Species sorting shapes the divergence of a traditional fermented dairy-derived bacterial community with repeatable functionality during propagation with alternative substrates
Author information
ShepherdNehanda1,2✉Email
AnnaY.Alekseeva2
Oscar
van
Mastrigt2
JustinChileshe1
BasJ.Zwaan2
EddyJ.Smid2
SijmenE.Schoustra2,3✉Email
1Department of Biomedical SciencesNational Health Research and Training Institute (Formerly Tropical Diseases Research Centre)NdolaZambia
2Laboratory of Genetics and Laboratory of Food MicrobiologyWageningen University and ResearchWageningenThe Netherlands
3Department of Food Science and NutritionThe University of ZambiaLusakaZambia
Shepherd Nehanda1,2*, Anna Y. Alekseeva2, Oscar van Mastrigt2, Justin Chileshe1, Bas J. Zwaan2. Eddy J. Smid2, and Sijmen E. Schoustra2,3*
1. National Health Research and Training Institute (Formerly Tropical Diseases Research Centre), Department of Biomedical Sciences, Ndola, Zambia.
2. Laboratory of Genetics and Laboratory of Food Microbiology, Wageningen University and Research, Wageningen, The Netherlands.
3. Department of Food Science and Nutrition, The University of Zambia, Lusaka, Zambia.
*Correspondence to Shepherd Nehanda - Email: nehandas@tdrc.org.zm or Sijmen E. Schoustra - Email: sijmen.schoustra@wur.nl
ABSTRACT
Species sorting underlies changes in microbial community composition under varying environments, yet predicting the species diversity and their functional outcomes when exposed to novel conditions remains challenging. We explored this using mabisi, a Zambian traditional fermented milk, by propagating a shared starting mabisi microbial community across five novel substrates - raw bovine milk (control), low-fat milk, full-cream milk, and the infant formulas F100 and S26 – under static conditions and fixed dilution for ~ 66 generations, at three rural farm sites. The microbial community composition was profiled through 16S rDNA sequencing, and community-level functioning through volatile organic compounds, pH, and consistency. We observed a substrate-driven divergence of microbial communities, with early-phase (~ 20 generations) communities enriched with Lactococcus, and transitioning to late-phase (~ 66 generations) communities enriched with Acetobacter, Lactiplantibacillus, Paucilactobacillus, Leuconostoc, Lacticaseibacillus, and Lactobacillus. This succession pattern remained consistent between sites. Despite community diversity shifts, community-level functionality remained largely repeatable. Our findings suggest that novel environments drive a species sorting process in natural microbial communities, and this process persists over time. Additionally, the maintenance of its community-level functionality despite community turnover points to underlying functional redundancy within diverse and successive microbial communities. Our study not only advances the understanding of how microbial community adapts to environmental changes but also provides a basis for harnessing the mabisi-derived microbial community for broad biotechnological applications, particularly supporting the feasibility and effectiveness of its use in an in-house formulated F100 infant formula for treating malnourished children in developing regions.
Key terms: adaptation, diversity, infant formula, lactic acid bacteria, natural microbial community, selection
A
A
INTRODUCTION
Under the conceptual frameworks of microbial community assembly (Vellend, 2010), species sorting is generally assumed to drive microbial community composition based on individual species' differential sensitivity traits to environmental selection (Blasche et al., 2021; Li & Ma, 2020; Nemergut et al., 2013), as opposed to a neutral process that assumes ecological equivalence (Sloan et al., 2006; Zhou et al., 2013). Species sorting is synonymous with the deterministic process, niche partitioning, and environmental filtering. Its role in governing the assemblage of microbial communities in natural habitats is critical for ecosystem functioning, ranging from organic matter decomposition in the soil (Maron et al., 2018); promoting health in the human gut (Rautmann & De La Serre, 2021; Selber-Hnatiw et al., 2017); to contributing beneficial properties in fermented foods (Smid & Lacroix, 2013). Yet, microbial communities are frequently faced with environmental changes in their natural habitats, which may consequently affect the prediction of their composition and functioning over time (Philippot et al., 2021). Under this topic, one of the questions is how species sorting sustains natural microbial communities and their functionality under novel environments in time and space.
Studies investigating associations between environmental variation and microbial community composition have gained traction. Recently, it was revealed that spatial variability plays a significant role in shaping microbial community diversity, primarily attributed to location-specific environmental factors, including micronutrient availability (Liao et al., 2016; Mandakovic et al., 2018; Zhang et al., 2020). Similar patterns have been observed in dairy ecosystems, where microbial community composition varies by location (Kochetkova et al., 2022; Moonga et al., 2020) and is linked to the location-specific environmental dynamics (Gobbetti et al., 2018; Quintana et al., 2020). Many of these studies, however, do not explicitly test the principle of the species sorting process, as they lack systematic tracking of a defined initial community (Johansen et al., 2019; Langenheder & Székely, 2011). Moreover, natural systems are generally highly dynamic, and it is difficult to separate short-term fluctuations (e.g., diurnal temperature changes) from long-term shifts, and later on discern the sequence and relative influence of these environmental changes across sites over time (Hillebrand & Kunze, 2020; Rodriguez-Ramos et al., 2021). These can potentially act as confounders, making it challenging to disentangle the specific mechanistic process of species sorting and to predict its role in sustaining microbial community diversity in natural habitats.
Furthermore, reconciling the species sorting process and microbial community functioning has remained inconclusive. For instance, species asynchrony was shown to be responsible for stabilizing community functions through the recruitment of alternative taxa to perform functions at different time scales (Wagg et al., 2021). Some studies, however, argue that changes in microbial diversity affect specific system functions (Chen et al., 2021; Peter et al., 2011). Additionally, other studies that have explored community assembly have either overlooked the linkage to functional outcomes (Dong et al., 2021) or restricted to the screening of genetic potential through transcriptomic (rRNA) analysis in artificially assembled communities (Blazewicz et al., 2013), which may not always be translated to functional metabolites in situ, i.e., in natural settings. With the advent of meta-omics (Ferrocino et al., 2023), it is now plausible to mechanistically complement species sorting processes with functional insights by associating the microbiome with metabolomic data. However, this approach remains challenging with complex field study models. Therefore, simpler and suitable study models are warranted to effectively test these processes and derive potential generalizable inferences.
In this study, we leverage mabisi, a traditional fermented milk beverage found in Zambia (Schoustra et al., 2013), to address how species sorting mechanisms govern a natural microbial community assembly and maintain their functionality upon exposure to novel environments in time and space. Mabisi microbial communities are self-assembled during the traditional fermentation, hence, they possess features representative of a natural community model system (Alekseeva et al., 2021; Blasche et al., 2017). These communities are dominated by beneficial bacterial guilds, including Lactococcus, Acetobacter, Leuconostoc, Lactiplantibacillus, Paucilactobacillus, and Lacticaseibacillus (Leale et al., 2023; Moonga et al., 2020), which underlie measurable functional parameters such as changes in pH, volatile organic compounds (VOC), and consistency during the culture processes (Groenenboom et al., 2022; Moonga et al., 2021). Thus, mabisi attracts usage as a model to study microbial community assembly, such as when communities from different origins were transferred into a shared but novel environment, and revealed patterns of coalescence and divergence (Groenenboom et al., 2022).
A
Under natural conditions at three rural farm sites in Zambia, we exposed a shared starting mabisi microbial community to five bovine-derived milk substrates. Among these, raw cow milk served as a control, given that it is the usual substrate for mabisi processing (Schoustra et al., 2013). Moreover, ultra-high temperature low-fat milk, ultra-high temperature full-cream milk, and the infant formulas F100 and S26 represented novel environments that varied in pH, pretreatment methods, nutritional properties, and purposes (Kunda et al., 2015; Nyirenda et al., 2009; Park et al., 2012). Each substrate was inoculated with a shared starting mabisi microbial community at a fixed dilution with three replicates, and repeatedly propagated over 10 cycles, categorized arbitrarily as early (1–3 cycles) and late (4–10 cycles) propagation phases (Fig. 1). Specifically, the bacterial community changes were analyzed by 16S rDNA sequencing and diversity (alpha and beta) metrics, while the community-level functionality was measured through monitoring volatile organic compounds, pH and consistency. This experimental setup enabled us to optimize the occurrence of the selection process in situ, that is, under natural field conditions. With this, we could simultaneously track how species sorting shaped the microbial community diversity and their functionality in time and space. We hypothesize that propagation within novel environments leads to a detectable species sorting process, revealing a substrate-driven divergence of bacterial community composition and functionality over time across sites. Alternatively, if species sorting is weaker, the resultant microbial community diversity and functional patterns would exhibit random radiation with no discernible differences between substrates. Our study informs mechanistic fundamental ecological insights on the microbial community responses to environmental changes, and also provides a basis for predicting how a natural mabisi microbial community can be diversified for biotechnological applications to enhance novel fermented food ingredients.
[Please insert Fig. 1 here]
Figure 1 The field experimental setup. Mabisi microbial communities from a common source (starting community) were inoculated (1:10 dilution ) into five milk substrates: raw cow milk (RCM), F100 infant formula (F100), S26 infant formula (S26), ultra-high temperature low-fat milk (LFM) and ultra-high temperature full cream milk (FCM), with 3 replicates per substrate at each of three farm sites (site 1, site 2 and site 3). Propagation was conducted by serially transferring 1:10 of cultures into fresh substrates every 48 h for 10 cycles
METHODS
Propagation experiment in the field
A
Between November to December 2020, a field experiment was set up at three nearby farms in the Copperbelt Province, Zambia (Latitude − 12.98330S, longitude 28.63330E). The sites were located within a radius of approximately two Km for logistical convenience. Each site had unique in-house mabisi processing conditions; site 1 involved incubation in an outdoor and elevated space; site 2 involved incubation on a wooden platform in an enclosure; and site 3 involved incubation on the floor, but also in an enclosure. The study utilized five substrates: raw cow milk (RCM) serving as a control (Schoustra et al., 2013), ultra-high temperature low-fat milk (LFM), ultra-high temperature full-cream milk (FCM), F100 infant formula (F100), and S26 infant formula (S26), representing novel environments differing in pretreatment and nutritional parameters (Table 1) (Kunda et al., 2015; Nyirenda et al., 2009; Park et al., 2012). The RCM was sourced and homogenized from three local dairy farmers. The F100 was prepared according to a World Health Organization (WHO) guided in-house protocol (World Health Organisation, 1999), while S26, LFM, and FCM were sourced ready for use from a local supermarket. The milk substrates were inoculated with a pooled mabisi sample, representing a source community, in the ratio of 1:10, in a total volume of 1 L. There were three replicates for each milk substrate at each farm site. The preparation was left to ferment for a complete cycle of 48 hrs. Analogous to an evolution experiment, a portion of the fermented products was serially transferred into a fresh set of its respective substrates in the same ratio over time: designated arbitrarily as early propagation phase (1st – 3rd cycle) and late propagation phase (4th – 10th cycle) for a total of 10 cycles (~ 66 bacterial generations). Culture products were sampled in 50 mL clean Falcon tubes at the end of each cycle, placed in a cooler box with ice, and transported to the central laboratory at the National Health Research and Training Institute (NHRTI) (formerly the Tropical Diseases Research Centre) for further analysis and storage at -20°C. A summary of the experimental setup is depicted above (Fig. 1).
Table 1
Summary of nutritional parameters for substrates utilized in this study
Substrate
Nutritional parameter (per 100g edible portion)
Reference
Energy (Kcal)
Protein (g)
Fat (g)
Carbohydrate (g)
Ca2+ (mg)
Fe (mg)
Zn (mg)
Vitamins
  
A (µg)
B1 (mg)
B2 (µg)
B3 (mg)
C (mg)
 
F100
100
6
12.2
4.2
140.9
1.0
5.0
-
0.2
0.7
2.4
23.4
(Park et al., 2012)
 
S26
570
12.5
30
-
370
10.6
-
661
-
0.92
8.3
48
(Nyirenda et al., 2009)
 
RCM
64
3.3
3.6
4.7
120
0.1
-
45
0.04
0.15
0.1
-
(Nyirenda et al., 2009)
 
LFM
62.4
-
3.2
-
119
-
-
-
-
-
-
-
Package labels*
 
FCM
37.44
-
0.5
-
123
-
-
-
-
-
-
-
Package labels*
 
Table S1
Alpha diversity of mabisi microbial communities assessed using Chao1 (richness) and Shannon (richness and evenness) indices. The pairwise Wilcoxon rank-sum test was applied to evaluate differences across substrate treatments, propagation phases, and farm sites, with p-values adjusted using the Benjamin-Hochberg method
Variable
Group 1
Group 2
Chao1
Adj. p-value
Shannon
Adj. p-value
Substrate variation
FCM
F100
0.198
0.001 *
 
LFM
F100
0.136
0.080
 
O
F100
0.087
0.006*
 
RCM
F100
0.767
0.412
 
S26
F100
0.541
0.062
 
LFM
FCM
0.767
0.209
 
O
FCM
0.087
0.001*
 
RCM
FCM
0.297
0.019*
 
S26
FCM
0.108
< 0.001*
 
O
LFM
0.087
0.001*
 
RCM
LFM
0.206
0.352
 
S26
LFM
0.097
0.001*
 
RCM
O
0.087
0.002*
 
S26
O
0.136
0.312
 
S26
RCM
0.457
0.004*
Propagation phase
Late phase
Early phase
0.068
0.072
 
O
Early phase
0.007*
0.014*
 
O
Late phase
0.068
0.043*
Farm site
Farm 2
Farm 1
0.978
0.994
 
Farm 3
Farm 1
0.243
0.375
 
O
Farm 1
0.056
0.039*
 
Farm 3
Farm 2
0.243
0.375
 
O
Farm 2
0.066
0.037*
 
O
Farm 3
0.056
0.037*
Note:
• ‘*’ represents statistically significant, while no esthetics represent a non-statistically significant result.
• Substrates are represented by - RCM: raw cow milk, F100: F100 infant formula, S26: S26 infant formula, LFM: ultra-high temperature low-fat milk, and FCM: ultra-high temperature full-cream milk, whereas O: refers to the starting mabisi microbial community for all variables.
Table S2
Dissimilarity in microbial community composition across sample groups based on substrate variation, propagation phases and farm site differences. The analysis was conducted using a permutational multivariate analysis of variance (ANOSIM), with free permutation (n = 999)
Parameter
Anosim statistic R
P value
Substrate variation
0.1635
0.001*
Propagation phase
0.4008
0.001*
Farm site
0.02767
0.014*
Note: Significance codes: ‘*’ represents significant, and no asterisk represents a non-significant result.
Table S3
Differential abundance of microbial communities across substrates, propagation phases and sites. The analysis was conducted by linear discriminant effect size (LEfSe) applying an LDA cut-off of 3.
Variable group
Marker
Feature
Enriched group
Linear discriminant analysis score
p-value
Adjusted p-value
Substrate variation
marker1
Citrobacter
F100
3.343751
1.046004e-03*
1.046004e-03*
 
marker2
Staphylococcus
F100
3.025378
8.673021e-07*
8.673021e-07*
 
marker3
Lactococcus
FCM
4.998115
6.150244e-03*
6.150244e-03*
 
marker4
Acetobacter
LFM
4.650600
1.516754e-13*
1.516754e-13*
 
marker5
Klebsiella
O
4.640921
1.176485e-12*
1.176485e-12*
 
marker6
Enterobacter
O
4.149835
1.497987e-09*
1.497987e-09*
 
marker7
Aeromonas
O
4.137861
4.399796e-03*
4.399796e-03*
 
marker8
Butyrivibrio
O
3.337407
2.919917e-02*
2.919917e-02*
 
marker9
Christensenellaceae_R7 group
O
3.288024
3.639161e-02*
3.639161e-02*
 
marker10
Acinetobacter
RCM
3.615725
6.939914e-05*
6.939914e-05*
 
marker11
Lactiplantibacillus
S26
4.344082
4.328440e-03*
4.328440e-03*
 
marker12
Leuconostoc
S26
4.322887
1.113412e-09*
1.113412e-09*
Propagation phase
marker1
Lactococcus
early_phase
4.928977
7.548243e-13*
7.548243e-13*
 
marker2
Enterococcus
early_phase
3.926898
1.739450e-26*
1.739450e-26*
 
marker3
Acinetobacter
early_phase
3.729863
6.362928e-15*
6.362928e-15*
 
marker4
Citrobacter
early_phase
3.492008
2.990196e-12*
2.990196e-12*
 
marker5
Macrococcus
early_phase
3.449128
2.609972e-22*
2.609972e-22*
 
marker6
Staphylococcus
early_phase
3.156242
8.856940e-05*
8.856940e-05*
 
marker7
Acetobacter
late_phase
4.541038
2.080057e-04*
2.080057e-04*
 
marker8
Lactiplantibacillus
late_phase
4.359025
3.700641e-20*
3.700641e-20*
 
marker9
Paucilactobacillus
late_phase
4.300808
3.652611e-26*
3.652611e-26*
 
marker10
Leuconostoc
late_phase
4.204485
3.337560e-02*
3.337560e-02*
 
marker11
Lacticaseibacillus
late_phase
4.159312
6.361086e-20*
6.361086e-20*
 
marker12
Clostridium
late_phase
3.730698
1.010663e-27*
1.010663e-27*
 
marker13
Lactobacillus
late_phase
3.674086
2.534239e-16*
2.534239e-16*
 
marker14
Acetobacterium
late_phase
3.230790
5.825901e-09*
5.825901e-09*
 
marker15
Marinobacter
late_phase
3.200596
3.837809e-07*
3.837809e-07*
 
marker16
Martelella
late_phase
3.104545
1.460685e-06*
1.460685e-06*
 
marker17
Turicibacter
late_phase
3.022426
1.213163e-08*
1.213163e-08*
 
marker18
Klebsiella
O
4.798854
3.326543e-13*
3.326543e-13*
 
marker19
Aeromonas
O
4.474495
4.066792e-03*
4.066792e-03*
 
marker20
Enterobacter
O
4.293117
9.222979e-16*
9.222979e-16*
 
marker21
Butyrivibrio
O
3.590815
2.606283e-10*
2.606283e-10*
 
marker22
Christensenellaceae R-7 group
O
3.561722
2.048142e-17*
2.048142e-17*
 
marker23
Ralstonia
O
3.281826
8.958810e-10*
8.958810e-10*
 
marker24
Lachnospiraceae UCG-008
O
3.235014
2.367676e-10*
2.367676e-10*
 
marker25
Desulfobulbus
O
3.193606
1.553939e-14*
1.553939e-14*
 
marker26
Eubacterium sulci group
O
3.114361
4.033568e-10*
4.033568e-10*
 
marker27
Lachnospiraceae NK4A136 group
O
3.085041
2.656831e-06*
2.656831e-06*
 
marker28
Lachnospiraceae
O
3.084323
7.195861e-11*
7.195861e-11*
 
marker29
Enterobacteriaceae
O
3.034241
1.512706e-05*
1.512706e-05*
 
marker30
Bacteroides
O
3.032954
1.159367e-08*
1.159367e-08*
 
marker31
Succiniclasticum
O
3.023009
3.879298e-10*
3.879298e-10*
Farm site
marker1
Acinetobacter
farm_1
3.594774
1.411522e-02*
1.411522e-02*
 
marker2
Klebsiella
O
4.665998
7.338709e-03*
7.338709e-03*
 
marker3
Aeromonas
O
4.358014
6.706068e-03*
6.706068e-03*
 
marker4
Enterobacter
O
4.156926
5.615375e-03*
5.615375e-03*
 
marker5
Butyrivibrio
O
3.450271
3.555629e-06*
3.555629e-06*
 
marker6
Christensenellaceae R-7 group
O
3.446018
9.215090e-03*
9.215090e-03*
 
marker7
Ralstonia
O
3.237125
6.966525e-03*
6.966525e-03*
 
marker8
Lachnospiraceae UCG-008
O
3.131719
1.479283e-06*
1.479283e-06*
 
marker9
Eubacterium sulci group
O
3.050074
2.686999e-06*
2.686999e-06*
 
marker10
Desulfobulbus
O
3.049411
6.426137e-04*
6.426137e-04*
 
marker11
Lachnospiraceae
O
3.000355
1.155345e-03*
1.155345e-03*
Note: Differentially enriched substrate groups are represented by RCM: raw cow milk, F100: F100 infant formula, S26: S26 infant formula, LFM: ultra-high temperature low-fat milk, and FCM: ultra-high temperature full-cream milk. Differentially enriched propagation phase groups are represented by O: starting mabisi microbial community, early_phase: early propagation phase, and late_phase: late propagation phase. Differentially enriched Farm site groups are represented by farm_1: farm site 1 and O: stating mabisi microbial community. ‘*’ represents statistically significant results; p < 0.05.
Table S4
The profile of volatile organic compounds (VOC) before and after repeated propagation of mabisi microbial community in varied milk substrates over time
 
Esters
Alcohols
Carboxylic acids
Ketones
Aldehydes
Before propagation
Ethyl acetate
Ethanol
Nonanoic acid
2-Heptanone
Hexanal
 
Butanoic acid, ethy ester
1-Butanol, 3-methyl-
Hexanoic acid
Acetone
Heptanal
 
Hexanoic acid, ethyl ester
1-Pentanol
Butanoic acid
1-Octen-3-one
Nonanal
 
Decanoic acid, ethyl ester
 
Octanoic acid
2-Nonanone
Benzaldehyde
 
Hexanoic acid, 3-hydroxy-, ethyl ester
   
2,4-Nonadienal
 
Ethyl 9-decenoate
   
Pentanal
 
1-Butanol, 3-methyl-, acetate
   
Octanal
After propagation
Ethy acetate
Ethanol
Acetic acid
2-Heptanone
Hexanal
 
Butanoic acid, ethy ester
1-Butanol, 3-methyl-
Hexanoic acid
2-Butanone, 3-hydroxy-
 
 
1-Butanol, 3-methyl-, acetate
Pentanol, 2,3-dimethyl-/1-Heptanol, 6-methyl-
Octanoic acid
2-Nonanone
 
 
Hexanoic acid, ethyl ester
Phenylethyl alcohol
   
 
Butanoic acid, 3-methylbutyl ester
    
 
Octanoic acid, ethyl ester
    
 
Decanoic acid, ethyl ester
    
Table S5
Variation in volatile organic compounds following the repeated propagation of mabisi in varied substrates at different farm sites over time. The analysis was conducted by a permutational multivariate analysis of variance – ADONIS through Bray-Curtis distance metrics, with a free permutation (n = 999). The p-values for multiple testing were corrected by the Benjamin Hochberg method.
Parameter
Df
SumOfSqs
R2
F
p-value
p- value
adjusted
Substrate variation
5
1.7750
0.62665
55.725
0.001*
-
Residual
166
1.0575
0.37335
   
Total
171
2.8325
1.00000
   
Pairwise analysis:
      
Substrate group 1
Substrate group 2
      
Starter
RCM
1
0.03009611
0.07865297
2.731756
0.029*
0.435
Starter
F100
1
0.06507900
0.28617819
13.230025
0.029*
0.435
Starter
S26
1
0.04450728
0.21398061
9.255931
0.025*
0.405
Starter
LFM
1
0.03270530
0.15741160
6.165030
0.023*
0.375
Starter
FCM
1
0.02394310
0.10499712
3.988705
0.029*
0.345
RCM
F100
1
0.10972165
0.17566761
13.851688
0.001*
0.015*
RCM
S26
1
0.09347474
0.15335987
11.955199
0.001*
0.015*
RCM
LFM
1
0.47015505
0.47120715
57.921482
0.001*
0.015*
RCM
FCM
1
0.47550045
0.46069321
56.379323
0.001*
0.015*
F100
S26
1
0.12179263
0.27209518
25.045001
0.001*
0.015*
F100
LFM
1
0.58452859
0.63403336
114.344305
0.001*
0.015*
F100
FCM
1
0.73197814
0.66640457
133.842081
0.001*
0.015*
S26
LFM
1
0.85556142
0.71648161
169.316241
0.001*
0.015*
S26
FCM
1
0.89018489
0.70775021
164.677668
0.001*
0.015*
LFM
FCM
1
0.01223147
0.03125150
2.161398
0.118
1.000
Propagation phase
2
0.32002
0.11298
10.763
0.001*
-
Residual
169
2.51251
0.88702
   
Total
171
2.83253
1.00000
   
Pairwise analysis:
      
Propagation group 1
Propagation group 2
      
Starter
Early phase
1
0.02564651
0.01687570
1.476222
0.171
0.513
Starter
Late phase
1
0.03762413
0.03562723
3.066304
0.027*
0.081
Early phase
Late phase
1
0.28998848
0.10347499
19.505617
0.001*
0.003*
Farm site
3
0.06822
0.02408
1.382
0.212
-
Residual
168
2.76431
0.97592
   
Total
171
2.83253
1.00000
   
Note:
• ‘*’ represents statistical significance, and no esthetics represent a non-statistically significant result.
• Substrate types include raw cow milk (RCM), F100 infant formula (F100), S26 infant formula (S26), ultra-high temperature low-fat milk (LFM), and ultra-high temperature full-cream milk (FCM), while ‘starter’ represents the starting mabisi microbial community for all variables.
Table S6
Assessment of pH variation following the propagation of the mabisi microbial community across varied substrate types. The statistical analysis was performed using the Kruskal-Wallis test, followed by Dunn’s pairwise comparisons, with p-values adjusted for multiple testing using the Benjamin-Hochberg method
Substrate variation
Chi-squired
Degree of freedom
p-value
 
Test: Kruskal-Wallis rank sum
220.02
4
1.854051e-46
 
Test: pairwise comparison (Dunn test)
Substrate group 1
Substrate group 2
Z-values
Adjusted p-value
 
F100
FCM
1.330
0.115
 
F100
LFM
1.722
0.061
 
FCM
LFM
0.393
0.347
 
F100
RCM
-1.023
0.170
 
FCM
RCM
-2.352
0.016*
 
LFM
RCM
-2.745
0.006*
 
F100
S26
11.978
< 0.001*
 
FCM
S26
10.648
< 0.001*
 
LFM
S26
10.256
< 0.001*
 
RCM
S26
13.001
< 0.001*
Note:
• ‘*’ represents statistical significance, and no esthetics represent a non-statistically significant result.
• Substrate types include raw cow milk (RCM), F100 infant formula (F100), S26 infant formula (S26), ultra-high temperature low-fat milk (LFM), and ultra-high temperature full-cream milk (FCM).
Table S7
Assessment of pH variation by propagation phase following repeated transfer of mabisi microbial communities in varied substrates over time. The statistical analysis was conducted using the Wilcoxon rank sum test
Propagation phase
W statistic
p-value
Test: Wilcoxon rank sum test
15774
1.397e-05*
Table S8
Assessment of pH by farm site following the repeated propagation of mabisi microbial community in varied substrates over time. The statistical analysis was performed using the Kruskal-Wallis test, followed by Dunn’s pairwise comparison, with p-values adjusted for multiple testing using the Benjamin-Hochberg method
Farm site
Chi-squared
Degree of freedom
P - value
 
Kruskal-Wallis rank sum
23.68994
2
7.174545e-06*
 
pairwise comparison (Dunn test)
Farm group 1
Farm group 2
Z-values
Adjusted
p-value
 
Farm 1
Farm 2
4.22
< 0.001*
 
Farm 1
Farm 3
0.01
0.496
 
Farm 2
Farm 3
-4.21
< 0.001*
Table S9
Analysis of consistency variation in samples following the repeated propagation of mabisi microbial communities in varied substrates at different farm sites over time. The statistical analysis was performed using the Kruskal-Wallis test (or Wilcoxon rank sum test when appropriate), followed by Dunn’s pairwise comparison, with p-values adjusted for multiple testing using the Benjamin-Hochberg method
Substrate variation
Chi-Square
Degrees of freedom
p-value
 
Test: Kruskal-Wallis rank sum
137.51
4
9.64372e-29
 
Test: Pairwise comparison (Dunn’s test)
Substrate group 1
Substrate group 2
Z-value
Adjusted
p-value
 
F100
FCM
5.645
< 0.001*
 
F100
LFM
0.278
0.3905
 
FCM
LFM
-5.367
< 0.001*
 
F100
RCM
-3.799
< 0.001*
 
FCM
RCM
-9.444
< 0.001*
 
LFM
RCM
-4.077
< 0.001*
 
F100
S26
-4.890
< 0.001*
 
FCM
S26
-10.535
< 0.001*
 
LFM
S26
-5.168
< 0.001*
 
RCM
S26
-1.091
0.1529
Propagation phase
W statistic
 
p-value
 
Test: Wilcoxon rank sum test
20748
 
0.6685
 
Farm site
Chi squire test
Degree of freedom
p-value
 
Test: Kruskal Wallis rank sum
0.65527
2
0.7206
 
Note:
• ‘*’ represents statistical significance, and no esthetics represent a non-statistically significant result.
• Substrate types include raw cow milk (RCM), F100 infant formula (F100), S26 infant formula (S26), ultra-high temperature low-fat milk (LFM), and ultra-high temperature full-cream milk (FCM).
[Please insert Table 1 here]
Composition and diversity of microbial communities
DNA extraction
For bacterial community profiling, mabisi samples from the 1st, 3rd, 6th, and 10th cycles of fermentation were selected. The DNA extraction was performed according to the previously described protocol (Schoustra et al., 2013), with minor modifications. Briefly, 1 mL mabisi sample was centrifuged in a 2 mL screw capped tube at 12,000 rpm for 2 min. The pellets were resuspended in a cell digestion solution containing 64 µl of a 0.5 M EDTA, 160 µl nuclei lysis reagent (Promega), 5 µl RNase (10 mg/mL), 120 µl of lysozyme (10 mg/mL), and 40 µl pronase E (20 mg/mL) reagents. The mixture was incubated automated heating block for 60 min at 37°C while shaking at 350 rpm. The tubes were subjected to bead beating with 2 scoops of sand-sized beads (Sigma, Germany) following an in-house Lactoccocus lysis protocol, while cooling on ice in between. After, 400 µl of ice-cold 0.5 M ammonium acetate (Sigma Aldrich) was added, mixed, and incubated for 15 min at room temperature. The tubes were centrifuged at 13,000 rpm for 4 min. Later, 700 µl of the supernatant was transferred into a sterile 1.5 mL capped cryovial, and an equal volume of molecular grade phenol pH 8.0 (Sigma Aldrich) was added. The tubes were spun at 12,000 rpm for 6 min, and 350 µl of the supernatant was transferred into a new 1.5 mL cryovial tube. An equal volume of chloroform (Sigma Aldrich) was added and centrifuged at 12000 rpm for 2 min to remove the phenol. Thereafter, 300 µl of the supernatant was transferred into a new 1.5 mL cryovial tube to which 400 µl of isopropyl alcohol (Sigma Aldrich) was added. The tubes were placed in a -20°C freezer overnight to precipitate the DNA. After, the tubes were centrifuged for 15 min at 13,000 rpm at 4°C and the DNA pellets were washed with 1ml ice-cold 70% ethanol by carefully inverting the tubes 10 times, followed by centrifugation at 12,000 rpm at 4°C for 10 min. The wash was repeated. The supernatant was carefully decanted, and the tubes were left to dry for 5 min the heating block at 37°C. After, the DNA was eluted by adding 20 µl of low EDTA elution buffer (10 mM Tris, bring to pH 8.0 with HCL; 1 mM EDTA) (Sigma Aldrich). A NanoDrop™ ND-2000 and Qubit TM 4 fluorometer (Thermal Fisher Scientific, UK) was used to check for the DNA quantity and quality and stored at -20°C until further needed.
16S rDNA sequencing
A
To profile the bacterial community structure and their temporal dynmics following the experimental treatments described earlier, the extracted DNA samples were sent for 16S rDNA sequencing to Novogene, United Kingdom. Polymerase chain reaction (PCR) was used for library preparation using 341F CCTAYGGGRBGCASCAG and 806R GGACTACNNGGGTATCTAAT universal primers targeting the 16S rDNA V3-V4 region, according to the previously described protocol (Schoustra et al., 2013), with modifications. Briefly, the PCR products were purified, end-repaired, A-tailed and ligated with Illumina adapters, and sequenced on the NovaSeq PE250 platform to generate 250 bp paired end raw reads. The barcode and primer sequences were truncated and FLASH (v 1.2.11) applied to merge the reads. Then, the reads underwent filtering, denoising, removal of chimera, and generation of amplicon sequence variants (ASV) with DADA2 R package along with annotation using a publicly available Silver database: silva_nr99_v138.2_toGenus_trainset.fa.gz (Wambua, 2025). Then, the ASVs were normalized by rarefying with random repeated sampling of samples to a minimum sequence reads of 19,534 without replacement, nonbacterial taxa excluded, and a cut-off relative abundance of 0.25% applied in at least each sample to exclude singleton or spurious taxa before downstream analysis (Reitmeier et al., 2021), with R (version 4.5.0) and phyloseq package (version 1.52.0).
Microbial community-level functionality
Volatile organic compounds
Volatile organic compounds (VOC) were also used as a proxy measure for the metabolic activity following propagation of mabisi microbial communities in varied milk substrates. The VOC were analyzed by Headspace-Solid Phase Microextraction Gas Chromatography-Mass Spectrometry (HS-SPME, GC-MS), Trace 1300 Gas Chromatograph (Thermo Fisher), TriPlus RSH autosampler (Thermo Fisher) and an ISQ QD mass spectrometer (Thermo Fisher) using an inhouse protocol, as previously described (Moonga et al., 2021). Briefly, 1mL of mabisi sample was injected into GC-MS labeled vials with caps fastened, and placed on the GC-MS platform to incubate at 60°C for 20 min. The VOCs were allowed to vaporize and adsorb on the SPME fiber (Car/DVB/PDMS/Supelco) at 60°C for 20 min. Next, the extracted VOCs were desorbed for 2 min onto a Stabilwax ®-DA column (30 m length, 0.25 mm ID, 0.5 µm df, Restek), PTV split-less mode at 250°C for 5 minutes with helium gas as carrier at 1.5 ml/min. The GC oven was set at 40°C for 2 min, raised to 240°C with a slope of 10°C/min, and kept at 240°C for 5 min. Mass spectra data were collected over a range of m/z 33–250 in full scan mode with 3.0030 scans/sec. The obtained data were analyzed by Chromeleon ® 7.2 software (Thermo Fisher) using the ICIS algorithm and the NIST main library for signal peak integration and compound hit annotation. The RSI match factor of > 750 was applied. The results were exported to Excel files for statistical analysis. Nine samples, spanning substrate type, propagation phases, and sites, showed no detectable values for all the tested VOCs and were therefore considered technical failures and excluded from downstream analysis.
pH
The fermentation process was monitored by recording changes in pH at the initial time point, after 24 hrs and 48 hrs, respectively, using a digital pH meter (Jenway, UK). The pH probe was disinfected with 70% ethanol and rinsed in sterile water before and in-between measurements of each sample.
Consistency
At the end of each fermentation cycle, consistency was measured by recording changes in viscosity of the samples using an Adam’s consistometer, according to the previously described protocol (Moonga et al., 2021). Briefly, fermented samples were decanted into a 17 mL capacity Adam’s consistometer cylinder placed on a graduated platform. The cylinder was lifted to allow the test material to spread freely for 30–60 sec. The degree of spread was recorded in centimeters following pre-marked readings on the platform.
Statistical analysis
The R statistical software (version 4.5.0) was used for all data analysis. The microbiome data were visualized by box plots, histographs, and non-metric multidimensional scaling plots. Furthermore, alpha (Chao1 and Shannon) and beta diversity metrics were applied with Wilcoxon rank-sum and PERMANOVA (ANOSIM) tests, corrected by the Benjamin-Hochberg method, to determine how microbial community diversity varied by study parameters. Species differential analysis was further explored through a linear discriminant effective size (LEfSe) analysis using the microbiomeMarker package (version 1.13.2).
The VOC data was plotted with heatmaps and principal component analysis (PCA) for visualization and analyzed by multivariate analysis (ADONIS) with default free permutation of 999 after normalization using a log transformation and median scaling by compound (column). The pH and consistency were summarized by median, lower and upper quartiles, and visualized by violin plots. Kruskal-Wallis and Dunn tests, with the Benjamin-Hochberg adjusted method, were applied whenever appropriate to analyze the statistical differences between experimental parameters. The significance test was set at 0.05 for all analyses.
RESULTS
Composition and diversity of microbial communities
A
A total of 4322 bacterial ASVs were obtained. At the phylum level of classification, these taxa were predominantly represented by the Bacillota, and this pattern was consistent with the starting mabisi microbial community (Figure S1). However, at the genus level, and specifically focusing on key lactic acid bacteria (LAB) and acetic acid (AAB) community members known for their important role in dairy ecosystems, the members, including Lactococcus, Acetobacter, Leuconostoc, Lactiplantibacillus, Paucilactobacillus, and Lacticaseibacillus were dominant in all substrate treatments at all farm sites over time (Fig. 2; Fig. S2).
[Please insert Fig. 2 here]
Figure 2 Distribution of propagated mabisi microbial community in different milk substrates over time. The y-axis represents the relative abundance (%) of each taxon in each sample, while the x-axis shows sample identities (Sample ID), faceted by propagation phases: starting mabisi microbial community (O), early phase (early_phase), and late phase (late_phase). Substrates are represented by raw cow milk (RCM), F100 infant formula (F100), S26 infant formula (S26), ultra-high temperature low-fat milk (LFM), and ultra-high temperature full-cream milk (FCM). The legend lists the most abundant genera; Acetobacter (dark teal), Clostridium (brownish orange), Enterobacter (warm terracotta), Enterococcus (soft lavender purple), Klebsiella (magenta), Lacticaseibacillus (mutated brick red), Lactiplantibacillus (bright olive green), Lactococcus (golden yellow), Leuconostoc (dark mustard yellow), Paucilactobacillus (earthly brown), and unassigned - referring to ASVs that could not be annotated in the silva database (medium gray)
Alpha and beta diversity analysis of microbial communities
A
To gain further insights into whether propagation of a shared starting mabisi microbial communities in varied substrates exerted diversity changes in the microbial community composition at different farm sites over time, alpha and beta diversity analysis was applied. The alpha diversity was analyzed by Chao1 (richness) and Shannon (richness and evenness) indices, with raw cow milk (RCM) used as a reference (the usual substrate for mabisi microbial community). Relative to the RCM, all substrate treatments did not show significant differences in the resultant community richness (Fig. 3; Table S1) or across sites (Fig. S3; Table S1). Also, the richness did not differ between the early and late propagation phases (Fig. 3; Table S1). However, both the richness and evenness of the propagated microbial community from FCM and S26-based substrate treatments increased significantly (p < 0.05), but not in the F100 and LFM-based treatments (p > 0.05) (Fig. 3; Table S1) relative to RCM. Between the early and late propagation phases or sites, the richness and evenness did not differ (p > 0.05) (Fig. S3; Table S1). Overall, this suggests that substrate variation constituted niche division, shaping differences in the community alpha diversity, while propagation phases or site differences did not.
A
To assess the dissimilarity in the community composition following the repeated propagation of mabisi microbial communities across substrates and sites over time, a non-metric multidimensional scaling (NMDS) with permutation of multivariate analysis (PERMANOVA) was conducted. The microbial community significantly differed in its composition mediated by the substrate variation (ANOSIM: R = 0.16, p < 0.05), propagation phases (ANOSIM: R = 0.40, p < 0.05), and site differences (ANOSIM: R = 0.03, p < 0.05) (Fig. 4, Table S2).
[Please insert Fig. 3 here]
Figure 3 Alpha diversity of mabisi microbial community by substrate treatment over time. Chao1 (richness) and Shannon (incorporating both richness and evenness) diversity metrics were applied to assess microbial community alpha diversity following propagation of a shared starting mabisi microbial community in varied milk substrates. The y-axis represents the diversity indices (Chao1 and Shannon), while the x-axis represents propagation phases: starting mabisi microbial community (O), early phase (early_phase), and late phase (late_phase). Box plots display the median, interquartile range, whiskers, and outliers. The legend indicates the substrate treatment: F100: F100 infant formula (greenish-blue), FCM: ultra-high temperature full-cream milk (redish-orange), LFM: ultra-high temperature low-fat milk (bluish-purple), O: starting mabisi microbial community (pinkish-purple), RCM: raw cow milk (yellow-green), and S26: S26 infant formula (mustard yellow)
[Please insert Fig. 4 here]
Figure 4 Dissimilarity in microbial communities by non-metric multidimensional scaling (NMDS). The NMDS was applied to show the shifts in microbial community diversity following the propagation of mabisi microbiota through varied milk substrates over time. Substrates are distinguished by colors - F100: F100 infant formula (teal), FCM: ultra-high temperature full-cream milk (orange), LFM: ultra-high temperature low-fat milk (purple), O: starting mabisi microbial community (magenta), RCM: raw cow milk (green), S26: S26 infant formula (yellow). Propagation phases are indicated by shape – early_phase: early phase (filled circle), late_phase: late phase (filled triangle point up), and O: starting mabisi microbial community (filled square)
Linear discriminant effect size (LEfSe) analysis of differential marker species
A
A
Further analysis by linear discriminant effect size (LEfSe), focusing on LAB and AAB that are known for their key roles in dairy ecosystems, revealed that there were significant differences in the relative enrichment of the mabisi microbial community between substrate treatment and propagation phases. Notably, LDA analysis showed that members of the Lactococcus (LDA = 4.9, p < 0.05 ) were significantly enriched in FCM, Acetobacter (LDA = 4.7, p < 0.05) were significantly enriched in LFM, while Lactiplantibacillus and Leuconostoc (LDA = 4.3, p < 0.05) were significantly enriched in S26 treatment (Fig. 5, Table S3). Similarly, members of the Lactococcus (LDA = 4.9, p < 0.05 ) were significantly enriched during the early phase, while Acetobacter (LDA = 4.5, p < 0.05 ), Lactiplantibacillus (LDA = 4.3, p < 0.05 ), Paucilactobacillus (LDA = 4.3, p < 0.05 ), Leuconostoc (LDA = 4.2, p < 0.05 ), Lacticaseibacillus (LDA = 4.2, p < 0.05 ) and Lactobacillus (LDA = 3.7, p < 0.05 ) were members which were significantly enriched during the late phases of propagation (Fig. 5, Table S3). However, only taxa other than those belonging to LAB and AAB were differentially enriched in farm site 1 (Fig. S4; Table S3). The differential enrichment outcome supports the observed community diversity changes.
[Please insert Fig. 5 here]
Figure 5 Linear discriminant analysis effect size (LEfSe) to identify differentially abundant microbial taxa following the propagation of mabisi in varied milk substrates over time. The x-axis shows the linear discriminant analysis (LDA) score (log 10 transformed effect size) of enriched taxonomic features according to substrate variation (Fig. 5a) and propagation phase (Fig. 5b). The y-axis lists the enriched taxa at genus level. The legends show the enriched groups: substrates - F100: F100 infant formula (dark teal), FCM: ultra-heat temperature full-cream milk (brownish orange), LFM: ultra-heat temperature low-fat milk (warm terracotta), O: starting mabisi microbial community (soft lavender purple), RCM: raw cow milk (magenta), S26: S26 infant formula (mutated brick red); propagation phases – early_phase: early phase (dark teal), late_phase: late phase (brownish orange), and O: starting mabisi microbial community (warm terracotta)
Microbial community-level functionality
To understand how the changes in the microbial community diversity influenced the community-level functionality following the repeated propagation of mabisi in varied substrates at different sites over time, volatile organic compounds (VOCs), pH, and consistency were analyzed as proxy indicators.
Volatile organic compounds
The obtained VOCs belong to the chemical classes of aldehydes, esters, carboxylic acids, alcohols, and ketones (Table S4). The VOC profiles exhibited differences between samples analyzed before and after the propagation of mabisi across substrates and farm sites over time. Particularly, samples analyzed before propagation displayed VOCs that are associated with photo oxidation and undesirable flavors, including octanoic acid, nonanoic acid, ethyl-9 decenoate, and 1-octen-3-one, among others (Fig. S5). Therefore, these specific samples were removed from downstream analysis.
A
Further analysis of propagated samples through principal component analysis (PCA) and PERMANOVA revealed that VOCs were significantly driven by both the substrate treatment, which separated along the PC1 axis explaining 37.4% of the variation, and the propagation phase, which separated along the PC2 axis explaining 22.4% of the variation (p < 0.05) (Fig. 6; Table S5). Specifically, the VOCs in the F100 and S26 treatments, exhibited higher levels of Ethyl acetate, Hexanal, and 1 Butanol 3-Methyl, which separated from those belonging to LFM and FCM, which showed higher levels of 2-Heptanone, 2-Nonanone, Butanoic acid, and 2-Butanone, Octanoic acid, and Hexanoic acid, whereas, those from RCM appeared to contribute shared VOC from either group (Fig. S6). However, the farm site did not impact any significant separation of VOCs (p > 0.05) (Fig. S7; Table S5).
[Please insert Fig. 6 here]
Figure 6 Volatile organic compounds from mabisi samples after propagation of mabisi microbiota in varied milk substrates over time. Each point represents an individual sample. Legends show substrates distinguished by color – starter: starting mabisi microbial community (orange), RCM: raw cow milk (sky blue), F100: F100 infant formula (green), S26: S26 infant formula (light pink), LFM: ultra-high temperature low-fat UHT (dark blue), and FCM: ultra-high temperature full-cream milk (dark orange). Propagation phases are represented by ellipses at 95% confidence interval – starter: starting mabisi microbial community (solid ellipse not formed due to inadequate data points), early_phase: early phase (dotted ellipse) and late_phase: late phase (dashed ellipse)
pH and consistency
A
Following propagation, the pH dropped in all substrates to a range between 3.98 and 4.51 (Fig. 7a) from a range between 5.69 to 6.77 before propagation (Fig. S8a). When compared to the RCM reference substrate, the median pH for LFM, FCM, and S26-based substrate treatments was significantly lower (p < 0.05), while that for F100 was not significantly different following the propagation process (p > 0.05) (Fig. 7a; Table S6). Further analysis revealed that the pH was significantly lower for propagated mabisi in the late propagation phase compared to the early phase (p < 0.05) (Fig. S8a; Table S7), and was also significantly lower for samples from farm 2 compared to farm 1 and 3 (p < 0.05) (Fig. S8b; Table S8). Thus, the pH was driven by differences in the substrates, propagation, and farm sites.
In addition, the substrate treatments also influenced the consistency outcomes. The consistency ranged between 1.5 to 4.11cm for all substrates following propagation of mabisi in varied substrates, with higher values observed in S26 and lower values observed in F100 treatments (Fig. 7b). Relative to the raw cow milk treatments, the median consistency was significantly lower for F100, FCM, and LFM (p < 0.05) while that for S26-based treatments was not statistically different (p > 0.05) (Fig. 7b; Table S9). However, consistency was not significantly different between early and late propagation phases (p > 0.05) (Fig. 7b; Table S9) or between sites (p > 0.05) (Fig. S8c; Table S9). These outcomes suggest that substrate variation was the key determinant for driving consistency patterns.
[Please insert Fig. 7 here]
Figure 7 The outcome of pH (Fig. 7a) and consistency (Fig. 7b) following repeated propagation of mabisi in varied milk substrates over time. The pH values are shown as medians, with interquartile ranges for each substrate treatment per propagation phase. The x-axis shows the propagation phases: early phase (early_phase) and late phase (late_phase), while the y-axis shows the pH and consistency (cm) measurements. Legends show the substrate treatment - F100: F100 infant formula (light teal), FCM: ultra-heat temperature full-cream milk (light yellow), LFM: ultra-high temperature low-fat milk (lavender), RCM: raw cow milk (coral), and S26: S26 infant formula (light blue). The dotted horizontal line represents the median value of pH (Fig. 7a) and consistency (Fig. 7b) for the reference substrate (RCM)
DISCUSSION
In this study, we aimed to investigate how species sorting mechanisms influence the assembly of natural microbial communities and maintain their functionality when exposed to novel environments across sites over time. Our findings partially supported our initial expectation, revealing a strong species sorting process evidenced by a substrate-driven divergence in microbial community composition linked to both the early and late propagation phases across sites. However, the community-level functionality was repeatable.
In our study, the propagated microbial communities remained diverse and dominated by community members belonging to lactic acid bacteria (LAB) and acetic acid bacteria (AAB), including Lactococcus, Acetobacter, Leuconostoc, Lactiplantibacillus, Paucilactobacillus, and Lacticaseibacillus. Accordingly, the spectra of LAB and AAB taxa observed here are consistent with previous reports in similar environments (Leale et al., 2023; Moonga et al., 2020), even from those found worldwide (Kochetkova et al., 2022; Liang et al., 2021). This suggests that these taxa are generalists and stable colonizers of mabisi niches, as they were able to repeatedly thrive in the novel environments imposed during our experiment. Microbial generalists are known to inherently possess metabolic flexibility to adapt to dynamic environments and, thus, have a wider niche breadth, as opposed to specialist taxa that require specific resources and conditions (Chen et al., 2021).
However, microbial communities undergo sorting, diverging into distinct clusters under the influence of environmental selection. This hypothesis has been tested in many studies, ranging from natural to controlled study models (Langenheder & Székely, 2011; Székely et al., 2013; Zhang et al., 2020; Zhu et al., 2020). Therefore, our results resonate with this hypothesis, given that the propagated microbial community diverged in composition, linked to each substrate treatment, thereby reflecting the mechanistic role of environmental selection processes in situ. Although the explicit mechanisms explaining how environmental selection shapes the assemblage of microbial communities are still unclear, we speculate that species sorting demonstrated in our findings could have been governed by physical-chemical and micronutrient variability between environments (Kochetkova et al., 2022; Zhang et al., 2020). The substrates used in our experiment were bovine-derived and homogeneous, yet they differed in pretreatment, pH, micronutrient content, and purpose (Kunda et al., 2015; Nyirenda et al., 2009; Park et al., 2012). As such, these abiotic factors likely exerted niche partitioning, driving differential adaptation of species, as observed in the consequent dissimilarity in community composition despite evolving from a shared starting community. This is because microbes capable of exploiting novel substrates (Cubas-Cano et al., 2019) may have gained a fitness advantage (e.g., abundance), while those that experienced negative selection declined under the same conditions (Lai et al., 2023). As such, our findings support the hypothesis that environmental changes drive niche differentiation, which acts as a filter during species sorting, ultimately shaping the microbial community divergence (Langenheder & Székely, 2011; Nguyen et al., 2021).
A
Importantly, our findings show that the influence of species sorting continues over temporal scales, especially in the late propagation phase, relative to the early phase, which was jointly supported by the enrichment of indicator species through differential abundance analysis. This pattern is concordant with previous observations (Johansen et al., 2019). In contrast, other studies indicate that species-sorting mechanisms are important during the initial phases of microbial assembly (Langenheder & Székely, 2011; Székely et al., 2013). The mechanisms underpinning substrate-driven microbial diversity over extended temporal scales are largely unknown, although this could be attributed to evolution through the accumulation of genetic mutations, which confer microbial fitness gains or losses under selective pressure (Cubas-Cano et al., 2019; Feng et al., 2018; Lawrence et al., 2012; Naseeb et al., 2017). Also, high nutrient availability has been shown to induce strong microbial interactions, resulting in altered chemical environments such as lowered pH that disfavor certain coexisting members (Ratzke et al., 2020). Consequently, this interaction predisposes other members to subsequent extinction and overall shifts in biodiversity. Furthermore, the evidence of a species-sorting process that led to successional patterns in microbial diversity over time in our study is reminiscent of alternative stable states conceptualized on the ecological equilibrium landscape (Shaw et al., 2019).
In addition, other studies indicate that species-sorting mechanisms are influenced by location (Kochetkova et al., 2022; Zhang et al., 2020). This is congruent with our findings, which revealed that site differences exerted significant differences in the community diversity outcomes, although this effect was negligible at the level of bacterial guilds for mabisi ecosystems (Leale et al., 2023; Moonga et al., 2020), as revealed by the differential abundance analysis. We mimicked the locally adopted culture conditions at respective sites; site 1 involved an outdoor-based incubation on an elevated location, site 2 involved incubation in an enclosure on a wooden platform, while site 3 involved incubation in an enclosure but on the floor. These features could attract site-specific ecological differences, including in-house microbiota and temperature variations (Gobbetti et al., 2018; Quintana et al., 2020) that could contribute to the niche division and varied diversity trajectories during the species sorting process, hence the differences in the diversity patterns observed between the studied sites (Kochetkova et al., 2022). Although we conducted a batch system, dispersal from exposure to in-house microbiota during experimental manipulations (Lee et al., 2013) could also have played a role during site-specific induced environmental selection. On the other hand, the three sites in our study comprised replicates of similar treatments and were located within a radius of two km, thereby assumed to experience similar weather conditions.
We further evaluated whether community-level functionality could mirror the trajectory of the observed microbial community diversity patterns. We found repeatable patterns in the overall community-level functionality, as evidenced by the proxies of VOC production, and decline in pH, as well as the consistency (Moonga et al., 2021). This suggests that the propagated microbial community displayed functional convergence (Groenenboom et al., 2022; Louca et al., 2016). However, the degree of specific functional capacities appeared to vary significantly. For instance, the VOC profile was significantly separated by substrate treatment along the PC1 axis, explaining 37.4% of the variation, and by propagation phases along the PC2 axis, accounting for 22.4% of the variation. This reflects that environmental-specific factors, such as variation of candidate micronutrient substrates for VOC production (Laëtitia et al., 2014; Smid & Kleerebezem, 2014), could have instigated the microbial metabolic capacities to varying degrees for this trait. In addition, previous studies have shown that the dynamic changes in the species relative abundance correlate with shifts in VOC production (Dan et al., 2017; Walsh et al., 2016), which mirrors substrate-driven microbial community divergence observed in our study. This is further in agreement with the reports that suggest that, despite the system’s functional repeatability, specific functions are impacted by the environmental selection during species sorting (Chen et al., 2021; Peter et al., 2011).
Conversely, the declining trend in pH, as in other fermented dairy systems (Sharma et al., 2023), appeared to be substrate-dependent between sites and over temporal scales in our study. This indicates that the observed community changes also performed the metabolic conversion of lactose to varying magnitudes. Our observations are consistent with a previous report, which revealed differences in pH reduction capacity due to microbial selection from temperature and processing effects (Moonga et al., 2021). Changes in pH further lead to strong niche partition and microbial interactions where better-adapted taxa are promoted while others are negatively selected (Mougi, 2023; Ratzke et al., 2020), reflected by the differential abundance in microbial community composition between environments studied here. For instance, Acetobacter, Lactiplantibacillus, Paucilactobacillus, Leuconostoc, Lacticaseibacillus, and Lactobacillus appeared to increase in frequency over the late phase of propagation, particularly in the S26 treatment, which exhibited the lowest pH during that phase. Most of these taxa are known to constitute superior buffering capacities for low pH among LAB through a two-component system mediated by histidine protein kinase and the corresponding response regulator, collectively facilitating proton pump, among other alleviative pathways for stress shock (Wang et al., 2018). Moreover, repeated propagation is reminiscent of adaptive evolution experiments, which have shown improved metabolic functional capacity towards desired functions following repeated exposure of microbial communities to selection (Konstantinidis et al., 2021; Rocchi et al., 2023). This underscores our observed high fermentation capacities reflected by the lower pH towards the late phase, compared to the early phase of propagation.
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The coagulation of milk protein under acid conditions, as well as the production of exopolysaccharides, underlie the decline in consistency of fermented dairy systems (Lucey, 2017; Nemati & Mozafarpour, 2024). We found that consistency was driven by the substrate variation, whereas it remained indifferent over temporal and site scales. While it was evident that the protein fraction in the studied environments was different (Kunda et al., 2015; Nyirenda et al., 2009; Park et al., 2012), this could not explain the observed consistency patterns, given that the substrate with the highest protein fraction - S26, displayed an indifferent median consistency, whereas the F100, FCM, and LFM-based substrates exhibited significantly lower median consistency compared to RCM. This outcome, therefore, suggests that other unknown selective factors, or the substrate differentially enriched taxa, governed the consistency functional property through differential production of exopolysaccharides (Nemati & Mozafarpour, 2024; Yang et al., 2023), whereas over temporal and spatial scales, this effect was negligible. Nevertheless, taken together, this could indicate that mabisi microbial community exhibits functional resilience when exposed to varied milk environments over time, regardless of site differences, and can be attributed to microbial community asynchrony, which promotes different taxa to perform overlapping functions over a temporal scale, thereby maintaining functional stability (Louca et al., 2016; Wagg et al., 2021).
Beyond the ecological implications highlighted above, our findings also hold biotechnological relevance. In particular, our study demonstrates that mabisi microbial communities can be harnessed for developing novel fermented food ingredients, including for purposes such as the fermentation of infant formula, where LAB may consequently confer probiotic benefits to infants (Radke et al., 2017). This further supports the feasibility and effectiveness of the current practice of its use in treating malnourished children in an in-house formulated F100 infant formula in low-income countries. Previous studies indicate that microbial communities can adapt and improve performance through adaptive evolutionary engineering (Konstantinidis et al., 2021; Rocchi et al., 2023). Accordingly, our study revealed that repeated propagation, reminiscent of adaptive evolution, represents a promising strategy to enhance such functional traits. Thus, future work should build on this approach by evaluating the efficacy of such novel fermented products in vivo, i.e., involving other spectra of human subjects, across age groups.
In our study, we were limited by the sole application of the 16S rRNA V3-V4 amplicon sequencing for microbial profiling. This method is only capable of detecting bacterial and archaea taxa (Langille et al., 2013) and does not resolve species to strain levels of taxonomy. While strain level information would be interesting, the V3-V4 amplicon sequencing approach did allow for comparative analysis of selective response between communities, addressing our main research question. However, 16S rDNA amplicon sequencing does not account for yeast. On the other hand, previous work showed that yeasts are not central members since they are not consistently present in mabisi, and when present, they are only represented by a single species (Moonga et al., 2020; Schoustra et al., 2013). This suggests that the bacteria (LAB and AAB) community underlie species sorting dynamics in mabisi niches. Further, our study approach could not account for genetic mutations (Feng et al., 2018) over the experimental evolution time scale, which could have complemented the observed trajectory of community diversity and its function. Nevertheless, by revealing dissimilarity in community diversity and repeatable community-level functionality in propagated novel environments across sites over time, this study has revealed mechanistic insights into how species sorting sustains a natural microbial community and functionality in situ.
In conclusion, our study has shown that, following exposure to novel environments, a natural microbial community from a common starting community diverges in composition, albeit through attaining alternative stable states on an ecological equilibrium landscape. The repeatability in metabolic profiles across environmental treatments also reflects functional redundancy. Our study not only serves to inform mechanistic fundamental ecological insights on the microbial community responses to environmental changes, but also provides a basis for harnessing a natural mabisi microbial community to be diversified for biotechnological applications to enhance novel fermented food ingredients.
DATA AVAILABILITY
The datasets generated during the current study are available online in the 4TU.ResearchData repository: https://doi.org/10.4121/82fa6380-c40c-4c40-b5ec-933b0253e6ce
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Acknowledgement
We sincerely thank the local farmer who provided their raw cow milk as one of the substrates, including permitting their pemises as sites for study activities. Furthermore, we are grateful to Judith Wolkers–Rooijackers for the GC-MS analysis and Francisca Reyes Marquez for the technical support during DNA extractions. We further extend our gratitude to Jay Sikalima for his assistance during field data collection.
Electronic Supplementary Material
Below is the link to the electronic supplementary material
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Author Contribution
SN: Conceptualization, data collection, analysis, and writing of original manuscript. AA and OM: Supervision, data collection, analysis, and writing (editing and reviews). BZ, ES, SS and JC: Project administration, conceptualization, supervision, data collection, analysis, and writing (editing and reviews).
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Data Availability
The datasets generated during the current study are available online in the 4TU.ResearchData repository: [https://doi.org/10.4121/82fa6380-c40c-4c40-b5ec-933b0253e6ce](https:/doi.org/10.4121/82fa6380-c40c-4c40-b5ec-933b0253e6ce)
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FUNDING
This work was made possible through the Wageningen Global Sustainability Programme (formerly known as INREF). The grant was awarded to S.E.S.
AUTHORS AND AFFILIATIONS
Laboratory of Genetics, Wageningen University and Research, Wageningen, The Netherlands.
Shepherd Nehanda, ORCID: 0009-0005-4297-8829.
Anna Y. Alekseeva, ORCID: 0000-0003-0164-0539.
Bas J. Zwaan, ORCID: 0000-0002-8221-4998.
Sijmen E. Schoustra, ORCID: 0000-0001-7843-5539.
Laboratory of Food Microbiology, Wageningen University and Research, Wageningen, The Netherlands.
Oscar van Mastrigt, ORCID: 0000-0001-6576-910X.
Eddy J. Smid, ORCID: 0000-0002-6687-5083.
National Health Research and Training Institute (Formerly Tropical Diseases Research Centre), Department of Biomedical Sciences, Ndola, Zambia.
Shepherd Nehanda, ORCID: 0009-0005-4297-8829.
Justin Chileshe, ORCID: 0000-0003-4134-2851.
Department of Food Science and Nutrition, The University of Zambia, Lusaka, Zambia.
Sijmen E. Schoustra, ORCID: 0000-0001-7843-5539.
Corresponding authors
Correspondence to Shepherd Nehanda; sheperd.nehanda@wur.nl or Sijmen E. Schoustra sijmen.schoustra@wur.nl
CONTRIBUTIONS
SN: Conceptualization, data collection, analysis, and writing of original manuscript. AA and OM: Supervision, data collection, analysis, and writing (editing and reviews). BZ, ES, SS and JC: Project administration, conceptualization, supervision, data collection, analysis, and writing (editing and reviews).
COMPETING INTERESTS
The authors declare no competing interests.
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Note
‘-’ means value missing and ‘*’ details obtained from manufacturer’s labels on the container. Substrates are represented by F100 infant formula (F100), S26 infant formula (S26), raw cow milk (RCM), ultra-high temperature low-fat milk (LFM), and ultra-high temperature full-cream milk (FCM).
Note
‘*’ represents statistical significance, and no esthetics represent a non-statistically significant result.
Note
‘*’ represents statistical significance, and no esthetics represent a non-statistically significant result.
Total words in MS: 8718
Total words in Title: 0
Total words in Abstract: 255
Total Keyword count: 0
Total Images in MS: 15
Total Tables in MS: 10
Total Reference count: 67