Superoxide dismutase measurements as a complement to tackle the responses of Cnemidocarpa verrucosa sp. A to sedimentation due to rapid climate change

• Main Authors: Ruiz, Micaela Belen, Servetto, Natalia, Alurralde, Gastón, Abele, Doris, Sahade, Ricardo José, Held, Christoph
• Format: Dataset
• Language: English
• Published: PANGAEA
• Subjects: Biological sample; BIOS; Caspase; Change of extinction; Cnemidocarpa verrucosa; superoxide dismutase; in extract; per protein mass; per wet mass; Cnemidocarpa verrucosa sp. A; PotterCove_CarliniStation_bio; PotterCove_CarliniStation_dive; Potter Cove; King George Island; Antarctica; Proteins; Sample ID; Sample volume; SCUBA-DIVE; sedimentation; see description in data abstract; Tissue; mass; Tissues; Volume; Antarctic; Antarctic Peninsula; Carlini Station; South Shetland Islands; Antarc*
• Online Access: https://doi.pangaea.de/10.1594/PANGAEA.945274

Rapid regional warming causes glacial retreat and melting of ice caps along the West Antarctic Peninsula, in consequence, sediment discharge into marine coastal areas reduces food availability and impairs respiratory performance of benthic filter-feeders. Here we analyzed the response of a highly abundant Antarctic ascidian Cnemidocarpa verrucosa sp. A to experimental changes in sedimentation rates through enzymatic measurements: Caspase and Superoxide Dismutase. Experimental work was carried out at Dallmann laboratory, Carlini Station in Potter Cove (58°40'W; 62°14'S), South Shetland Islands, Antarctica; during the summer campaign 2015/2016. Animals were collected by SCUBA diving at 20-30 m water depth (58°39'37,86W; 62°14'6, 153S), placed in containers with seawater from the sampling site, and immediately transferred to the experimental facilities of the laboratory. Specimens were placed in a 100 L container after cleaning their tunics from large epibionts. Both species were kept in an open flow system with unfiltered natural seawater (0 ± 1 °C) directly pumped from the cove for ten days, to allow for recovery from sampling and acclimation to the experimental system. Thereafter, specimens (n=10) with similar body sizes (approximately 10cm high) were selected, and 1-2 individuals were placed randomly in six aquaria (8 L), with individual closed circulation systems (EHEIM universal 300 Water Pump (300l/h)) and a venturi to assure constant aeration inside the aquaria. The six aquaria were placed in a 90 L running seawater bath (open system) for the incubation experiments in order to keep constant temperature (1.76 ± 0.37 °C). Treatment was applied to three aquaria which consisted in applying a single pulse of 200 mg L-1 of sediment per experimental aquarium. The experiment was stopped when turbidity was no longer observed in the water (36 h after exposure). The control treatments were maintained in seawater without sediment addition. Sediment used for the treatment was obtained using a grab sampler at 20 m depth ...