Contributors | Affiliation | Role |
---|---|---|
Edwards, Matthew | San Diego State University (SDSU) | Principal Investigator |
Konar, Brenda | University of Alaska Fairbanks (UAF) | Co-Principal Investigator |
Bland, Aaron S. | University of Alaska Fairbanks (UAF) | Contact |
Copley, Nancy | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
This dataset includes epibenthic community abundance collected offshore by trawls and reported as numbers per 100 square meters.
Sampling locations were from the Aleutian Archipelago offshore between longitude 173.9 and -167.6 in June 2016 and July 2017.
Trawls were conducted with a 3.05 m plumb-staff beam trawl with a 7-mm mesh and a 4-mm codend liner (Gunderson & Ellis, 1986). For each trawl, the trawl net was towed for approximately 3 minutes on the seafloor with the vessel traveling at 1.5 knots. A temperature-depth recorder was attached to the trawl net to determine effective trawling distances. The start of each trawl was determined by the time at which the trawl net stopped descending in the depth profile, and the end of each trawl was determined by the time the trawl net began ascending. Trawl distances were determined by referencing the GPS coordinates of the research vessel for the start and end times of each trawl event. Occasionally, the trawl net became damaged by rocks during a trawl event, preventing effective sampling after the collision. For these trawls, the collision point was detectable by a sudden decrease in depth of the trawl net, and the effective trawling swath was assumed to be from the beginning of the trawl up to the collision point.
Organisms were sorted and identified to the lowest taxonomic level feasible. Members of each taxonomic group were counted and their damp-biomass (including shells for mollusks and crabs) was determined. Voucher specimens were prepared in 10% buffered formalin for those taxa that could not be identified in the field.
Some large samples were split in half. This is Indicated as the subsaample_factor. A value of 2 (trawl 24) indicates that half of the trawl contents were taken for biomass and count measurements. The biomass and count values in the area-standardized data sheets are estimated by doubling the values recorded for the subsampled portion.
BCO-DMO Processing Notes:
- added conventional header with dataset name, PI name, version date
- modified parameter names to conform with BCO-DMO naming conventions
- corrected spelling of 4 taxa to agree with World Register of Marine Species names. See Parameter list below for submitted names, in parentheses.
File |
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abund_trawl.csv (Comma Separated Values (.csv), 28.24 KB) MD5:3d6e418e51a88b0550f379b7b450eec0 Primary data file for dataset ID 729630 |
Parameter | Description | Units |
Island | sampled Island location | unitless |
Region | A priori region designation: central; east; west; far-west | unitless |
Trawl_Distance_m | Effective trawling distance based on estimates of trawling start/end locations | meters |
Trawl_Area | Effective trawling area; trawl distance multiplied by the trawling width of the net (2.26 m) | meters^2 |
Subsample_Factor | Subsample indicator. Value of 2 indicates that half of the trawl contents were taken for biomass and count measurements. | unitless |
Start_Latitude | Estimated location of the research vessel when the trawl net reached the bottom | decimal degrees |
Start_Longitude | Estimated location of the research vessel when the trawl net reached the bottom | decimal degrees |
End_Latitude | Estimated location of the research vessel when the trawl net reached the bottom OR the net collided with a rock (ending effective trawling) | decimal degrees |
End_Longitude | Estimated location of the research vessel when the trawl net reached the bottom OR the net collided with a rock (ending effective trawling) | decimal degrees |
Start_Date_UTM | Starting time for each trawl event; UTC | unitless |
Sample | sample identifier | unitless |
Acmaea_mitra | abundance of Acmaea mitra | individuals per 100m^2 |
Actinaria_sp_1 | abundance of Actinaria sp. 1 | individuals per 100m^2 |
Actinaria_sp_3 | abundance of Actinaria sp. 3 | individuals per 100m^2 |
Agonidae | abundance of Agonidae | individuals per 100m^2 |
Agonidae_juvenile | abundance of Agonidae; juvenile | individuals per 100m^2 |
Ammodytes_hexapterus | abundance of Ammodytes hexapterus | individuals per 100m^2 |
Ammodytidae_sp | abundance of Ammodytidae sp. | individuals per 100m^2 |
Ampelisca_sp | abundance of Ampelisca sp. | individuals per 100m^2 |
Amphiophiura_sp | abundance of Amphiophiura sp. | individuals per 100m^2 |
Amphipoda | abundance of Amphipoda | individuals per 100m^2 |
Amphiura_spp | abundance of Amphiura spp. | individuals per 100m^2 |
Anonyx_spp | abundance of Anonyx spp. | individuals per 100m^2 |
Anoplarchus_insignis | abundance of Anoplarchus insignis | individuals per 100m^2 |
Aptocyclus_ventricosus | abundance of Aptocyclus ventricosus | individuals per 100m^2 |
Arctonoe_vittata | abundance of Arctonoe vittata | individuals per 100m^2 |
Argis_sp | abundance of Argis sp. | individuals per 100m^2 |
Artedius_lateralis | abundance of Artedius lateralis | individuals per 100m^2 |
Aspidophoroides_monopterygius | abundance of Aspidophoroides monopterygius | individuals per 100m^2 |
Asteroidea_no_ID | abundance of Asteroidea; un-ID | individuals per 100m^2 |
Atheresthes_spp | abundance of Atheresthes spp. | individuals per 100m^2 |
Axinella_blanca | abundance of Axinella blanca | individuals per 100m^2 |
Bathyagonus_alascanus | abundance of Bathyagonus alascanus | individuals per 100m^2 |
Bathyagonus_nigripinnis | abundance of Bathyagonus nigripinnis | individuals per 100m^2 |
Bathymaster_signatus | abundance of Bathymaster signatus | individuals per 100m^2 |
Bathypolypus_spp | abundance of Bathypolypus spp. | individuals per 100m^2 |
Bathyraja_parmifera | abundance of Bathyraja parmifera | individuals per 100m^2 |
Blepsias_bilobus | abundance of Blepsias bilobus | individuals per 100m^2 |
Boltenia_ovifera | abundance of Boltenia ovifera | individuals per 100m^2 |
Boreotrophon_spp | abundance of Boreotrophon spp. | individuals per 100m^2 |
Brachiopoda | abundance of Brachiopoda | individuals per 100m^2 |
Brachyura_no_ID | abundance of Brachyura; un-ID | individuals per 100m^2 |
Buccinidae | abundance of Buccinidae | individuals per 100m^2 |
Ceramaster_arcticus | abundance of Ceramaster arcticus | individuals per 100m^2 |
Ceramaster_patagonicus | abundance of Ceramaster patagonicus | individuals per 100m^2 |
Cheiraster_Luidiaster_dawsoni | abundance of Cheiraster (Luidiaster) dawsoni | individuals per 100m^2 |
Chionoecetes_bairdi | abundance of Chionoecetes bairdi | individuals per 100m^2 |
Chionoecetes_opilio | abundance of Chionoecetes opilio | individuals per 100m^2 |
Chirona_evermanni | abundance of Chirona evermanni | individuals per 100m^2 |
Chiton_no_ID | abundance of Chiton; un-ID | individuals per 100m^2 |
Chlamys_rubida | abundance of Chlamys rubida | individuals per 100m^2 |
Chrysaora_melanaster | abundance of Chrysaora melanaster | individuals per 100m^2 |
Ciliatocardium_ciliatum | abundance of Ciliatocardium ciliatum | individuals per 100m^2 |
Clinocottus_sp | abundance of Clinocottus sp. | individuals per 100m^2 |
Colus_sp | abundance of Colus sp. | individuals per 100m^2 |
Cottoidea_juvenile | abundance of Cottoidea; juvenile | individuals per 100m^2 |
Crangonidae | abundance of Crangonidae | individuals per 100m^2 |
Cranopsis_sp | abundance of Cranopsis sp. | individuals per 100m^2 |
Crepidula_sp | abundance of Crepidula sp. | individuals per 100m^2 |
Crossaster_papposus | abundance of Crossaster papposus | individuals per 100m^2 |
Cryptacanthodes_aleutensis | abundance of Cryptacanthodes aleutensis | individuals per 100m^2 |
Cryptonatica_spp | abundance of Cryptonatica spp. | individuals per 100m^2 |
Crystallichthys_cyclospilus | abundance of Crystallichthys cyclospilus | individuals per 100m^2 |
Ctenodiscus_sp | abundance of Ctenodiscus sp. | individuals per 100m^2 |
Cucumaria_fallax | abundance of Cucumaria fallax | individuals per 100m^2 |
Cucumaria_sp | abundance of Cucumaria sp. | individuals per 100m^2 |
Cup_coral_unid | abundance of Cup coral unid. | individuals per 100m^2 |
Dendraster_sp | abundance of Dendraster sp. | individuals per 100m^2 |
Dendronotus_sp | abundance of Dendronotus sp. | individuals per 100m^2 |
Diaulula_sandiegensis | abundance of Diaulula sandiegensis | individuals per 100m^2 |
Diaulula_sp | abundance of Diaulula sp. | individuals per 100m^2 |
Diplopteraster_multipes | abundance of Diplopteraster multipes | individuals per 100m^2 |
Doridoidea | abundance of Doridoidea | individuals per 100m^2 |
Doris_odhneri | abundance of Doris odhneri | individuals per 100m^2 |
Doris_sp | abundance of Doris sp. | individuals per 100m^2 |
Echinarachnius_parma | abundance of Echinarachnius parma | individuals per 100m^2 |
Elassochirus_spp | abundance of Elassochirus spp. | individuals per 100m^2 |
Erimacrus_isenbeckii | abundance of Erimacrus isenbeckii | individuals per 100m^2 |
Eumicrotremus_orbis | abundance of Eumicrotremus orbis | individuals per 100m^2 |
Eupentacta_sp | abundance of Eupentacta sp. | individuals per 100m^2 |
Fish_larvae_no_ID | abundance of Fish larvae; un-ID | individuals per 100m^2 |
Flabellina_spp | abundance of Flabellina spp. | individuals per 100m^2 |
Flatfish_juvenile | abundance of Flatfish; juvenile | individuals per 100m^2 |
Flatfish_no_ID | abundance of Flatfish; un-ID | individuals per 100m^2 |
Fusitriton_oregonensis | abundance of Fusitriton oregonensis | individuals per 100m^2 |
Gadus_chalcogrammus | abundance of Gadus chalcogrammus | individuals per 100m^2 |
Gastropoda_sp_1 | abundance of Gastropoda sp. 1 | individuals per 100m^2 |
Glebocarcinus_oregonensis | abundance of Glebocarcinus oregonensis | individuals per 100m^2 |
Glebocarcinus_sp | abundance of Glebocarcinus sp. | individuals per 100m^2 |
Gobiesocidae | abundance of Gobiesocidae | individuals per 100m^2 |
Gorgonocephalus_eucnemis | abundance of Gorgonocephalus eucnemis | individuals per 100m^2 |
Gymnocanthus_galeatus | abundance of Gymnocanthus galeatus | individuals per 100m^2 |
Gymnocanthus_tricuspis | abundance of Gymnocanthus tricuspis | individuals per 100m^2 |
Halocynthia_aurantium | abundance of Halocynthia aurantium | individuals per 100m^2 |
Hemilepidotus_hemilepidotus | abundance of Hemilepidotus hemilepidotus | individuals per 100m^2 |
Hemilepidotus_jordani | abundance of Hemilepidotus jordani | individuals per 100m^2 |
Hemilepidotus_spinosus | abundance of Hemilepidotus spinosus | individuals per 100m^2 |
Hemithiris_psittacea | abundance of Hemithiris psittacea | individuals per 100m^2 |
Hemitripterus_bolini | abundance of Hemitripterus bolini | individuals per 100m^2 |
Henricia_leviuscula_complex | abundance of Henricia leviuscula (complex) | individuals per 100m^2 |
Henricia_sp_1 | abundance of Henricia sp. 1 | individuals per 100m^2 |
Henricia_sp_2 | abundance of Henricia sp. 2 | individuals per 100m^2 |
Hermissenda_sp | abundance of Hermissenda sp. | individuals per 100m^2 |
Hiatella_arctica | abundance of Hiatella arctica | individuals per 100m^2 |
Hippasteria_phrygiana | abundance of Hippasteria phrygiana | individuals per 100m^2 |
Hippoglossoides_dubius | abundance of Hippoglossoides dubius | individuals per 100m^2 |
Hippoglossoides_elassodon | abundance of Hippoglossoides elassodon | individuals per 100m^2 |
Hippoglossus_stenolepis | abundance of Hippoglossus stenolepis | individuals per 100m^2 |
Hippolytidae | abundance of Hippolytidae | individuals per 100m^2 |
Horned_sculpin_maybe | abundance of Horned sculpin (?) | individuals per 100m^2 |
Hyas_spp | abundance of Hyas spp. | individuals per 100m^2 |
Hypsagonus_quadricornis | abundance of Hypsagonus quadricornis | individuals per 100m^2 |
Icelinus_borealis | abundance of Icelinus borealis | individuals per 100m^2 |
Isopoda | abundance of Isopoda | individuals per 100m^2 |
Kallymeniopsis_sp_drift | abundance of Kallymeniopsis sp.; drift | individuals per 100m^2 |
Labidochirus_sp | abundance of Labidochirus sp. | individuals per 100m^2 |
Labidochirus_splendescens | abundance of Labidochirus splendescens | individuals per 100m^2 |
Lacuna_sp | abundance of Lacuna sp. | individuals per 100m^2 |
Lamellaria_sp | abundance of Lamellaria sp. | individuals per 100m^2 |
Laminaria_longipes_drift | abundance of Laminaria longipes; drift | individuals per 100m^2 |
Leodice_valens | abundance of Leodice valens | individuals per 100m^2 |
Lepeta_sp | abundance of Lepeta sp. | individuals per 100m^2 |
Lepidopsetta_bilineata | abundance of Lepidopsetta bilineata | individuals per 100m^2 |
Leptasterias_Hexasterias_alaskensis | abundance of Leptasterias (Hexasterias) alaskensis | individuals per 100m^2 |
Leptasterias_Hexasterias_coei_truculenta | abundance of Leptasterias (Hexasterias) coei truculenta | individuals per 100m^2 |
Leptasterias_arctica | abundance of Leptasterias arctica | individuals per 100m^2 |
Leptasterias_hylodes | abundance of Leptasterias hylodes | individuals per 100m^2 |
Leptasterias_nitida | abundance of Leptasterias nitida | individuals per 100m^2 |
Leptasterias_spp | abundance of Leptasterias spp. | individuals per 100m^2 |
Leptocottus_armatus | abundance of Leptocottus armatus | individuals per 100m^2 |
Leptychaster_anomalus | abundance of Leptychaster anomalus | individuals per 100m^2 |
Leptychaster_arcticus | abundance of Leptychaster arcticus | individuals per 100m^2 |
Leptychaster_pacificus | abundance of Leptychaster pacificus | individuals per 100m^2 |
Lethasterias_nanimensis | abundance of Lethasterias nanimensis | individuals per 100m^2 |
Limneria_prolongata | abundance of Limneria prolongata | individuals per 100m^2 |
Liparidae | abundance of Liparidae | individuals per 100m^2 |
Liparis_cyclopus | abundance of Liparis cyclopus | individuals per 100m^2 |
Liparis_sp | abundance of Liparis sp. | individuals per 100m^2 |
Lumpenus_sagitta | abundance of Lumpenus sagitta | individuals per 100m^2 |
Lycodes_brevipes | abundance of Lycodes brevipes | individuals per 100m^2 |
Malacocottus_zonurus | abundance of Malacocottus zonurus | individuals per 100m^2 |
Maxillopoda | abundance of Maxillopoda | individuals per 100m^2 |
Metridium_spp | abundance of Metridium spp. | individuals per 100m^2 |
Modiolus_modiolus | abundance of Modiolus modiolus | individuals per 100m^2 |
Molgula_sp | abundance of Molgula sp. | individuals per 100m^2 |
Musculus_discors | abundance of Musculus discors | individuals per 100m^2 |
Musculus_sp | abundance of Musculus sp. | individuals per 100m^2 |
Myoxocephalus_polyacanthocephalus | abundance of Myoxocephalus polyacanthocephalus | individuals per 100m^2 |
Myoxocephalus_scorpius | abundance of Myoxocephalus scorpius | individuals per 100m^2 |
Naticidae | abundance of Naticidae | individuals per 100m^2 |
Nemertea | abundance of Nemertea | individuals per 100m^2 |
Neoptilota_sp_drift | abundance of Neoptilota sp.; drift | individuals per 100m^2 |
Neptunea_sp | abundance of Neptunea sp. | individuals per 100m^2 |
Nereididae | abundance of Nereididae | individuals per 100m^2 |
Octopoda_juvenile | abundance of Octopoda; juvenile | individuals per 100m^2 |
Odontohenricia_ahearnae | abundance of Odontohenricia ahearnae | individuals per 100m^2 |
Odontohenricia_fisheri | abundance of Odontohenricia fisheri | individuals per 100m^2 |
Odontohenricia_sp | abundance of Odontohenricia sp. | individuals per 100m^2 |
Oenopota_sp | abundance of Oenopota sp. | individuals per 100m^2 |
Ophiolimna_sp | abundance of Ophiolimna sp. | individuals per 100m^2 |
Ophiopholis_aculeata | abundance of Ophiopholis aculeata | individuals per 100m^2 |
Ophiura_sarsii | abundance of Ophiura sarsii | individuals per 100m^2 |
Oregonia_gracilis | abundance of Oregonia gracilis | individuals per 100m^2 |
Orthasterias_koehleri | abundance of Orthasterias koehleri | individuals per 100m^2 |
Pagurus_spp | abundance of Pagurus spp. | individuals per 100m^2 |
Pandora_glacialis | abundance of Pandora glacialis | individuals per 100m^2 |
Pandora_wardiana | abundance of Pandora wardiana | individuals per 100m^2 |
Patinopecten_caurinus | abundance of Patinopecten caurinus | individuals per 100m^2 |
Pedicellaster_magister | abundance of Pedicellaster magister | individuals per 100m^2 |
Peltodoris_nobilis | abundance of Peltodoris nobilis | individuals per 100m^2 |
Peribolaster_biserialis | abundance of Peribolaster biserialis | individuals per 100m^2 |
Pleurogrammus_monopterygius | abundance of Pleurogrammus monopterygius | individuals per 100m^2 |
Plicifusus_sp | abundance of Plicifusus sp. | individuals per 100m^2 |
Pododesmus_macrochisma | abundance of Pododesmus macrochisma | individuals per 100m^2 |
Podothecus_accipenserinus | abundance of Podothecus accipenserinus | individuals per 100m^2 |
Polychaeta | abundance of Polychaeta | individuals per 100m^2 |
Polynoidae | abundance of Polynoidae | individuals per 100m^2 |
Poroclinus_rothrocki | abundance of Poroclinus rothrocki | individuals per 100m^2 |
Psychrolutes_paradoxus | abundance of Psychrolutes paradoxus | individuals per 100m^2 |
Pteraster_marsippus | abundance of Pteraster marsippus | individuals per 100m^2 |
Pteraster_militaris | abundance of Pteraster militaris | individuals per 100m^2 |
Pteraster_sp | abundance of Pteraster sp. | individuals per 100m^2 |
Pteraster_tesselatus | abundance of Pteraster tesselatus | individuals per 100m^2 |
Ptilosarcus_gurneyi | abundance of Ptilosarcus gurneyi | individuals per 100m^2 |
Pugettia_gracilis | abundance of Pugettia gracilis | individuals per 100m^2 |
Pycnogonida | abundance of Pycnogonida | individuals per 100m^2 |
Pycnopodia_helianthoides | abundance of Pycnopodia helianthoides | individuals per 100m^2 |
Rhamphostomella_costata | abundance of Rhamphostomella costata | individuals per 100m^2 |
Rocinela_angustata | abundance of Rocinela angustata | individuals per 100m^2 |
Ronquil_no_ID | abundance of Ronquil; un-ID | individuals per 100m^2 |
Ronquilus_jordani | abundance of Ronquilus jordani | individuals per 100m^2 |
Rossia_pacifica | abundance of Rossia pacifica | individuals per 100m^2 |
Sabellidae | abundance of Sabellidae | individuals per 100m^2 |
Saccharina_sp_drift | abundance of Saccharina sp.; drift | individuals per 100m^2 |
Sarritor_frenatus | abundance of Sarritor frenatus | individuals per 100m^2 |
Sculpin_no_ID | abundance of Sculpin; un-ID | individuals per 100m^2 |
Sebastes_alutus | abundance of Sebastes alutus | individuals per 100m^2 |
Sebastes_ciliatus | abundance of Sebastes ciliatus | individuals per 100m^2 |
Sergeant_poacher | abundance of Sergeant poacher | individuals per 100m^2 |
Serripes_groenlandicus | abundance of Serripes groenlandicus | individuals per 100m^2 |
Similipecten_greenlandicus | abundance of Similipecten greenlandicus | individuals per 100m^2 |
Sipuncula_sp_1 | abundance of Sipuncula sp. 1 | individuals per 100m^2 |
Sipuncula_sp_2 | abundance of Sipuncula sp. 2 | individuals per 100m^2 |
Solariella_spp | abundance of Solariella spp. | individuals per 100m^2 |
Solaster_spp | abundance of Solaster spp. | individuals per 100m^2 |
Stegocephalus_sp | abundance of Stegocephalus sp. | individuals per 100m^2 |
Stomphia_sp | abundance of Stomphia sp. | individuals per 100m^2 |
Strongylocentrotus_spp | abundance of Strongylocentrotus spp. | individuals per 100m^2 |
Suberites_spp | abundance of Suberites spp. | individuals per 100m^2 |
Tachyrhynchus_sp | abundance of Tachyrhynchus sp. | individuals per 100m^2 |
Tonicella_sp | abundance of Tonicella sp. | individuals per 100m^2 |
Triglops_macellus | abundance of Triglops macellus | individuals per 100m^2 |
Triglops_pingelii | abundance of Triglops pingelii | individuals per 100m^2 |
Triopha_catalinae | abundance of Triopha catalinae | individuals per 100m^2 |
Tripoplax_trifida | abundance of Tripoplax trifida | individuals per 100m^2 |
Tritonia_spp | abundance of Tritonia spp. | individuals per 100m^2 |
Tunicata_sp_1 | abundance of Tunicata sp. 1 | individuals per 100m^2 |
Tunicata_sp_1a | abundance of Tunicata sp. 1 | individuals per 100m^2 |
Urticina_sp | abundance of Urticina sp. | individuals per 100m^2 |
Velutina_spp | abundance of Velutina spp. | individuals per 100m^2 |
Volutopsius_sp | abundance of Volutopsius sp. | individuals per 100m^2 |
Dataset-specific Instrument Name | |
Generic Instrument Name | Beam Trawl |
Dataset-specific Description | A 3.05 m plumb-staff beam trawl with a 7-mm mesh and a 4-mm codend liner |
Generic Instrument Description | A beam trawl consists of a cone-shaped body ending in a bag or codend, which retains the catch. In these trawls the horizontal opening of the net is provided by a beam, made of wood or metal, which is up to 12 m long. The vertical opening is provided by two hoop-like trawl shoes mostly made from steel. No hydrodynamic forces are needed to keep a beam trawl open. The beam trawl is normally towed on outriggers, one trawl on each side.
While fishing for flatfish the beam trawl is often equipped with tickler chains to disturb the fish from the seabed. For operations on very rough fishing grounds they can be equipped with chain matrices. Chain matrices are rigged between the beam and the groundrope and prevent boulders/stones from being caught by the trawl. Shrimp beam trawls are not so heavy and have smaller mesh sizes. A bobbin of groundrope with rubber bobbins keeps the shrimp beam trawl in contact with the bottom and gives flatfish the opportunity to escape.
Close bottom contact is necessary for successful operation. To avoid bycatch of most juvenile fishes selectivity devices are assembled (sieve nets, sorting grids, escape holes). While targeting flatfish the beam trawls are towed up to seven knots, therefore the gear is very heavy; the largest gears weighs up to 10 ton. The towing speed for shrimp is between 2.5 and 3 knots.
(from: http://www.fao.org/fishery/geartype/305/en) |
Website | |
Platform | R/V Oceanus |
Start Date | 2016-06-17 |
End Date | 2016-07-02 |
Description | Project: Changes in Ecosystem Production and Benthic Biodiversity |
Website | |
Platform | R/V Oceanus |
Start Date | 2017-07-18 |
End Date | 2017-07-25 |
Description | Project: Changes in Ecosystem Production and Benthic Biodiversity |
NSF abstract:
In many ecosystems the presence of a single dominant species can modify the physical conditions of the environment and alter patterns of biodiversity, nutrient cycling, and primary production. Losses of these "ecosystem engineers" can have profound impacts to how ecosystems function. Coastal kelps provide excellent examples of organisms whose structure modifies the physical characteristics of their habitats (light, nutrients, water motion) and supports enhanced biodiversity. The kelp forests in the coastal waters of the Aleutian Archipelago have suffered large-scale declines over the past several decades. This project will examine how these losses impact patterns of ecosystem production and biodiversity using a combination of techniques ranging from in situ benthic chambers and shipboard incubations to remote sensing using satellite imagery. The results will provide an understanding of how such events may impact this and other ecosystems. This project will support graduate students and will introduce the public to the Aleutian ecosystems in a series of videos. The investigators will also work with a San Diego high school teacher to integrate project findings into classroom activities, and they expect to involve a teacher in their field program.
The investigators will ask two highly integrated questions: 1) How do the widespread losses of kelp forests impact benthic productivity across the Aleutian Archipelago? 2) How do the widespread losses of kelp forests impact benthic biodiversity and community structure across the archipelago? To address these, the investigators will estimate changes to productivity at ten islands where they have historic data on seaweed community composition and estimates of kelp canopy cover. They will use in situ benthic chambers placed in both kelp forests and urchin barrens to measure plot-scale patterns of net ecosystem productivity (NEP), and shipboard incubations to examine net primary productivity (NPP) for the dominant macroalgae. Data for individual species rates of NPP will be scaled by their biomass and combined with in situ plot-scale benthic chamber experiments of whole communities to estimate NEP at the islands visited. These estimates will be scaled up to calculate NEP across the entire archipelago by first extrapolating results from the study sites to entire islands, and then across the archipelago. They will also estimate broad-scale patterns in production by characterizing water column irradiances across the archipelago and modeling NPP using species-level relationships between irradiance and photosynthesis. Coupling these with estimates of water column irradiance and community respiration will allow modeling of NEP across this region. Benthic biodiversity will be assessed using diver surveys and shipboard benthic trawls. Following these activities, satellite remote sensing of the kelp canopies dating back to the 1980s and the investigators' own historical data on benthic macroalgal abundances at these and other islands will be used to estimate the temporal and spatial patterns of change across the archipelago.
For more information see:
Project blog: http://sdsukelp.weebly.com/blog
Project website: http://www.uaf.edu/cfos/research/projects/collaborative-research--/
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) | |
NSF Division of Ocean Sciences (NSF OCE) |