Spring Bloom Sampling in California

One of the reasons I haven’t posted for a bit besides the normal-busy routine is that it is Spring Time! What’s that got to do with anything you ask?

BLOOMS! BLOOMS OF EVERYTHING!

Me in the Anza-Borrego Desert next to an Ocotillo plant
Me in the Anza-Borrego Desert in California, next to a flowering Ocotillo plant

Besides blooms of flowers in the desert  (such as those in the Anza-Borrego Desert), we also get blooms of phytoplankton along the coast in Southern California.

Here, in the spring we get very high winds that can result in upwelling events in the coastal ocean, pushing waters offshore and bringing up cold, nutrient rich water from the bottom ocean layers to the top layers.

This increase in nutrients (such as nitrogen, phosphorous, iron, etc.) can result in massive ‘blooms’ or increases in specific phytoplankton species (diatoms, dinoflagellates, etc.), since typically their densities are limited by nutrient availability. During these blooms, whoever wins the space and resource competition will dominate… until they get run down by grazers, parasites or viruses.. or run out of their limiting nutrient. Once these species decline this then provides space/resources for the next dominating species.

Upwelling Diagram from Sanctuary Quest 2002, NOAA/OER
of Upwelling (Image from Sanctuary Quest 2002, NOAA/OER)

These upwelling events also offer AWESOME opportunities for scientists to examine the species dynamics, and the mechanisms that result in some species or functional groups of phytoplankton to dominate over others.

This year, our laboratory  (the Caron Laboratory at USC) decided to start our sampling period after we noticed strong winds on April 9th.. and I mean Strong! I was biking to my circus class that evening, and a branch literally flew and hit me.. luckily I was wearing a helmet 🙂  During lab meeting that week, we were all telling each other the horror stories of the strong wind, and realized.. ‘woah!’… we should start our spring sampling asap! So we quickly contacted the amazing Santa Monica Pier Aquarium (Heal The Bay) and received permission to use some of the space there to do our sample processing for three weeks. Then we finalized our schedules, rotating each daily to sample and process the water off of the Santa Monica Pier. Each day at 8:30am, we get to the aquarium, load up our cart with the RBR (an oceanographic instrument that measures temperature, salinity, chlorophyll and dissolved oxygen), a bucket and container for loading up sea water, and a 20 micron plankton net to collect a concentrated water sample. Then by 9am, we are loading up water into our collection container, and then rolling the water back to the aquarium to filter some of it down as fast as possible onto filters that we flash freeze for DNA/RNA extractions. We also preserve some of the whole sea water for relative abundance counts of the different organisms via microscopy, and we  sample the water for extraction of chlorophyll and domoic acid (toxin produced by some diatoms). Once we get back to the lab, we inspect the concentrated samples from the plankton net to get a quick overview of who is in the water, and who is the dominating species.

 

This year the sampling has been super interesting! It started off with a diatom and dinoflagellate bloom, and it looks like the diatoms have been CRUSHED by a parasitoid, Cryothecomonas spp.! Once the diatoms crashed, the dinoflagellates  increased more, in particular two species are currently dominating: Akashiwo sanguinea and Cochlodinium spp. (species will be determined after we get our molecular sequences back). I also found some tintinnid ciliates parasitized by Eudoboscquella parasitoids.. so beautiful.

 

In addition to using molecular sequences for identification of the different taxa, our laboratory also analyzes the RNA sequences (using bioinformatics) to examine gene expression of the different taxa that are increasing and decreasing during the bloom. These methods can help us determine when species are taking up specific nutrients, when they are multiplying, when they are stressed, and even if they are being attacked by parasites. Lastly, my work in particular during this spring bloom will examine the dynamics of these species and their parasites through time using qPCR (quantifies the relative number of the hosts and parasites by comparing samples to standard curves).

We have five more days left of daily sampling, and I will be sure to follow up with another blog on the results of this spring bloom sampling period. I will also post soon about the exciting results from a massive laboratory experiment that I just finished. Stay tuned!

New Post-doc Position at USC!

I am taking a small break from my blog tutorials on using microsatellite markers in population genetic studies to make an exciting announcement: I recently started a new 1-year Post-doc position at the University of Southern California in Dr. Dave Caron’s laboratory (more time pending funding from fellowships)!

USC-Dornsife-Cardinal-Black-on-White-RGBAlthough it is sad that my Delta Science fellowship is over, as it was a wonderful opportunity, I will still be working/writing hard to finish up my publications from this work and I will of course share these with all of you as they are published.phd011817s

In the mean time- I am moving back into marine study systems to examine the diversity and function of protists in the marine phytoplankton community!  Click here to check out the fascinating research in Dave Caron’s lab.  In addition to dabbling in several different ongoing projects in Dave’s lab- I am also very excited about starting up some of my own projects (pending funding) on the abundance, diversity and consequences of parasite-host interactions in the phytoplankton community.  As some of you might already know- I am an extreme parasite enthusiast, and only recently have researchers started to examine the potential abundance and importance of parasites in the marine phytoplankton community!

Recently, researchers in the Tara-Oceans Expedition found that parasitic interactions were the most abundant pattern in the global marine phytoplankton interactome (Lima-Mendez et al. 2015). Results from the V9-18S tag-sequence processing revealed parasite-host associations that included the copepod parasites: Blastodinium (Dinophyceae: Blastodiniaceae), Ellobiopsis (Marine Alveolate Group I: Ellobiopsidae), and Vampyrophrya (Ciliophora: Oligohymenophorea: Foettingeriida) and alveolate parasitoids of dinoflagellates and ciliates (Lima-Mendez et al. 2015). The alveolate parasitoids in particular were recognized for their top-down effects on zooplankton and microphytoplankton (Lima-Mendez et al. 2015).

 

Screenshot 2018-05-12 12.38.19
Figure from: Lima-Mendez G, Faust K, Henry N, et al. (2015) Ocean plankton. Determinants of community structure in the global plankton interactome. Science 348, 1262073.

Parasitoids are parasites that kill their host in order to complete their development (Lafferty and Kuris 2002) and increased abundance of alveolate parasitoids have been linked to declines of dinoflagellate blooms (Coats et al. 1996, Coats 1999, Chambouvet et al. 2008, Mazzillo 2011, Jephcott et al. 2016) and have been shown to regulate their dinoflagellate host populations in laboratory experiments (Noren 2000, Coats and Park 2002). The most researched alveolate parasitoids include several strains of Amoebophrya ceratii (Marine Alveolate Group II: Syndiniales) . These parasitoids have small flagellated infective stages that penetrate and multiply inside the dinoflagellate host cell, and produce numerous infective flagellates after killing and exiting the host (Cachon & Cachon 1987; Jephcott et al. 2016). For example A. ceratii can produce 60-400 new infective dinospores from its host in less than 48 hours (Chambouvet et al. 2008; Mazzillo 2011), and the generalist parasitoid, Parvilucifera sinerae, can produce 170 to > 6000 zoospores per sporangium, depending on the species and size of its host (Garces et al. 2013), with zoospore release within 72 hours of infecting a host (Alacid et al. 2015).

Below for your viewing pleasure is an example of these parasitoids- the life cycle diagram and life-cycle stages from Alacid et al. 2015, and Alacid et al. 2016 (respectively) of the generalist parasitoid Parvilucifera sinerae, in its host dinoflagellates.

So now of course the question you might have is: “why do we need to research these parasites/parasitoids further?” Well, we simply do not  know enough about these amazing parasite-host interactions, and most of our knowledge is currently limited to the photic zone of the ocean, and concentrated on just a few of these parasite species (there are many parasites out there just waiting to be discovered!). For those of you that don’t think ‘not knowing enough’ merits more work- my reply to this is that: mortality rates in the phytoplankton community have an incredible significance regarding the total primary production and biogeochemical processes in the ocean. However, how can we account for the mortality rates in the phytoplankton community and consequences for primary production if we are not accounting for a large % of contribution to mortality due to parasites that have not yet been characterized? And this folks.. is the reason why this research should be funded (aside from the obvious fact that parasites are absolutely fascinating, and the evolution and ecology of parasites can tell us a lot about related free-living species as well (that is another blog topic I will save for the future).

Of course my new Post-doc research in this field is still a bit tentative as it depends on gaining further funding- but in the mean time I am posting some lovely photos of parasites (Euduboscquella spp.) in tintinnid ciliate hosts (Eutintinnus spp.) that I have been finding from some local net tows (marine sampling nets that concentrates organisms of different size classes). So exciting- it is like a treasure hunt every time!

 

References (highly recommended reads also!)

Alacid E, Rene A, Garces E (2015) New insights into the parasitoid Parvilucifera sinerae life cycle: the development and kinetics of infection of a bloom-forming dinoflagellate host. Protist 166, 677-699.

Alacid, E., Park, M. G., Turon, M., Petrou, K. & Garces, E. (2016) A game of Russian roulette for a generalist dinoflagellate parasitoid: host susceptibility is the key to success. Front Microbiol 7, 769.

Cachon J, Cachon M (1987) Parasitic dinoflagellates. In: Biology of dinoflagellates, pp. 571-610. Blackwell, New York.

Coats DW (1999) Parasitic life styles of marine dinoflagellates. Journal of Eukaryotic Microbiology 46, 402-409.

Coats DW, Adam EJ, Gallegos CL, Hedrick S (1996) Parasitism of photosynthetic dinoflagellates in a shallow subestuary of Chesapeake Bay, USA. Aquatic Microbial Ecology 11, 1-9.

Coats DW, Park MG (2002) Parasitism of photosynthetic dinoflagellates by three strains of Amoebophrya (Dinophyta): Parasite survival, infectivity, generation time, and host specificity. Journal of Phycology 38, 520-528.

Chambouvet A, Morin P, Marie D, Guillou L (2008) Control of toxic marine dinoflagellate blooms by serial parasitic killers. Science 322, 1254-1257.

Garces E, Alacid E, Bravo I, Fraga S, Figueroa RI (2013) Parvilucifera sinerae (Alveolata, Myzozoa) is a generalist parasitoid of dinoflagellates. Protist 164, 245-260.

Jephcott TG, Alves-De-Souza C, Gleason FH, et al. (2016) Ecological impacts of parasitic chytrids, syndiniales and perkinsids on populations of marine photosynthetic dinoflagellates. Fungal Ecology 19, 47-58.

Lafferty KD, Kuris AM (2002) Trophic strategies, animal diversity and body size. Trends in Ecology & Evolution 17, 507-513.

Mazzillo FFM (2011) Novel insights on the dynamics and consequence of harmful algal blooms in the California Current System: from parasites as bloom control agents to human toxin exposure PhD dissertation, University of California, Santa Cruz.

Lima-Mendez G, Faust K, Henry N, et al. (2015) Ocean plankton. Determinants of community structure in the global plankton interactome. Science 348, 1262073.