Evaluation of three common methods of bulk lipid quantification in soft tissues of marine benthic invertebrates
Artikel-Kategorie: Original Research Paper
Online veröffentlicht: 19. Sept. 2025
Seitenbereich: 160 - 170
Eingereicht: 08. Apr. 2025
Akzeptiert: 28. Juli 2025
DOI: https://doi.org/10.26881/oahs-2025.1.16
Schlüsselwörter
© 2025 Adam Sokołowski et al., published by Sciendo
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License.
Lipids (fats) are one of the main classes of biomolecules found in tissues of aquatic animals (Imbs et al., 2021; Koutsouveli et al., 2022; Lordan et al., 2017). The principal functions of lipids include energy storage, cell membrane construction, signalling, insulation and cell protection (Ridgway & McLeod, 2016). They form efficient storage depots, cellular barriers and extracellular and intracellular messenger molecules. Being largely composed of carbon and hydrogen, lipids are highly hydrophobic and can act as a solvent and absorption carrier for organic contaminants, providing efficient indication of pollutant bioaccumulation in marine ecosystems (Parrish, 2025). They are highly reduced non-polymeric chemical compounds and are, thus, essential fuels for oxidation (Parrish, 2013). Due to their high energy value (twice the specific energy, kJ · g−1, of proteins or carbohydrates), lipids are usually stored prior to periods of low food availability (e.g. in winter) and/or periods of enhanced energy expenditures, such as during reproduction or larval development, to serve as an important energy source. For example, Marshall et al. (2000) found a direct link between total egg production in cod and total lipid energy in the livers of mature females. Quantitative analyses of individually measured lipid classes or bulk lipid content in marine organisms have therefore become widely used in laboratory and field studies aiming at assessment of organisms’ responses to changes of physic-chemical conditions, biochemical adaptations to different habitats, modifications of food alimentary value, in trophic ecology and bioaccumulation studies (Hines et al., 2007; Lee et al., 2006; Parrish, 2013; Peters et al., 2006; Prato et al., 2019). The content of lipid reserves along with energetic balance, metabolic rate and overall physiological performance have been shown to respond directly to alterations in the marine and coastal environments induced by human activity or resulting from natural processes (Acevedo-Whitehouse & Duffus, 2009). For example, significant differences in the content and composition of lipid compounds between two cryptic forms of the beadlet anemone (
Although recent advances in chromatography and mass spectrometry have permitted the identification and quantitation of single lipid molecular species (lipidomic approach) and metabolic networking (Parrish, 2025), bulk lipid determination remains useful in ecophysiological and ecological studies. There are several different analytical methods for bulk lipid measurement in the soft tissues of marine organisms. The simplest and still broadly employed methods, which require basic analytical equipment and relatively little labour intensity, include the gravimetric method (Inouye & Lotufo, 2006) and the Marsh and Weinstein method (Marsh & Weinstein, 1966) after quantitative chloroform/methanol total lipid extraction following the protocol of Bligh and Dyer (1959). Advances in medical diagnostics and analytical technology allowed the development of the colourimetric method in 1970 (Frings & Dunn, 1970) and several methods based on thin-layer chromatography in the 80s and 90s (Gardner et al., 1985; Parrish, 1987). The gravimetric method (Lehtonen, 1996; Lehtonen & Andersin, 1998; Nielsen et al., 2005), the method described by Marsh and Weinstein (1966) and the colourimetric method of Barthel (1986) have been most commonly employed in biochemical studies of marine abiotic matrices (Dong-Young et al., 2022; Naeun et al., 2022; Pusceddu et al., 2009) and macrobenthic organisms (e.g. da Costa et al., 2013; da Silva-Castiglioni et al., 2010; Gora et al., 2018; Graham et al., 2024; Stelzer et al., 2021; Wołowicz et al., 2006) due to their relative ease of use in laboratory analytics. However, their utility for quantitative lipid determination has not been assessed yet, and evaluation of these methods for batch measurement of total lipid content in macrozoobenthic invertebrates provides an important and useful subject of comparative laboratory studies.
This study aimed to evaluate three methods of quantitative bulk lipid determination in the soft tissues of marine benthic invertebrates of different taxonomic groups in terms of their efficiency and labour intensity: the gravimetric, Marsh and Weinstein (1966) and Frings and Dunn (1970) methods. Such evaluation can serve as a baseline for the selection of analytical methods for marine animals originating from wild populations and aquaculture, and for interlaboratory comparisons.
Comparative analyses of bulk lipid content were carried out using three macrobenthic invertebrate species, representing various taxonomical classes and of different lipid compositions and contents in their soft tissues: the common ragworm

Location of sampling sites in the Gulf of Gdańsk.
Special care was taken to select individuals of a limited length range i.e.
Before the analysis, thick-walled SCHOTT DURAN (Germany) tubes were quenched several times in boiling and cold water (0°C). All test tubes and glass balls were washed with dishwashing liquid, rinsed with distilled water and dried at room temperature. To ensure that all residual lipids were removed, the tubes were rinsed with chloroform and dried in a laboratory air dryer at 45°C (Christian, 2009).
The same extraction method (Bligh & Dyer, 1959) was used for all lipid determination methods. A weight of 10 ± 0.1 mg of homogenised tissue (in 20 replicates for each species and each method,
Tubes with the extracted lipids were pre-weighted on a laboratory balance with a readability of 0.01 mg. Lipid content was determined using the following equation:
The original method developed by Marsh and Weinstein (1966) was modified to dissolve the entire residue at the bottom of the test tubes. The modification included the addition of 10 cm3 of 95% sulphuric acid to the tubes with the residue instead of 2 cm3 H2SO4 and heating at 200°C for 20 min instead of 15 min. After heating, 2 cm3 of the solution was transferred to new thin-walled glass test tubes and the original procedure described by Marsh and Weinstein (1966) was then followed. In order to make a calibration curve, tripalmitate (SIGMA-ALDRICH® (Germany), ≥99%) was chosen from a list of standards as proposed in the original procedure. A stock standard solution (SSS) with a concentration of 750 μg · cm−3 was prepared by adding 15 mg of tripalmitate to 20 cm3 of chloroform. Two series of standard solutions were prepared by diluting the tripalmitate stock solution with chloroform to obtain the following final concentrations: 0.0, 187.5, 375.0, 562.5 and 750.0 mg · cm−3.
Based on the linear regression function between the concentrations of the standard solutions and their absorbance, which was measured at a wavelength of 360 nm, the lipid content in the samples was determined according to the following formula:
The procedure described by Frings and Dunn (1970) was modified because the original method was based on lipid determination in liquid serum, whilst powdered precipitate was used in this study. Serum-like liquid was made by dissolving the precipitate. The serum was prepared by adding 0.5 cm3 of 99.8% ethanol to each tube containing the residue. 0.1 cm3 of the solution was then transferred to new thin-walled glass tubes. Further steps were carried out according to the original procedure. To prepare a calibration curve, cholesterol was chosen from a list of standards proposed by Frings and Dunn (1970). A SSS with a concentration of 10 mg · cm−3 was prepared by adding 500 mg of cholesterol to 50 cm3 of 99.8% ethanol. Two series of standard solutions were prepared by diluting the cholesterol stock solution with ethanol to obtain the following final concentrations: 0, 1, 2 and 4 mg · cm−3.
Based on the linear regression function between the concentrations of the standard solutions and their absorbance, which was measured at a wavelength of 540 nm, the lipid content in the samples was determined according to the following formula:
Data quality control was provided by a separate comparative study of 10 procedural blanks, which were analysed simultaneously according to the same procedures as the samples for each lipid determination method. In order to assess recovery (R), a method of standard addition of a known amount of analyte (1.9 ± 1.0 mg of tripalmitate) was used in five replicates for each method. The procedures of lipid extraction and lipid determination according to the analysed method were then followed.
Routine quality control validation parameters and the time required for completing analysis (used here as a proxy of sample throughput) were determined for each method as factors that allowed evaluation of the lipid determination methods. In order to assess the efficiency of each method, precision (CD), limit of detection (LOD) and recovery (R) were calculated (Araujo, 2009) using the following formulas:
Labour intensity (workload) of each lipid determination method was calculated as the average time (rounded to 1 min) needed for performing the analysis of one series of samples (
The Shapiro–Wilk normality test was used to verify the distribution of data, and the Levene test was employed to check the homogeneity of variance. The significance of differences between variables for the main effects and interactions between them was estimated by analysis of variance (ANOVA), followed by Tukey’s post-hoc test (α/
Soft tissue lipid content varied significantly amongst the invertebrate species and three analytical methods for
Mean lipid content (%) in soft tissues of marine benthic invertebrates from the southern Baltic Sea determined by three analytical methods of quantitative bulk lipid determination following the Bligh and Dyer extraction.
Analytical method | Species | Mean | SD | SE | |
---|---|---|---|---|---|
Gravimetric | 14.85 | 2.95 | 0.66 | 20 | |
6.37 | 2.08 | 0.49 | 18 | ||
10.81 | 2.36 | 0.53 | 20 | ||
Marsh and Weinstein | 13.79 | 0.55 | 0.13 | 19 | |
7.41 | 0.34 | 0.08 | 18 | ||
10.44 | 0.65 | 0.15 | 19 | ||
Frings and Dunn | 13.27 | 1.20 | 0.27 | 20 | |
7.38 | 1.04 | 0.23 | 20 | ||
10.64 | 1.08 | 0.24 | 20 |
SD, standard deviation; SE, standard error;
Results of one-way ANOVA of differences in bulk lipid content amongst macrobenthic invertebrate species analysed by different analytical methods (a) and amongst three analytical methods for the same species (b).
a) | |||
---|---|---|---|
Analytical method | df | ||
Gravimetric | 54.380 | 2 | |
Marsh and Weinstein | 670.220 | 2 | |
Frings and Dunn | 142.186 | 2 |
b) | |||
---|---|---|---|
Species | df | ||
3.441 | 2 | ||
3.544 | 2 | ||
0.276 | 0.759 | 2 |
ANOVA, analysis of variance.
Significant values are in bold.
The highest lipid contents in the mussels (mean ± standard error [SE]; 14.85 ± 2.95%,
The largest CDs in routine replicated assays for all analysed species were recorded for the data obtained using the gravimetric method, the lower CDs were calculated using the Frings and Dunn method, and the highest precision was obtained for the Marsh and Weinstein method (Table 3). The results for lipid content in the tissues of
Precision (CD, %), limit of detection (LOD, %) and recovery (R, %) for analyses of bulk lipid content in marine benthic invertebrates using the gravimetric, Marsh and Weinstein and Frings and Dunn methods
Analytical method | Species | CD | LOD | R |
---|---|---|---|---|
Gravimetric | 19.85 | 1.12 | 89.06 | |
32.68 | 0.98 | 101.67 | ||
21.88 | 0.11 | 97.30 | ||
Marsha and Weinstein | 4.30 | 0.01 | 102.50 | |
4.56 | 0.03 | 95.17 | ||
6.21 | 0.01 | 100.79 | ||
Frings and Dunn | 9.05 | 0.27 | 95.16 | |
14.05 | 0.29 | 94.85 | ||
10.12 | 0.32 | 98.16 |
The lowest LOD for all species was obtained using the Marsh and Weinstein method, and the highest, except for the nereid tissues, using the gravimetric method (Table 3). The Frings and Dunn method provided intermediate LOD; exceptions were the nereid tissues for which the LOD value was highest.
Recovery ranged from 89.1% to 102.5% with the highest value obtained by the Marsh and Weinstein method, except for
An assay of 20 samples using the gravimetric method took only about 45 min, whereas analysis of a series of 20 replicates consumed 1 hr 15 min and 2 hr when using the Marsh and Weinstein and Frings and Dunn method, respectively (Table 4). In addition, the latter two procedures required prior preparation of SSSs, which ran for 20 min and 35 min, respectively. The preparation of the phospho-vanillin solution by the Frings and Dunn method took an additional 20 min. The average total time needed to complete the analysis using the gravimetric, Marsh and Weinstein and Frings and Dunn methods was estimated at 45 min, 95 min and 175 min, respectively.
Time consumption (min) of analyses of 20 samples (20S), preparation of SSS and OR using three analytical methods of quantitative bulk lipid determination
Analytical method | Time consumption | |||
---|---|---|---|---|
20S | SSS | OR | Total | |
Gravimetric | 45 | 0 | 0 | 45 |
Marsha and Weinstein | 75 | 20 | 0 | 95 |
Frings and Dunn | 120 | 35 | 20 | 175 |
OR, other reagents; SSS, stock standard solution.
Bulk lipid content in soft tissues of marine macrobenthic fauna varies with environmental conditions (e.g. temperature, salinity, food quantity and its nutritional value) and biological factors (e.g. species, physiological state, age and sex) and increases before reproduction and during periods of low food availability (Lehtonen, 2004; Wiklund et al., 2009). For example, lipid content in tissues of the brown shrimp
In the shallow coastal waters of the southern Baltic, lipid content in soft tissue of the mussel
Empirical data on the lipid content in tissues of
The quality of the results of biochemical analyses is affected by several factors e.g. diligence of sampling, sample pretreatment and laboratory procedures, analytical equipment and quality of reagents. In order to manage the quality of the analytical method, control analysis and analysis of procedural blank samples are routinely performed (Skoog et al., 2013). In this study, standard validation parameters were calculated for each method, including precision, LOD and recovery. Tukey’s post-hoc tests showed no significant differences in the bulk lipid content of a given species between paired analytical methods; the exception was
The Marsh and Weinstein method offers the most accurate analytical protocol for lipid quantification (the highest precision, low LOD, SD and SE) regardless of the analysed animal tissue. The obtained recovery (mean for three invertebrate species, 99.5%) was similar to that reported by Reisenbichler and Bailey (1991) (95%–100% depending on the analysed standard), who indicated that the possible difference in
Besides high precision and accuracy, consideration should also be given to another important design criterion of the quantitative lipid determination method: workload. Estimates of the workload required to complete laboratory analysis can vary widely with analyst experience and practical skills, ease of operation of analytical equipment, organisation of laboratory workspace and complexity of the analytical procedure. According to Harvey (2000), depending on the technical advancement of the analytical equipment, the time spent on staff training should also be considered working time. Several steps in analytical procedures have, however, fixed times (e.g. centrifuging, drying, etc.), which do not vary with analyst or laboratory conditions. In the case of a single run of many series of samples, the most optimal in terms of time consumption are continuous and/or automated methods (Webster et al., 2005). However, these methods were not used in this study due to the small number of samples (
The results of labour intensity estimates showed that bulk lipid content determination using the gravimetric method is the most time-effective. Two other methods were more complex and included several additional phases such as dosing reagents, sample incubation and optical density measurements, which all extended the total time required to complete the analysis. Larger quantities of the SSSs (and the phospho-vanillin solution in the case of the Frings and Dunn method) can be, however, used in subsequent analyses to reduce the average time for one series of samples. González et al. (2004) indicated that maintaining a balance between time consumption and reliability of the obtained results can be done by selecting the appropriate number of quality control analyses and choosing less or more accurate analytical methods. The gravimetric method is a fast alternative to colourimetric methods but has the lowest precision and the highest LOD values. The choice of analytical method requires, therefore, careful consideration of different criteria.
Although all methods of bulk lipid quantification in the whole body of marine benthic invertebrates proved accurate and highly reproducible, comparative studies unravelled important differences in yield and efficiency. The gravimetric method appeared most advantageous in terms of labour intensity but was the worst-performing when considering the validation parameters. The Marsh and Weinstein method provided an analytical procedure with the highest precision and recovery, and the lowest LOD. It was more time-consuming than the gravimetric method but less labour-intensive than the Frings and Dunn method. The Frings and Dunn method produced more reliable results than the gravimetric method, but completing the analysis required the most time.