Figure 1. Study site of project. Twenty humpback whale (Megaptera novaeangliae) fecal samples were collected near the western entrance to the Juan de Fuca Strait, off the southwest coast of Vancouver Island, British Columbia, Canada.
Sample ID | Particle Count | Sample Mass (g) | AP/g Dry | AP/g Wet |
---|---|---|---|---|
194f1 | 12.78 | 0.47 | 27.19 | 6.80 |
194f2 | 15.78 | 1.85 | 8.53 | 2.13 |
199f1 | 13.78 | 2.03 | 6.79 | 1.70 |
228f1 | 5.78 | 1.17 | 4.94 | 1.24 |
234f1 | 4.78 | 1.38 | 3.46 | 0.87 |
234f2 | 0.78 | 1.25 | 0.62 | 0.16 |
234f3 | 11.78 | 1.31 | 8.99 | 2.25 |
235f1 | 5.78 | 1.19 | 4.86 | 1.21 |
235f2 | 9.78 | 1.20 | 8.15 | 2.04 |
235f3 | 3.78 | 0.71 | 5.32 | 1.33 |
235f4 | 6.78 | 2.22 | 3.05 | 0.76 |
235f5 | 7.78 | 2.09 | 3.72 | 0.93 |
236f1 | 7.78 | 1.28 | 6.08 | 1.52 |
236f2 | 1.78 | 1.43 | 1.24 | 0.31 |
255f1 | 7.78 | 2.37 | 3.28 | 0.82 |
256f1 | 5.78 | 1.62 | 3.57 | 0.89 |
261f2 | 7.78 | 0.41 | 18.98 | 4.74 |
263f1 | 16.78 | 0.75 | 22.37 | 5.59 |
The total number of anthropogenic particles across all the samples (N=18) is 169.
The dry fecal AP concentration ranges from 0.62 to 27.19 (mean 7.84 ± 7.41 AP/g).
The wet fecal AP concentration ranges from 0.16 to 6.8 (mean 1.96 ± 1.85 AP/g).
The final AP/g is lower when only using counts ≥ limit of quantification (LOQ). This value can be seen at end of the document.
Sample ID | Particle Count | Sample Mass (g) | AP/g Dry | AP/g Wet |
---|---|---|---|---|
194f2 | 5 | 0.31 | 16.13 | 4.03 |
199f1 | 6 | 0.32 | 18.75 | 4.69 |
228f1 | 5 | 0.31 | 16.13 | 4.03 |
234f1 | 10 | 0.31 | 32.26 | 8.06 |
234f2 | 4 | 0.21 | 19.05 | 4.76 |
234f3 | 22 | 0.32 | 68.75 | 17.19 |
235f1 | 10 | 0.36 | 27.78 | 6.94 |
235f2 | 9 | 0.16 | 56.25 | 14.06 |
235f4 | 2 | 0.10 | 20.00 | 5.00 |
235f5 | 1 | 0.10 | 10.00 | 2.50 |
236f1 | 9 | 0.30 | 30.00 | 7.50 |
236f2 | 2 | 0.10 | 20.00 | 5.00 |
255f1 | 1 | 0.10 | 10.00 | 2.50 |
256f1 | 4 | 0.33 | 12.12 | 3.03 |
261f2 | 3 | 0.19 | 15.79 | 3.95 |
263f1 | 1 | 0.06 | 16.67 | 4.17 |
The total number of anthropogenic particles across all samples (N=16) is 94.
The dry fecal AP concentration ranges from 10 to 68.75 (mean 24.36 ± 16.37 AP/g).
The wet fecal AP concentration ranges from 2.5 to 17.19 (mean 6.09 ± 4.09 AP/g).
Figure 2. Bar chart of the concentration and polymer composition of anthropogenic particles (AP) isolated from caustically digested humpback whale fecal samples (N=18).
Figure 3. Bar chart of the concentration and polymer composition of anthropogenic particles (AP) isolated from enzymatically digested humpback whale fecal samples (N=15).
Some anthropogenic particles were too small and degraded for FTIR spectroscopy. Therefore, only a subset of particles have a polymer ID. This subset of scanned particles are used for figure 4, 5, and tables 3, 4 below.
57.99 % of anthropogenic particles isolated via caustic digestion were analyzed with FTIR (98 out 169 total particles).
Additionally, 69.15 % of anthropogenic particles isolated via enzymatic digestion were analyzed with FTIR (65 out 94 total particles).
Figure 4. Bar chart depicting the frequncy of occurence for anthropogenic particles isolated from humpback whale feces via caustic and enzymatic digestion.
Figure 5. Pie chart of polymer distributions between caustic and enzymatic digestions.
Colour | Polymer ID | Morphology | Count | Percentage (of scanned particles) |
---|---|---|---|---|
Clear | Cellulose | Fiber | 15 | 15.3 |
Clear | Polyester | Fiber | 13 | 13.3 |
Clear | Polyethylene | Fiber | 8 | 8.2 |
Black | Polyester | Fiber | 5 | 5.1 |
Clear | polyamide | Fiber | 5 | 5.1 |
Colour | Polymer ID | Morphology | Count | Percentage (of scanned particles) |
---|---|---|---|---|
Blue | Cellulose | Fiber | 21 | 32.3 |
Black | Cellulose | Fiber | 16 | 24.6 |
Black | PTFE | Fiber | 5 | 7.7 |
Red | Cellulose | Fiber | 5 | 7.7 |
Black | Polyester | Fiber | 3 | 4.6 |
Figure 6. Examples of anthropogenic particles isolated from humpback whale feces via caustic digestion. A: Polyester fiber from sample 194F1, B: Polypropylene fiber from sample 194F2, C: Polyamide fiber from sample 194F2, D: Cellulose fiber from sample 236F1, E: Cellulose fiber from sample 194F1, F: Polyethylene fragment from sample 199F1, G: Acrylic fragment from sample 255F1, H: Polyethylene fiber from sample 199F1, I: Polyethylene fragment from sample 261F2.
Figure 7. Principle component spectrum of polyethylene fiber isolated from sample 261F2 via caustic digestion.
Table 5. Length and width of 169 isolated anthropogenic particles. | |||
Measurement | Mean | Min | Max |
---|---|---|---|
Length (μm) | 1564.12 | 35.85 | 21949.35 |
Width (μm) | 59.29 | 3.16 | 1238.82 |
Table 6. Morphology of 169 isolated anthropogenic particles. | ||
Morph | Count | Percent |
---|---|---|
Fiber | 143 | 84.62 |
Fragment | 21 | 12.43 |
Film | 4 | 2.37 |
Sphere | 1 | 0.59 |
Table 7. Colour of 169 isolated anthropogenic particles. | ||
Colour | Count | Percent |
---|---|---|
Clear | 78 | 46.15 |
Black | 29 | 17.16 |
Blue | 15 | 8.88 |
Yellow | 15 | 8.88 |
Red | 12 | 7.10 |
Green | 11 | 6.51 |
Grey | 7 | 4.14 |
Brown | 1 | 0.59 |
Pink | 1 | 0.59 |
Table 8. Polymer ID of 98 scanned anthropogenic particles. | ||
Polymer | Count | Percent |
---|---|---|
Polyester | 27 | 27.55 |
Cellulose | 25 | 25.51 |
Polyethylene | 23 | 23.47 |
Polyamide | 11 | 11.22 |
Polypropylene | 7 | 7.14 |
PTFE | 4 | 4.08 |
Acrylic | 1 | 1.02 |
Figure 8. Examples of anthropogenic particles isolated from humpback whale feces via enzymatic digestion. A: Polyester fiber from sample 199F1, B: Polypropylene fiber from sample 199F1, C: PTFE fiber from sample 234F2, D: Polyurethane fiber from sample 235F1, E: Cellulose fiber from sample 234F1, F: PTFE fiber from sample 234F3, G:Polypropyelene fiber from sample 235F4, H: Cellulose fiber from sample 234F3, I: Cellulose fiber from sample 263F1.
Figure 9. Principle component spectrum of polypropylene fiber isolated from sample 199F1 via enzymatic digestion.
Table 9. Length and width of 94 isolated anthropogenic particles. | |||
Measurement | Mean | Min | Max |
---|---|---|---|
Length (μm) | 841.53 | 3.16 | 5367.65 |
Width (μm) | 29.67 | 1.42 | 510.24 |
Table 10. Morphology of 94 isolated anthropogenic particles. | ||
Morph | Count | Percent |
---|---|---|
Fiber | 88 | 93.62 |
Fragment | 4 | 4.26 |
Film | 2 | 2.13 |
Table 11. Colour of 94 isolated anthropogenic particles. | ||
Colour | Count | Percent |
---|---|---|
Black | 44 | 46.81 |
Blue | 26 | 27.66 |
Grey | 7 | 7.45 |
Red | 7 | 7.45 |
Green | 3 | 3.19 |
Orange | 3 | 3.19 |
Brown | 2 | 2.13 |
Clear | 2 | 2.13 |
Table 12. Polymer ID of 65 scanned anthropogenic particles. | ||
Polymer | Count | Percent |
---|---|---|
Cellulose | 47 | 72.31 |
PTFE | 7 | 10.77 |
Polyester | 6 | 9.23 |
Polyamide | 2 | 3.08 |
Polypropylene | 2 | 3.08 |
Polyurethane | 1 | 1.54 |
We must decide which fecal microplastic concentration is more accurate (caustic versus enzymatic) for use in the stochastic simulation model.
Based on the literature, the caustic method of digesting organic material is harsh on certain kinds of anthropogenic particles, especially nylon and PTFE (Turri et al., 2024; Karami et al., 2016). Regenerated cotton, although not plastic, is readily degraded by caustic reagents (i.e., nitric acid and hydrogen peroxide) (Pfieffer & Fischer, 2020). Therefore, it is reasonable to assume the caustic data will underestimate the true fecal anthropogenic particle concentration.
That said, approximately 5x more sample mass was used with the caustic digestion compared to the enzymatic method. As consequence of more sample mass, the total number of anthropogenic particles is greater in the caustic versus enzymatic data (169 versus 94). Further, the caustic data have a greater diversity of polymer IDs. This can be attributed to the heterogeneous distribution of anthropogenic particles in biological samples with larger samples encapsulating a greater diversity of potential particle variants (Cross et al., 2025).
Enzymes like proteinase K have little to no effect on anthropogenic particles (Cole et al., 2014), potentially providing a more accurate picture of AP loads in whale feces. However, the digestive efficacy of Proteinase K is low compared to nitric acid and hydrogen peroxide, so less sample mass can be processed. The question remains whether a low sample mass with no anthropogenic particle degredation (i.e., enzymatic digestion) is better than a high sample mass with moderate anthropogenic particle degredation (i.e., caustic digestion).
In either digestion method, modified cellulose is quite abundant. This makes sense.
“Most fibers floating in the world’s oceans are not plastic but dyed cellulose.” https://pmc.ncbi.nlm.nih.gov/articles/PMC7274779/
Aside from the digestion methodologies themselves, the caustic and enzymatic experiments deal with contamination in different ways. In both datasets, APs which match the polymer ID, colour, and morphology of particles found in field and laboratory controls were removed from analyses. However, the laboratory procedural blanks were treated differently between digestion methods. With the caustic method, there were enough procedural blanks (n=9) to subtract an averaged count value (average #AP/blank) from each of the fecal samples. Further, the average #AP/blank was used to calculate a limit of detection (LOD; mean + 3 X SD) and limit of quantification (LOQ; mean + 10 X SD) for the caustic digestion study (Bråte et al., 2022). Using samples which satsify a particle count ≥ LOQ, the dry fecal microplastic concentration ranges from 0.62 to 27.19 AP/g (mean 7.84 ± 7.41). Further, the wet fecal microplastic concentration ranges from 0.16 to 6.8 AP/g (mean 1.96 ± 1.85). In comparison, the enzymatic method had too few procedural blanks (n=2) to accurately subtract an average # AP/PB from each fecal sample. Instead, procedural blanks were treated in the same way as all other controls by omitting fecal MPs which match the characteristics of particles found in procedural blanks (clear fibers).
Ultimately, the average dry concentration of anthropogenic particles isolated via caustic digestion is 7.84 ± 7.41 MP/g and the average dry concentration of anthropogenic particles isolated via enzymatic digestion is 24.36 ± 16.37 MP/g.
A Shaprio-Wilk test was used to assess normality of AP/sample data. The data was not normal so a Wilcoxon Rank Sum test was used to differentiate between the anthropogenic particle abundance in controls and samples.
Figure 10: Comparison of anthropogenic particle abundance (AP/sample) between samples and controls. The points represent the mean particle count of each sample type. Horizontal bars indicate group means ± standard deviation. A Mann–Whitney U test revealed a significant difference between groups. ****(P<<0.05).
For the caustic digestion, the AP concentration in the sample data was significantly greater than the controls and therefore reliable for reporting. The difference was not statistically significant (p = 0.02861) with the enzymatic digestions
A total of 85 anthropogenic particles were isolated across a variety of controls. Here is the breakdown:
Control Type | Particle Count | Percent |
---|---|---|
Seawater blank (n=18) | 50 | 58.8 |
Field air control (n=12) | 5 | 5.9 |
Fecal aliquot air control (n=12) | 5 | 5.9 |
Lyphophilizer air control (n=2) | 9 | 10.6 |
Caustic procedural blank (n=9) | 6 | 7.1 |
Enzymatic procedural blank (n=2) | 10 | 11.8 |
|
LOD and LOQ calculated from caustic procedural blanks are 3.26 and 9.33, respectively. |
|
Enzymatic LOD and LOQ are both 0 since clear fibers were omitted from analyses. |
Figure 11: Polymer & morphology of particles in seawater blanks. 68 % of anthropogenic particles isolated in seawater procedural blanks were analyzed with FTIR (34 out 50 total particles).
Figure 12: Polymer & morphology of particles in field air controls. 60 % of anthropogenic particles isolated in field air controls were analyzed with FTIR (3 out 5 total particles).
Figure 13: Polymer & morphology of particles in laboratory air controls. 64.29 % of anthropogenic particles isolated in laboratory air controls were analyzed with FTIR (9 out 14 total particles).
Table 16. Colour of particles isolated from seawater blanks. | ||
Colour | Count | Percent |
---|---|---|
Clear | 42 | 84 |
Black | 3 | 6 |
Blue | 3 | 6 |
Green | 1 | 2 |
Red | 1 | 2 |
Table 17. Colour of particles isolated from field air controls. | ||
Colour | Count | Percent |
---|---|---|
Blue | 4 | 80 |
Black | 1 | 20 |
Table 18. Colour of particles isolated from lab air controls. | ||
Colour | Count | Percent |
---|---|---|
Black | 9 | 64.29 |
Blue | 3 | 21.43 |
Clear | 2 | 14.29 |
Sample ID | Particle Count | Sample Volume (ml) |
---|---|---|
194f1sn | 8 | 5 |
194f2sn | 2 | 160 |
199f1sn | 0 | 185 |
228f1sn | 1 | 80 |
234f1sn | 0 | 20 |
234f2sn | 0 | 30 |
234f3sn | 11 | 200 |
235f1sn | 4 | 80 |
235f2sn | 0 | 250 |
235f3sn | 2 | 160 |
235f4sn | 2 | 40 |
235f5sn | 1 | 130 |
236f1sn | 2 | 80 |
236f2sn | 0 | 10 |
255f1sn | 0 | 140 |
256f1sn | 0 | 130 |
258f1sn | 0 | 40 |
261f1sn | 0 | 40 |
261f2sn | 1 | 40 |
263f1sn | 0 | 10 |
Figure 14. Bar chart showing the count and polymer composition of anthropogenic particles (AP) isolated from humpback whale fecal supernatant.
Table 20. Colour of particles isolated from supernatants. | ||
Colour | Count | Percent |
---|---|---|
Black | 16 | 47.06 |
Blue | 10 | 29.41 |
Red | 3 | 8.82 |
White | 3 | 8.82 |
Brown | 1 | 2.94 |
Green | 1 | 2.94 |
Figure 15. Stacked bar graph showing colour proportion of anthropogenic particles (AP) isolated from caustic digestions and associated supernatants.
Figure 16. Stacked bar graph showing colour proportion of anthropogenic particles (AP) isolated from enzymatic digestions and associated supernatants.
After excluding particles matching those seen in controls (procedural blanks and channel controls), there was a total of 44 APs found in 314.21 liters of seawater among nine samples. Each sample was an average of 31.421 liters.
AP length range was 26.837733, 4014.218224 µm (mean 1001.5233 µm) and width was 1.265143, 1528.677931 µm (mean 50.5874292 µm).
Morphology | Count | Percent (%) |
---|---|---|
Fiber | 33 | 75.0 |
Fragment | 7 | 15.9 |
Film | 4 | 9.1 |
Colour | Count | Percent (%) |
---|---|---|
Red | 17 | 38.6 |
Blue | 15 | 34.1 |
Clear | 5 | 11.4 |
Black | 4 | 9.1 |
Green | 1 | 2.3 |
Grey | 1 | 2.3 |
Yellow | 1 | 2.3 |
Polymer ID | Count | Percent (%) |
---|---|---|
Cellulose | 20 | 62.5 |
Polyester | 4 | 12.5 |
Poly(vinyl alcohol) | 2 | 6.2 |
Polyamide | 2 | 6.2 |
Polysulfone | 2 | 6.2 |
PTFE | 1 | 3.1 |
Polypropylene | 1 | 3.1 |
Sample ID | Count | Volume (l) | Depth (m) | Concentration (AP/M3) | Category |
---|---|---|---|---|---|
0715-25m | 0 | 15.033 | 25.4220 | 0.00000 | Very Low |
0715-50m | 3 | 20.042 | 52.1500 | 149.68566 | Very High |
0716-100m | 10 | 24.529 | 99.9300 | 407.68070 | Very High |
0716-50m | 10 | 40.297 | 50.7970 | 248.15743 | Very High |
0719-50m | 1 | 40.158 | 46.2677 | 24.90164 | Very High |
0911-5m | 10 | 40.247 | 5.1460 | 248.46572 | Very High |
0914-25m | 4 | 40.074 | 25.4000 | 99.81534 | Very High |
0914-50m | 1 | 40.338 | 50.4000 | 24.79052 | Very High |
0916-50m | 4 | 13.377 | 50.4000 | 299.02071 | Very High |
0917-25m | 1 | 40.115 | 25.6900 | 24.92833 | Very High |
Figure 17: Anthropogenic particle concentration (AP/M3) across multiple depths (5, 25, 50, and 100 m). Each yellow dot represents a sample (n=10) collected by the Ascension
Figure 18: Bar chart of the number of anthropogenic particles and polymer composition of subsurface seawater samples collected with the Ascension
Sample ID | AP Count |
---|---|
asens-pb | 2 |
Sample ID | AP Count |
---|---|
0916-cntr-7 | 9 |
0911-cntrl | 4 |
0916-cntr-4 | 3 |
0914-cntr-7 | 2 |
Colour | Count | Percent (%) |
---|---|---|
Clear | 15 | 83.3 |
Black | 2 | 11.1 |
Blue | 1 | 5.6 |
Morphology | Count | Percent (%) |
---|---|---|
Fiber | 17 | 94.4 |
Fragment | 1 | 5.6 |
Polymer Category | Count | Percent (%) |
---|---|---|
Cellulose | 7 | 87.5 |
Polyester | 1 | 12.5 |
Colour | Count | Percent (%) |
---|---|---|
Clear | 1 | 50 |
Grey | 1 | 50 |
Morphology | Count | Percent (%) |
---|---|---|
Fiber | 2 | 100 |
Polymer Category | Count | Percent (%) |
---|---|---|
Cellulose | 1 | 50 |
PTFE | 1 | 50 |
The data from the subsurface seawater samples are highly suspect. The sample volume is too small to capture the expected particle abundance in the water column. Based on literature, the AP/m3 in the Northeast Pacific is likely somewhat low, < 15 particles per m3 (Choy et al., 2019).
Figure 19: Plot of sampling volume needed to detect microplastics versus expected microplastic concentrations in sewater. The blue line shows the volume needed for a laboratory with a MDA of 7.