Xia "Summer" XueBishwo N. AdhikariBecky A. BallJohn "Jeb" E. BarrettJinxin MiaoAmmon PerkesMac MartinBreana L. SimmonsDiana H. WallByron J. Adams 2021-09-08 tabular digitial data McMurdo Dry Valleys LTER McMurdo Dry Valleys LTER 10.6073/pasta/4478f48a6ff6cfc0b221cfa14a6a0dfa https://mcm.lternet.edu/content/environmental-molecular-and-life-history-data-associated-ecological-and-evolutionary Elemental stoichiometry is a useful theoretical framework for understanding the sources and controls on nutrient availability that can structure the composition, diversity, and life history of biotic communities. One such relationship, as postulated by the growth rate hypothesis (GRH), is that organismal development rate is positively linked to cellular phosphorus (P). To test the GRH as part of the McMurdo Dry Valleys Long Term Ecological Research (LTER) program, we examined the effects of phosphorus (P) availability both in situ and in vitro, on the evolution of growth and development of free-living soil nematodes (primarily Plectus murrayi) that occur in the McMurdo Dry Valleys of Antarctica. During the 2008-2009 austral summer, we collected soils from two glacial till sequences, the Ross Sea till and Taylor II till, occurring in the Lake Fryxell and Lake Bonney basins, respectively, of Taylor Valley. Through a variety of subsequent analyses, we generated the environmental, molecular, and life history trait data contained herein. In addition, this package contains body size and biomass data for nematodes isolated from soil samples collected during the 1999-2000 and 2004-2005 austral summers. Funding for these data was provided by the National Science Foundation for Long Term Ecological Research via grants #OPP-1115245 and #OPP-1637708 to BJA and #OPP-0423595 and #OPP-9810219 to DHW. 1999-12-04 2016-06-30 ground condition As needed This plot correspond to the Biotic Effects Experiment at the south side of Lake Bonney  162.311996459961 162.311996459961 -77.724998474121 -77.724998474121 Biotic Effects Experiment Fryxell Plot 163.248001098633 163.248001098633 -77.608001708984 -77.608001708984 LTER Core Areas inorganic nutrients population dynamics None <cntperp> <cntper>McMurdo Dry Valleys LTER Information Manager</cntper> </cntperp> <cntemail>im@mcmlter.org</cntemail> Name: Renée F. Brown Role: data manager Not Applicable Not Applicable Field and/or Lab Methods Determination of available soil phosphorusOrtho-phosphate (PO4-2) content of the soil was measured by extracting 10 g of soil in 50 ml of 0.5M NaHCO3 at pH 8.5. Extracts were shaken for 90 min at 170 rpm, then decanted into centrifuge tubes and spun at 27,216 x g for 10 min. Supernatant was poured into Nalgene bottles and acidified to approximately pH 2. The acidified filtrate was stored at -20 ºC, shipped to Dartmouth College, and analyzed on a Lachat QuikChem 8500 (Lachat Instruments)1. Soil sampling and nematode isolationSoils were sub-sampled within 48 hours of collection under a laminar flow hood in at McMurdo Station, Antarctica to provide material for invertebrate and chemical analyses. Nematodes were extracted from sieved soil samples using a sugar-centrifugation technique modified for Antarctic soils2. Determination of somatic phosphorusNematodes were identified based on morphology under light microscopy and picked into RNAlater® (Ambion Inc.) solution. Nematodes preserved in RNAlater® were shipped to Brigham Young University, Provo for RNA extraction and further analyses. Nematode samples preserved in RNAlater were washed twice with a 5% PBS (Phosphate-Buffered Saline) solution and shipped to ALS Laboratory Group at Salt Lake City for total phosphorus analysis. To test if preservation in PBS had any effect on nematode P-content, samples containing 10, 50, and 100 Heterorhabditis bacteriophora nematodes stored in distilled water and PBS for two weeks were analyzed and compared for body P-content. For Scottnema lindsayae and Plectus murrayi, six bulk samples containing 25 nematodes each were used for total phosphate measurement and the P-content of individual nematodes was calculated. Measurement of total P in whole nematode body was done by using inductively coupled plasma mass spectrometry (ICP-MS). The total nematode body phosphorus content was measured on pooled samples (25 individual nematodes per sample) using Inductively Coupled Plasma Mass Spectrometry (ICP-MS, ALS laboratory group in Salt Lake City) with external calibration set according to the manufacturer’s standard protocol. Nematode body size and biomassIn 2002 the climate regime of MCM soil ecosystems dramatically shifted from a decadal cooling trend3 to a warmer, wetter, climate with greater interannual variability4. To account for potential effects of this climate shift on habitat suitability and nematode phenotypes, we measured adult S. lindsayae of each sex from each till type (N = 118 (1999), 94 (2004) for Ross Sea till and N = 46 (1999), 54 (2004) for Taylor II till) sampled from 6 different soil monitoring plots per till type during the 1999-2000 and 2004-2005 austral summers. All nematode samples were preserved in 10% hot formalin (~ 60ºC). Animals were photographed using SPOT 3.0 imaging software for microscope digital cameras (SPOT Imaging, Diagnostics Instruments). The images were measured (lengths from tail to mouth, widths from just behind the basal pharyngeal bulb) using Carnoy 2.0 digital image analysis program (Biovolution). Biomass calculations were made using the formula of Andrassy (1956)5 as directed by Freckman (1982)6. Experimental evolution: Culturing conditionsCultures of P. murrayi were established according to Adhikari et al (2010)7. Caenorhabditis elegans strain N2 (CGC, University of Minnesota) and P. murrayi were reared on media of two different P concentrations for 46 months which is 23-31 generations for P. murrayi and around 345 generations for C. elegans. Nematodes were grown on phosphorous sand agar media, which includes 15g Agar, 965 mL H2O, 20 ml BMB for both P-poor and P-rich plates, and 1.033 mg K2HPO4 for P-poor and 10.33 mg K2HPO4 for P-rich. The pH was adjusted 7.0, H2O was added to 1.0 L, and the mixture was autoclaved for 20 minutes at 120 °C. Sterile builder’s sand was poured onto cooled 60-mm plates and stored at 4 °C. The plates were then inoculated with 30µL of stock OP-50 and incubated at 37 °C for 2 days. Nematodes were transferred onto the plates and incubated at 27 °C for 1 week, followed by incubation at 15 °C for 3 weeks. The process was then repeated for each successive generation7. For all subsequent comparative tests, populations were reared on common plates of P-rich and P-poor nematode growing media (NGM)8 for at least two generations. RNA extraction and real-time PCRNematodes stored in RNAlater solution were washed twice with a 5% solution of phosphate buffer saline (PBS) before RNA extraction. Total RNA for Quantitative real-time PCR (qRT-PCR) was extracted using Trizol reagent (Molecular Research Center Inc.). Three replications of each sample were used for RNA extraction, yielding three independent RNA extracts for each bulk sample. Nematodes were directly homogenized in liquid nitrogen, mixed with Trizol Reagent, and the suspension was exposed to three freeze-thaw cycles using liquid nitrogen and 37ºC water bath. The suspension was ground using mortar and pestle, vortexed, and phase separated using chloroform. After centrifugation (15 min, 12000 g, 4 °C), the aqueous phase containing RNA was separated from the other phases, which were stored for DNA preparation (see below). The colorless upper aqueous phase was transferred into fresh vials to precipitate the RNA by addition of 100 ml isopropyl alcohol. The samples were incubated for 10 min and centrifuged (20 min, 12000 g, 4 °C). The RNA precipitates were then washed twice with 75% ethanol, air-dried, eluted in nuclease-free water, and quantified and quality-checked via spectrophotometer (A260/A280&gt;1.9; NanoDrop ND-1000, NanoDrop Technologies, Thermo Fisher Scientific Inc.) and agarose gel electrophoresis. Reverse transcription (RT) was performed with 1µg of total RNA extracted from pooled sample of nematodes. The RT of polyadenylated mRNA to cDNA was done using the ImPromp-II™ reverse transcriptase (Promega Corporation) and a random hexamer primer. Total RNA was incubated with 20 pmol random hexamer primer at 70 °C for 5 min and then quickly chilled on ice. The reverse transcription mixture (20 µl) was mixed with RNA template and incubated at 25 °C for 5 min to encourage annealing and the first strand was extended for 60 min at 42°C. The cDNA was precipitated in 100% ethanol and washed twice with 75% ethanol, air-dried, and dissolved in DEPC-treated water. Quantitative real-time PCR was performed with LightCycler 480 SYBER Green I Mastermix (three replicate samples for each extraction) and gene specific primers in a Light Cycler 480 RT-PCR system (Roche Applied Science) equipped with LightCycler 480 software with the following program: 3 min at 95 °C; 45 cycles of 30 s at 94 °C, 30 s at 58 °C and 1 min at 72 °C followed by a standard melt curve. The RT-PCR reaction had a final volume of 10 μl including SYBR Green Mastermix (Roche Applied Science), and template DNA. Negative control reactions containing water in place of cDNA were included in each batch of PCR reactions to ensure that contamination was not a problem. We used nematode ß-actin, ß-tubulin and GAPDH genes as internal control for natural population of S. lindsayae and P. murrayi and ß-actin for laboratory population of P. murrayi and C. elegans. Life history trait observationsP. murrayi and C. elegans were grown in 50 of P-poor and 50 of P-rich plates as described above, 10 cultured plates with healthy populations were randomly selected for further observation (without contamination). For each of the 10 cultured nematode populations, 20 pregnant females were individually picked onto fresh petri dishes that contain regular P and seeded with OP50 Escherichia coli as a food source. All plates were kept at 15 ℃ and checked daily to record eggs laying. After hatching, juveniles were individually transferred to new plates and observed three times a day. The hatching day was recorded as day 0, the development duration was defined by their body volume based on de Tomasel’s study9. The duration of each stage and total egg abundance of each culture plate were observed and recorded. Photographs were taken daily, and juvenile body sizes were captured using a CKX 41 Olympus inverted microscope and body sizes, including body lengths and volumes, were measured and calculated by the modified Andrássy formula 9 in MatLab (MATLAB 6.1, 2000). Analyses notesTotal biomass calculations were calculated by determining the average individual dry weight from individual lengths and widths and corrected for water content using standard calculations5,7. For qRT-PCR experiments, gene expression level changes (fold change) of the rRNA gene was normalized to single-copy nuclear gene expression (ß-actin, ß-tubulin and GAPDH). The fold change in expression of rRNA in samples from Taylor Ⅱ till is as equal to one. ß-actin, ß-tubulin and GAPDH were also used as internal controls to minimize genomic template contamination bias and correct the variations among samples10. Environmental analyses were performed by the BYU Environmental Analytics Lab. Temporal rangeSamples from which animals were isolated and measured for body size  and biomass were collected and preserved during the 1999-2000 and 2004-2005 austral summer and accessioned into the BYU Life Science Museum. Soil samples from which animals were originally isolated and cultured, measured for somatic phosphorus, and for which the soil chemistry analyses were conducted, were collected during the 2008-2009 austral summer. Real-time PCR experiments were conducted in 2009 and 2015. Measurements of life history of cultured animals were completed in 2015. Transcriptome data were collected in 2016. Geographic locationSoil samples used in this study were collected from Taylor Valley, Antarctica, from the southeast end of the Lake Fryxell basin at -77° 36.48 S, 163° 14.94 E, and from the southwest end of the Lake Bonney basin at -77°43.56 S 162°18.84 E. 1 Ball, B. A., Adams, B. J., Barrett, J. E., Wall, D. H. &amp; Virginia, R. A. Soil biological responses to C, N and P fertilization in a polar desert of Antarctica. Soil Biology and Biochemistry 122, 7-18, doi:https://doi.org/10.1016/j.soilbio.2018.03.025 (2018).2 Freckman, D. &amp; Virginia, R. Low-diversity Antarctic soil nematode communities: Distribution and response to disturbance. Ecology, 363-369 (1997).3 Doran, P. T. et al. Antarctic climate cooling and terrestrial ecosystem response. Nature 415, 517-520, doi:10.1038/nature710 (2002).4 Gooseff, M. N. et al. Decadal ecosystem response to an anomalous melt season in a polar desert in Antarctica. Nature Ecology &amp; Evolution 1, 1334-1338, doi:10.1038/s41559-017-0253-0 (2017).5 Andrassy, I. Die Rauminhalts und Gewichtsbestimmung der fadenwurmer (Nematoda). Acta Zoologica Hungary 2, 1-15 (1956).6 Freckman, D. &amp; DW, F. Parameters of the nematode contribution to ecosystems.  (1982).7 Adhikari, B. N., Tomasel, C. M., Li, G., Wall, D. H. &amp; Adams, B. J. Culturing the Antarctic nematode Plectus murrayi. Cold Spring Harb Protoc 2010, pdb prot5522, doi:10.1101/pdb.prot5522 (2010).8 Chaudhuri, J., Parihar, M. &amp; Pires-daSilva, A. An introduction to worm lab: from culturing worms to mutagenesis. J Vis Exp, 2293, doi:10.3791/2293 (2011).9 de Tomasel, C. M., Adams, B. J., Tomasel, F. G. &amp; Wall, D. H. The Life Cycle of the Antarctic Nematode Plectus murrayi Under Laboratory Conditions. Journal of Nematology 45, 39-42 (2013).10 Vandesompele, J. et al. Accurate normalization of real-time quantitative RT-PCR data by geometric averaging of multiple internal control genes. Genome Biology 3 (2002). Determination of available soil phosphorusOrtho-phosphate (PO4-2) content of the soil was measured by extracting 10 g of soil in 50 ml of 0.5M NaHCO3 at pH 8.5. Extracts were shaken for 90 min at 170 rpm, then decanted into centrifuge tubes and spun at 27,216 x g for 10 min. Supernatant was poured into Nalgene bottles and acidified to approximately pH 2. The acidified filtrate was stored at -20 ºC, shipped to Dartmouth College, and analyzed on a Lachat QuikChem 8500 (Lachat Instruments)1.Soil sampling and nematode isolationSoils were sub-sampled within 48 hours of collection under a laminar flow hood in at McMurdo Station, Antarctica to provide material for invertebrate and chemical analyses. Nematodes were extracted from sieved soil samples using a sugar-centrifugation technique modified for Antarctic soils2.Determination of somatic phosphorusNematodes were identified based on morphology under light microscopy and picked into RNAlater® (Ambion Inc.) solution. Nematodes preserved in RNAlater® were shipped to Brigham Young University, Provo for RNA extraction and further analyses. Nematode samples preserved in RNAlater were washed twice with a 5% PBS (Phosphate-Buffered Saline) solution and shipped to ALS Laboratory Group at Salt Lake City for total phosphorus analysis. To test if preservation in PBS had any effect on nematode P-content, samples containing 10, 50, and 100 Heterorhabditis bacteriophora nematodes stored in distilled water and PBS for two weeks were analyzed and compared for body P-content. For Scottnema lindsayae and Plectus murrayi, six bulk samples containing 25 nematodes each were used for total phosphate measurement and the P-content of individual nematodes was calculated. Measurement of total P in whole nematode body was done by using inductively coupled plasma mass spectrometry (ICP-MS). The total nematode body phosphorus content was measured on pooled samples (25 individual nematodes per sample) using Inductively Coupled Plasma Mass Spectrometry (ICP-MS, ALS laboratory group in Salt Lake City) with external calibration set according to the manufacturer’s standard protocol.Nematode body size and biomassIn 2002 the climate regime of MCM soil ecosystems dramatically shifted from a decadal cooling trend3 to a warmer, wetter, climate with greater interannual variability4. To account for potential effects of this climate shift on habitat suitability and nematode phenotypes, we measured adult S. lindsayae of each sex from each till type (N = 118 (1999), 94 (2004) for Ross Sea till and N = 46 (1999), 54 (2004) for Taylor II till) sampled from 6 different soil monitoring plots per till type during the 1999-2000 and 2004-2005 austral summers. All nematode samples were preserved in 10% hot formalin (~ 60ºC). Animals were photographed using SPOT 3.0 imaging software for microscope digital cameras (SPOT Imaging, Diagnostics Instruments). The images were measured (lengths from tail to mouth, widths from just behind the basal pharyngeal bulb) using Carnoy 2.0 digital image analysis program (Biovolution). Biomass calculations were made using the formula of Andrassy (1956)5 as directed by Freckman (1982)6.Experimental evolution: Culturing conditionsCultures of P. murrayi were established according to Adhikari et al (2010)7. Caenorhabditis elegans strain N2 (CGC, University of Minnesota) and P. murrayi were reared on media of two different P concentrations for 46 months which is 23-31 generations for P. murrayi and around 345 generations for C. elegans. Nematodes were grown on phosphorous sand agar media, which includes 15g Agar, 965 mL H2O, 20 ml BMB for both P-poor and P-rich plates, and 1.033 mg K2HPO4 for P-poor and 10.33 mg K2HPO4 for P-rich. The pH was adjusted 7.0, H2O was added to 1.0 L, and the mixture was autoclaved for 20 minutes at 120 °C. Sterile builder’s sand was poured onto cooled 60-mm plates and stored at 4 °C. The plates were then inoculated with 30µL of stock OP-50 and incubated at 37 °C for 2 days. Nematodes were transferred onto the plates and incubated at 27 °C for 1 week, followed by incubation at 15 °C for 3 weeks. The process was then repeated for each successive generation7. For all subsequent comparative tests, populations were reared on common plates of P-rich and P-poor nematode growing media (NGM)8 for at least two generations.RNA extraction and real-time PCRNematodes stored in RNAlater solution were washed twice with a 5% solution of phosphate buffer saline (PBS) before RNA extraction. Total RNA for Quantitative real-time PCR (qRT-PCR) was extracted using Trizol reagent (Molecular Research Center Inc.). Three replications of each sample were used for RNA extraction, yielding three independent RNA extracts for each bulk sample. Nematodes were directly homogenized in liquid nitrogen, mixed with Trizol Reagent, and the suspension was exposed to three freeze-thaw cycles using liquid nitrogen and 37ºC water bath. The suspension was ground using mortar and pestle, vortexed, and phase separated using chloroform. After centrifugation (15 min, 12000 g, 4 °C), the aqueous phase containing RNA was separated from the other phases, which were stored for DNA preparation (see below). The colorless upper aqueous phase was transferred into fresh vials to precipitate the RNA by addition of 100 ml isopropyl alcohol. The samples were incubated for 10 min and centrifuged (20 min, 12000 g, 4 °C). The RNA precipitates were then washed twice with 75% ethanol, air-dried, eluted in nuclease-free water, and quantified and quality-checked via spectrophotometer (A260/A280>1.9; NanoDrop ND-1000, NanoDrop Technologies, Thermo Fisher Scientific Inc.) and agarose gel electrophoresis.Reverse transcription (RT) was performed with 1µg of total RNA extracted from pooled sample of nematodes. The RT of polyadenylated mRNA to cDNA was done using the ImPromp-II™ reverse transcriptase (Promega Corporation) and a random hexamer primer. Total RNA was incubated with 20 pmol random hexamer primer at 70 °C for 5 min and then quickly chilled on ice. The reverse transcription mixture (20 µl) was mixed with RNA template and incubated at 25 °C for 5 min to encourage annealing and the first strand was extended for 60 min at 42°C. The cDNA was precipitated in 100% ethanol and washed twice with 75% ethanol, air-dried, and dissolved in DEPC-treated water.Quantitative real-time PCR was performed with LightCycler 480 SYBER Green I Mastermix (three replicate samples for each extraction) and gene specific primers in a Light Cycler 480 RT-PCR system (Roche Applied Science) equipped with LightCycler 480 software with the following program: 3 min at 95 °C; 45 cycles of 30 s at 94 °C, 30 s at 58 °C and 1 min at 72 °C followed by a standard melt curve. The RT-PCR reaction had a final volume of 10 μl including SYBR Green Mastermix (Roche Applied Science), and template DNA. Negative control reactions containing water in place of cDNA were included in each batch of PCR reactions to ensure that contamination was not a problem. We used nematode ß-actin, ß-tubulin and GAPDH genes as internal control for natural population of S. lindsayae and P. murrayi and ß-actin for laboratory population of P. murrayi and C. elegans.Life history trait observationsP. murrayi and C. elegans were grown in 50 of P-poor and 50 of P-rich plates as described above, 10 cultured plates with healthy populations were randomly selected for further observation (without contamination). For each of the 10 cultured nematode populations, 20 pregnant females were individually picked onto fresh petri dishes that contain regular P and seeded with OP50 Escherichia coli as a food source. All plates were kept at 15 ℃ and checked daily to record eggs laying. After hatching, juveniles were individually transferred to new plates and observed three times a day. The hatching day was recorded as day 0, the development duration was defined by their body volume based on de Tomasel’s study9. The duration of each stage and total egg abundance of each culture plate were observed and recorded. Photographs were taken daily, and juvenile body sizes were captured using a CKX 41 Olympus inverted microscope and body sizes, including body lengths and volumes, were measured and calculated by the modified Andrássy formula 9 in MatLab (MATLAB 6.1, 2000).Analyses notesTotal biomass calculations were calculated by determining the average individual dry weight from individual lengths and widths and corrected for water content using standard calculations5,7. For qRT-PCR experiments, gene expression level changes (fold change) of the rRNA gene was normalized to single-copy nuclear gene expression (ß-actin, ß-tubulin and GAPDH). The fold change in expression of rRNA in samples from Taylor Ⅱ till is as equal to one. ß-actin, ß-tubulin and GAPDH were also used as internal controls to minimize genomic template contamination bias and correct the variations among samples10. Environmental analyses were performed by the BYU Environmental Analytics Lab.Temporal rangeSamples from which animals were isolated and measured for body size  and biomass were collected and preserved during the 1999-2000 and 2004-2005 austral summer and accessioned into the BYU Life Science Museum. Soil samples from which animals were originally isolated and cultured, measured for somatic phosphorus, and for which the soil chemistry analyses were conducted, were collected during the 2008-2009 austral summer. Real-time PCR experiments were conducted in 2009 and 2015. Measurements of life history of cultured animals were completed in 2015. Transcriptome data were collected in 2016.Geographic locationSoil samples used in this study were collected from Taylor Valley, Antarctica, from the southeast end of the Lake Fryxell basin at -77° 36.48 S, 163° 14.94 E, and from the southwest end of the Lake Bonney basin at -77°43.56 S 162°18.84 E.1 Ball, B. A., Adams, B. J., Barrett, J. E., Wall, D. H. & Virginia, R. A. Soil biological responses to C, N and P fertilization in a polar desert of Antarctica. Soil Biology and Biochemistry 122, 7-18, doi:https://doi.org/10.1016/j.soilbio.2018.03.025 (2018).2 Freckman, D. & Virginia, R. Low-diversity Antarctic soil nematode communities: Distribution and response to disturbance. Ecology, 363-369 (1997).3 Doran, P. T. et al. Antarctic climate cooling and terrestrial ecosystem response. Nature 415, 517-520, doi:10.1038/nature710 (2002).4 Gooseff, M. N. et al. Decadal ecosystem response to an anomalous melt season in a polar desert in Antarctica. Nature Ecology & Evolution 1, 1334-1338, doi:10.1038/s41559-017-0253-0 (2017).5 Andrassy, I. Die Rauminhalts und Gewichtsbestimmung der fadenwurmer (Nematoda). Acta Zoologica Hungary 2, 1-15 (1956).6 Freckman, D. & DW, F. Parameters of the nematode contribution to ecosystems.  (1982).7 Adhikari, B. N., Tomasel, C. M., Li, G., Wall, D. H. & Adams, B. J. Culturing the Antarctic nematode Plectus murrayi. Cold Spring Harb Protoc 2010, pdb prot5522, doi:10.1101/pdb.prot5522 (2010).8 Chaudhuri, J., Parihar, M. & Pires-daSilva, A. An introduction to worm lab: from culturing worms to mutagenesis. J Vis Exp, 2293, doi:10.3791/2293 (2011).9 de Tomasel, C. M., Adams, B. J., Tomasel, F. G. & Wall, D. H. The Life Cycle of the Antarctic Nematode Plectus murrayi Under Laboratory Conditions. Journal of Nematology 45, 39-42 (2013).10 Vandesompele, J. et al. Accurate normalization of real-time quantitative RT-PCR data by geometric averaging of multiple internal control genes. Genome Biology 3 (2002).  unknown SOILS_GRH_BIOMASS Nematode biomass data Dataset code Internal dataset code. The data provider Internal dataset code. Year Year of sample collection. The data provider calendar date/time YYYY gregorian calendar Lake basin Lake basin of sample collection site (i.e., Fryxell or Bonney). The data provider Lake basin of sample collection site (i.e., Fryxell or Bonney). Sample location Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. The data provider Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. Treatment Experimental treatment. In this case, samples were collected from c=control plots located in the BEE experiment. The data provider Experimental treatment. In this case, samples were collected from c=control plots located in the BEE experiment. Replicate Sample replicate number. The data provider Sample replicate number. Sex Gender of nematode (i.e., m=male, f=female). The data provider Gender of nematode (i.e., m=male, f=female). Length Length of nematode. The data provider micrometer Width Width of nematode. The data provider micrometer Biomass Biomass of nematode. The data provider microgram Corrected biomass Corrected nematode biomass (refer to methods for specifics). The data provider microgram McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_biomass-20210909.csv None SOILS_GRH_GENOMIC Manifest table for genomic data archived in NCBI Dataset code Internal dataset code. The data provider Internal dataset code. BioProject Accession Number NCBI BioProject accession number. The data provider NCBI BioProject accession number. SRA Experiment Accession Number NCBI Sequence Read Archive (SRA) accession number associated with the experiment. The data provider NCBI Sequence Read Archive (SRA) accession number associated with the experiment. SRA Run Accession Number NCBI Sequence Read Archive (SRA) accession number associated with the sequencing run. The data provider NCBI Sequence Read Archive (SRA) accession number associated with the sequencing run. Experiment name Name of the experiment in the NCBI data portal. The data provider Name of the experiment in the NCBI data portal. Sample name Name of the sample in the NCBI data portal. The data provider Name of the sample in the NCBI data portal. Species Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. The data provider Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. Phosphorus media Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. The data provider Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. Library name Name of the sequencing library in the NCBI data portal. The data provider Name of the sequencing library in the NCBI data portal. Library strategy Library strategy employed, where RNA-Seq = random sequencing of whole transcriptome. The data provider Library strategy employed, where RNA-Seq = random sequencing of whole transcriptome. Library source Library source, where TRANSCRIPTOMIC = Transcription products or non genomic DNA (EST, cDNA, RT-PCR, screened libraries). The data provider Library source, where TRANSCRIPTOMIC = Transcription products or non genomic DNA (EST, cDNA, RT-PCR, screened libraries). Library layout Library layout, where the options are single or paired-end. The data provider Library layout, where the options are single or paired-end. Sequencing platform Sequencing platform used. The data provider Sequencing platform used. Sequencing instrument Model of sequencing instrument used. The data provider Model of sequencing instrument used. Sequencing design Description of the sequencing design. The data provider Description of the sequencing design. File type File type The data provider File type McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_genomic-20210909.csv None SOILS_GRH_LIFEHISTORY Nematode life history traits Dataset code Internal dataset code. The data provider Internal dataset code. Species Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. The data provider Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. Phosphorus media Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. The data provider Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. Replicate Sample replicate number. The data provider Sample replicate number. Total egg count Total number of eggs laid. The data provider dimensionless Hatch rate Egg hatch rate. The data provider dimensionless EGG_LENGTH_MM Egg length. The data provider millimeter EGG_VOLUME_MM3 Egg volume. The data provider cubicMillimeter Emerge days Number of days to emergence (hatching). The number of days since the egg is laid until it is hatched. The data provider dimensionless Pre-adult days Number of days from hatching (emergence day) until adult stage. The data provider dimensionless Adult days Number of days from adult day (DAYS_TO_ADULT) to pregnancy. The data provider dimensionless Pregnant day Day when eggs were first observed. The data provider dimensionless Lay egg day Day of start of laying eggs. The data provider dimensionless Dead day The day of nematode death. The data provider dimensionless ADULT_LENGTH_MM Adult length. The data provider millimeter ADULT_VOLUME_MM3 Adult volume. The data provider cubicMillimeter McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_lifehistory-20210909.csv None SOILS_GRH_PO4 Environmental (soil) and nematode somatic phosphorus Dataset code Internal dataset code. The data provider Internal dataset code. Sample type Code for sample type, i.e., sample blank or bulk soils. The data provider Code for sample type, i.e., sample blank or bulk soils. Lake basin Lake basin of sample collection site (i.e., Fryxell or Bonney). The data provider Lake basin of sample collection site (i.e., Fryxell or Bonney). Sample location Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. The data provider Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. Replicate Sample replicate number. The data provider Sample replicate number. PO4 in diluted extracts PO4 content in extracted samples that were diluted. The data provider milligramsPerLiter EXT_DILUTION_FACTOR Extract dilution factor The data provider dimensionless PO4 in undiluted extracts PO4 content in extracted samples that were undiluted. The data provider milligramsPerLiter Extract volume Volume of extract. The data provider liter PO4 in entire extract PO4 content in entire sample extracts. The data provider milligramsPerLiter Corrected PO4 in entire extract Corrected PO4 content in entire sample extracts (-blank). Refer to methods for specifics. The data provider milligramsPerLiter Soil extract weight Weight of soil extract. The data provider grams Soil moisture Soil moisture percentage. The data provider percent Soil dry weight Weight of dry soil. The data provider grams Soil phosphorus Phosphorus content of soil replicate 1. The data provider milligramsPerLiter Soil phosphorus Phosphorus content of soil replicate 2. The data provider milligramsPerLiter Soil phosphorus Phosphorus content of soil replicate 3. The data provider milligramsPerLiter McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_po4-20210909.csv None SOILS_GRH_QPCRFIELD qPCR of 18S rRNA expression from field-collected samples Dataset code Internal dataset code. The data provider Internal dataset code. Lake basin Lake basin of sample collection site (i.e., Fryxell or Bonney). The data provider Lake basin of sample collection site (i.e., Fryxell or Bonney). Sample location Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. The data provider Location of sample collection (i.e., F6 or SSLB = South Side Lake Bonney). Samples were collected from control plots located in the BEE experiment. Species Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. The data provider Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. FOLD_CHANGE Expression fold change. The data provider dimensionless SE Standard error The data provider dimensionless McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_qpcrfield-20210909.csv None SOILS_GRH_QPCRLAB qPCR of 18S rRNA and Beta actin expression from laboratory-reared animals Dataset code Internal dataset code. The data provider Internal dataset code. PCR_POSITION Cell number on the PCR machine. The data provider Cell number on the PCR machine. Species Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. The data provider Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. Phosphorus media Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. The data provider Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. Replicate Sample replicate number. The data provider Sample replicate number. CtSYBR Ct value for each cell. CtSYBR = threshold cycle. The data provider dimensionless TargetSYBR Targeted gene name. TargetSYBR = targeted gene name; 18s = small ribosomal subunit RNA; Bactin = beta-actin. The data provider Targeted gene name. TargetSYBR = targeted gene name; 18s = small ribosomal subunit RNA; Bactin = beta-actin. McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_qpcrlab-20210909.csv None SOILS_REPRODUCTION Fecundity of C. elegans and P. murrayi in P-poor and P-rich media Dataset code Internal dataset code. The data provider Internal dataset code. Species Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. The data provider Abbreviated code for the species name of the associated organism. Matches nematode species name codes used elsewhere in this data package. C_elegans = Caenorhabditis elegans. P_murrayi = Plectus murrayi. Phosphorus media Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. The data provider Phosphorus media type (i.e., rich or poor) that associated nematode populations were reared on. Matches codes used elsewhere in this data package. Replicate Sample replicate number. The data provider Sample replicate number. Day Observation day (1-20). The data provider Observation day (1-20). Egg count Number of eggs laid on the day of observation. The data provider dimensionless McMurdo Dry Valleys LTER The data distributor shall not be liable for innacuracies in the content http 1 0 1 column , https://mcm.lternet.edu/sites/default/files/data/mcmlter-soil-xue-grh_reproduction-20210909.csv None 2021-09-08 2021-09-08 McMurdo Dry Valleys LTER http://mcmlter.org/ Biological Data Profile of the Content Standards for Digital Geospatial Metadata devised by the Federal Geographic Data Committee. Drupal Ecological information Management Systems, version D7, Biological Data Profile module