Tag Archives: Algae

What Controls Levels of Fukushima Radioisotopes in Marine Organisms?

By Jay T. Cullen

This post is part of an ongoing effort to communicate the risks to people living on the west coast of North America resulting from the ongoing release of radionuclides from the Fukushima-Daiichi nuclear power plant after the Tohoku earthquake and subsequent triple reactor meltdowns in March 2011. The purpose of this post is to explain how the concentration of radionuclides in seawater impacts the amount of radioactive elements taken up by the marine biota.

The goal is to answer questions like:

How high can we expect radioactive element concentrations to get in marine organisms?

What might be the exposure of marine organisms and human consumers of these organisms to Fukushima sourced radionuclides?

Continue reading What Controls Levels of Fukushima Radioisotopes in Marine Organisms?

Peak Concentrations of Radioactive Iodine From Fukushima in North American Rain Water and Seaweed

by Jay T. Cullen


The purpose of this post is to summarize results from various studies that monitored the timing of arrival and activity of radioactive iodine falling from the atmosphere in western North America following the Fukushima disaster in 2011.  Determining the activity of 131-I (half life ~8 day) in rain and seaweed, which serves as a biological monitor, is important because of the isotopes short half life and its propensity to concentrate in the human body, specifically the thyroid gland. This combination of rapid energy release and biological tissue targeting can represent a potential radiological health risk. Measurements of 131-I in rain collected in the San Francisco Bay area and southern British Columbia, Canada indicate that the atmospheric transport brought contaminated air from Fukushima to North America by March 18 roughly 1 week after the earthquake and tsunami. Depending on location, activities of 131-I in rain peaked between March 20-24 and were observed to decrease to background levels in the first week of April. Peak activities in seaweed occurred later on March 28 and were observed to return to background levels in mid-May. Maximum 131-I activities in rain resulting from Fukushima were a factor of 10 lower for rainwater and a factor of 40-80 lower for seaweed compared to similar measurements made following the Chernobyl disaster in 1986. Observed 131-I activities suggest that the upper limit of radiation dose to the public resulting from Fukushima was similarly an order of magnitude lower than that from Chernobyl suggesting that the short and long-term impact on human health in western North America is expected to be minor.

How Scientists Talk About Radioactivity

Scientists use a variety of units to measure radioactivity. A commonly used unit is the Becquerel (Bq for short) which represents an amount of radioactive material where one atom decays per second and has units of inverse time (per second). Another unit commonly used is disintegrations per minute (dpm) where the number of atoms undergoing radioactive decay in one minute are counted (so 1 Bq = 60 dpm).

131-Iodine Releases From Fukushima

As a result of the great eastern Japan earthquake and tsunami on March 11, 2011 three of six reactors melted down resulting in releases of radionuclides from the Fukushima Dai-ichi nuclear power plant to the environment. In terms of absolute activity released and potential for causing harm to organisms, 131-I (half life ~8 day) was one of the most significant. Given its volatility and the damage to reactor fuel rods large releases of ~2000 PBq (petaBequerel = 10^15 Bq) to the atmosphere and ocean occurred in the weeks following the disaster. Prevailing atmospheric circulation brought this plume of contaminated air to North America within one half life of 131-I where rain and fallout of aerosol particles delivered 131-I and other isotopes to land and coastal waters.

Monitoring of 131-I in the environment is important because as an essential nutrient when concentrated in the human body in the thyroid gland the decay of the isotope can cause damage resulting in negative health impacts like cancer. After the triple meltdowns stations in North America began monitoring the activities of released radionuclides in air, rainwater and seaweed to determine the risk to public health.

Rainwater activities of 131-I
Rainwater in the San Francisco Bay area was monitored and the results published in the open-access, peer reviewed journal PLOSOne in 2011 by Norman and co-workers. Measurements were made for the period March 16-26, 2011 on rainwater collected in Oakland, Berkeley hills and Albany, CA. Results of these measurements are summarized in the figure below:

Activity concentrations of 131,132-I, 132-Te, and 134,137-Cs in Bq/L measured in San Francisco Bay area rain water as a function of time.

This first sample with Fukushima radionuclides above background concentrations was collected on March 18 and activities peaked at 16 Bq/L rainwater on March 24.

Similar activities and timing of arrival of the atmospheric plume of 131-I were observed in southern British Columbia, Canada. Chester and colleagues published this work in the peer-reviewed Journal of Environmental Radioactivity in 2013. Maximum activity of 131-I of 5.8 Bq/L was detected in the Vancouver, BC area nine days after the Fukushima disaster on March 20, 2011. The activity of 131-I returned to background by early April 2011. Results are summarized in the figure below.

Activity of 131-I measured in rainwater collected in southwestern British Columbia following the Fukushima disaster in 2011
131-I measured in seaweed

131-I levels in seaweed are known to correlate strongly with levels in rain and seaweeds are useful monitors for human made radionuclides in the environment as the concentrate isotopes from their surroundings and are geographically widespread. Seaweeds were collected along the Canadian west coast by Chester and colleagues and analyzed for 131-I following the Fukushima disaster. Results of these analyses are summarized in the figure below:

131-I activities measured in seaweed collected along the BC coast in 2011.

Maximum 131-I was detected in BC seaweed on March 22 near Vancouver and on March 28 off the west coast of Vancouver Island some 250 km to the west of the city. Peak activities were 130 and 67 Bq/kg respectively. By mid-May activities had returned to background activities in the seaweed.

Summary: Health Implications and Comparison to Chernobyl

The maximum levels of 131-I in rainwater can be compared to limits allowed in drinking water in both the USA and Canada. Maximum activities in rain were in the range ~6-16 Bq/L. For example the maximum allowable concentration (MAC) or activity allowed in Canadian drinking water is 6 Bq/L. The MAC for 131-I is calculated using a reference dose level of 0.1 mSv (where mSv = 0.001 Sv) for 1 year’s consumption of drinking water, assuming a consumption of 2 L/day at the MAC. This compares to an effective dose received by someone living in Vancouver of about 1.3 mSv. Given the short half-life of 131-I of ~8 days the actual dose attributable to Fukushima fallout in precipitation is likely to be much lower than the 0.1 mSv upper limit on which the drinking water MAC is based.

Indeed, comparing measurements in the studies above to measurements made on the west coast of North America in the aftermath of the Chernobyl disaster in 1986 suggests that doses experienced by the public post Fukushima fallout were an order of magnitude lower. Measurements in the same species of seaweed in 1986 (behind paywall) are compared to the measurements of Chester and others here:

The calculated dose estimates to Canadians following the Chernobyl disaster were on the order of ~1 micoSievert (0.000001 Sv) (What is a Sievert, Sv?) while the peak 131-I activities present in rainwater after Fukushima suggest an upper dose of 0.1 microSv which is an order of magnitude lower dose.

These data have led health professionals in the US and Canada to expect that short-term and longer-term impact of Fukushima on public and environmental health to be very small compared to other radiological impacts from natural and legacy sources of radiation.

Is Fukushima Radioactivity Making the North Pacific Ocean a “Dead Zone”?

The purpose of this post is to address what impact the Fukushima Dai-ichi disaster has had and is having on the growth of photosynthetic algae or phytoplankton in the North Pacific Ocean ecosystem. There is some concern among the public that the radioactivity released from Fukushima represents a potentially acute and chronic risk to algae or phytoplankton that represent the base of the marine food web. A simple internet search will raise stories which speculatively describe the North Pacific Ocean as a “dead-zone” suggesting that activities of radionuclides from Fukushima are killing phytoplankton and leading to biological desert-like conditions in this important ecosystem. Microbes, algae included, are some of the most radiation resistant organisms on the planet that can survive acute and chronic doses of radiation that would kill multi-cellular organisms like ourselves.  Satellite data can estimate phytoplankton biomass from space and this post uses NASA’s MODIS satellite data accessed through their really useful GIOVANNI data portal.

Satellite measurements of ocean temperature and the abundance of marine algae going back to 1997 suggest that Fukushima has had little if any impact on phytoplankton in the coastal waters of Japan and offshore waters of the North Pacific to this point.  This diary is not meant to be an exhaustive survey of the state of the North Pacific ecosystem but is aimed at using remote sensing to address whether or not widespread collapse of phytoplankton populations occurred in the Pacific following the Fukushima disaster. As stated above all the animations and data in this diary can be accessed using NASA’s fantastic online portal called Giovanni.

What are algae and why do we care?

Algae, also called phytoplankton, are autotrophic organisms that can use sunlight as an energy source to produce glucose. They are the base of the food web and ultimately the yield of the major world fisheries depends on how productive these microscopic plants are year to year in the ocean. On long timescales the carbon dioxide they transform into organic matter at the ocean surface helps to determine how much carbon dioxide is the in atmosphere which helps to control Earth’s climate. Given the importance of phytoplankton to the health of the marine ecosystem, fisheries productivity and the capacity of the oceans to absorb fossil fuel derived carbon dioxide from the atmosphere there is much interest in the oceanographic research community to determine what controls the growth of algae in the ocean.

What controls how much and when phytoplankton grow?

To grow algae need light (which decreases exponentially with depth in the ocean) and nutrients like nitrogen and phosphorus (like fertilizer for your garden) which are dissolved in seawater. As algae grow they remove dissolved nutrients, including carbon dioxide, from the surrounding seawater and make new microscopic copies of themselves. The cells that grow eventually die and sink out of the surface of the ocean to the dark ocean interior where they rot, decompose, and return the nutrients again to dissolve in the subsurface ocean water. The growth of phytoplankton thus leaves the surface ocean with very low nutrient concentrations and when they run out of nutrients their growth stops. So, there is lots of light at the surface but very little nutrients and lots of nutrients but very little light in the deeper parts of the ocean. It can be tough being marine algae, or in other words, it ain’t easy being green.

Marine algae and radiation tolerance

Significant amounts (as reported in Povinec et al. 2013; open-access) of radioactive isotopes were released directly and indirectly via the atmosphere to the Pacific Ocean following the Fukushima Dai-ichi nuclear power plant disaster in March 2011. Releases to the coastal ocean continue to this day though at levels that are much diminished compared to release rates in March and April 2011 with maximum activities occurring off the coast and in Spring 2011 and 10,000-100,000 fold lower activities that are about 100-1000 fold higher than pre-Fukushima background ~1 km from the plant site. How the activities of these radionuclides will impact marine organisms is an ongoing concern and the focus of much research.

Marine algae are made up of both prokaryotic (e.g. cyanobacteria) and eukaryotic (e.g. diatoms and coccolithophores) organisms. Generally microorganisms tend to be more tolerant of of ionizing radiation than animals with members of marine photosynthetic algae being well represented (e.g. Singh and Gabani 2011 Journal of Applied Microbiology). Recently, as an extreme example, a eukaryotic algae (link, link) was isolated from the spent fuel pool of a research reactor in France that can resist a dose of 20,000 Gy or more than 2,000 times the lethal dose to human beings. Basically, these amazing organisms live in distilled water and withstand withering amounts of radioactivity. Given that maximum offshore activities of Fukushima derived isotopes like cesium (137-Cs half life ~30 yr and 134-Cs half life ~2 yr) are ~20 Bq/m3 in seawater (Kumamoto et al. 2014) dose rates experienced by microbes are not likely to approach levels known to induce phytoplankton mortality.

Seasonal cycle of phytoplankton growth in the North Pacific

In the North Pacific, where there is a strong seasonal cycle between colder, dark winters and warm light filled summers, there is also a strong seasonal cycle in phytoplankton growth. Over the winter the upper ocean is mixed with the deeper ocean because cooling of surface water makes it more dense and stronger winds from winter storms stirs the soup. This brings nutrient-rich water to the surface. But, the lights aren’t on yet and there is not enough sunlight to make the phytoplankton happy. When spring rolls around and the sun shines bright the phytoplankton have all they need to be happy (light and nutrients) and the grow quickly. When they grow very quickly their numbers increase exponentially and we call this a spring bloom. Nutrients are used up quickly and chlorophyll a, the pigment that helps the plants harvest the suns energy, increases in concentration at the oceans surface in parallel with the numbers of algae. This leads to a strong seasonal cycle where chlorophyll a concentrations are low in the winter and increase dramatically in spring.

Shown below is the seasonal cycle of sea surface temperature in the North Pacific.

Sea surface temperatures as determined by the NASA MODIS satellite for the year 2010 (http://modis.gsfc.nasa.gov/). Warm colors correspond to warm sea surface temperature in celsius.

Cold surface temperatures dominate in the norther hemisphere winter that warm as we head into spring. Warming is accompanied by increased hours and intensity of sunlight. Cooling conditions dominate in late fall as day length and incoming solar energy intensity diminish.

The biological response to this seasonal cycle is shown in the animation of chlorophyll a concentrations below.

Chlorophyll a concentrations, a measure of phytoplankton biomass, in the North Pacific over an entire seasonal cycle in 2010

Algal biomass is low in the winter as deep mixing and lack of light limits the growth of the phytoplankton. However, this mixing returns nutrients to the surface that were depleted during the previous seasons growth. As the spring comes on more light warms the surface and allows a bloom of phytoplankton to develop that propagates northward following the sun. Very low amounts of phytoplankton are observed in the south as the summer progresses given that nutrients have been used up and surface warming prevents mixing of the more dense subsurface, nutrient rich waters up into the sunlit upper ocean.

Long term trends in algae growth in the North Pacific: Does Fukushima have a negative effect?

The following figure shows how this seasonal cycle of spring bloom and winter crash has operated over the period covered by satellite observations between 1997 and the present.

Chlorophyll a concentrations in mg/m3 for the North Pacific off of Japan as determined by NASA SeaWiFS and MODIS satellites (http://oceancolor.gsfc.nasa.gov/SeaWiFS/)(http://modis.gsfc.nasa.gov/)

Peak chlorophyll concentrations during the Spring bloom fall in a range between ~0.75 and 1.9 mg/m3 over the period with the minimum occurring in 2008 and the maximum in 2004. The spring bloom in 2011, coincident with the disaster, was an average year for phytoplankton growth followed by the second highest bloom in the satellite record in 2012. In 2013 chloropyll concentrations were lower than in either 2011 or 2012, similar to 2003 and greater than 2008, 2007 and 1999. Most recent data for 2014 indicate that the spring bloom is underway with more data coming in at each months end.

Long-term trends do not indicate that there has been a collapse of the phytoplankton population following the Fukushima disaster. We kept an eye on what the spring bloom peak looked like for 2014.  The following figure updates the data presented above with the chlorophyll a concentrations averaged for the month of April 2014. Chlorophyll a concentrations are significantly greater than those in 2013 and similar to levels in 2011 and 2012 and record levels in 2004. Given that it August now the bloom has subsided with a modest increase in chlorophyll expected in the Fall.

More study on the impacts of the Fukushima disaster on populations of marine organisms are required given the persistence and potential to concentrate in the biota of certain of the radionuclides.

Personal Aside: I recall seeing some of the first SeaWiFS images as a graduate student and being amazed at the productivity of the oceans. The power of remote sensing is impressive and affords us a great tool for studying the oceans.