Skip to main content
. 2021 Nov 10;11(22):16126–16142. doi: 10.1002/ece3.8293

TABLE 3.

Conceptual summary table containing the main results obtained with different methodological approaches for sardinella (Sardinella aurita), anchovy (Engraulis encrasicolus), and sardine (Sardina pilchardus)

Methodological approach Variable Species
S. aurita E. encrasicolus S. pilchardus

Stable isotopes

δ13C and δ15N

δ13C–TL relationship Positive a Positive a (ns)
δ15N–TL relationship (ns) (ns) Negative a
Isotopic niche area Widest 0.46‰2 0.21‰2 0.38‰2
Isotopic niche overlap S. auritaE. encrasicolus > S. auritaS. pilchardus
Stomach contents (visual analysis) SFD–TL relationship Positive a Negative a Negative a
Parasites Highest Lowest
Anthropogenic pollution Highest Lowest
Stomach contents corrected by DNA metabarcoding Prey number (main contribution) euph./decap./malac. (highest abundance) euph./decap./malac. cal.cop./euph.
Prey biomass (main contribution) euph./decap./malac. euph./decap./malac. euph./decap./malac.
Shannon diversity index 2.31 1.51 1.84
PPSR >75% large prey ~60% large prey >75% large prey
PPBR >80% large prey ~60% large prey >75% large prey
Relative diet dissimilarity Highest difference in jelly/siph. Highest RDI between E. Encrasicolus–S. pilchardus
Beta‐diversity Lowest individual variation in prey composition Most different due to higher prey replacement (turnover)
Similar nestedness in the three species
a

Denotes significant difference (p < .01); ns means not significant relationship; “cal.cop.”: calanoid copepods; “euph.”: euphausiids; “decap.”: decapods; “malac.”: malacostracans; “jelly”: jelly organisms; “siph.”: siphonophores.