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Influence of consumption of the food additive carrageenan on the gut microbiota and the intestinal homeostasis of mice

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

Received 26th March 2024 , Accepted 22nd May 2024

First published on 23rd May 2024


Abstract

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.


Introduction

Food additives are substances intentionally added during the technological preparation of processed foods in order to improve their safety, taste, texture or appearance, among other things. Carrageenans (CGNs) are widely used due to convenient physicochemical properties, such as gelling, thickening and stabilizing properties, and protein reactivity.1 CGNs are linear sulfated polygalactans that, depending on their structural characteristics and sulfation patterns, are divided into several types.2 For example, kappa- (κ-), iota- (ι-), and lambda- (λ-)CGN have one, two, and three sulfate groups in the disaccharide repeating units, respectively.3 Particularly, κ-CGN is commonly used for industrial purposes in the production of dairy products, juice drinks, ice cream, sugar products, meat products, beer, etc., and has the EU additive code E407.4

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 (200[thin space (1/6-em)]000–800[thin space (1/6-em)]000 Da) and the low Mw of the products of hydrolysis of CGN, degraded CGN or polygeenan (10[thin space (1/6-em)]000–40[thin space (1/6-em)]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.

Materials and methods

Animals and experimental design

Young (8 weeks old) ICR-CD1 female (FC8w) and male (MC8w) mice were housed (five per cage and separated by sex) and maintained with ad libitum access to food (A04 diet, Panlab S.L., Barcelona, Spain) and tap water under light (12/12 h reversed light/dark cycle; lights off at 8[thin space (1/6-em)]:[thin space (1/6-em)]00 A.M.), and controlled temperature (22 ± 2 °C) and humidity (50–60%).

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.

Faecal analyses

Microbiota composition. Faecal material was collected individually from each mouse before and after the two weeks of treatment. About 200 mg were washed with 0.9% peptone water and centrifuged (15[thin space (1/6-em)]000g, 10 min), and the pellet used for genomic DNA purification. DNA was extracted using an E.Z.N.A. Stool DNA Kit (Omega Bio-tek) and quantified using a NanoDrop 1000 UV/VIS Spectrophotometer (Thermo Fisher). DNA samples were analyzed via amplicon-based metagenomic sequencing of the 16S rDNA V3–V4 region, performed by Novogen (Cambridge, UK) on an Illumina platform, to generate 250 bp paired-end reads. Bacterial taxonomy was assigned to the obtained ASVs (Amplicon Sequence Variants) by using the QIIME2 software. The absolute abundance of ASVs was normalized using a standard of the sequence number corresponding to the sample with the least sequences. Subsequent analyses of alpha diversity and beta diversity were all performed based on the normalized data. PICRUSt2 (V2.3.0) was used to predict the metagenomic functions according to 16S rRNA gene sequencing data based on Cluster of Orthologous Genes (COG), Enzyme Commission (EC), and Pathway (PWY) databases. The raw generated sequences were deposited in the Digital.CSIC database (https://doi.org/10.20350/digitalCSIC/16174).
Analyses of SCFAs and ammonium. Short-chain fatty acids (SCFAs) were analysed in the supernatant samples of the peptone-washed faeces, via HPLC as previously described.22 SCFAs were separated on a Rezex ROA organic acid column (Phenomenex) at 56 °C using a linear gradient of 5 mM sulphuric acid at 0.6 mL min−1. Quantification of SCFAs in the samples was achieved through calibration curves of succinic, lactic, acetic, propionic and butyric acids at concentrations between 0.5 and 100 mM. Ammonium content was determined using Nessler's reagent (Sigma-Aldrich), as described by Doo et al.23
Cytotoxicity of fecal content. Supernatants from the peptone-washed fecal material were used to evaluate Caco-2 cell viability as described earlier,24 by using the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide (MTT) assay. Caco-2 cells (1 × 104 per well) incubated for 7 days in 96-well adhesion plates were treated with the fecal supernatants for 24 h and then treated with 0.5 mg mL−1 MTT for 3 h at 37 °C. Cytotoxicity was calculated as the percentage of the viability of treated cells compared with that of the control cells and expressed as the mean of three independent experiments.

Analysis of immune function parameters

The immune analyses were carried out with peritoneal leukocytes that were obtained as previously described.25 The peritoneal suspensions were adjusted with Hanks’ solution (Sigma-Aldrich) to a specific concentration of macrophages, lymphocytes or total leukocytes, which were identified and quantified using Neubauer chambers (Blaubrand). Cellular viability (higher than 95 ± 1%) was checked using trypan blue (Sigma-Aldrich).

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.

Evaluation of oxidative stress parameters

The oxidative parameters were assayed with mouse peritoneal leukocytes adjusted to 106 cells per mL in Hanks’ solution. The glutathione content (reduced, GSH, and oxidized, GSSG) of sonicated leukocyte suspensions (106 mL−1) was assayed using o-phthalaldehyde at pH 8 and pH 12, respectively, as previously described.16 The protein content of the samples was determined following the BCA Protein Assay Kit protocol (Sigma-Aldrich). The results were expressed as nmol per mg protein. The GSSG/GSH ratio was calculated for each sample.

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.

Statistical analyses

Results were expressed as mean ± standard error of the mean (SEM) or median and interquartile range (IQR). One-way analysis of variance (ANOVA) and Tukey's multiple comparison tests (when samples were normally distributed) or Klustal–Wallis analysis were performed to determine differences between treatment groups, employing SPSS Statistics for Windows, version 29.0 (IBM Corporation). Student’s t-test (when samples were normally distributed) or Mann–Whitney U analysis was performed for comparison between controls and CGN-fed mice under the same conditions. The significance level of the statistical tests was set to p < 0.05. Pearson's correlation (r, *p < 0.05, **p < 0.01) was used to analyse the correlation between cytotoxicity and immune and oxidative functions. Heatmap plots were obtained applying the ClustVis webtool (https://biit.cs.ut.ee/clustvis/, accessed on 15 January 2024).27

Results

Housing and animal weight

During the experimental period (two weeks), the mice of the control groups (male and female) increased in weight with respect to the initial value (Table 1), in accordance with the normal pattern of weight gain of the ICR mice.28 The administration of CGN (540 mg kg−1 day−1) during the two weeks, however, limited weight gain in both female (F) and male (M) groups, resulting in a non-significant weight increase in the CGN-fed mice during the two weeks of treatment.
Table 1 Weight (g) and faecal microbiota alpha-diversity index (Shannon and Simpson) values (mean ± SEM) of the female (F) and male (M) mice at the start of the study (age 8 weeks) and after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w)
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)


Gut microbiota composition and metabolism

The microbiota composition was obtained from the ASV-based analysis of the 16S rRNA gene amplicon sequences obtained from the mouse faecal DNA. The results indicated a decrease in the estimated bacterial richness (Shannon index) of the microbiome and its evenness (Simpson index) during the 2-week experimental period, which was similar for female and male mice in both the control and the CGN groups (Table 1).

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).


image file: d4fo01418a-f1.tif
Fig. 1 Relative abundance bar chart of the top six most abundant phyla (A) and boxplots representing interquartile ranges and medians of the relative abundance of representative families (B) of the female (F) and male (M) mice at the start of the study (age 8 weeks) and after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w).

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.

Table 2 Median (IQR) values of genera representing at least 0.1% relative abundance in the faecal microbiota of the female (F) and male (M) mice at the start of the study (8w) and after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w)
  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.


image file: d4fo01418a-f2.tif
Fig. 2 Heatmap of the top thirteen most abundant clusters of orthologous genes (COGs) in the carbohydrate transport and metabolism category predicted by PICRUSt2 analysis from the 16S rRNA gene sequencing data of the faecal microbiota from the female (F) and male (M) mice at the start of the study (age 8 weeks) and after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w).

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.

Table 3 Short-chain fatty acid (SCFA) and ammonium values (mean ± SEM) of the female (F) and male (M) mice at the start of the study (age 8 weeks) and after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w)
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)


Cytotoxicity and physiological effects

In addition to intestinal microbiota changes associated with CGN intake, we studied possible physiological effects caused by CGN feeding during the two weeks of the experimental period. In previous studies, we observed that hydrolyzed CGN caused cytotoxicity towards Caco-2 cells at the IC50 value of 100 μg mL−1 (Bellanco et al., unpublished results). The results shown in Table 4 indicate a significant increase in toxicity of the supernatants from the peptone-washed fecal material of the mice from the CGN groups. The possible CGN-permeabilization effect in the gut was correlated with changes in some immune function parameters (Fig. S4), such as the proliferative capacity of lymphocytes stimulated by concanavalin A (Pearson 0.561***, p < 0.001) and the macrophage phagocytic efficiency (Pearson 0.515**, p < 0.01). Other parameters that significantly worsened during the CGN intake were the NK cell cytotoxicity, the macrophage phagocytic index and the GR activity (Table 4).
Table 4 Cytotoxicity (expressed as % cell viability) towards Caco-2 cells after 24 h incubation with peptone-washed fecal material and the immune functions (anti-tumor cytotoxic activity of natural killer (NK) cells, lymphoproliferative response to the mitogens concanavalin A (ConA) and lipopolysaccharide (LPS), and efficiency (PE) and index (PI) of phagocytosis) as well as the glutathione reductase (GR) activity. Values are expressed as mean and SEM of the female (F) and male (M) mice after two weeks of intake of carrageenan (CGN10w) or PBS in the controls (C10w)
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)


Discussion

Carrageenan (CGN) is one of the authorized food additives that encounter a substantial number of controversial opinions in the scientific literature. Favorable considerations are based on its worldwide approved use in foods by regulatory authorities,31 and the long-term consumption habit in Asia of macroalgaes and their commercial application for CGN extraction,32 which is based on its convenient technological properties as a gelling, thickening, and stabilizing agent.1 In addition, there are a number of in vitro studies that indicate potential health benefits of CGN, such as antioxidant, anticoagulant and antiviral activities, among others.5 On the other hand, CGN has been used in animal models to induce inflammation.33 Moreover, it has been demonstrated to contribute to earlier relapse in patients with ulcerative colitis in remission34 and to alter the gastrointestinal degradation of proteins, reducing protein and peptide bioaccessibility.8

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.

Author contributions

MDLF, MCMC and TR conceived and designed the experiments, acquired funding and supervised all experimental works. AB, JF and EDDC performed experiments. AB, JF, MDLF and TR carried out data analyses. AB, MDLF and TR drafted the manuscript. All authors have made critical revisions to the manuscript and read and approved the final manuscript.

Conflicts of interest

The authors declare no conflicts of interest.

Acknowledgements

This research is part of the grants from the Spanish State Research Agency PID2019-106071RB-I00, PID2022-136874OB-C31 and PID2022-136874OB-C32 (funded by MCIN/AEI/10.13039/501100011033). The authors are indebted to E.F. Sáez Martínez for technical support. We acknowledge the CSIC Open Access Publication Support (URICI).

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