Attachment

INFORMATION BRIEFING

TO: Outfall Monitoring Science Advisory Panel, Dr. Andrew Solow, Chair
FROM: Dr. Michael J. Mickelson, Environmental Quality Dept., MWRA
THROUGH: Dr. Andrea C. Rex, Director, Environmental Quality Dept., MWRA
DATE: April 4, 2001
RE: Technical issues with MWRA outfall monitoring program chlorophyll analyses

ACTION For information. A recent quality assurance review found analytical errors in the chlorophyll measurement method used by the MWRA outfall monitoring program during 1998-2000. This briefing describes the steps we are taking to correct the errors and to prevent their recurrence. This briefing describes technical issues related to chlorophyll data obtained using a lab fluorometer to analyze sample filters.

Technical issues and corrections. In our evaluation of the fluorescence and bottle chlorophyll data from Fall 2000, the project team identified two technical issues requiring action. Both issues relate to the standard solution that was used to calibrate the fluorometer. Each issue leads to an upward bias in the extracted chlorophyll data.

In the laboratory, chlorophyll a is measured by fluorometric analysis of acetone-extracted filters before and after acidification (Albro et al. 1998). The method used in MWRA’s program from 1998-2000 refers to an SOP (Standard Operating Procedure; Battelle 1999) and to EPA method 445.0 (Arar and Collins 1992) for detail. The SOP checks for degradation of the chlorophyll standard solution during the acidification step and determines the concentration of the standard solution from the weight of chlorophyll reagent powder added to a known volume of solvent; this assumes that the purchased reagent is of known weight purity as supplied by the manufacturer. A spectrophotometer should have been used to determine the purity and concentration of the chlorophyll standard, but this was not done.

The analytical problems resulted from:

  1. Degraded standard. By mistake, a chlorophyll standard that was degraded was used to calibrate the samples from late September 2000 and October 2000 water column surveys (the period of the fall bloom). The error led to an upward bias of about 40%. We have corrected the error using a recommendation (Jay O’Reilly and Kristen Kohlberg pers. comm.) to numerically recalibrate the dataset on the phaeophytin of the acidified standard.

  2. Impurity of standard. The project team mistakenly believed that the standards we were using were pure chlorophyll a. We now know that the standards were not pure, and that the manufacturer’s stated purity varied by lot number (90.7% or 94.8% depending on lot number). Furthermore, the purchased chlorophyll standard appears to have variable and unknown weight purity from ampule to ampule when we evaluated this with a spectrophotometer. We speculate that this is due to differences in dryness of the reagent due to imperfectly sealed ampules. We will evaluate this further on additional ampules, and examine our data on a secondary standard (coproporphyrin) that was run with every batch of analyses. The purity issues may affect all data from 1998 to the end of 2000.

The chlorophyll data from 1992-1997 were measured using a spectrophotometer-checked standard and should be immune to the purity issue. We are nevertheless expanding our review to include those years. We are extending the review to ensure that the entire chlorophyll baseline is fully comparable and as error-free as feasible.

We are immediately reviewing and revising our SOP for chlorophyll analysis to ensure that the purity of the standard is known and certified.

These investigations are ongoing, especially the evaluation of the variability in purity of the purchased chlorophyll standard. In situ fluorescence data, from which the chlorophyll thresholds are calculated (see accompanying briefing on thresholds calculation), are calibrated against the results of these extracted chlorophyll samples and are therefore also under review. Until we have the results of that evaluation, MWRA cannot validate the calibrated fluorescence data for the purposes of calculating either the chlorophyll baseline (data through August 2000) or for testing the Fall 2000 seasonal chlorophyll threshold. We anticipate completing this evaluation and reporting to OMSAP within 60 days.

REFERENCES

Albro CS, Trulli HK, Boyle JD, Sauchuk SA, Oviatt CA, Keller AA, Zimmerman C, Turner JT, Borkman D, Tucker J. 1998. Combined work/quality assurance plan for baseline water quality monitoring: 1998-2000. Boston: Massachusetts Water Resources Authority. Report ENQUAD ms-048. 121 p. http://www.mwra.state.ma.us/harbor/enquad/pdf/ms-048.pdf

Arar EJ, Collins GB. 1992. In Vitro Determination of Chlorophyll a and Phaeophytin a in Marine and Freshwater Phytoplankton by Fluorescence. Method 445.0 Version 1.1 (November 1992). U.S. Environmental Protection Agency, Environmental Monitoring Systems Laboratory, Office of Research and Development, Cincinnati, OH. http://www.epa.gov/nerlcwww/marinmet.htm

Battelle. 1999. SOP No. 5-265, Extraction and Analysis of Chlorophyll a and Phaeophytin a in Seawater using a Turner [Designs] Model 10AU Fluorometer.

Appendix 1. Excerpt of methods, from Albro et al. (1998)

Onboard Sample Processing for Chlorophyll a and Phaeophytin

Samples for chlorophyll a/phaeophytin determination will be processed according to Battelle SOP No. 5-265, Extraction and Analysis of Chlorophyll a and Phaeophytin a in Seawater using a Turner [Designs] Model 10AU Fluorometer. Samples for chlorophyll a analysis will be collected on Whatman 47-mm-diameter GF/F using a vacuum-filter system. A saturated solution of MgCO3 will be added to the sample during filtration to aid retention and buffer the sample against low pH (which converts chlorophyll to phaeophytin). The filter will be stored frozen until analyzed.

Laboratory Sample Processing and Analysis for Chlorophyll a and Phaeophytin

Samples for chlorophyll a/phaeophytin will be processed according to Arar and Collins (1992) and Battelle SOP 5-265, Extraction and Analysis of Chlorophyll a and Phaeophytin a in Seawater Using a Turner Designs Model 10AU Fluorometer. Samples will be processed in subdued light and stored at -20º C between handling steps. The chlorophyll a/phaeophytin will be extracted from the cells retained on the GF/F filter, by mechanical grinding followed by a 2-4 hour steep in 90% acetone at -20º C. The sample will then be centrifuged and the extract analyzed using a Turner Designs Fluorometer. Two drops of 1 N HCl will be added to the extract and the extract remeasured to determine phaeophytin concentrations. The grinding apparatus and cuvette are rinsed between samples by using 90% acetone.

Calibration procedures and preventive maintenance

Model 10AU Turner Designs Fluorometer, using a two point and then a six-point dilution calibration requiring linearity with r>0.995. Data quality objectives are to once per day check that the filter blank is <5 times MDL. Also once per batch of 20 samples check that standards and duplicates have <15% relative percent difference (RPD = [(absolute value (replicate 1 - replicate 2)*2/(replicate 1 + replicate 2)] * 100%.). If these are not met results must be examined by subcontractor lab manager, task leader, or project manager. Corrective action (e.g., re-extraction, reanalysis, data qualifier) is documented. The estimated Method Detection Limit is 0.036 m g/L.