Abstract
Knowledge of concentrations and elemental ratios of suspended particles are important for understanding many biogeochemical processes in the ocean. These include patterns of phytoplankton nutrient limitation as well as linkages between the cycles of carbon and nitrogen or phosphorus. To further enable studies of ocean biogeochemistry, we here present a global dataset consisting of 100,605 total measurements of particulate organic carbon, nitrogen, or phosphorus analyzed as part of 70 cruises or time-series. The data are globally distributed and represent all major ocean regions as well as different depths in the water column. The global median C:P, N:P, and C:N ratios are 163, 22, and 6.6, respectively, but the data also includes extensive variation between samples from different regions. Thus, this compilation will hopefully assist in a wide range of future studies of ocean elemental ratios.
Background & Summary
One of the fundamental tenets of ocean biogeochemistry is the Redfield ratio. Redfield identified a similarity between the N:P ratio of plankton living in the surface ocean and that of dissolved nitrate and phosphate in the deep ocean1,2. He hypothesized that the deep ocean nutrient concentrations were controlled by the elemental requirements of the surface plankton. This concept has been extended to include other elements like carbon and remains a cornerstone for our understanding of ocean biogeochemistry. Despite the importance of this ratio, there is no obvious mechanism for a globally consistent C:N:P ratio of 106:16:1 (i.e., Redfield ratio), and there is substantial elemental variation among ocean taxa3–6. Furthermore, many small plankton are not homeostatic but instead, the cellular elemental content varies depending on growth conditions7. Thus, it has become apparent that changes in biodiversity or cell physiology can lead to variations in marine plankton elemental stoichiometry.
Variations in elemental content and ratios of marine microbial communities have multiple important implications. Broecker and Henderson have proposed that increased plankton C:N:P ratios and thus increased CO2 uptake in the ocean could explain the glacial to inter-glacial variation in atmospheric CO2 concentration8. Rates of N2 fixation as well as competition between phytoplankton and N2-fixers are also dependent upon an assumed N:P ratio (specifically the Redfield ratio). Recently, multiple researchers have argued that our understanding (or lack thereof) of cellular elemental stoichiometry has a large influence on our ability to estimate the global ocean N budget9,10.
It has been observed that specific phytoplankton groups as well as particulate organic matter display regional differences in elemental stoichiometry11–14. For example, the C:P, N:P, and C:N ratios all appear to be above Redfield proportions in the oligotrophic gyres, near Redfield proportions in upwelling regions like the Eastern Equatorial Pacific Ocean, and below Redfield proportions in colder, nutrient rich high latitude environments11,12. The ratios may also vary between the gyres depending on the nutrient supply ratio and the resulting degree of nitrogen versus phosphorus limitation. Thus, rather than globally static C:N:P ratios, differences in environmental conditions and plankton community composition can lead to variations in the elemental composition of plankton and particulate organic material4,11–13,15. In addition, we also observe extensive variations in the ratios of particulate nutrients which cannot be explained with common physio-chemical parameters11,12. Thus, future studies are needed to identify factors causing this variation.
The elemental stoichiometry of ocean plankton communities has also been the focus in many model studies10,15–17. This includes models describing cellular elemental composition in response to changes in light intensity, nutrients, or other environment conditions16,17. Other models focus on identifying regional differences in the elemental stoichiometry15. Thus, models have indicated that the elemental stoichiometry of cells, communities, and ocean regions are not constant but vary depending on biodiversity and environmental conditions. However, we currently do not have global datasets to evaluate the output of such models.
To address this issue, we here present a compilation of measurements of marine particulate organic carbon (POC), nitrogen (PON), and phosphorus (POP) from 70 cruises or time-series during the last 40 years (Table 1 (available online only))12,18–67. The dataset includes a total of 100,605 discrete measurements of particulate organic nutrients including 6940 POP, 46728 PON, and 46937 POC measurements. This leads to 5948 N:P, 5573 C:P, and 45476 C:N observations. Due to the common concurrent and largely automated measurements of PON and POC, these two particulate nutrients are over-represented in comparison to the sparse measurements of POP.
Table 1. Summary of cruises and time-series in this dataset including number of stations and POM samples as well as the mean elemental ratios.
Cruise | #Sta | Year |
Latitude
|
Longitude
|
POC | PON | POP | C:P * | N:P | C:N | Ref. | ||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
min | max | min | max | (#samples) | |||||||||
AMT1 | 23 | 1995 | −51 | 49 | −57 | −9 | 23 | 23 | — | — | — | 8.0 | 18 |
AMT10 | 42 | 2000 | −35 | 49 | −49 | −6 | 57 | 57 | — | — | — | 9.5 | 19 |
AMT12 | 14 | 2003 | −38 | 45 | −38 | −19 | 72 | 72 | — | — | — | 8.3 | 18 |
AMT13 | 10 | 2003 | −36 | 40 | −34 | −18 | 50 | 50 | — | — | — | 7.7 | 18 |
AMT14 | 15 | 2004 | −47 | 49 | −50 | −16 | 71 | 78 | — | — | — | 7.0 | 18 |
AMT15 | 21 | 2004 | −40 | 39 | −25 | 10 | 100 | 100 | — | — | — | 8.7 | 18 |
AMT16 | 32 | 2005 | −32 | 47 | −46 | 17 | 191 | 191 | — | — | — | 12 | 18 |
AMT17 | 33 | 2005 | −35 | 49 | −39 | 14 | 178 | 178 | — | — | — | 9.0 | 18 |
Antares3 | 20 | 1995 | −59 | −48 | 62 | 74 | 146 | 146 | — | — | — | 8.8 | 20 |
Antares4 | 25 | 1999 | −46 | −43 | 62 | 65 | 364 | 356 | — | — | — | 8.0 | 21 |
ANTVI | 61 | 1992 | −60 | −47 | −50 | −6 | 582 | 582 | — | — | — | 6.7 | 22 |
ANTXXIII | 26 | 2005 | −26 | 50 | −21 | 9 | 120 | 120 | — | — | — | 7.6 | 23 |
Arabesque | 14 | 1994 | 8 | 19 | 58 | 67 | 70 | 52 | — | — | — | 7.0 | 24 |
Atlantic | 4 | 1973 | 31 | 31 | −10 | −10 | 19 | 19 | 19 | 110 | 17 | 6.6 | 25 |
Atlantic Ocean | 160 | 1990–95 | 24 | 61 | −65 | −10 | 1174 | 1174 | — | — | — | 10 | 24 |
ATP3 | 13 | 2006 | 21 | 32 | −66 | −64 | 129 | 129 | 130 | 297 | 56 | 5.3 | 12 |
BATS | 73 | 2003–10 | 31 | 32 | −64 | −64 | 722 | 722 | 661 | 188 | 36 | 5.2 | 26 |
Bering Sea | 75 | 2009–10 | 54 | 63 | −179 | −161 | 291 | 272 | 296 | 84 | 9.8 | 8.1 | 12 |
BIOSOPE | 21 | 2004 | −35 | −8 | −141 | −73 | 162 | 156 | 164 | 171 | 21 | 7.9 | 27 |
BloomER | 2 | 2007 | 23 | 24 | −159 | −159 | 16 | 16 | — | — | — | 9.7 | 28 |
Blue Water Zone | 49 | 2004–06 | −64 | −60 | −63 | −53 | 260 | 259 | — | — | — | 7.1 | 29 |
BULA/CMORE | 9 | 2007 | −16 | 17 | −170 | −159 | 45 | 45 | 48 | 278 | 50 | 5.5 | 30 |
BV37+39 | 12 | 2007 | 20 | 34 | −66 | −64 | 46 | 46 | 181 | 448 | 60 | 7.1 | 12 |
CARIACO | 156 | 1995–2010 | 11 | 11 | −65 | −65 | 2893 | 2885 | — | — | — | 7.4 | 31 |
CCU LTER process | 68 | 2006–08 | 32 | 35 | −124 | −120 | 798 | 798 | — | — | — | 6.1 | 32 |
CCU LTER survey | 818 | 2004–09 | 30 | 74 | −124 | −117 | 4406 | 4406 | — | — | — | 6.4 | 32 |
Copin-Montegut | 10 | 1974 | −56 | −26 | 61 | 75 | 9 | 10 | 10 | 80 | 13 | 6.2 | 33 |
Copin-Montegut | 1 | 1975 | 42 | 42 | 5 | 5 | 6 | 6 | 6 | 121 | 19 | 6.3 | 25 |
CYCLOPS | 66 | 1971–72 | −35 | 56 | −18 | 142 | 66 | 66 | — | — | — | 9.4 | 34 |
DCM | 17 | 1996 | 7 | 34 | −54 | −23 | 119 | 113 | — | — | — | 14 | 35 |
DIAPAZON | 62 | 2002–03 | −24 | −20 | 166 | 168 | 202 | 203 | 305 | 238 | 27 | 8.8 | 36 |
EDT1 2004 | 17 | 2004 | 30 | 31 | −66 | −64 | 259 | 259 | — | — | — | 6.8 | 37 |
EDT2 2004 | 8 | 2004 | 30 | 32 | −66 | −64 | 244 | 244 | — | — | — | 6.8 | 37 |
EDT3 2005 | 12 | 2005 | 30 | 32 | −67 | −64 | 231 | 231 | — | — | — | 5.4 | 37 |
EDT4 2005 | 15 | 2005 | 30 | 30 | −69 | −68 | 224 | 224 | — | — | — | 5.5 | 37 |
EUMELI | 18 | 1991–92 | 18 | 21 | −31 | −21 | — | 318 | 327 | — | 18 | — | 38 |
FLUPAC | 42 | 1994 | −14 | 6 | −179 | −149 | 374 | 375 | 400 | 132 | 16 | 8.2 | 39 |
FRUELA 95 | 35 | 1995–96 | −65 | −63 | −66 | −59 | 306 | 306 | — | — | — | 6.1 | 40 |
Gulf of St Lawrence | 36 | 1992–94 | 43 | 50 | −66 | −60 | 397 | 398 | — | — | — | 6.1 | 24 |
HOT | 195 | 1989–2009 | 23 | 23 | −158 | −158 | 1632 | 1632 | 1581 | 161 | 25 | 6.5 | 41 |
IronEx II | 11 | 1995 | −7 | −4 | −111 | −105 | 114 | 114 | — | — | — | 5.9 | 42 |
JGOFS Arabian Sea | 120 | 1995 | 10 | 24 | 57 | 69 | 1229 | 1217 | — | — | — | 4.9 | 43 |
JGOFS EqPac | 99 | 1992 | −12 | 12 | −141 | −135 | 803 | 1468 | — | — | — | 7.3 | 44 |
JGOFS S. Ocean | 175 | 1996–98 | −78 | −53 | −178 | 180 | 2150 | 2135 | — | — | — | 8.8 | 45 |
Kahler | 10 | 2002 | 18 | 32 | −30 | −30 | 59 | 59 | 60 | 152 | 22 | 7.0 | 46 |
Keycop | 12 | 1999–2000 | 39 | 40 | 25 | 26 | 70 | 59 | — | — | — | 1.1 | 47 |
Latitud-II | 11 | 1995 | −33 | 25 | −45 | −18 | 16 | 16 | — | — | — | 12.3 | 48 |
Line P | 100 | 1992–97 | 49 | 50 | −145 | −127 | 997 | 970 | — | — | — | 6.8 | 49 |
Loh and Bauer | 4 | 1996 | −54 | 36 | −176 | −122 | 31 | 31 | 31 | 255 | 34 | 7.5 | 50 |
MD03/ICHTYO | 123 | 1974 | −56 | −24 | 26 | 78 | 159 | 159 | 159 | 93 | 15 | 6.4 | 33 |
MEDAR | 97 | 1991 −2001 | 41 | 45 | 5 | 14 | 1256 | 1160 | 190 | 165 | 21 | 8.1 | 51 |
Meteor 36–2 | 32 | 1996 | 33 | 60 | −22 | −20 | 96 | 96 | — | — | — | 5.9 | 52 |
Meteor 36–6 | 8 | 1996 | 46 | 48 | −20 | −18 | 73 | 73 | — | — | — | 6.9 | 53 |
MOOGLI | 10 | 1997–99 | 43 | 43 | 5 | 5 | 114 | 121 | 123 | 182 | 22 | 8.1 | 54 |
NABE | 20 | 1989 | 18 | 34 | −31 | −21 | 237 | 236 | 239 | 72 | 11 | 6.6 | 55 |
NOPACCS | 110 | 1992–95 | −36 | 48 | 143 | 175 | 1405 | 1405 | — | — | — | 7.0 | 56 |
OLIPAC | 13 | 1994 | −16 | 1 | −150 | −150 | — | 152 | 152 | — | 20 | — | 57 |
OMEX | 228 | 1993–95 | 47 | 50 | −16 | −7 | 2216 | 1261 | 735 | 294 | 25 | 9.7 | 58 |
OPEREX | 8 | 2008 | 22 | 26 | −160 | −157 | 58 | 58 | — | — | — | 6.1 | 59 |
PALLTER Seasonal | 650 | 1991–2010 | −65 | −64 | −65 | −64 | 5775 | 5743 | — | — | — | 7.2 | 60 |
PALLTER Survey | 679 | 1991–2010 | −70 | −79 | 7278 | 7232 | — | — | — | 6.6 | 60 | ||
PROSOPE | 22 | 1999 | 31 | 43 | −10 | 22 | 217 | 221 | 223 | 115 | 16 | 7.1 | 61 |
SBC LTER | 307 | 2000–10 | 34 | 35 | −121 | −119 | 4594 | 4593 | — | — | — | 6.3 | 62 |
SEED | 12 | 2001 | 49 | 49 | 164 | 165 | 129 | 129 | 57 | 140 | 17 | 8.4 | 63 |
SOIREE | 13 | 1999 | −61 | −61 | 140 | 141 | 102 | 102 | — | — | — | 5.9 | 64 |
SUPER-HI-CAT | 13 | 2008 | 28 | 35 | −155 | −138 | 83 | 83 | 81 | 250 | 35 | 7.2 | 65 |
Tuamotu | 15 | 1985–96 | −18 | −15 | −148 | −141 | 16 | 16 | 14 | 158 | 21 | 7.6 | 66 |
WCSI | 18 | 2007–08 | 16 | 74 | 68 | 68 | — | — | — | 5.9 | 67 | ||
X0705 | 29 | 2007 | 27 | 38 | −66 | −56 | 215 | 213 | 238 | 161 | 29 | 5.6 | 12 |
X0804 | 34 | 2008 | 20 | 32 | −66 | −45 | 1256 | 1160 | 190 | 107 | 24 | 4.5 | 12 |
*Geometric means of elemental molar ratios.
It is worth noting that this represents an aggregated dataset collected by many independent researchers (Table 1 (availale online only)). Even though most studies utilize the same techniques and sample volumes, there are likely many small deviations in the technical approach. As a result, some care should be taken when comparing values.
The data covers 5336 unique stations from all major ocean regions (Figure 1). 89% of the samples originate from the top 200 m of the water and thus the dataset is skewed towards processes occurring in or near the euphotic zone (Figure 2a). The data is also biased towards regions of oceanographic research. This includes samples near the Palmer Station in the Southern Ocean, North Atlantic Ocean and Eastern North Pacific Ocean (including the HOT site and California Current) (Figure 2b and Figure 2c). Thus, this compilation of data identifies regions where we currently have very sparse data (e.g., the South Pacific, South Atlantic, and Eastern Indian Ocean). Overall, the median C:P, N:P, and C:N ratios are 163, 22, and 6.6, respectively, in this dataset but the data span a wide range for all three ratios (Figure 2d–f). Combined with the wide geographic extent of the data, this compilation will enable a range of analyses of elemental concentrations or ratios in particulate organic matter.
Methods
Nearly all POC and PON measurements were done by collecting seawater particles onto glass-fibers filters (i.e., GF/F) and quantified using an combustion GC-IR based elemental analyzer68. The only exceptions were ‘EUMELI’ and ‘OLIPAC’, where PON was measured using a chemical oxidation technique38. Particulate phosphorus was quantified using the ash-hydrolysis method26,69. We operationally defined station IDs as samples taken within a 1°×1° area on the same day11.
The data was gathered by searching available databases (i.e., PANGAEA, BCO-DMO, JGOFS, and IFREMER) as well as published literature. We aggregated all available datasets in order to create the most exhaustive global description of particulate organic nutrients and thus did not exclude any specific cruises or time-series. The only data excluded were samples subjected to a prior manipulation or incubation.
Data Records
The dataset includes the following fields for each record:
Cruise
Year
Month
Day
Latitude (−90 to 90)
Longitude (−180 to 180)
Sampling depth (m)
Particulate organic Carbon (μM)
Particulate organic Nitrogen (μM)
Particulate organic Phosphorus (μM)
Data Record 1
The database files (June 20, 2014 version) in csv format were uploaded to Dryad (Data Citation 1). A file containing all the fields listed above is available. ‘−9999’ denotes missing data.
Data Record 2
The particulate nutrient data were also uploaded to the Biological and Chemical Oceanography Data Management Office system (BCO-DMO) (Data Citation 2) with all the fields listed above. The database is organized at level 0 by cruise dataset (Table 1 (availale online only)), level 1 by stations, and level 2 with the POM data. ‘−9999’ describes missing data. This dataset will be updated if new data becomes available.
Technical Validation
In our experience, when all precautions are taken, variance between replicate samples for elemental analysis can be <5%, assuming the actual sample is above the analytical blank. However, not all precautions are always taken, for example it is rare that when sampling for POC that the entire Niskin bottle is drained, well mixed and then subsampled. It is known that as the sample sits in the bottle, large particles sink to the bottom and often below the spigot resulting in an underestimation of particulate matter concentrations in the seawater sample70. There is also the question of limit of detection. For particulate analyses, this depends in part upon the volume you are filtering, the concentration of your analyte of interest and overall cleanliness of your procedures71. For example, in the Sargasso Sea, where particulate nutrients are very low, we filter 4 liters of seawater for particulate organic phosphorus26 to ensure that the sample well exceeds the blank. In our experience making these measurements using the methods reported here, reasonable blank measurements for POC, PON and POP are ~0.5 μM, ~0.04 μM and ~3 nM, respectively. It is common practice to subtract blanks from analyzed samples, and we assume that has been done for all reported data however, we cannot be fully confident in how that blank correction was conducted. Whether blank-corrected samples are significantly different than zero is a different question and depends upon the actual value and variability of the blank which is not commonly reported in published works or available datasets. However, we are confident that blank-corrected particulate organic matter concentrations greater than ~0.5 μM POC, ~0.05 μM PON and 5 nM POP are valid numbers to report. This benchmark may change between ocean regimes and with specific protocols. We should also note that some samples give either very high or low elemental ratios. These could arise from analytical artifacts, for example, one or both values in the ratio being close to the analytical detection limit, as well as other sampling artifacts. However, we currently do not have a good handle on the spatio-temporal variation in particulate nutrient concentrations and ratios and thus, it is difficult to give precise guidelines for flagging possible artifacts and thus really high/low values should be examined more closely and used with caution.
Usage Notes
The dataset can be used to identify novel regional or environmentally driven patterns in both the concentration of particulate organic matter as well as the ratios of different elements. Within this dataset are observations from time-series stations and thus temporal analysis of particulate organic matter concentrations and ratios can also be evaluated. Further, the data can be utilized to evaluate outputs from ocean biogeochemical models.
Additional information
Table 1 is only available in online version of this paper.
How to cite this article: Martiny, A. C. et al. Concentrations and ratios of particulate organic carbon, nitrogen, and phosphorus in the global ocean. Sci. Data 1:140048 doi: 10.1038/sdata.2014.48 (2014).
Supplementary Material
Acknowledgments
We would like to thank all the researchers for sharing their data with us and making this compilation possible as well as Cyndy Chandler and Steve Gegg for enabling the posting of the data at The Biological and Chemical Oceanography Data Management Office (BCO-DMO). We would like to acknowledge the NSF Dimensions of Biodiversity and Biological Oceanography programs (A.C.M. and M.W.L.) and the UCI Environment Institute (A.C.M. and J.A.V.) for supporting our research.
Footnotes
The authors declare no competing financial interests.
Data Citations
- Martiny A. C., Vrugt J. A., Lomas M. W. 2014. Dryad. http://dx.doi.org/10.5061/dryad.d702p [DOI] [PMC free article] [PubMed]
- Martiny A. C., Vrugt J. A., Lomas M. W. 2014. The Biological and Chemical Oceanography Data Management Office. http://www.bco-dmo.org/dataset/526747
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Citations
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