog were found to have resistance to PAHs via the reduced sensitivity of the CYP1A gene.5 These fish also have high reproductive potential and are restricted to travel within limited areas, which are favorable conditions for the selection of a particular phenotype.

Species undergoing pollution-induced evolution are not restricted to marine habitats. An interesting example of this phenomenon has occurred due to a major consequence of pollution: global warming. Tawny owls in Finland are adapting to the gradual climate change. Naturally, the dominant color of tawny owls is grey, whereas brown owls had been associated with higher mortality rates in the winter due to lack of camouflage. Yet as winters have become warmer, the snow has become less of an evolutionary pressure, which allows for the elevated presence of brown owls.6 Therefore, as the temperature increases as a result of humans’ destruction of the ozone layer, so does the ratio of brown owls to the previously dominant grey owls.

The Negative Effects of Genetic Mutations

There are often physical trade-offs that work against the fitness of the mutated organism. Gene mutations that help prevent harmful effects of an environment seem like a beneficial act of nature; these species can now protect themselves from the damaging man-made substances now present in their habitats. However, many studies of these micro-evolution events have shown that this may not be the case. When such rapid evolutionary changes occur, there are often physical trade-offs that work against the fitness of the mutated organism. For instance, the organism may suffer an increased sensitivity to other environmental stressors.3 Moreover, once the particular substance that the mutation protects against is removed, the organism’s overall functioning diminishes. If the fitness of the organism is so low that it cannot reproduce, the entire population could undergo genetic change. When the pollution was present, the non-mutated organisms without resistance were selected against, ultimately leading to a decrease in the population of the wild type phenotype. If the pollution is finally removed, the mutated offspring are now being selected against. This can result in drastic changes in both the genetics and size of the population.

The dramatic effects of pollution on the genetic diversity of certain species change the overall biodiversity of our ecological environment. But what about humans? As the highest level of the food chain, we are susceptible to the effects of contaminant transfer from prey to predator. If a prey species (such as the tomcod), is resistant to pollution, a higher level of contaminants will be observed at higher feeding levels, even if the predator is not subject to the same pollutant stress.3 Ethics prevents the controlled study of the pollution’s direct effects on humans. There have been no reported cases of micro-evolution as a result of a pollutant in mammals in a natural setting.

On the other hand, studies have demonstrated pollution’s effect on the genome of mammals and their offspring. Somers, of the department of Biology at McMaster University; Yauk, of Health Canada; and fellow scientists found that PAHs present in the air can also induce heritable mutations. Mice exposed to the air within an integrated steel mill had much higher expanded simple tandem repeat (ESTR) germline mutation rates than mice exposed to a rural environment. The ESTR loci are especially susceptible to genetic mutation and are therefore reliable tools for measuring the mutating ability of contamination. The study also found that the ESTR mutations were passed on to laboratory-reared offspring of the exposed mice. Interestingly, only the paternal mice had a significant mutation rate (the maternal mutation rate was only slightly elevated). How does this study apply to the human population? There are many humans living or working near steel mills. Steelworkers who are exposed to PAHs are susceptible to mutations and can pass on these mutations on to their children.7 The direct impact of repetitive DNA mutations (such as ESTR) in humans is unknown, but certainly have the potential to change coding genes (and thus possibly the phenotype) through alteration of DNA replication and repair.

Consequences for Ourselves and Our Natural World

Humans have an advantage over other species. As previously noted, there are no human case studies of micro-evolution due to pollution. Humans have an advantage over other species; not only are we highly mobile, but our habitats are not nearly as restricting and our generations are much longer. Humans, especially recently, also have the ability to identify sources of pollution and are learning to avoid them. Humans may be able to undergo evolutionary changes similar to other mammals. According to the “fireside hypothesis,” when early human populations migrated from Africa, certain groups (those that migrated to colder climates) were exposed to fire earlier than others. Epidemiologic studies have shown that the incidence of lung cancer is inversely proportional to the reliance on fire in different geographic populations during human evolution.8 This theory is backed by multiple studies that found certain polymorphisms present in cytochrome p450 and other liver drug-metabolizing enzyme genes in humans can influence susceptibility of lung cancer.9

However, this hypothesis is not nearly the same as the cases of evolution of pollution resistance being discovered now. First of all, the time and strength of the exposure is a stark contrast to the other cases. The affected populations of the recent evolution involve persistent, severe amounts of pollution within decades. In the case of the fireside hypothesis, the exposure was progressive and much less powerful, resulting in a much longer time scale. Although this case of human evolution was certainly beneficial to the health of those who gained resistance, the current cases of micro-evolution may be considered harmful in the long-term, despite the short-term benefits.

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Pielago

20 Août 2014,

Publié par Bioécologie

Una pelicula de Raffa Herrero Massieu.

El alma del océano, una vasta extensión de mar de más de un billón de kilómetros cúbicos de agua. Un mundo oculto con una vida sorprendente de la que apenas conocemos algo.

The soul of the ocean, a vast area of sea with more than one billion cubic kilometers of water. A hidden world with a surprising life that we hardly know.

La tache de Darwin, voyage dans la diversité des formes animales

14 Août 2014,

Publié par Bioécologie

La tache de Darwin, voyage dans la diversité des formes animales

Ce webdocumentaire du journal Le Monde mêle textes, explications sonores, photographies et vidéos. On y suivra les recherches de Nicolas Gompel et Benjamin Prud’homme, qui travaillent sur les bases génétiques déterminant l’incroyable diversité des formes du vivant.

PhD Student: Evolution of colour signals in lizards

10 Août 2014,

Publié par Bioécologie

The Lizard lab (Australia): "We are looking for a PhD student interested in studying the evolution of colour signals in lizards. The overarching aim of the project is to study adaptive co-variation across and between lizard colour patterns/signals in relation to socio-ecological factors (e.g. mating system, environmental conditions) and individual traits (e.g. age, sex, size, competitive ability, health or social status), and in a phylogenetic context. Among the specific aims of this project is to address some poorly understood questions in the evolution of animal colour signals. For example, this project will explore whether social and ecological factors affect the evolution of signal reliability, and whether different color-producing mechanisms place different constraints on the evolution of chromatic signal honesty and reliability.

The research project involves extensive fieldwork in Europe (Mediterranean basin) and potentially in Australia. The student will be mainly based at Macquarie University, Sydney but, conducting field/experimental work in Europe while based at the Cavanilles Institute of Biodiversity and Evolutionary Biology (University of Valencia, Spain). The PhD will be co-supervised by Dr. Martin Whiting (Macquarie University, Sydney) and Dr. Pau Carazo (currently at the University of Oxford but moving to the University of Valencia before the beginning of this PhD), with the possibility of obtaining a joint PhD from both Universities.

For further information, please contact Martin Whiting (Macquarie University; martin.whiting@mq.edu.au) and/or Pau Carazo (University of Oxford; pau.carazoferrandis@zoo.ox.ac.uk)."

More information here