Population dynamics and parasite load of a foraminifer on its antarctic scallop host with their carbonate biomass contributions

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Abstract

We studied the population dynamics and parasite load of the foraminifer Cibicides antarcticus on its host the Antarctic scallop Adamussium colbecki from three localities differing by sea ice cover within western McMurdo Sound, Ross Sea, Antarctica: Explorers Cove, Bay of Sails and Herbertson Glacier. We also estimated CaCO3biomass and annual production for both species. Cibicides populations varied by locality, valve type, and depth. Explorers Cove with multiannual sea ice had larger populations than the two annual sea ice localities, likely related to differences in nutrients. Populations were higher on Adamussium top valves, a surface that is elevated above the sediment. Depth did not affect Cibicides distributions except at Bay of Sails. Cibicides parasite load (the number of complete boreholes in Adamussium valves) varied by locality between 2% and 50%. For most localities the parasite load was <20%, contrary to a previous report that ∼50% of Cibicides were parasitic. The highest and lowest parasite load occurred at annual sea ice localities, suggesting that sea ice condition is not important. Rather, the number of adults that are parasitic could account for these differences. Cibicides bioerosion traces were categorized into four ontogenetic stages, ranging from newly attached recruits to parasitic adults. These traces provide an excellent proxy for population structure, revealing that Explorers Cove had a younger population than Bay of Sails. Both species are important producers of CaCO3. Cibicides CaCO3biomass averaged 47-73 kg ha-1and Adamussium averaged 4987-6806 kg ha-1by locality. Annual production rates were much higher. Moreover, Cibicides represents 1.0-2.3%of the total host-parasite CaCO3biomass. Despite living in the coldest waters on Earth, these species can contribute a substantial amount of CaCO3to the Ross Sea and need to be incorporated into food webs, ecosystem models, and carbonate budgets for Antarctica.

Figures

  • Fig 1. Localities in McMurdo Sound, Ross Sea, Antarctica.Mapmodified with permission from Antarctic New Zealand.
  • Fig 2. Trace Measurements and Sectors used to ExamineCibicides Population Structure on Adamussium. A. iSolution Lite image showing polygons that were used to measure exterior resting trace and interior borehole diameter. B. Sectors on Adamussium shell that were used to examine the spatial distribution ofCibicides bioerosion traces.
  • Fig 3. Experiment that Demonstrates AttachedCibicides are Alive. A. Live Adamussium deployed at EC in 2005 with attachedCibicides. Arms from a sea star can be seen behind the scallop, contributing to the scallop’s death. B. Top valve retrieved after one year and stained with Rose Bengal that stains living tissue pink. Inset: slightly decalcifiedCibicides showing Rose Bengal-stained cytoplasm in living individuals. Arrow in A and B point to the three Cibicides that are figured in inset. Scale bar is 20 mm for A and B; inset scale bar is 1 mm.
  • Table 1. Cibicides antarcticus Populations by Antarctic Locality, Depth, and Valve Type. The number of attachedCibicides is reported in the numerator and the number of bioerosion traces is reported in the denominator (attachedCibicides/bioerosion traces). The frequency of occurrence within parentheses depicts the number of either attachedCibicides or bioerosion traces for each locality divided by the total pooled for all localities. The mean shell area for the Antarctic scallop Adamussium colbecki was used to determine the mean density of Cibicides.
  • Fig 4. Generalized Linear Model ofCibicidesAbundance by Shell Area. Localities: Explorers Cove (EC), Bay of Sails (BOS) and Herbertson Glacier (HG).
  • Fig 5. Cibicides Populations on Top and Bottom Valves by Locality. A. AttachedCibicides. B.Cibicides traces. C. AttachedCibicideswith traces pooled. Top = top valves; Bot = bottom valves of Adamussium colbecki.
  • Fig 6. Cibicides Populations by Depth and Locality. A. AttachedCibicides. B. Cibicides traces. C. PooledCibicides with traces. Localities: Explorers Cove (EC), Bay of Sails (BOS), and Herbertson Glacier (HG). Depths are 9 and 18 m.
  • Fig 7. Cibicides Parasite Load by Locality, Depth and Valve Type. For A and B, localities are Explorers Cove (EC), Bay of Sails (BOS), and Herbertson Glacier (HG). A. Mean number of complete boreholes (Bor) compared toCibicides without boreholes (NoBor), error bars are 95% CIs. B. Frequency ofCibicides boreholes by locality and depth. Frequency was calculated by dividing the number ofCibicides boreholes by the total population of Cibicides. C. Boreholes on top and bottom valves by locality.

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APA

Hancock, L. G., Walker, S. E., Pérez-Huerta, A., & Bowser, S. S. (2015). Population dynamics and parasite load of a foraminifer on its antarctic scallop host with their carbonate biomass contributions. PLoS ONE, 10(7). https://doi.org/10.1371/journal.pone.0132534

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