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AMT14 major ions and trace metals in aerosol samples

Originator's Protocol for Data Acquisition and Analysis

Atmospheric sampling was conducted on the JCR's monkey island when wind conditions permitted, i.e. the apparent wind direction was forward of the monkey island ensuring no contamination from the ship's stacks. Samplers were in general turned off while on station unless the bridge were confident of remaining head to wind throughout all manoeuvring. Sampling throughout passage allowed 16-20 hours sampling per day. Two high volume aerosol samplers (approx. 1 m 3 min -1 ) were deployed. One was for major ions and used conventional Whatman 41 filter substrates. One for trace metals and used conventional Whatman 41 filter substrates after rigorous acid pre-cleaning. Filters were changed in a laminar flow cabinet and subsequently frozen. On most occasions, cascade impactors were used for major ion and trace metals sampling to allow discrimination between aerosol particles < and > 1 µm.

Analyses were carried out once the samples were returned to the laboratory at the University of East Anglia (UEA). The methodology followed that detailed in Baker et al. (2006) and the main analytical technique for each parameter is listed in the table below.

References Cited

Baker A.R., Jickells T.D., Biswas K.F. and French M., (2006). Nutrients in atmospheric aerosol particles along the Atlantic Meridional Transect. Deep Sea Research: Part II, 53, 1706-1719.

Instrumentation Description

Not relevant to this data set.

BODC Data Processing Procedures

Data were submitted to BODC on three occasions, when the data from each successive file superseded the previous data with additional parameters included in the latest submission. The most recent submission was received on 10/11/2008 and contained the data from AMT cruises 12-17 and was loaded to the archive with BODC accession number UEA060021. Data were submitted in an Excel spreadsheet with the following metadata; Sampling start and end date and time, Latitude and Longitude. Sample metadata were checked against information held in the database - there were no metadata in the database, so the data for the sampling events were loaded from the originator's file. Parameter codes were assigned to the variables; trace metal parameters were provided in pmol m -3 and all the major ion parameters except PO4 were supplied in nmol m -3 . Parameters supplied in nmol m -3 were converted to pmol m -3 to be consistent with parameters in the BODC parameter database. Data were loaded into BODC's database using established BODC data banking procedures.

A parameter mapping table is provided below;

Originator's Parameter Units Description BODC Parameter Code BODC StDev Parameter Code Units Comments
Na Fine (<1 µm) nmol m -3 Concentration of sodium {Na} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACNAAE01 ASDNAA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Na Coarse (>1 µm) nmol m -3 Concentration of sodium {Na} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACNAAE02 ASDNAA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Na Total nmol m -3 Concentration of sodium {Na} per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACNAXX01 ASDNAX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NH4 Fine (<1 µm) nmol m -3 Concentration of ammonium {NH 4 } per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACAMAE01 ASDAMA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NH4 Coarse (>1 µm) nmol m -3 Concentration of ammonium {NH 4 } per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACAMAE02 ASDAMA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NH4 Total nmol m -3 Concentration of ammonium {NH 4 } per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACNH4X01 ASDAMX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Mg Fine (<1 µm) nmol m -3 Concentration of magnesium {Mg} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACMGAE01 ASDMGA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Mg Coarse (>1 µm) nmol m -3 Concentration of magnesium {Mg} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACMGAE02 ASDMGA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Mg Total nmol m -3 Concentration of magnesium {Mg} per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACMGXX01 ASDMGX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
K Fine (<1 µm) nmol m -3 Concentration of potassium {K} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACKAER01 ASDKIC01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
K Coarse (>1 µm) nmol m -3 Concentration of potassium {K} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACKAER02 ASDKIC02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
K Total nmol m -3 Concentration of potassium {K} per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACKXXX01 ASDKIX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Ca Fine (<1 µm) nmol m -3 Concentration of calcium {Ca} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACCAAE01 ASDCAI01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Ca Coarse (>1 µm) nmol m -3 Concentration of calcium {Ca} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACCAAE02 ASDCAI02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Ca Total nmol m -3 Concentration of calcium {Ca} per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACCAXX01 ASDCAX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Cl Fine (<1 µm) nmol m -3 Concentration of chloride {Cl} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACCLAE01 ASDCLA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Cl Coarse (>1 µm) nmol m -3 Concentration of chloride {Cl} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACCLAE02 ASDCLA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Cl Total nmol m -3 Concentration of chloride {Cl} per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACCLXX01 ASDCLX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NO3 Fine (<1 µm) nmol m -3 Concentration of nitrate {NO 3 } per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACNITA01 ASDNIT01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NO3 Coarse (>1 µm) nmol m -3 Concentration of nitrate {NO 3 } per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACNITA02 ASDNIT02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
NO3 Total nmol m -3 Concentration of nitrate {NO 3 } per unit volume of the atmosphere [aerosol phase] by filtration and ion chromatography ACNO3X01 ASDNIX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
SO4 Fine (<1 µm) nmol m -3 Concentration of sulphate {SO 4 } per unit volume of the atmosphere [aerosol <1um phase] by filtration and colorimetric analysis ACSUAE01 ASDSUA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
SO4 Coarse (>1 µm) nmol m -3 Concentration of sulphate {SO 4 } per unit volume of the atmosphere [aerosol >1um phase] by filtration and colorimetric analysis ACSUAE02 ASDSUA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
SO4 Total nmol m -3 Concentration of sulphate {SO 4 } per unit volume of the atmosphere [aerosol phase] by filtration and colorimetric analysis ACSO4X01 ASDSUX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Oxalate Fine (<1 µm) nmol m -3 Concentration of oxalate {C 2 O 4 } per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACOXAE01 ASDOXA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Oxalate Coarse (>1 µm) nmol m -3 Concentration of oxalate {C 2 O 4 } per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACOXAE02 ASDOXA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Oxalate Total nmol m -3 Concentration of oxalate {C 2 O 4 } per unit volume of the atmosphere [aerosol] by filtration and ion chromatography ACOXAX01 ASDOXX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Methane sulphonic acid (MSA) Fine (<1 µm) nmol m -3 Concentration of methane sulphonic acid {CH 3 SO 3 H} per unit volume of the atmosphere [aerosol <1um phase] by filtration and ion chromatography ACMSAE01 ASDMSA01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Methane sulphonic acid (MSA) Coarse (>1 µm) nmol m -3 Concentration of methane sulphonic acid {CH 3 SO 3 H} per unit volume of the atmosphere [aerosol >1um phase] by filtration and ion chromatography ACMSAE02 ASDMSA02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Methane sulphonic acid (MSA) Total nmol m -3 Concentration of methane sulphonic acid {CH 3 SO 3 H} per unit volume of the atmosphere [aerosol] by filtration and ion chromatography ACMSAX01 ASDMSX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
PO4 Fine (<1 µm) pmol m -3 Concentration of phosphate {PO 4 } per unit volume of the atmosphere [aerosol <1um phase] by filtration and colorimetric analysis ACPAER01 ASDPAE01 pmol m -3 No unit conversion necessary
PO4 Coarse (>1 µm) pmol m -3 Concentration of phosphate {PO 4 } per unit volume of the atmosphere [aerosol >1um phase] by filtration and colorimetric analysis ACPAER02 ASDPAE02 pmol m -3 No unit conversion necessary
PO4 Total pmol m -3 Concentration of phosphate {PO 4 } per unit volume of the atmosphere [aerosol phase] by filtration and colorimetric analysis ACPAER03 ASDPAE03 pmol m -3 No unit conversion necessary
TDN Fine (<1 µm) nmol m -3 Concentration of nitrogen (total) per unit volume of the atmosphere [aerosol <1um phase] by filtration and high temperature Pt catalytic oxidation ACTNCO01 ASDTNC01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
TDN Coarse (>1 µm) nmol m -3 Concentration of nitrogen (total) per unit volume of the atmosphere [aerosol >1um phase] by filtration and high temperature Pt catalytic oxidation ACTNCO02 ASDTNC02 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
TDN Total nmol m -3 Concentration of nitrogen (total) per unit volume of the atmosphere [aerosol phase] by filtration and high temperature Pt catalytic oxidation ACNTCX01 ASDTNX01 pmol m -3 Conversion factor x1000 applied for conversion from nmol m -3 to pmol m -3
Soluble Fe Fine (<1 µm) pmol m -3 Concentration of iron (soluble) {Fe} per unit volume of the atmosphere [aerosol <1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACSFEA01 ASDSFE01 pmol m -3 No unit conversion necessary
Soluble Fe Coarse (>1 µm) pmol m -3 Concentration of iron (soluble) {Fe} per unit volume of the atmosphere [aerosol >1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACSFEA02 ASDSFE02 pmol m -3 No unit conversion necessary
Soluble Fe Total pmol m -3 Concentration of iron (soluble) {Fe} per unit volume of the atmosphere [aerosol phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACSFEX01 ASDFEX01 pmol m -3 No unit conversion necessary
Soluble Al Fine (<1 µm) pmol m -3 Concentration of aluminium (soluble) {Al} per unit volume of the atmosphere [aerosol <1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACALAE01 ASDALE01 pmol m -3 No unit conversion necessary
Soluble Al Coarse (>1 µm) pmol m -3 Concentration of aluminium (soluble) {Al} per unit volume of the atmosphere [aerosol >1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACALAE02 ASDALE02 pmol m -3 No unit conversion necessary
Soluble Al Total pmol m -3 Concentration of aluminium (soluble) {Al} per unit volume of the atmosphere [aerosol phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACALAX01 ASDALX01 pmol m -3 No unit conversion necessary
Soluble Mn Fine (<1 µm) pmol m -3 Concentration of manganese (soluble) {Mn} per unit volume of the atmosphere [aerosol <1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACMNAE01 ASDMNE01 pmol m -3 No unit conversion necessary
Soluble Mn Coarse (>1 µm) pmol m -3 Concentration of manganese (soluble) {Mn} per unit volume of the atmosphere [aerosol >1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACMNAE02 ASDMNE02 pmol m -3 No unit conversion necessary
Soluble Mn Total pmol m -3 Concentration of manganese (soluble) {Mn} per unit volume of the atmosphere [aerosol phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACMNAX01 ASDMNX01 pmol m -3 No unit conversion necessary
Soluble Zn Fine (<1 µm) pmol m -3 Concentration of zinc (soluble) {Zn} per unit volume of the atmosphere [aerosol <1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACZNAE01 ASDZNE01 pmol m -3 No unit conversion necessary
Soluble Zn Coarse (>1 µm) pmol m -3 Concentration of zinc (soluble) {Zn} per unit volume of the atmosphere [aerosol >1um phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACZNAE02 ASDZNE02 pmol m -3 No unit conversion necessary
Soluble Zn Total pmol m -3 Concentration of zinc (soluble) {Zn} per unit volume of the atmosphere [aerosol phase] by filtration and inductively-coupled plasma atomic emission spectroscopy ACZNAX01 ASDZNX01 pmol m -3 No unit conversion necessary

Data Quality Report

BODC were not advised of specific quality checks carried out by the data originator. A number of the samples had concentrations lower than the detection limit. This detection limit was calculated assuming a sample volume of 1400m 3 , but since there was variation in the volumes sampled the concentrations quoted in conjunction with the 'below detection limit' flag (<) are reported as 75% of the concentration with a 1400m 3 volume.

Problem Report

Not relevant to this data set.