| Carbonate chemistry, shell growth, and respiration data from laboratory experiments on California mussel larvae condcuted at the Hatfield Marine Science Center, Newport, OR in 2013 | | biological oxygen demand (BOD) bottles |
| Water samples from CTD casts and vehicle-mounted bottles from the R/V Atlantis, R/V Ronald Brown, R/V Falkor, & E/V Nautilus in the Gulf of Mexico & Florida from 2010 to 2014 (Lophelia OA project) | Water samples collected by vehicle-mounted bottle
| Vehicle mounted bottle |
| Major ion and carbonate chemistry of water in which oyster larvae were reared from Whiskey Creek Shellfish Hatchery in Netarts Bay, OR, USA from 2009-2011 | | amber glass bottles |
| Diatom cultures used to generate DNA reference library from samples collected from sites in Alpena, Michigan and Palm Coast, Florida between July 2021 & 2022. | | 250mL Nalgene bottles |
| Diel variability in discrete samples of reef seawater temperature, salinity, dissolved inorganic carbon, pH, and stable carbon isotopes from Willemstad, Curaçao from February 2023 to May 2025 | Water samples from each Niskin cast were transferred without exposure to the atmosphere to 300 ml Wheaton borosilicate glass BOD bottles and immediately poisoned with saturated mercuric chloride for dissolved inorganic carbon analyses.
| Wheaton 300 mL BOD borosilicate glass bottles with stoppers |
| Dissolved oxygen and potential density measurements from the R/V Atlantis, R/V Ronald Brown, & E/V Nautilus in the Gulf of Mexico & Florida from 2010-2014 (Lophelia OA project) | Water samples collected by vehicle-mounted bottle
| Vehicle mounted bottle |
| Elemental compositions (Mg, Ca, Sr, N, C) of larval oyster shells from Whiskey Creek Shellfish Hatchery in Netarts Bay, OR, USA from 2009-2011 | | amber glass bottles |
| Dissolved lead data collected from the R/V Pourquoi pas (GEOVIDE) in the North Atlantic, Labrador Sea (section GA01) during 2014 | The General Oceanics Inc Model 1018 Intelligent Rosette was equipped with 22 new 12L GO-FLO bottles.
| 12L GO-FLO |
| Lead isotope data collected from the R/V Pourquoi pas (GEOVIDE) in the North Atlantic, Labrador Sea (section GA01) during 2014 | The General Oceanics Inc Model 1018 Intelligent Rosette was equipped with 22 new 12L GO-FLO bottles.
| 12L GO-FLO |
| Measurement of dissolved CFC-11, CFC-12, CFC-113, and SF₆ from Niskin bottles on the US GEOTRACES GP-17 OCE cruise RR2214 on R/V Roger Revelle from December 2022 to January 2023 | | BOD bottle |
| Water temperature, salinity, and other data from CTD taken from the RV Sikuliaq in the Pacific Ocean between San Diego, California and Manzanillo, Mexico from 2016-12-21 to 2017-01-13. | | |
| Isotopes in methane in natural waters of Alaska | Sample collection followed previously established methods into glass wheaton bottles, as did measurement of methane concentration.
| glass wheaton bottles |
| Winter survey data from Lake Erie from Feb 2022 to Mar 2022 | Water samples are then transferred to 1 L polyethylene storage bottles or 2 L plastic storage bottles, and stored in a dark place at 4 oC until picked up by personnel on the same day.
Total and dissolved nutrient samples will be held in acid-washed 250 mL polyethylene bottles, and stored in a dark freezer at -20 oC until they are ready to be analyzed.
| Sample bottles, 1 or 2 L (Nalgene or equivalent), Plastic wash bottle, 500 mL |
| Winter survey data from Lake Erie from Mar 2023 to May 2024 | Water samples are then transferred to 1 L polyethylene storage bottles or 2 L plastic storage bottles, and stored in a dark place at 4 oC until picked up by personnel on the same day.
Total and dissolved nutrient samples will be held in acid-washed 250 mL polyethylene bottles, and stored in a dark freezer at -20 oC until they are ready to be analyzed.
| Sample bottles, 1 or 2 L (Nalgene or equivalent), Plastic wash bottle, 500 mL |
| Measured and calculated geochemistry values and uncertainty for water samples taken from the water column of Celestun Lagoon, Yucatan, Mexico in May of 2015 | LDPE bottles: water samples were collected in acid-washed LDPE bottles for trace metals.
Rubber septum glass vials: water samples were collected in ashed glass bottles for nutrients.
| |
| Methane concentrations from depths of 5 to 175 meters at Station ALOHA collected during Hawaii Ocean Time-Series cruises between 2008 and 2016 | These Niskin-like bottles were designed by John Bullister (NOAA Pacific Marine Environmental Laboratory (PMEL)) to specifically minimize contamination for trace gases, in particular chlorofluorocarbons and sulfur hexafluoride (Bullister and Wisegarver, 2008).
| water sampling bottles to reduce trace gas contamination |
| Q incubation data from the R/V Melville (MV1405) cruise along the California coast during July 2014 | Contained seawater samples
| LDPE bottles |
| Water characteristics measured in Narragansett Bay over two years, from March 2021 to September 2023 | Water was collected from a dock in a 1 L bottle.
| bottle |
| Nitrous oxide concentrations from depths of 5 to 175 meters at Station ALOHA collected during Hawaii Ocean Time-Series cruises between 2008 and 2016 | These Niskin-like bottles were designed by John Bullister (NOAA Pacific Marine Environmental Laboratory (PMEL)) to specifically minimize contamination for trace gases, in particular chlorofluorocarbons and sulfur hexafluoride (Bullister and Wisegarver, 2008).
| water sampling bottles to reduce trace gas contamination |
| Environmental and physical data associated with ocean acidification microbe adaptation from 2012-2014 | Used in nutrient analysis
| HDPE bottle |
| Chemistry and organism response data from Waldbusser et al. 2015, Nature Climate Change; from experiments conducted at the Hatfield Marine Science Center, Newport, OR in 2013 | | Biological Oxygen Demand (BOD) bottles |
| Water column particulate silica, standing stocks, and productivity rates from R/V Atlantic Explorer cruises AE1218, AE1228, AE1319, AE1322 in Bermuda, and NW Atlantic from 2012-2013 (Si_in_Syn project) | | |
| Phytoplankton abudance and physical environmental data from niskin bottles off the coast of Juneau, Alaska from 2015-2016 (SEAK-AHAB project) | 2.2L horizontal pvc
| Bottle |
| Cyanobacterial and diatom samples collecteced between April and September 2022, and sequenced for metabarcodig of 16S and rbcL. | | 250mL Nalgene bottles |
| The effect of altered carbonate system chemistry on the abiotic formation of Transparent Exopolymer Particles (TEP) from UCSB MSI Passow Laboratory from 2009 to 2010 (OA - Ocean Acidification and Aggregation project) | Experiments 3 and 4, respectively, were conducted with 10 μm pre-filtered natural seawater and 10 μm pre-filtered sea water first incubated in 20 L bottles (bottle blooms).
| bottle |
| The effect of altered carbonate system chemistry on the abiotic formation of Transparent Exopolymer Particles (TEP).from UCSB MSI Passow Lab from 2009 to 2010 (OA - Ocean Acidification and Aggregation project) | Experiments 3 and 4, respectively, were conducted with 10 μm pre-filtered natural seawater and 10 μm pre-filtered sea water first incubated in 20 L bottles (bottle blooms).
| Bottle |
| Winter survey data from Lake Erie from Dec 2022 to Mar 2023 | Water samples are then transferred to 1 L polyethylene storage bottles or 2 L plastic storage bottles, and stored in a dark place at 4 oC until picked up by personnel on the same day.
Total and dissolved nutrient samples will be held in acid-washed 250 mL polyethylene bottles, and stored in a dark freezer at -20 oC until they are ready to be analyzed.
| Sample bottles, 1 or 2 L (Nalgene or equivalent), Plastic wash bottle, 500 mL |
©2020 Biological and Chemical Oceanography Data Management Office.