TEPCO may have located melted fuel for 1st time at Fukushima plant
Tokyo Electric Power Co. said Jan. 30 it may have finally pinpointed the location of melted fuel at the Fukushima No. 1 nuclear plant, nearly six years after the triple meltdown unfolded there.
If confirmation is made, it would represent a breakthrough in the daunting task of decommissioning the stricken nuclear plant.

A remote-controlled camera fitted on a long pipe detected black lumps on grating in the lower part of the containment vessel of the No. 2 reactor at the plant early on Jan. 30, TEPCO said.
The wire-mesh grating is located below the pressure vessel of the reactor. The lumps were not there before the Great East Japan Earthquake and tsunami on March 11, 2011, caused the nuclear disaster, according to TEPCO.

The utility plans to determine whether the lump is melted fuel based on images and radiation levels taken by an investigative robot and other data. The robot, called “Sasori” (scorpion) and fitted with two cameras, a dosimeter and a temperature gauge, will be sent into the No. 2 reactor containment vessel next month.

High radiation levels have hampered efforts at the nuclear plant to determine the condition and location of melted nuclear fuel.
TEPCO tried–and failed–three times to locate melted fuel using an industrial endoscope at the No. 2 reactor.
The latest investigation inside the No. 2 reactor began on Jan. 26 to locate the melted fuel.
The company is preparing to devise a method to retrieve the melted fuel in fiscal 2018 as part of the decommissioning work.
http://www.asahi.com/ajw/articles/AJ201701300058.html
The image shows what is believed to be the remains of melted nuclear fuel that seeped through the grating below the pressure vessel of the No. 2 reactor at the Fukushima No. 1 nuclear power plant. (Provided by Tokyo Electric Power Co.)
TEPCO reinserts camera in Fukushima reactor 2

What appears to be rust is seen on a foothold inside the containment vessel of the No. 2 reactor at the Fukushima No. 1 nuclear plant in this image provided by Tokyo Electric Power Co.
TEPCO reinserts camera in Fukushima reactor
TEPCO, the operator of the damaged Fukushima Daiichi nuclear plant, has again begun using a camera probe inside the containment vessel of the No. 2 reactor.
Taking pictures of the molten fuel inside is regarded as an important step towards decommissioning the reactors that melted down.
On Tuesday, workers at the plant tried to insert a camera into a pipe leading into the containment vessel.
But the camera got stuck in the pipe’s opening. The rubber, which had shrunk due to cold, blocked it.
In a second attempt on Thursday, workers tried to push the camera into the pipe while warming the rubber with thermal material. They were successful.
Footage from the camera shows a black substance adhering to the surface of metal rails in the vessel. The rails will be used as tracks for a robot to do a survey in February.
TEPCO expects the camera may capture footage of molten fuel for the first time since the 2011 meltdown
https://www3.nhk.or.jp/nhkworld/en/news/20170126_31/
TEPCO begins taking video inside Fukushima No. 1 nuke plant reactor
Tokyo Electric Power Co. (TEPCO) began work on Jan. 26 to take video inside the No. 2 reactor at its tsunami-hit Fukushima No. 1 nuclear plant, company officials said.
A camera attached to the tip of a pipe was inserted into the reactor containment vessel to shoot video inside of the vessel to check the condition of the melted fuel within. It was also done in preparation for sending in a camera-equipped robot to get a closer look at conditions. The robot will follow 7.2-meter-long rails leading to an area just below the reactor’s pressure vessel.
Video released by TEPCO on Jan. 26 shows dripping liquid and what appears to be steam drifting inside the containment vessel. What looks like rust is seen on a foothold and the rails, but nothing that could block the robot has been found.
TEPCO is poised to use a longer pipe to check if there is any obstacle inside the reactor next week and beyond. Company officials said the firm may be able to photograph the melted fuel.
http://mainichi.jp/english/articles/20170127/p2a/00m/0na/002000c
Plans to remove nuclear fuel at Fukushima N° 3 reactor delayed again

A member of the media, wearing a protective suit and a mask, looks at the No. 3 reactor building at Tokyo Electric Power Co’s (TEPCO) tsunami-crippled Fukushima Daiichi nuclear power plant in Okuma town, Fukushima prefecture, Japan February 10, 2016.
A plan to remove spent nuclear fuel from Tokyo Electric Power Co Holdings Inc’s Fukushima Daiichi nuclear plant hit by the March 2011 tsunami has been postponed again due to delays in preparation, the Nikkei business daily reported on Thursday.
Work is now set to begin in fiscal 2018 at the earliest, the Nikkei said.
Removal of the spent fuel from the No. 3 reactor was originally scheduled in the first half of fiscal 2015, and later revised to fiscal 2017 due to high levels of radioactivity around the facilities, the Japanese business daily reported.
The timeline has been changed again as it was taking longer than expected to decontaminate buildings and clean up debris, the news agency reported.
The report comes a few months after the Japanese government said in October the cost of cleaning up the Fukushima plant may rise to several billion dollars a year, adding that it would look into a possible separation of the nuclear business from the utility.
http://uk.reuters.com/article/uk-japan-fukushima-idUKKBN1592WI
Fukushima camera probe hits a snag
Workers attempting to get a better look inside a damaged reactor at the Fukushima Daiichi nuclear power plant have encountered a problem.
On Tuesday they inserted a camera in a pipe leading into the container vessel of the No. 2 reactor, with the aim of capturing footage of molten fuel inside.

But plant operator Tokyo Electric Power Company says the camera, which is marginally smaller than the pipe, quickly became stuck.
TEPCO says a simulated trial run went off without a hitch. The utility will investigate what went wrong before deciding whether to try again.
Workers need a clearer picture of the debris to determine how best to remove it, an important step in the decommissioning process for the 3 reactors that suffered meltdowns.
Did Fukushima Daiichi Cause Cancer in Children and Plant Workers?

Here is the latest update on news about Fukushima children’s thyroid cancer rate and cancer among workers at the plant:
10 more thyroid cancer cases diagnosed in Fukushima. The Mainichi, December 28, 2016 (Mainichi Japan) http://mainichi.jp/english/articles/20161228/p2a/00m/0na/008000c
FUKUSHIMA — Ten more people were diagnosed with thyroid cancer as of late September this year in the second round of a health survey of Fukushima Prefecture residents, which began in April 2014, a committee overseeing the survey disclosed on Dec. 27. The number of people confirmed to have cancer during the second round of the survey stands at 44, while the overall figure including cases detected in the first round stands at 145.
… Some have pointed to the danger of “excessive diagnoses” during health checks in which doctors find cases of cancer that do not require surgery, which could place a physical and mental burden on patients. There have accordingly been calls for the Fukushima Prefectural Government to scale down the scope of its health survey.
Plant worker’s thyroid cancer certified as linked to nuclear disaster. The Mainchi, December 17, 2016 (Mainichi Japan) http://mainichi.jp/english/articles/20161217/p2g/00m/0dm/025000c
TOKYO (Kyodo) — A worker exposed to radiation when disaster struck the Fukushima nuclear plant has been found to have developed thyroid cancer caused by an industrial accident, the labor ministry said Friday.
The employee of Tokyo Electric Power Company Holdings Inc., the operator of the Fukushima Daiichi nuclear power plant, is the third person determined to be entitled to benefits due to illness caused by exposure to radiation released when three reactors melted down in the days after a massive earthquake and ensuing tsunami in March 2011.
The man is the first to be certified for developing thyroid cancer because of the nuclear disaster. The first two persons suffer from leukemia.
Here is some BACKGROUND ON THE DEBATES ABOUT FUKUSHIMA EFFECTS ON CHILDREN IN JAPAN excerpted from my book, Crisis Communication, Liberal Democracy and Ecological Sustainability
…Children are likely at greatest risk for health consequences from exposure because they are biologically more vulnerable to radiation since their cells are dividing faster. The thyroid is particularly susceptible to radiation-induced damage because it bioaccumulates radioactive iodine. People with thyroid conditions have an increased risk of dying because of damage that occurs prior to treatment.[i]
Potassium iodide helps block absorption of radioactive iodine but as mentioned earlier in the chapter, distribution was delayed. Consequently, many children in Japan became internally contaminated with radioiodine, in addition to whatever other radionuclides internalized through inhalation and ingestion.
July 6, 2011 the Japanese press Kyodo reported that in a March 2011 survey of 1,080 children aged 0 to 15 in Iwaki, Kawamata, and Iitate 45 percent of kids in Fukushima survey had thyroid exposure to radiation.[ii]
A separate study measuring thyroid exposure to Iodine-131 conducted between April 12, 2011 and April 16, 2011 and published in Research Reports found “extensive measurements of the exposure to I-131 revealing I-131 activity in the thyroid of 46 out of the 62 residents and evacuees measured”[iii]
In August of 2011, NHK reported that Japan’s nuclear commission had erased children’s exposure data derived from a test of 1,000 children aged 15 or younger who had been screened for radiation affecting their thyroid.[iv] By February of 2014, there were 75 confirmed or suspected thyroid cancer cases among 270,000 Fukushima Prefecture individuals screened, who were 18 or under at the time of the disaster.[v]
The screening committee claimed the Fukushima disaster was an unlikely cause.[vi] However, the observed frequency of thyroid cancer and nodules exceeds established incident rates. For example, the prevalence of thyroid nodules in children typically ranges from 0.2-5.0 percent,[vii] while in Fukushima, 42 percent of 133,000 children were found to have thyroid nodules and cysts two years after the disaster.[viii]
In 2015 two research articles were published arguing that the rate of thyroid cancer among Fukushima children was excessive.
The first study noted that the surge of thyroid cancers detected among 370,000 Fukushima residents aged 18 or younger was “unlikely to be explained by a screening surge” given the incident rate was found to be 20 to 50 times the national average at the close of 2014.[ix]
The second study observed that the rate of thyroid cancer being detected in Fukushima’s children exceeded the rate found after Chernobyl.[x] However, Shoichiro Tsugane, Director of the Research Center for Cancer Prevention and Screening, asserted that “Unless radiation exposure data are checked, any specific relationship between a cancer incidence and radiation cannot be identified,” and noted there exists a “global trend of over-diagnosis of thyroid cancer….”[xi]
Fukushima Prefecture residents’ concerns about living in a radiation-contaminated zone are too often trivialized by government officials. In 2015, evacuees from Naraha located in Fukushima Prefecture challenged a government official who described their concerns about drinking water contamination as a “psychological issue” after the Ministry of Education reported up to 18,7000 Becquerels of radioactive cesium per kilogram of soil taken from the bottom of a reservoir at Kido Dam which serves as the community’s drinking water source.[xii]
Dr. Shunichi Yamashita of Japan’s Atomic Bomb Research Institute produced widespread outrage for claiming that radiation does not harm people who are happy and that there is little risk from annual exposure levels below under 100 millisieverts.[xiii]
[i] Anne Laulund, Mads Nybo, Thomas Brix, Bo Abrahamsen, Henrik Løvendahl Jørgensen, Laszlo Hegedüs, “Duration of Thyroid Dysfunction Correlates with All-Cause Mortality. The OPENTHYRO Register Cohort,” PLOS, 9.10(2014): 1-8, e110437-110 DOI: 10.1371/journal.pone.0110437.
[ii] “45% of kids in Fukushima survey had thyroid exposure to radiation,” The Mainichi (July 5, 2011): http://mdn.mainichi.jp/mdnnews/news/20110705p2g00m0dm079000c.html.
[iii] Shinji Tokonami, Masahiro Hosoda, Suminori Akiba, Atsuyuk Sorimachi, Ikuo Kashiwakura, and Mikhail Balonov “Thyroid doses for evacuees from the Fukushima nuclear accident.” Scientific Reports, 2(507)(2012): 1. doi:10.1038/srep00507.
[iv] “Nuclear Commission erases children’s exposure data,” NHK (August 11, 2011). http://www3.nhk.or.jp/daily/english/11_14.html.
[v] Nose, T., & Oiwa, Y. (2014, February 8). Thyroid cancer cases increase among young people in Fukushima. The Asahi Shimbun. Available: http://ajw.asahi.com/article/0311disaster/fukushima/AJ201402080047
[vi] “Eight more Fukushima kids found with thyroid cancer; disaster link denied,” The Japan Times (February 7, 2014): http://www.japantimes.co.jp/news/2014/02/07/national/eight-more-fukushima-kids-found-with-thyroid-cancer-disaster-link-denied/#.U2Zvr61dVXo
[vii] Gerber, M. E., Reilly, B. K., Bhayani, M. K., Faust, R. A., Talavera, F., Sadeghi, N. & Meyers, A. D. “Pediatric thyroid cancer,” Emedicine. (2013): http://emedicine.medscape.com.ezproxy1.lib.asu.edu/article/853737-overview.
[viii] Haworth, A. (2013, February 23). After Fukushima: Families on edge of meltdown. The Guardian. Available http://www.theguardian.com/environment/2013/feb/24/divorce-after-fukushima-nuclear-disaster.
[ix] Toshihide Tsuda, Akiko Tokinobu, Eiji Yamamoto and Etsuji Suzuki, “Thyroid Cancer Detection by Ultrasound Among Residents Ages 18 Years and Younger in Fukushima Japan: 2011 to 2014,” Epidemiology (2015), 1-7.
[x] Shigenobu Nagataki and Takamura, Noboru, “A review of the Fukushima nuclear reactor accident: radiation effects on the thyroid and strategies for prevention. Current Opinion in Endocrinology, Diabetes & Obesity, 21.5 (October 2014): 384–393. doi: 10.1097/MED.0000000000000098, available http://journals.lww.com/co-endocrinology/pages/articleviewer.aspx?year=2014&issue=10000&article=00012&type=abstract.
[xi] “New Report Links Thyroid Cancer Rise to Fukushima Nuclear Crisis,” The Japan Times, Oct 7, 2015, accessed October 8, 2015, available http://www.japantimes.co.jp/news/2015/10/07/national/science-health/new-report-links-thyroid-cancer-rise-fukushima-nuclear-crisis/#.VhU3aCtBmFt
[xii] “Fukushima town residents protest official’s comment about radiation safety,” The Mainichi (July 7 2015). Date accessed July 8, 2015. Available: http://mainichi.jp/english/english/newsselect/news/20150707p2a00m0na019000c.htm.
[xiii] ‘Studying the Fukushima Aftermath: “People Are Suffering from Radiophobia”’ (19 August 2011), Der Spiegel, http://www.spiegel.de/international/world/0,1518,780810,00.html, date accessed 4 September 2011.
http://majiasblog.blogspot.fr/2017/01/did-fukushima-daiichi-cause-cancer-in.html
AMS analyses of I-129 from the Fukushima Daiichi nuclear accident in the Pacific Ocean waters of the Coast La Jolla – San Diego, USA April 2015
It is very convenient for the nuclear industry to focus only on Cesium 137 and omit talking about all the other radionuclides released in our environment thanks to the Fukushima Daiichi nuclear disaster. Though less detectable and usually not looked for they are nevertheless present and harmful to life. This study from April 2015 about the Iodine-129 release is quite revealing, knowing that if Iodine-129 half life is 15,7 Million years, its full life is multiplied by 10: 157 million years.
Royal Society of Chemistry, National Institute for Physics & Nuclear Engineering, Romania, 2015:
AMS analyses of I-129 from the Fukushima Daiichi nuclear accident in the Pacific Ocean waters of the Coast La Jolla, San Diego, USA — This paper presents the results of an experimental study we performed by using the Accelerator Mass Spectrometry (AMS) method with iodine 129 (Halflife = 15.7 Million years], to determine the increase of the radionuclide content in the USA West Pacific Coast waters, two years after the March 2011 Fukushima Daiichi nuclear power plant accident… The results of the experiments showed a significant increase of the radionuclide concentration during the late spring of 2013. Compared to the isotopic ratio 129I/127I, measured at a 40 km distance, offshore of Fukushima and immediately after the accident, our results show an increase on the USA West Coast that was more than a 2.5 factor higher. Also, compared with the pre-Fukushima background values [in San Diego], our results show an isotopic ratio of about two orders of magnitude higher…
The Fukushima Daiichi nuclear power plant… released an enormous amount of liquid waste of 129I and other fission isotopes directly into the Pacific Ocean that were subsequently dispersed eastwards. This paper reports on the determination of the nuclear plume impact on the West Coast of the USA that happened during April–July 2013… The determined maximum 129I concentration increase was in an amount of more than 2 times greater than the concentration of the isotope measured offshore of Fukushima at a 40 km distance immediately after the accident…

129I concentrations were measured… from the ocean water of the West Coast of the USA [at] La Jolla, San Diego… This work reports two sudden increases of the 129I/127I isotopic concentration in the ocean water, which were observed at the end of spring 2013…
Our exploratory measurements on the USA West Coast started on samples collected at the beginning of 2013. The lowest 129I concentrations that we measured had values between [6-20 million] atoms per L. Such values correspond to the equilibrium concentration of iodine… offshore of La Jolla, San Diego…
Our results… measured offshore of Cove La Jolla, San Diego, USA, during the spring of 2013, are presented in Fig. 5. Two high and distinct spike maxima are visible. They reveal the maximum concentration values of [1.2 billion] atoms per L measured on May 24, 2013 and [1.7 billion] atoms per L measured on June 18, 2013, with 24 days in between. Both peaks occurred in the measurement spectrum after a slow increase in concentration that started about 15-20 days before the main increase…

Samples collected [by Fukushima Daiichi, Jun 2011] at a distance of about 40 km away from the coast [had] a maximum concentration value of [620 million] atoms per L for 129I in the surface water of the ocean. Taking into account this value as a reference value, the maximum 129-iodine concentration reaching the USA West Coast was 2.5 times stronger than in the contaminated ocean water offshore of Fukushima after the accident. If we compare it to the equilibrium value of 129I concentration in the ocean water [near San Diego], then during the impact its concentration was about 100 times higher…
AMS measurements of 129I were performed on ocean water… offshore of Cove La Jolla, San Diego, USA, and definitely have shown an increase of the radioactivity more than two orders of magnitude over the natural level of the Pacific Ocean before the accident…
Doped carbon could partially treat contaminated water from Fukushima Daiichi removing nearly 93 percent of cesium and 92 percent of strontium in a single pass
Nothing new here. There are lots of ways of pulling radionuclides out of water : activated carbon, ion exchange, chemical affinity, sunflowers (phytoremediation). But still can’t deal with tritium. All costs money, and results in just shifting the contamination to a different material. Radionuclides cannot be simply destroyed, they can only be shifted from one location/ source to another.

Doped carbon could treat water from Fukushima
US and Russian scientists have discovered a new way to remove radioactivity from water, which could be used to treat contaminated water at Japan’s Fukushima nuclear plant.
The researchers, from Rice University and Kazan Federal University, used oxidatively modified carbon (OMC) material to remove caesium and strontium from samples of water. Published in the journal Carbon, their work details how over 90 per cent of the radioactive elements were extracted using OMC column filtration.
“Just passing contaminated water through OMC filters will extract the radioactive elements and permit safe discharge to the ocean,” said Rice chemist James Tour, who led the project with Ayrat Dimiev, a former postdoctoral researcher in his lab and fuknow a research professor at Kazan Federal University. “This could be a major advance for the cleanup effort at Fukushima.”
According to Tour, OMC makes good use of the porous nature of two specific sources of carbon. One is an inexpensive, coke-derived powder known as C-seal F, used by the oil industry as an additive to drilling fluids. The other is a naturally occurring, carbon-heavy mineral called shungite, which is found mainly in Russia.
The team found that the two types of OMC were efficient at extracting cesium, which has been the hardest element to remove from radioactive water stored at Fukushima. The OMC was also much easier and less expensive than previously used filtration materials such as graphene oxide.
“We know we can use graphene oxide to trap the light radioactive elements of relevance to the Fukushima cleanup, namely caesium and strontium,” Tour said. “We learned we can move from graphene oxide, which remains more expensive and harder to make, to really cheap oxidised coke and related carbons to trap these elements.”
As well as being cheaper than other materials, OMC has the added advantage of not having to be stored alongside the radioactive waste it is used to treat.
“Carbon that has captured the elements can be burned in a nuclear incinerator, leaving only a very small amount of radioactive ash that’s much easier to store,” said Tour.
https://www.theengineer.co.uk/doped-carbon-could-treat-fukushima-water/
Treated carbon pulls radioactive elements from water
Researchers at Rice, Kazan universities develop unique sorbents, target Fukushima accident site
Researchers at Rice University and Kazan Federal University in Russia have found a way to extract radioactivity from water and said their discovery could help purify the hundreds of millions of gallons of contaminated water stored after the Fukushima nuclear plant accident.
They reported that their oxidatively modified carbon (OMC) material is inexpensive and highly efficient at absorbing radioactive metal cations, including cesium and strontium, toxic elements released into the environment when the Fukushima plant melted down after an earthquake and tsunami in March 2011.

C-seal F, a source used to synthesize oxidatively modified carbon, is seen magnified 20 times by a scanning electron microscope. The material is highly effective at removing radionuclides from water, according to researchers at Rice University and Kazan Federal University. Click on image for a larger version. Courtesy of Kazan Federal University
OMC can easily trap common radioactive elements found in water floods from oil extraction, such as uranium, thorium and radium, said Rice chemist James Tour, who led the project with Ayrat Dimiev, a former postdoctoral researcher in his lab and now a research professor at Kazan Federal University.
The material makes good use of the porous nature of two specific sources of carbon, Tour said. One is an inexpensive, coke-derived powder known as C-seal F, used by the oil industry as an additive to drilling fluids. The other is a naturally occurring, carbon-heavy mineral called shungite found mainly in Russia.
The results appear this month in Carbon.
Tour and researchers at Lomonosov Moscow State University had already demonstrated a method to remove radionuclides from water using graphene oxide as a sorbent, as reported in Solvent Extraction and Ion Exchange late last year, but the new research suggests OMC is easier and far less expensive to process.
Treating the carbon particles with oxidizing chemicals increased their surface areas and “decorated” them with the oxygen molecules needed to adsorb the toxic metals. The particles were between 10 and 80 microns wide.
While graphene oxide excelled at removing strontium, Tour said, the two types of OMC were better at extracting cesium, which he said has been the hardest element to remove from water stored at Fukushima. The OMC was also much easier and less expensive to synthesize and to use in a standard filtration system, he said.
“We know we can use graphene oxide to trap the light radioactive elements of relevance to the Fukushima cleanup, namely cesium and strontium,” Tour said. “But in the second study, we learned we can move from graphene oxide, which remains more expensive and harder to make, to really cheap oxidized coke and related carbons to trap these elements.”
While other materials used for remediation of radioactive waste need to be stored with the waste they capture, carbon presents a distinct advantage, he said. “Carbon that has captured the elements can be burned in a nuclear incinerator, leaving only a very small amount of radioactive ash that’s much easier to store,” Tour said.

C-seal F, a carbon source, magnified 200 times reveals its high surface area of 12.5 square meters per grams. Processing it into oxidatively modified carbon raises its surface area to 16.9 square meters per gram while enhancing its ability to remove radioactive cesium and strontium from water, according to researchers at Rice University and Kazan Federal University. Click on image for a larger version. Courtesy of Kazan Federal University
“Just passing contaminated water through OMC filters will extract the radioactive elements and permit safe discharge to the ocean,” he said. “This could be a major advance for the cleanup effort at Fukushima.”
The two flavors of OMC particles – one from coke-derived carbon and the other from shungite — look like balls of crumpled paper, or roses with highly irregular petals. The researchers tested them by mixing the sorbents with contaminated water as well as through column filtration, a standard process in which fluid is pumped or pulled by gravity through a filter to remove contaminants.
In the mixing test, the labs dispersed nonradioactive isotopes of strontium and cesium in spring water, added OMC and stirred for two hours. After filtering out the sorbent, they measured the particles left in the water.
OMC1 (from coke) proved best at removing both cesium and strontium from contaminated water, getting significantly better as the sorbent was increased. A maximum 800 milligrams of OMC1 removed about 83 percent of cesium and 68 percent of strontium from 100 milliliters of water, they reported.
OMC2 (from shungite) in the same concentrations adsorbed 70 percent of cesium and 47 percent of strontium.
The researchers were surprised to see that plain shungite particles extracted almost as much cesium as its oxidized counterpart. “Interestingly, plain shungite was used by local people for water purification from ancient times,” Dimiev said. “But we have increased its efficiency many times, as well as revealed the factors behind its effectiveness.”
In column filtration tests, which involved flowing 1,400 milliliters of contaminated water through an OMC filter in 100-milliliter amounts, the filter removed nearly 93 percent of cesium and 92 percent of strontium in a single pass. The researchers were able to contain and isolate contaminants trapped in the filter material.
Co-authors of the paper are Artur Khannanov, Vadim Nekljudov, Bulat Gareev and Airat Kiiamov, all of Kazan Federal University. Tour is the T.T. and W.F. Chao Chair in Chemistry as well as a professor of computer science and of materials science and nanoengineering at Rice. The Russian Government Program of Competitive Growth of Kazan Federal University supported the research.
Fukushima Daiichi Nuclear Disaster Tests Pacific Ocean’s Ecosystem

By Cole Hambleton
On Friday March 11, 2011, following a major earthquake, a 15-meter tsunami disabled the power supply and cooling of three reactors at the Fukushima Daiichi power plant, causing a nuclear accident. All three reactor cores largely melted in the first three days, but were stabilized in the following weeks with seawater. By July 2011, they were being cooled with recycled water from a new treatment plant. An official “cold shutdown condition” was eventually achieved in mid-December 2011.
In November 2011, the Japanese Science Ministry reported that long-lived radioactive cesium had contaminated 11,580 square miles of the land surface of Japan – of which approximately 4,500 square miles (an area almost the size of Connecticut) was found to have radiation levels that exceeded Japan’s pre-earthquake allowable exposure rate of 1 millisievert (mSV) per year.1,2
The Fukushima Daiichi nuclear disaster also produced the largest discharge of radioactive material into the Pacific Ocean in history. Fifteen months after a quantity of radioactive cesium were deposited into the Pacific Ocean, 56% of all fish catches off the coast of Japan were found to be contaminated. 3 Fishing continues to be banned off the coast of Fukushima up to 20 kilometers from the nuclear plant, where 40 percent of bottom-dwelling fish were recently found to have radioactive cesium levels higher than current Japanese regulatory limits for human consumption. Contamination levels are also still unacceptably high in the base levels of the food chain, including algae and plankton. With contamination being found through the whole food chain, scientists believe that the long-term effects on the Japanese human population’s diet will be significant.4
What Has Been Released Into the Pacific Ocean?
Many different radioactive elements are contained in the water leaking from Fukushima. Plutonium 239, which can cause death if inhaled in microgram-sized doses, is found in the released water and can bio-accumulate in the food chain leading to leukemia and bone cancers if ingested by humans. Both short-lived radioactive elements, such as iodine-131, and longer-lived elements such as cesium-137 with a half-life of 30 years, that have been found in the discharged water can be absorbed by phytoplankton, zooplankton, kelp, and other marine life and then can be transmitted up the food chain, to fish, marine mammals, and humans. Other radioactive elements, including plutonium, which has been detected outside the Fukushima plant, also pose a threat to marine life. 5
Capacity of Ocean to Recover?
The Chernobyl accident in 1986 gave scientists a small amount of information on what to expect during a nuclear meltdown on land, but the world has not experienced a meltdown that affects the ocean. 6 Scientists generally agree that oceans have the unparalleled ability to dilute most contaminants to manageable levels and eventually break down those contaminants over time.
Unfortunately, the types of contaminants released due to the Fukushima disaster are substantially different from the more common oil or other chemical spills experienced by the world’s oceans. How the radioactive materials released from the Fukushima plant will behave in the ocean will depend on their chemical properties and reactivity.
If the radionuclides are in soluble form, they will behave differently than if they are absorbed into particles. Soluble iodine will disperse rapidly. But if a radionuclide reacts with other molecules or gets deposited on existing particulates – minerals, for example – they can be suspended in the water or, if larger, may drop to the sea floor where the water is not circulated or blended as often as the water closer to the surface. 7
If the contaminants make it to the ocean floor, they may be able to avoid being broken down by natural processes for a longer period of time. This type of pollution has never been seen before so the long-term consequences are not fully understood. Scientists are currently monitoring the ocean and land contamination. 8
While most scientists believe that the ocean’s powers of dilution will eventually spread the contamination in its suspended and soluble states over time and return the ocean to normal levels of radioactivity, those same scientists do not agree on the amount of time that this dilution will require. As Fukushima continues to dump contaminated water into the ocean, for the sake of the Pacific Ocean food chain, we must hope that the dilution occurs sooner rather than later.
1 About a month after the disaster, on April 19, 2011, Japan chose to drastically increase its “safe” radiation exposure levels from 1 mSV to 20 mSV per year, 20 times higher than the U.S. limit. This allowed the Japanese government to downplay the dangers of the fallout and avoid evacuation of many badly contaminated areas.
2http://www.psr.org/environment-and-health/environmental-health-policy-institute/responses/costs-and-consequences-of-fukushima.html
3 Roslin, Alex. “Post-Fukushima, Japan’s Irradiated Fish Worry B.C. Experts.” Straight.com 19 Jul. 2012. Web. 6 Nov. 2012 <http://www.straight.com/article-735051/vancouver/japans-irradiated-fish-worry-bc-experts>
4http://www.bloomberg.com/news/articles/2011-07-24/threat-to-japanese-food-chain-multiplies-as-cesium-contamination-spreads
5http://e360.yale.edu/feature/radioactivity_in_the_ocean_diluted_but_far_from_harmless/2391/
6http://www.world-nuclear.org/info/Safety-and-Security/Safety-of-Plants/Chernobyl-Accident/
7http://e360.yale.edu/feature/radioactivity_in_the_ocean_diluted_but_far_from_harmless/2391/
8http://e360.yale.edu/feature/radioactivity_in_the_ocean_diluted_but_far_from_harmless/2391/
Fukushima Daiichi: (Nitrogen?) Device Screenshots
I’m assuming this very large device is what injects nitrogen into the reactors to prevent the buildup of explosive gasses.
I’ve seen the device many times before and it usually is placed in service when atmospheric emissions start to thicken, as illustrated by this screenshot from earlier today:
Jan 20 00:33


It is huge, as illustrated here when the crane pulls it out of the building and drops it in the foreground of the building (reactor1) where it had been embedded:

http://majiasblog.blogspot.fr/2017/01/fukushima-daiichi-nitrogen-device.html
Long-distance transport of radioactive plume by nocturnal local winds
Long-distance transport of radioactive plume by nocturnal local winds
Abstract
Radioactive plumes can spread far and wide depending on wind conditions. The plumes often frequently reached the Tokyo metropolitan area, which is approximately 200 km away from the Fukushima Daiichi nuclear power plant, under spatially heterogeneous wind fields in March 2011. To reduce exposure to radioactive plumes, the behaviour of the plumes must be known. However, the transport mechanism of radioactive plumes is not fully understood. Using a regional climate model, we show that multiple diurnal cycle processes play a key role in the frequent transport of radioactive plumes to the Tokyo metropolitan area. The observed data and hindcast results indicate that the radioactive plume moves along the local winds, which comprise the northeasterly local wind (NELW) associated with the meso-scale low-pressure system (meso-low) and the northerly sea wind (NSW) during the night. The long-term analysis and sensitivity simulations also show the nocturnal processes that the NELW caused by the meso-low and the NSW are formed east of the Tokyo metropolitan area and from Fukushima offshore east of the Tokyo metropolitan area, respectively, when neither winter monsoons nor extra-tropical cyclones are predominant. These findings indicate that the radioactive plumes could reach faraway places frequently via nocturnal local processes.
Introduction
Radioactive plumes can scatter widely under the strong influence of the weather1,2,3,4,5,6,7,8. After the accident at the Fukushima Daiichi nuclear power plant in March 2011, the Japanese government evacuated the area within a 20-km radius of the power plant and advised residents within a 20-km to 30-km radius of the power plant to stay inside their homes9. However, high air doses were observed in faraway places outside the 30-km radius (Fig. 1a,b). In such situations, exposure should be minimized because the released radioactive material (131I) is assumed to have the potential to cause thyroid cancer10. Therefore, when and where radioactive plumes will travel should be known in advance.
Figure 1: A common feature of the atmospheric fields when a high air dose was observed in the Tokyo metropolitan area.

(a) The locations of Fukushima, Tokai-mura, and the Tokyo metropolitan area. (b) Time variations of the observed air doses at the observation sites in Tokai-mura. Cases 1, 2, 3, and 4 correspond to the spikes in the air dose. (c) The wind field and geo-potential height of MSM-GPV (975 hPa) at midnight before each of the four cases. Dark areas indicate low pressure. The maps were created by using GrADS 2.0.1 (http://cola.gmu.edu/grads/) (a,c) and Microsoft Excel for Mac 2011 (b).
The movement of a radioactive plume is not only influenced by large-scale events, such as monsoons and extra-tropical cyclones, but also by local-scale events4,5. For example, local-scale events, including land/sea breezes, are predominant under calm weather conditions11,12. A land/sea breeze can cause severe atmospheric pollution even in areas that are distant from the emission source13,14,15. A contamination could occur in a specific area because of the local circulation if large amounts of radioactive materials are emitted over a long period.
A large quantity of radioactive 131I, estimated to be between 1.8 × 1012 and 8.9 × 1015 Bq h−1, was released from the Fukushima Daiichi nuclear power plant by the end of March 201116,17,18. To represent the transport and deposition distribution of radioactive materials in Japan, several numerical simulations have been performed using the estimated emission data3,4,5,6,7,8,16,17,18. However, simulating the distributions is difficult because many uncertainties affect numerical simulations. One such uncertainty is the chaotic behaviour of the atmosphere19,20, which amplifies prediction errors resulting from imperfections in the model formulation or the sensitive dependence on the initial conditions. Indeed, if chaotic behaviour were predominant, the movement of the radioactive plume would be difficult to predict accurately.
In contrast, predicting the movement of a radioactive plume would be relatively simple if large-scale events, such as monsoons and extra-cyclones, were predominant because the wind field would be expected to be temporally constant and spatially homogeneous. However, radioactive plumes often reached the Tokyo metropolitan area, even under spatially heterogeneous wind fields5. The types of atmospheric events that might have affected the wind field and the mechanisms by which the radioactive plumes travelled over long distances remain poorly understood. The chaotic behaviour of the atmosphere might be associated with the movement of the radioactive plume. Here, we investigate the mechanism of radioactive plume transport from Fukushima to the Tokyo metropolitan area using a regional climate model.
Results
High air doses, indicated by the spike in Fig. 1b, were often observed at Tokai-mura in the eastern coastal region of the Tokyo metropolitan area in the morning. At approximately the same time, the NSW and the NELW commonly occurred near the coastal area of the northeastern region of the Tokyo metropolitan area at 975 hPa (see Supplementary Fig. S1), whereas these winds were not detected at 850 hPa (see Supplementary Fig. S2). Another common feature, the nocturnal meso-low, formed in the Tokyo metropolitan area before the high dose rates were observed east of the Tokyo metropolitan area in the morning (Fig. 1c). We conducted a hindcast (HC run) to confirm the relationship between the observed high air radiation doses and the radioactive plume simulated using a regional climate model21 (see Methods). The simulated radioactive plume occurred from Fukushima to the northeastern part of the Tokyo metropolitan area in all cases (see Supplementary Fig. S3).
We assumed that the NSW, NELW, and nocturnal meso-low strongly influenced the radioactive plume transport when neither winter monsoons nor extra-cyclones were predominant. Some diurnal cycle processes could have formed the NSW, NELW, and nocturnal meso-low if the diurnal variations of those atmospheric fields were confirmed in the long-term composite data during calm weather. To verify this hypothesis, we defined a typical day when diurnal wind was observed as a calm day using station data for the central part of the Tokyo metropolitan area. The four cases shown in Fig. 1 were included in the calm day. The diurnal variations were investigated by using the operational meteorological analysis dataset for March from 2008 to 2014 (see Supplementary Fig. S4 and Methods). Seven-year composite would be sufficient to detect the signal of diurnal cycle significantly.
The results demonstrated that the NSW, NELW, and meso-low were clearly evident in the composite of the calm day (Fig. 2b,c) at 975 hPa at night, whereas these atmospheric fields were unclear at 850 hPa (Fig. 2g–i). The meso-low could strongly influence the formation of the NELW. Additionally, the NSW and NELW could be formed as gravity currents induced by the meridional temperature gradient because no predominant forcing exists except for the temperature gradient at night under calm conditions. In contrast, the onshore wind, which is intensified by the heat-low at the mountains of central Japan14, is clearly evident in the daytime (Fig. 2a,d). Almost 30% of the days in March from 2008 to 2014 were calm days (see Supplementary Fig. S5). Thus, diurnal cycle processes are not rare events but are important contributors to the regional climate in March.
Figure 2: Diurnal variation of the wind fields under calm conditions.

Diurnal variation of the composite data of wind fields, geo-potential height, and temperature at 975 hPa and 850 hPa on calm days from 2008 to 2014 according to the MSM-GPV data. The dark areas indicate areas of low geo-potential height (low pressure). The maps were created by using GrADS 2.0.1 (http://cola.gmu.edu/grads/).
The nocturnal meso-low forms in various areas worldwide22,23,24,25,26. The topographical heat-low in the daytime could be a trigger of the meso-low23. However, the nocturnal meso-low has been observed to persist until the morning (Fig. 2c). If the convergence caused by the NSW sustains the meso-low, the topographic effect and meridional temperature gradient could be important in the formation of the meso-low.
To elucidate the formation mechanisms of the NSW, NELW, and meso-low, we conducted simple sensitivity tests (see Methods). The effect of the meridional temperature gradient was investigated by adapting a monthly averaged global zonal mean field in March 2011 as the initial and boundary conditions (Ex. 1); the effect of geography, including the land/sea contrast, was investigated by adapting the area-averaged atmospheric field around east Japan (Ex. 2) (see Supplementary Fig. S6). The result shows that Ex. 1 simulates the NSW, NELW, and meso-low but Ex. 2 does not (Fig. 3). This finding indicates that the meridional temperature gradient is essential in the formation of the diurnal cycle of the atmospheric field.
Figure 3: Sensitivity test.

The wind fields, geo-potential heights, and temperatures at 975 hPa in the morning (6 JST) of Ex. 1 and Ex. 2. The atmospheric fields of the global zonal mean and area-averaged values in March 2011 were applied as the lateral boundary conditions of Ex. 1 and Ex. 2, respectively. The maps were created by using GrADS 2.0.1 (http://cola.gmu.edu/grads/).
Discussion
A schematic of the transport of radioactive materials is presented in Fig. 4. The radioactive materials are transported to an area offshore of Fukushima by the land breeze, and then, the plume moves to the south via the NSW (Fig. 4a). In the morning, the radioactive plume flows into the Tokyo metropolitan area via the NELW, which is formed by the nocturnal meso-low (Fig. 4b). In the afternoon, the plume moves to the mountain area located to the northeast of the Tokyo metropolitan area because of the intensified sea breeze induced by the heat-low over the mountains in central Japan (Fig. 4c).
Figure 4: Long-distance transport of the radioactive plume via multiple diurnal processes.

The 3D image of the mixing ratio of 131I in Case 1. The maps were created by using Volume Data Visualizer for Google Earth (VDVGE) 1.1.7 ESC JAMSTEC (https://www.jamstec.go.jp/esc/research/Perception/vdvge.ja.html) and Adobe Illustrator CS5
The northeasterly wind accompanied by rain is often observed around the Tokyo metropolitan area during winter mornings27,28,29. The developed nocturnal meso-low is responsible for this precipitation. Consequently, it was reassuring that no rainfall was detected on 15 March 2011, when the highest air doses were observed (case 1 in Fig. 1). If rainfall had occurred, the serious contamination would have also caused in the Tokyo metropolitan area.
In the seven-year simulation with the constant emission of radioactive materials (CE run), a high deposition of 131I was simulated from Fukushima to the Tokyo metropolitan area in the morning, with increased deposition occurring the mountains located east of the Tokyo metropolitan area in the evening (see Supplementary Fig. S7 and Methods). The diurnal variation of the deposition could be explained by the movement of the radioactive plume corresponding to the diurnal wind field shown in Fig. 4. Thus, diurnal processes strongly influence the deposition distribution.
The amounts of radioactive materials deposited, especially 137Cs, depend strongly on the precipitation30. Generally, precipitation is difficult to simulate using a numerical model quantitatively with high accuracy because of the non-linearity of the precipitation process. Therefore, accurately estimating the deposition at a specific point without observations would be difficult. Therefore, using only the simulated deposition (exposure by groundshine), determining whether immediate evacuation should be enforced is problematic. Our new findings will be useful for determining the time to take shelter to avoid exposure to the radioactive plume (by cloudshine and/or intake) when a large-scale event is not predominant. Additionally, by applying the transport mechanism clarified here, we could potentially reduce the uncertainties relating to the deposition of radioactive materials. Therefore, we should continue improving existing numerical models to more accurately represent the local circulation caused by diurnal cycle processes. This finding could also useful to improve the local depositions simulated by a global circulation model31.
Generally, local circulation is not simple because various factors, such as land use, geographical features, and synoptic wind, strongly influence the local wind field12. The findings of this study indicate that when a severe nuclear power plant accident occurs, radioactive plumes could reach faraway places via multiple diurnal cycle processes. Therefore, establishing a detailed mechanism of local circulation in every area is necessary to make any progress in reducing the uncertainties related to exposure.
Yoshikane, T. et al. Long-distance transport of radioactive plume by nocturnal local winds. Sci. Rep. 6, 36584; doi: 10.1038/srep36584 (2016).
http://www.nature.com/articles/srep36584
Tepco Recognizes only 15 Workers’ Cancers at Fukushima Daiichi

A new report was released by TEPCO stating that 15 workers from Fukushima Daiichi nuclear plant have develop cancer so far : 8 cases of leukemia, 5 cases of malignant lymphoma, 2 cases of multiple myeloma.
These cancers are recognized sufficiently linked to their work at the nuclear plant and caused by their radiation exposure . Their exposure dose superior to 100 mSv or more and the period from their radiation exposure to their onset of cancer is more than 5 years. Those 15 workers eligible to receive compensation.
These counts does not include the SDF and Tokyo Fire Department workers who responded to the disaster at Fukushima daiichi on March 2011.
Source : http://www.tepco.co.jp/nu/fukushima-np/roadmap/2017/images1/l170117_09-j.pdf
Construction of a New Cover Building Installation for Spent Fuel Removal at Unit 3

This installation will enable robotic removal of spent fuel removal to begin at Fukushima Daiichi Unit 3. Plans to remove this fuel have been complicated by high radiation levels.
To install the cover building’s cylindrical portion workers will have to enter the area to manually bolt the cover to the deck structure.
Installation of the “stopper” by a crane near the spent fuel pool began on January 17 as the first step to construct a new roof for the Unit 3 spent fuel removal. Over the pool some additional structural equipment has also been installed.


Tepco will proceed with the roof construction toward eventual fuel removal with safety as a top priority.
Source : http://www.tepco.co.jp/en/nu/fukushima-np/handouts/2017/images/handouts_170117_01-e.pdf
Local Winds Brought Radioactive Materials From Fukushima To Tokyo

Nocturnal local winds carried radioactive material from Fukushima to Tokyo following the 2011 Fukushimia Daiichi nuclear accident.
AsianScientist (Jan. 17, 2017) – Nocturnal local winds were responsible for transporting radioactive material over 200km from the Fukushimia Daiichi nuclear accident to the Tokyo metropolitan area.
These findings by researchers from the University of Tokyo have been published in Scientific Reports. A research group led by Project Researcher Takao Yoshikane and Associate Professor Kei Yoshimura analyzed observational data and ran computer simulations to determine whether the radioactive plumes were carried by chance haphazard activity in the air or by a regular mechanism in the atmosphere. They found that the radioactive plume moves along two local wind systems that appear during the night on calm days when the impact of northwesterly seasonal winds and low-pressure systems are low. These nighttime local winds were formed by a difference in temperature between the North and the South, which created an upper layer of warm arm and a lower layer of cold air.
These findings indicate that should radioactive material be released over a long period of time, radioactive plumes could be frequently carried even to faraway places by such nocturnal local systems, and cause serious contamination in those areas.
On the other hand, the data show that it is possible to make a rough prediction of when, where, and how the radioactive plumes will travel by knowing the cycle of the winds. The current results could prove useful in determining when to seek shelter to avoid exposure to radiation.
“Stronger risk management strategies that allow for quick and cool-headed response to unforeseen situations are being sought,” said Yoshikane. “It is necessary to take into account local factors specific to each area, such as geographical features and traffic conditions.” “We hope that by expanding our study we can contribute to the development of risk management strategies through exchanges with people in other fields, government agencies, and local governments.”
The article can be found at: Yoshikane et al. (2016) Long-distance Transport of Radioactive Plume by Nocturnal Local Winds. ——— Source: University of Tokyo;
http://www.asianscientist.com/2017/01/in-the-lab/winds-radioactive-materials-fukushima-tokyo/
Law to make Tepco retain money for decommissioning costs

Workers check a transport container and a crane in preparation for the removal of spent nuclear fuel from a pool at No. 4 reactor building of Tepco’s Fukushima No. 1 nuclear power plant in Okuma, Fukushima Prefecture, in November 2013.
The government plans to legally oblige Tokyo Electric Power Company Holdings Inc. to retain money to cover costs for decommissioning its crippled Fukushima No. 1 nuclear power plant, Jiji Press has learned.
A draft of a bill to revise the law on the Nuclear Damage Compensation and Decommissioning Facilitation Corp. states that business operators that caused nuclear accidents are obliged to deposit funds to cover related costs at the organization every fiscal year, informed sources said Friday.
By clarifying Tepco’s duty to build up funds by law, the government aims to steadily implement work to decommission the Tepco plant in Fukushima Prefecture.
The Ministry of Economy, Trade and Industry plans to submit the amendment to this year’s ordinary session of the Diet, slated to start next Friday.
The draft says the amount of money to be put aside will be decided by the organization and should be approved by the industry minister each fiscal year.
The deposited funds can be withdrawn based on a plan compiled jointly by the organization and the business operators that caused nuclear accidents and will be approved by the minister.
The revised law would allow the industry ministry and the organization to conduct on-site inspections if needed.
Tepco is set to decommission all six reactors at the Fukushima No. 1 plant, which was heavily damaged in the March 2011 earthquake and tsunami. Unprecedentedly, nuclear fuel melted at three of the six reactors.
If work to remove the melted fuel is fully launched, annual decommissioning costs are expected to balloon to several hundreds of billions of yen from the current ¥80 billion ($700 million), with the total costs seen amounting to ¥8 trillion.
The ministry is planning to have Tepco bear all the decommissioning costs.
What Was Dumped in and Cemented West of Reactor #1?

Citizen scientists at work! This is what we can all do to ensure the truth remains clear, in spite of the barrage of corporate propaganda. Thanks Ray Masalas
Ray Masalas found this early picture in his files {May 8th 2011 still a road west of reactor #1} and of course the later {Late July 2011} below picture showing the huge concrete pour west of reactor #1.
You can guess what got dumped in there and cemented over? No wonder the aquifer is hot. Anyway, at least we have a timeline on the mysterious boat shaped, concrete pour. By Aug. 2011 it became covered with sand and they pretended they were just regrading the road.
Ray Masalas guesses the blob from the north wall of reactor #4 and a pile of blown out fuel rod chunks went in there. He really wishes he had a picture of how deep they dug it but we know how the Japanese media release only films where Tepco lets them. If he didn’t go frame by frame we never even would have had this. You know how they like to swing the camera past the important stuff.
And in both pics you can see the 45 degree angle of the roof of Reactor #1 collapsing from south to north after the blast. It’s sitting on the fuel pool. No one has been in there since they put the tent over it in Oct 2011. Maybe some poor slob has to go check the hoses in the fuel pool but the reactor core is long gone. This one was blown by the earthquake {Shhh big secret} and might have been in meltdown before the tsunami hit, an hour and a half later.
Special credits and thanks to Ray Masalas.
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