Alicia
Bellanco
a,
Judith
Félix
b,
Estefanía
Díaz Del Cerro
b,
M. Carmen
Martínez Cuesta
a,
Mónica
De la Fuente
b and
Teresa
Requena
*a
aDepartment of Food Biotechnology and Microbiology, Instituto de Investigación en Ciencias de la Alimentación CIAL-CSIC, Madrid, Spain. E-mail: t.requena@csic.es
bDepartment of Genetics, Physiology and Microbiology (Animal Physiology Unit), Faculty of Biological Sciences, Complutense University of Madrid, 28040 Madrid, Spain
First published on 23rd May 2024
The safety of the carrageenan (CGN) consumption as a food additive is under debate, with negative effects being associated with the products of hydrolysis of CGN. Moreover, there is an increasing need to integrate gut microbiome analysis in the scientific risk assessment of food additives. The objective of this study was to test the effects of CGN consumption on the gut microbiota and the intestinal homeostasis of young male and female mice. Female and male ICR-CD1 mice (8 weeks old) orally received 540 mg kg−1 day−1 of CGN, representing the maximum-level exposure assessment scenario surveyed for children, over the course of two weeks. Fecal material and peritoneal immune cells were analyzed to determine changes in the fecal microbiota, based on the analysis of bacterial 16S rRNA gene amplicon sequences and short-chain fatty acid (SCFA) concentrations, and some immune functions and redox parameters of peritoneal leukocytes. Non-significant microbiota taxonomical changes associated with CGN intake were found in the mouse stools, resulting the housing time in an increase in bacterial groups belonging to the Bacteroidota phylum. The PICRUSt2 functional predictions showed an overall increase in functional clusters of orthologous genes (COGs) involved in carbohydrate transport and metabolism. A significant increase in the cytotoxicity of fecal supernatants was observed in CGN-fed mice, which correlated with worsening of immune functions and oxidative parameters. The altered immunity and oxidative stress observed in young mice after the consumption of CGN, along with the fecal cytotoxicity shown towards intestinal epithelial cells, may be associated with the gut microbiota’s capacity to degrade CGN. The characterization of the gut microbiota’s ability to hydrolyze CGN should be included in the risk assessment of this food additive.
For the characterization of CGNs, they are frequently evaluated in vitro for beneficial properties such as antioxidant, anti-inflammatory, or antithrombotic activities;5 however, they are applied as a model in vivo to induce impairing effects such as paw edema, intestinal inflammation or colon ulcerative lesions.6 This disparity in scientific outcomes has been attributed to molecular weight (Mw) differences between the assayed compounds, differentiating between the high Mw of the food additive (200000–800
000 Da) and the low Mw of the products of hydrolysis of CGN, degraded CGN or polygeenan (10
000–40
000 Da). The latter is not authorized as a food additive4 and is classified as a potential human carcinogen by the International Agency for Research on Cancer.7
CGN hydrolysis during passage through the gastrointestinal tract has been barely described; in addition, due to protein reactivity, CGN may attenuate protein digestibility by pepsin.8 Likewise, little is known about the ability of the gut microbiota to hydrolyze CGN and, in such a case, the safe threshold limit of the low-molecular-weight products. Bacteria able to hydrolyze CGN into sulfated oligosaccharides have been isolated mainly from marine environments,9,10 but no conclusive information exists about CGN-degrading bacteria present in the human intestine. In addition to changes in polysaccharide molecular weight, the sulfated CGN products can be degraded by bacterial sulfatases and sulfate reductases to produce hydrogen sulfide, which has been implicated in inflammatory bowel diseases.11
The increasing knowledge of the interactions between the gut microbiome and dietary components has motivated food safety authorities, such as the EFSA, to explore integrating gut microbiome analysis into the regulatory scientific risk assessment of food additives and xenobiotics, among other things.12,13 In recent work using a dynamic gut microbiota simulator (BFBL Gut Model,14), we have observed a dose-dependent response in the permeabilizing effect of supernatants from CGN-fed microbiota when incubated with intestinal epithelium Caco-2 line cells, but no effect with an equal amount of CGN in the incubation medium.15 When performing in vivo studies, the intestinal homeostasis can be assessed as it is achieved via adequate communication among the gut microbiota, immune cells, and epithelium. In mice, the functional capacity and redox state of peritoneal leukocytes are good markers of intestinal homeostasis, but also of the general homeostatic response and the health condition of the animals.16–18 There are scarce studies on the effects of CGN on the function and oxidative stress of leukocytes, and these have shown contradictory results.19–21 Moreover, the effects of CGN ingestion on several relevant immune functions and redox parameters of peritoneal leukocytes from mice are unknown. Therefore, the objective of this study was to test the in vivo effects of feeding CGN, at exposure values assessed for children,4 on the gut microbiota and the intestinal homeostasis of young male and female mice.
The animals (n = 40) were distributed into control and experimental groups (10 per group and sex). The mice orally received 540 mg kg−1 day−1 of κ-carrageenan resuspended in 200 μL of PBS for 15 days in the experimental groups (FCGN10w and MCGN10w) and PBS in the control groups (FC10w and MC10w). The administered CGN dose was selected at the maximum-level exposure assessment scenario surveyed for children.4 Body weight was monitored before and after the two-week experimental period.
The protocol was approved by the Experimental Animal Committee of the Complutense University of Madrid and Community of Madrid (PROEX. 224.0/21). The animals were treated in accordance with the guidelines of Royal Decree 118/2021 of 23 February 2021 (BOE no. 47) on the protection of animals used for experimentation and other scientific purposes.
The natural killer (NK) cell cytotoxicity was evaluated via the lysis of murine YAC-1 lymphoma cells (105 mL−1) induced by peritoneal leukocytes (106 mL−1) by quantifying the lactate dehydrogenase released into the medium (CytoTox 96, Promega). The results were expressed as the percentage of tumor cells killed (% lysis), as previously described.17
The proliferative capacities of lymphocytes, basal and stimulated by the mitogens concanavalin A (ConA) (1 μg mL−1; Sigma-Aldrich) and lipopolysaccharide (LPS) (1 μg mL−1, Escherichia coli 055:B5; Sigma-Aldrich), were evaluated in 106 leukocytes per mL incubated with 3H-thymidine (0.5 μCi, MP Biomedicals) for 24 h.25 The 3H-thymidine uptake by the lymphocytes was quantified in a liquid scintillation beta counter (LKB) and the results were expressed in counts per minute (cpm). The percentage of stimulation was expressed as the % mitogen-stimulated lymphoproliferation in relation to the basal cpm.
Macrophage phagocytosis was evaluated based on their capacity to take in latex beads (1% in PBS).17 The number of latex beads ingested per 100 macrophages (phagocytic index) and the percentage of macrophages that ingested at least one latex bead (phagocytic efficacy) were determined.
The glutathione reductase (GR) activity of the leukocyte suspension (106 cells per ml) was measured with 80 mM GSSG (Sigma-Aldrich) as the substrate, as previously described.26 For the glutathione peroxidase (GPx) activity, the leukocytes were tested with cumene hydroperoxide as the substrate (cumene-OOH; Sigma-Aldrich).26 The enzymatic activities are expressed in mU of GR or GPx activity per mg protein.
Group | N | Weight (g) | Shannon | Simpson |
---|---|---|---|---|
*, significant differences (p < 0.05) between the start (8w) and after two weeks (10w) of treatment (C or CGN), using Student’s t-test analysis. | ||||
FC8w | 18 | 29.52 (0.62) | 6.39 (0.12) | 0.963 (0.005) |
FC10w | 9 | 31.30* (0.63) | 5.90* (0.16) | 0.941* (0.010) |
FCGN10w | 9 | 29.23 (0.53) | 5.92* (0.07) | 0.947* (0.003) |
MC8w | 19 | 34.63 (0.47) | 6.79 (0.08) | 0.976 (0.002) |
MC10w | 8 | 36.58* (0.55) | 5.81* (0.20) | 0.945* (0.011) |
MCGN10w | 8 | 35.64 (0.46) | 6.10* (0.27) | 0.942* (0.013) |
The microbial changes observed during the 2-week experimental period can be attributed to the decrease in the relative abundance (%; mean ± SEM) of populations of the phyla Bacillota (syn. Firmicutes), 70.30 ± 1.29 vs. 43.35 ± 1.85, and Actinomycetota (syn. Actinobacteria), 2.16 ± 0.23 vs. 0.96 ± 0.14, and the corresponding increase in the relative abundances in the phyla Bacteroidota (syn. Bacteroidetes), 25.61 ± 1.32 vs. 50.78 ± 1.68, Verrucomicrobiota (syn. Verrucomicrobia), 0.24 ± 0.15 vs. 2.45 ± 0.63, and Pseudomonadota (syn. Proteobacteria), 0.18 ± 0.04 vs. 0.74 ± 0.15. The changes were observed in both male and female mice and were not related to the CGN intake (Fig. 1A). The mentioned changes could be attributed to decreases in the families Lachnospiraceae and Ruminococcaceae and increases in Muribaculaceae and Bacteroidaceae (Fig. 1B).
Table 2 shows the bacterial genera representing at least 0.1% relative abundance in any of the tested mice. Most of the differences were observed after the two weeks of the experimental period, with only the increase in Alloprevotella being associated with CGN intake in both the female and male CGN10w mouse groups. However, the observed CGN effect on this genus’ abundance cannot provide enough information to infer a positive29 or negative effect.30Bacteroides was the genus showing the highest increase during the experimental period in both F and M mouse groups, whereas the Eubacterium xylanophilum group showed the most marked decrease during the assayed time (Table 2). Differences between the F and M groups were only observed in the relative abundances of Lactobacillus and Bifidobacterium.
FC8w | FC10w | FCGN10w | MC8w | MC10w | MCGN10w | |
---|---|---|---|---|---|---|
*, significant differences (p < 0.05) between the start (8w) and after two weeks (10w) of treatment (C or CGN). ‡, significant differences between F and M under the same conditions, using the Mann–Whitney analysis. | ||||||
Lactobacillus | 8.93 (5.35–11.05) | 3.79 (2.33–4.78) | 10.56 (3.73–12.31) | 1.75‡ (1.14–3.66) | 3.08 (2.55–8.53) | 2.60‡ (1.67–4.99) |
Turicibacter | 0.08 (0.04–0.13) | 0.13 (0.09–0.37) | 0.56 (0.36–1.59) | 0.07 (0.04–0.26) | 0.42 (0.33–0.70) | 0.07 (0.02–0.10) |
Alloprevotella | 3.97 (2.26–5.49) | 3.08 (1.77–9.55) | 12.13* (5.95–14.99) | 1.87 (1.54–3.14) | 4.40 (1.32–6.11) | 6.46* (2.95–8.91) |
Eubacterium xylanophilum group | 2.78 (1.29–3.99) | 0.96* (0.63–1.71) | 0.69* (0.51–0.83) | 4.45 (3.26–5.85) | 0.28* (0.13–0.48) | 0.91* (0.44–1.70) |
Akkermansia | 0.05 (0.02–0.15) | 0.11 (0.04–1.81) | 0.16 (0.06–0.80) | 0.02 (0.01–0.10) | 2.26* (0.19–8.52) | 0.07 (0.01–0.12) |
Bacteroides | 1.83 (1.35–2.74) | 6.08* (3.82–7.60) | 4.84* (3.33–5.64) | 1.89 (1.20–2.12) | 4.76* (2.94–6.66) | 3.58* (2.87–3.87) |
Bifidobacterium | 0.00 (0.00–0.01) | 0.10* (0.04–0.45) | 0.15* (0.05–0.31) | 0.01 (0.00–0.02) | 0.00‡ (0.00–0.01) | 0.00‡ (0.00–0.00) |
Alistipes | 1.01 (0.73–1.41) | 0.72 (0.50–1.44) | 0.86 (0.71–1.31) | 0.74 (0.63–1.30) | 1.48 (0.62–2.88) | 1.42 (1.31–1.92) |
Romboutsia | 0.00 (0.00–0.00) | 0.04* (0.01–0.07) | 0.07* (0.05–0.13) | 0.01 (0.00–0.05) | 0.18 (0.10–0.33) | 0.06 (0.02–0.10) |
Enterorhabdus | 1.65 (1.30–2.66) | 0.79* (0.54–1.07) | 0.52* (0.44–0.64) | 1.67 (1.29–2.40) | 0.61* (0.42–0.68) | 0.39* (0.26–0.40) |
Odoribacter | 0.57 (0.31–1.11) | 0.63 (0.55–1.18) | 0.65 (0.43–1.20) | 0.56 (0.33–1.59) | 0.44 (0.33–2.17) | 0.92 (0.77–1.38) |
Lachnoclostridium | 0.88 (0.69–1.24) | 0.40* (0.23–0.61) | 0.44* (0.32–0.47) | 0.76 (0.61–1.05) | 0.23* (0.18–0.35) | 0.27* (0.26–0.44) |
Eubacterium coprostanoligenes group | 1.36 (0.94–1.94) | 0.53* (0.49–0.58) | 0.85* (0.70–0.90) | 1.66 (0.90–1.88) | 1.00 (0.60–1.62) | 1.04 (0.37–1.76) |
Ruminococcus | 0.72 (0.56–0.97) | 0.15* (0.08–0.41) | 0.44* (0.35–0.55) | 0.85 (0.62–1.29) | 0.30* (0.22–0.46) | 0.44 (0.28–1.11) |
Blautia | 0.52 (0.37–0.66) | 0.15 (0.13–0.58) | 0.41 (0.24–0.80) | 0.45 (0.29–0.62) | 0.16 (0.06–0.25) | 0.31 (0.21–0.57) |
Roseburia | 0.39 (0.21–0.67) | 0.31 (0.18–0.73) | 0.20 (0.18–0.37) | 0.69 (0.41–1.15) | 0.39 (0.17–1.02) | 0.28 (0.16–0.63) |
Erysipelatoclostridium | 0.12 (0.08–0.23) | 0.12 (0.05–0.30) | 0.13 (0.10–0.17) | 0.16 (0.13–0.37) | 0.10 (0.06–0.22) | 0.07 (0.05–0.10) |
Muribaculum | 1.01 (0.68–1.50) | 2.14 (1.68–2.40) | 1.34 (1.12–2.02) | 1.01 (0.72–1.21) | 1.26 (0.94–1.51) | 1.10 (1.00–1.32) |
Monoglobus | 0.27 (0.19–0.33) | 0.15* (0.04–0.30) | 0.09* (0.07–0.13) | 0.41 (0.27–0.65) | 0.07* (0.04–0.08) | 0.13* (0.10–0.19) |
Oscillibacter | 0.57 (0.30–0.68) | 0.22* (0.20–0.29) | 0.27* (0.25–0.32) | 0.68 (0.58–0.94) | 0.20* (0.14–0.26) | 0.42* (0.27–0.46) |
Parabacteroides | 0.04 (0.03–0.07) | 0.10* (0.07–0.12) | 0.17* (0.09–0.24) | 0.03 (0.02–0.05) | 0.14* (0.06–0.22) | 0.23* (0.13–0.26) |
Colidextribacter | 0.38 (0.28–0.58) | 0.13* (0.10–0.18) | 0.20* (0.14–0.23) | 0.51 (0.41–0.61) | 0.12* (0.09–0.17) | 0.24* (0.21–0.26) |
Parasutterella | 0.06 (0.04–0.09) | 0.33* (0.13–0.90) | 0.21* (0.16–0.42) | 0.04 (0.03–0.07) | 0.10* (0.05–0.29) | 0.05 (0.04–0.19) |
Anaerotruncus | 0.14 (0.08–0.19) | 0.09* (0.05–0.09) | 0.05* (0.04–0.06) | 0.17 (0.13–0.28) | 0.05* (0.04–0.09) | 0.10* (0.05–0.16) |
Butyricicoccus | 0.13 (0.11–0.15) | 0.08* (0.03–0.09) | 0.07* (0.06–0.10) | 0.16 (0.13–0.24) | 0.03* (0.02–0.06) | 0.07* (0.05–0.08) |
The PICRUSt2 functional predictions based on 16S rDNA amplicons showed an overall clustering of samples according to age (ESI: Fig. S1, COGs; Fig. S2, Pathway; Fig. S3, EC†). The predicted functions of COGs related to carbohydrate transport and metabolism were examined in more detail (Fig. 2). Shifts in functional COGs of the gut microbiota involved in carbohydrate transport and metabolism during the experimental period indicated an increase in function related to complex glycan hydrolysis, such as arabinogalactan, glucan and polygalacturan-related enzyme activities, among others. Conversely, a decrease in bacterial polysaccharide transport systems and galactosidase and glucosidase activities could coincide with the changes in microbial composition.
Table 3 shows changes in the microbial metabolism, assessed as the concentration of SCFAs and ammonium. The results indicated a decrease in succinic acid with time, independently of the CGN intake, and a trend of increasing concentration of acetic and propionic acids, being only significantly higher in the M10w groups.
Group | Succinate | Lactate | Acetate | Propionate | Butyrate | Ammonium |
---|---|---|---|---|---|---|
*, significant differences (p < 0.05) between the start (8w) and after two weeks (10w) of treatment (C or CGN), using Student’s t-test analysis. | ||||||
FC8w | 13.16 (1.95) | 59.26 (10.64) | 15.61 (1.81) | 2.34 (0.32) | 3.78 (0.77) | 0.78 (0.09) |
FC10w | 6.66* (1.98) | 47.79 (13.53) | 19.22 (2.85) | 3.25 (0.75) | 2.99 (0.69) | 0.46 (0.08) |
FCGN10w | 5.92* (0.63) | 53.99 (13.71) | 22.68 (2.79) | 4.46 (1.18) | 2.03 (0.32) | 0.96 (0.38) |
MC8w | 12.70 (0.91) | 45.09 (4.89) | 12.78 (1.68) | 2.81 (0.32) | 2.69 (0.19) | 0.71 (0.07) |
MC10w | 5.18* (0.96) | 65.45 (10.90) | 26.78 (3.24) | 6.45* (1.53) | 2.09 (0.26) | 1.05 (0.35) |
MCGN10w | 4.04* (0.59) | 79.54 (11.70) | 22.23 (1.86) | 6.94* (1.56) | 2.48 (0.36) | 0.77 (0.19) |
Group | Cytotoxicity (% cell viability) | NK (%) | ConA (%) | LPS (%) | PE | PI | GR |
---|---|---|---|---|---|---|---|
*, significant differences (p < 0.05) between the mouse control and the mice fed CGN under the same conditions, using Student’s t-test analysis. | |||||||
FC10w | 56.74 (6.58) | 45.16 (2.90) | 114.99 (2.60) | 107.18 (3.39) | 83.75 (1.00) | 576.12 (33.94) | 9.25 (2.44) |
FCGN10w | 7.46* (2.57) | 35.72* (1.65) | 104.70* (1.22) | 101.29 (2.68) | 76.62* (1.29) | 340.67* (43.88) | 1.94* (0.53) |
MC10w | 65.69 (6.59) | 45.14 (2.87) | 118.38 (2.84) | 108.21 (3.16) | 84.25 (0.84) | 579.14 (59.29) | 3.36‡ (0.69) |
MCGN10w | 17.46* (5.82) | 35.70* (3.92) | 94.67* (3.02) | 89.75* (6.11) | 78.86* (1.03) | 390.37* (26.27) | 1.01* (0.52) |
A scoping review on the gut effects of the food additive CGN35 and other recent reports36,37 state, as hallmark conclusions, the importance of addressing the interaction of the additive with the gut microbiome. Our results show that adverse effects, such as reduced animal weight and lowered immune functions (Tables 1 and S1†), were observed in spite of non-significant microbiota taxonomical changes associated with CGN intake (Table 2). The results show a significant effect of the housing time on the microbiota (Tables 1 and 2, Fig. 1), characterized by a decrease in the Shannon (microbial richness) and Simpson (microbial evenness) taxonomic indices, a lower relative abundance of Bacillota and an increase in bacterial groups belonging to the Bacteroidota phylum. Such a swift change has been observed in this type of mouse strain after weaning38 and it has been associated with the adaptation to changes in solid diets.39
Regarding the adverse effects of CGN observed in our study (Tables 1, 4 and S1†), an extensive body of evidence explains the damage as being related to CGN degradation to low molecular weight (average 20 to 30 kDa) compounds,25,27,30 which have demonstrated mainly inflammatory effects along with decreasing barrier function and/or increasing permeability.35 In previous studies,15 we have observed that the same CGN brand supplied to the mice, evaluated at values as high as 3 mg mL−1, did not have any impact either on Caco-2 cell viability or on the epithelial monolayer integrity; however, hydrolysed CGN (heated at 121 °C for 15 min at pH < 2) decreased cellular viability and increased epithelial permeability at an IC50 value of 0.1 mg mL−1. The results in Table 4, showing that the fecal content of mice fed CGN increased the cytotoxicity towards Caco-2, would indicate some degree of CGN hydrolysis through intestinal transit and/or degradation by the gut microbiota. Considering that the formation of fragments with Mw lower than 50 kDa from CGN, using an artificial stomach, resulted in about 3% hydrolysis,40 additional CGN degradation by the gut microbiota could trigger intestinal barrier damage. The increased abundance of ASVs assigned to Bacteroidota, in particular to the genus Bacteroides, in 10w mice (Fig. 1, Table 2) would provide the mouse microbiota with an increased potential utilization of complex carbohydrates, such as arabinogalactans, glucans, xylose, polygalactans and betagalactans, among others (Fig. 2). Actually, gut microbiotas with a marked abundance of Bacteroides have been described to be effective at utilizing galactans, including CGN.41–43
The cytotoxicity and permeabilizing effect of degraded CGN in the gut mucosal barrier could be associated with the physiological damage observed in the mice, such as delayed growth (Table 4). Body weight loss after intragastric administration of CGN has also been shown in BALB/c mice.44 In addition, in male and female mice, the ingestion of CGN caused lower values in relevant immune functions associated with health condition, such as natural killer antitumor activity, lymphoproliferative response to the mitogen ConA, and phagocytosis capacity (Tables 4 and S1†). These results agree with some previous studies in which immune suppressant effects of CGN in vivo have been observed.21 Considering that degraded CGN is used as an experimental inflammation model, similar to the dextran sulfate sodium (DSS) colitis model,45 the potential hydrolysis of CGN by the gut microbiota could have favored the damage caused by low-Mw CGN products to the intestinal barrier permeability.35 The sulfate groups from the polygalactan could facilitate disturbing the intestinal mucus layer by making it more permeable to gut microbiota that reach the epithelial cells and trigger an inflammatory reaction.46 Thus, a correlation between mouse fecal cytotoxicity and altered leukocyte function parameters, such as the proliferative capacity of lymphocytes stimulated by ConA and the macrophage phagocytic efficiency, was detected in the present study (Fig. S4†). In addition, taking into account that inflammation and oxidation are two processes that occur together,47 and that oxidative stress is the basis of deteriorated function of immune cells,48 the lower antioxidant activity observed in leukocytes from mice after CGN ingestion could explain their worse immune function.
In conclusion, the altered immunity and oxidative stress observed in young mice after the consumption of CGN, along with the cytotoxicity shown towards intestinal epithelial cells incubated with their fecal supernatants, may be associated with the gut microbiota’s capacity to hydrolyze the CGN, although non-significant bacterial taxonomic changes have been observed. The identification of microbiota species that hydrolyze sulfated polysaccharides is still limited, as is the knowledge of the long-term effects of current scenarios of increasing food-additive consumption, which is bound to have an impact on human health.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d4fo01418a |
This journal is © The Royal Society of Chemistry 2024 |