EPA-NERL: 445.0:  Chlorophyll and Pheophytin in Algae by Fluorescence

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
In Vitro Determination of Chlorophyll a and Pheophytin a in Marine and Freshwater Algae by Fluorescence
Current Revision
Revision 1.2, September 1997
Media
WATER
Instrumentation
Fluorescence Spectroscopy
Method Subcategory
Biochemical
Method Source
  EPA-NERL
Citation
  Methods for Determination of Chemical Substances in Marine and Estuarine Matrices - 2nd Edition (EPA/600/R-97/072)
Brief Method Summary
Chlorophyll-containing phytoplankton in a measured volume of sample water are concentrated by filtration at low vacuum through a glass fiber filter. The pigments are extracted from the phytoplankton in 90% acetone with the aid of a mechanical tissue grinder and are allowed to steep 2-24 hours. The resulting slurry is centrifuged to clarify the solution, and the fluorescence of the supernatant liquid is measured before an after acidification. Sensitivity calibration factors, previously determined on solutions of pure chlorophyll a of known concentration are used to calculate the concentration of chlorophyll a and pheophytin a in the sample extract.
Scope and Application
This method determines low levels of chlorophyll a (chl a) and its magnesium-free derivative, pheophytin a (pheo a), in marine and freshwater phytoplankton using fluorescence detection. Phaeophorbides present in the sample are determined collectively as pheo a.
Applicable Concentration Range
Not available.
Interferences
(A) Fluorescing materials, generally: Any substance in the sample that fluoresces in the red region of the spectrum may interfere.

(B) Spectral overlap of pigments: The relative amounts of chlorophyll a, b, and c vary with the taxonomic composition of the phytoplankton. Chlorophylls b and c may significantly interfere with chlorophyll a and pheophytin a measurements depending on the amounts present. Knowledge of the taxonomy of the algae under consideration will aid in determining if the spectrophotometric method using trichromatic equations (EPA Method 446.0) or an HPLC Method (EPA Method 447.0) is more appropriate.

(C) Quenching: Quenching effects are observed in highly concentrated solutions of chlorophylls or carotenoids. Minimum sensitivity settings on the fluorometer should be avoided; samples should be diluted instead.

(D) Temperature and light: Fluorescence is temperature and light sensitive. All samples and standards should be measured at an ambient temperature which does not vary by more than +/- 3oC in subdued light conditions. During storage, samples must be kept at -20 to -70oC in the dark, to prevent degradation.

(E) Turbidity: Samples must be clarified by centrifugation prior to analysis.
Quality Control Requirements
Each laboratory using this method is required to use a formal quality control program. At a minimum, this program should include an initial demonstration of laboratory capability and the continued analysis of laboratory reagent blanks, field duplicates, and quality control samples as a continuing check on performance.
Sample Handling
Samples are collected using a pump or grab sampler. Enough water should be collected to concentrate phytoplankton on three or more filters. Four liters may be required for ocean water (where phytoplankton density is usually low), whereas one liter is generally sufficient for lake, bay, and estuarine water. The method provides detailed information on the procedure for collecting samples. Once collected and filtered, the sample may be stored 2-4 hours on ice in the dark, but should be stored at -20 or -70oC as soon as possible. Filters frozen at -20oC may be stored as long as 3.5 weeks without significant loss of chlorophyll a.
Maximum Holding Time
3.5 weeks at -20oC
Relative Cost
Unknown
Sample Preparation Methods