Hostname: page-component-78c5997874-m6dg7 Total loading time: 0 Render date: 2024-11-10T08:24:03.357Z Has data issue: false hasContentIssue false

Impact of protein on the composition and metabolism of the human gut microbiota and health

Published online by Cambridge University Press:  22 December 2020

Sylvia H. Duncan*
Affiliation:
Gut Health Group, Rowett Institute, University of Aberdeen, Foresterhill, AberdeenAB25 2ZD, Scotland, UK
Ajay Iyer
Affiliation:
Gut Health Group, Rowett Institute, University of Aberdeen, Foresterhill, AberdeenAB25 2ZD, Scotland, UK
Wendy R. Russell
Affiliation:
Gut Health Group, Rowett Institute, University of Aberdeen, Foresterhill, AberdeenAB25 2ZD, Scotland, UK
*
*Corresponding author: Sylvia H. Duncan, email Sylvia.duncan@abdn.ac.uk
Rights & Permissions [Opens in a new window]

Abstract

The composition and metabolic activity of the bacteria that inhabit the large intestine can have a major impact on health. Despite considerable inter-individual variation across bacterial species, the dominant phyla are generally highly conserved. There are several exogenous and gut environmental factors that play a role in modulating the composition and activities of colonic bacteria including diet with intakes of different macronutrients, including protein, accounting for approximately 20% of the microbial variation. Certain bacterial species tend to be considered as generalists and can metabolise a broad range of substrates, including both carbohydrate- and protein-derived substrates, whilst other species are specialists with a rather limited metabolic capacity. Metabolism of peptides and amino acids by gut bacteria can result in the formation of a wide range of metabolites several of which are considered deleterious to health including nitrosamines, heterocyclic amines and hydrogen sulphide as some of these products are genotoxic and have been linked to colonic disease. Beneficial metabolites however include SCFA and certain species can use amino acids to form butyrate which is the major energy source for colonocytes. The impact on health may however depend on the source of these products. In this review, we consider the impact of diet, particularly protein diets, on modulating the composition of the gut microbiota and likely health consequences and the potential impact of climate change and food security.

Type
Research Article
Copyright
Copyright © The Author(s), 2020. Published by Cambridge University Press on behalf of The Nutrition Society.

The human colon is an anoxic and dynamic environment which constantly interacts with the host's immune system. The colon harbours a dense collection of bacteria that inhabit the large intestine that mainly belongs to five different phyla. These phyla comprise many hundreds of different species and most of these bacteria are anaerobes. Given the advances in the molecular methods available to profile the gut microbiota(Reference Walker, Duncan and Louis1), there is currently a good understanding of composition. Moreover, affordable complete genome sequencing of gut bacteria has meant that it is feasible to mine the genomes of many human gut bacterial species for traits of interest. For example, certain bacterial species, often with large genomes, such as some Bacteroides species, are considered generalists as these have a remarkable repertoire of enzymes(Reference Lapébie, Lombard and Drula2) which allows these bacterial cells to metabolise a broad range of substrates as carbon, nitrogen and energy sources.

Numerous factors influence gut microbial composition such as host genetics, general health status, exposure to microbes during early life and consumption of antibiotics. Diet however is a major contributor to microbial structure and the main dietary macronutrients: carbohydrate, proteins and fat will influence gut microbial activities and metabolic outputs. Also, the types of foods consumed, cooking processes used and the balance of macronutrients and micronutrients are likely to be important drivers of health. The major products of fermentation include the SCFA and butyrate, in particular, has a special role for the host and it is the major energy source for colonocytes(Reference Louis and Flint3). Other bacterial metabolites formed mainly from the metabolism of proteins can result in the formation of less beneficial products including N-nitrosamines and heterocyclic amines that can be deleterious to health(Reference Scott, Gratz and Sheridan4). The overall balance of benefit and detriment for the host will therefore depend on the status of the microbial community in terms of its distribution, diversity, species composition and metabolic outputs(Reference Flint, Scott and Louis5).

Increasingly, there are considerable concerns about the types of foods we eat and the global impact of both climate change and the SARS-Cov-2 pandemic has highlighted the urgency to maintain food security. Moreover, this pandemic has highlighted the need for many countries, including the UK, to consider more sustainable food chains and reducing transportation of imported foods. The UK currently imports about half the food consumed. Consideration therefore needs to be given to agricultural practices and food production systems with an additional aim of reducing greenhouse gas emissions(Reference Smith and Gregory6). The food we eat impacts on the overall metabolic activities of colonic microbes and dietary changes will have an impact on health and disease. In this review, we consider the complex relationship between diet, particularly protein content, and the gut microbiota and its metabolism and how this may impact on health whilst outlining the impact of different protein diets on the environment.

The human gut microbial ecosystem

The human large intestine performs several key functions including degradation of dietary substrates, nutrient absorption, excretion of waste and is the major site of salt and water absorption. Other than diet, the composition of the gut microbiota may be influenced by many external factors including host genetics which has been estimated to explain approximately 9 % of the variation(Reference Goodrich, Davenport and Beaumont7). Other factors that impact on microbial variation may include age, geographical location and antibiotic usage(Reference Wu, Chen and Hoffmann8).

Moreover, some host factors may also impact on gut microbial composition including gut transit which can vary. The mean gut transit time across the complete length of the intestinal tract in healthy adults has been estimated to be between 26 and 35 h(Reference Wang, Mohammed and Farmer9,Reference Abuhelwa, Foster and Upton10) , but can be up to several days thereby allowing for the establishment of an abundance of microorganisms(Reference Macfarlane and Macfarlane11). There are many discrete physiological environments within the human gastrointestinal tract, which includes the highly acidic conditions in the stomach(Reference Abuhelwa, Foster and Upton10), to the more alkaline pH in the small intestine with changes in pH along the large intestine.

Importantly, diet is thought to explain approximately 20 % of the variation in gut microbial composition(Reference Johnson, Vangay and Al-Ghalith12). Undigested dietary material that escapes digestion by host enzymes enters the colon and is rapidly fermented by the resident microbiota. This results in rapid microbial growth and production of SCFA and other metabolites, which in turn lowers the pH(Reference Cummings and Macfarlane13). As the digesta moves towards the distal colon, carbohydrate sources become depleted; therefore, microbial growth and carbohydrate fermentation decrease whilst peptide fermentation increase, depending on dietary intake, resulting in the formation of a range of nitrogenous products including ammonia which is one of the products that drives an increase in pH towards neutrality(Reference Cummings and Macfarlane13).

Colonic microbial composition

The human large intestine harbours viruses many of which are bacteriophages(Reference Columpsi, Sacchi and Zuccaro14,Reference Hofer15) , fungi including the dimorphic Candida species(Reference Gouba, Raoult and Drancourt16) and bacteria. The latter include thousands of different bacterial species that reach their highest density in the large intestine. The composition and metabolic activities of these microbes are likely to be strongly influenced by diet which will impact the health and disease(Reference Flint, Scott and Louis5,Reference Johnson, Vangay and Al-Ghalith12) .

The adult microbial community usually contains about 1011 bacterial cells/g of faeces(Reference Zoetendal, Raes and van den Bogert17). The gut microbiome also contains many more genes (approximately 150-times more) than the human genome, which is currently estimated to possess around 24 000 genes, providing the host with greatly expanded functionality, particularly with regard to complex carbohydrate metabolism(Reference Bäckhed, Ley and Sonnenburg18), and although gut bacterial composition can be decidedly variable, functionally it is somewhat more highly conserved(Reference Qin, Li and Raes19).

Despite inter-individual variability at the genus and species level, in the composition of the gut microbiota, there are core species that are found in most healthy individuals. At the phylum level, Firmicutes and Bacteroidetes are the most dominant. The less abundant phyla are the Proteobacteria, Actinobacteria and Verrucomicrobia(Reference Duncan, Louis and Flint20). A key species of the latter is the mucin-degrading bacterium Akkermansia muciniphila (Reference Derrien, Vaughan and Plugge21) which is considered to be health protective.

Bacteroidetes usually comprise about 30 % of the total microbiota, although this can vary, and it is becoming increasingly apparent that there is a divergence with some individuals tending to be either Bacteroides or Prevotella dominant(Reference Wu, Chen and Hoffmann8). Bacteroides and Prevotella species can utilise carbohydrate- or protein-derived substrates(Reference Macy and Probst22). Commonly occurring species include B. vulgatus, B. fragilis, B. distasonis, B. uniformis, B. thetaiotaomicron and B. eggerthii (Reference Salyers, Vercellotti and West23).

The Firmicutes are members of the clostridia class and the predominant human colonic species mainly belong to two phylogenetic groups. One group is the Lachnospiraceae that includes genera such as Eubacterium, Roseburia, Butyrivibrio, Coprococcus and Lachnospira and the second is the Ruminococcaceae that encompasses Faecalibacterium and Ruminococcus species. Other commonly reported genera found in lower abundance include Bifidobacterium and Veillonella species(Reference Duncan, Louis and Flint20,Reference Neish24,Reference Isolauri, Kirjavainen and Salminen25) .

Facultative anaerobes are usually much less dominant in the healthy colon but their abundance may be elevated in certain diseases(Reference Lopez-Siles, Khan and Duncan26) and includes Enterobacteriaceae species. A number of other, specialised groups may exist at lower levels including the sulphate-reducing bacterial species Desulfovibrio (Reference Marquet, Duncan and Chassard27). Proteobacteria are usually in low abundance in the healthy gut but are often more prevalent in frail elderly(Reference O'Toole and Jeffery28). Archaeal methanogens may also be present in approximately 50 % of adults with Methanobrevibacter smithii as the predominant species(Reference Eckburg, Bik and Bernstein29) and methane, which is a major end product, may slow gut transit.

Role of gut environmental factors including anaerobiosis, pH and bile on microbiota composition

There are many factors that are likely to impact on the composition of the gut microbiota. This includes host factors as well as gut environmental factors such as anaerobicity, pH and bile salt levels.

Anaerobic ecosystem

The two dominant phyla that inhabit the large intestine are the Firmicutes and Bacteroidetes and their niche in the colon may partly be driven by redox potential (Eh) and gas phase. Gut microorganisms persist in an environment with low partial oxygen pressures and this anaerobic ecosystem has an Eh value of about −250 mV. Anaerobes generally lack electron transport chains found in facultative anaerobic bacteria to regenerate the reduced cofactors and therefore do not gain further energy by electron transport-level phosphorylation. Instead, metabolic intermediates are reduced mainly to acidic fermentation products and gases. Some gut bacteria including Proteobacteria perform anaerobic respiration involving electron transport chains by using electron acceptors such as sulphate or carbon dioxide(Reference Duncan, Louis and Flint20).

Bacteroides species have been described as nanaerobes as many species can survive for several hours in the presence of oxygen but require anoxic conditions to grow. By comparison, many gut bacterial species belonging to the Firmicutes are considered as strict anaerobes and are unable to survive for even a few minutes upon exposure to air(Reference Flint, Scott and Louis5). Interestingly, one of the most abundant Firmicutes species in the large intestine, Faecalibacterium prausnitzii, has adapted to using an electron shuttle of thiols and flavins to transfer electrons to oxygen(Reference Khan, Duncan and Stams30).

Gastrointestinal pH

As much of the metabolism of gut anaerobes is given over to fermenting dietary macronutrients, particularly non-digestible carbohydrates to SCFA, the pH of the proximal colon which is the most active site of fermentation in healthy subjects is mildly acidic (about pH 5⋅5–6⋅0). There are usually less carbohydrates available in the distal colon; bacteria that are resident in this section are also reliant on the metabolism of peptides and amino acids as sources of carbon and nitrogen. This is likely to result in the formation of higher levels of nitrogenous products including ammonia and will contribute to driving pH values closer to neutrality. Many of the Gram-positive Firmicutes species are more tolerant of the mildly acidic conditions in the proximal colon which is likely to provide a competitive advantage for these bacterial species, whereas the growth of Bacteroidetes species are likely to be restricted here but are likely to be more active in the distal colon where the pH is closer to neutrality(Reference Marquet, Duncan and Chassard27). This has been supported by studies that revealed the major changes in species composition and metabolic products when comparing the impact of pH 5⋅5 and 6⋅5 in model colonic in vitro fermentor systems(Reference Walker, Duncan and McWilliam Leitch31) whereby mildly acidic conditions (about pH 5⋅5) is favoured by, for example, butyrate producing Roseburia species. When the pH is closer to neutrality (pH 6⋅5), Bacteroides spp. that have a role in peptide metabolism tend to be favoured(Reference Flint, Duncan, Batt and Tortorello32).

Bile salts

Enzymes in the liver convert cholesterol to bile acids which are secreted into the intestine from the gall bladder. More cholesterol is formed when diets are high in saturated fats and consequently the secretion of bile increases when consuming these diets. The bile acids made in the liver are known as primary bile acids, and in human subjects, there are two major types such as cholic acid and deoxycholic acid. Within the liver, these are usually conjugated into two amino acids, either glycine or taurine. The latter is biosynthesised from methionine and cysteine whilst glycine is from serine.

Interestingly, it is the type of dietary macronutrients that largely dictates whether the bile acids are conjugated with glycine which is likely to be largely plant based or alternatively to taurine which is most likely to occur when diets are high in animal protein and fat. When these conjugated bile acids reach the large intestine, certain gut bacterial species that possess bile salt hydrolases can cleave the linkages that bond the bile acids to the amino acids. In the case of taurocholic acid, the deconjugation process results in the release of taurine and choline into the intestine. Certain bacterial species such as Bilophila wadsworthii can metabolise taurine to form ammonia, acetate and hydrogen sulphide and the latter product is genotoxic. Clostridium scindens can remove the hydroxyl group from choline to form deoxy choline which is a tumour-promoting agent(Reference Flint33). The activities of these bacterial species in the colon are therefore considered likely to contribute to the promotion of colorectal cancer(Reference Ridlon, Harris and Bhowmik34).

Moreover, habitual intakes of a typical western-style diet which is usually considered to be low in fibre, but high in refined sugar and fat, have been associated with increased levels of endotoxin-producing bacteria such as Escherichia coli. This may be due to high fat resulting in increased bile formation and that these species may be more tolerant of bile than other bacteria that are dominant in the large intestine.

Impact of diet on modulating the gut microbiota

Recent major advances in molecular profiling technologies have progressed our understanding of the composition of the gut microbiota and how it changes through life stages from birth(Reference Dominguez-Bello, Costello and Contreras35) to the elderly(Reference Duncan and Flint36). In adults, short-term dietary interventions have demonstrated that these shifts occur rapidly(Reference David, Maurice and Carmody37); however, these changes may be transient.

Dietary influences on the gut microbiota of infants, adults and elderly

Diet is a factor that shapes the composition of the gut microbiota across all the different life stages. The gastrointestinal tract of a fetus is usually considered sterile; then following birth, the gut microbiota of babies is likely to depend on the mode of delivery(Reference Dominguez-Bello, Costello and Contreras35), bile acids(Reference van Best, Rolle-Kampczyk and Schaap38) and feeding regimen, including whether babies are breast- or formula-fed(Reference Timmerman, Rutten and Boekhorst39). The intestinal tract of breast-fed babies is largely dominated by members of the Bifidobacterium genus, which appear to be exquisitely adapted to utilise human milk oligosaccharides (HMO)(Reference Vandenplas, Carnielli and Ksiazyk40). Breast milk is a rich source of peptides, from casein and whey, in addition to non-digestible sugars, usually referred to as HMO is likely to drive bifidobacterial population establishment in the colon. HMO are amongst the most abundant components of human milk after water and lactose. These HMO have a degree of polymerisation from three to thirty-two with about fifty of these different carbohydrates present in mother's milk. Major HMO include lacto-N-tetraose, lacto-N-neotetraose and lacto-N-hexaose along with fucosylated molecules. Formula-fed babies, in contrast, usually possess a more complex gut microbiota that is more adult-like in composition(Reference Praveen, Jordan and Priami41). The introduction of solid foods at weaning results in completely altered substrate availability in the colon and triggers the expansion of obligate anaerobic bacterial groups such as the Bacteroidetes and Firmicutes, which are able to breakdown and metabolise more complex polysaccharide sources(Reference Flint, Scott and Duncan42).

Following weaning and up to about 3 years of age, the microbiota of infants tends to become more diverse with a high rate of microbial instability and therefore this is a crucial period for the development of the gut microbiota which may impact on long-term health. Beyond 3 years of age, the gut microbiota tends to stabilise, although dietary intakes will influence the microbiota composition. Changes in the composition of the gut microbiota may however undergo more prolonged development than previously suspected with the microbial diversity of children having perhaps greater diversity than that of healthy adults.

Despite a tendency for microbial stability in adulthood with habitual diet providing a constant source of nutrients, the gut microbiota is in a constant state of flux. A diverse diet that includes a number of different types of plant foods has been associated with greater bacterial diversity. A positive relationship has been observed between dietary diversity and microbial stability with F. prausnitzii being increased in individuals that consumed more than thirty plant types per week compared to those that consumed less than ten per week(Reference Leeming, Johnson and Spector43).

In the elderly, previous studies have compared the differences in the microbiota in the elderly within community dwellers to those who are staying in care homes as the latter tend to have more health problems(Reference Harmsen, Wildeboer-Veloo and Raangs44,Reference Jeffery, Claesson and O'Toole45) . The study found that care home dwellers had a higher proportion of Bacteroidetes than that found in community dwellers. Roseburia species that are known butyrate producers were also present in lower abundance in care home residents and F. prausnitzii was lower in abundance in frail elderly. Moreover, the elderly population (>65 years old) has been found to have a gut microbiota that is less diverse than in healthy young adults which may be due to the reduction in diet variation and also deterioration in dentition, salivary function and gut transit(Reference Duncan and Flint36).

Ageing may also affect the ileal microbiota, as has been suggested by examinations of the ileal contents of sudden death elderly patients, which revealed that their microbial community contained high proportional abundances of Proteobacteria, Bacillus, Streptococcus and Lactobacillus species when compared to that of adult ileostomy patients which were observed to have a lower proportional abundance of Proteobacteria and higher abundance of species belonging to Firmicutes(Reference Booijink, El-Aidy and Rajilić-Stojanović46).

Dietary macronutrients

Diet has a key role in modulating the composition of the human intestinal microbiota which impacts on health. The balance, type and amount of dietary macronutrients, including carbohydrates and protein, can have a major impact on the composition of the intestinal microbiota whilst micronutrient status including vitamin availability, some of which is derived from the certain species of the microbial community, is also important for health. Many of the dominant bacteria that reside in the human colon may be auxotrophic and therefore are unable to synthesis all vitamins required for growth. These species are therefore dependent on the host or other bacteria for certain vitamins to facilitate growth(Reference Soto-Martin, Warnke and Farquharson47).

Dietary carbohydrates

Complex dietary fibre is the most commonly accepted nutrient to exert a beneficial effect on microbial composition(Reference Flint, Scott and Louis5). The main carbohydrate consumed by adults and available for utilisation by intestinal microbes includes resistant starches followed by NSP and oligosaccharides(Reference Cummings and Macfarlane13). The amounts of these macronutrients consumed daily can be highly variable with intakes of resistant starch ranging from <10 to >40 g daily. Resistant starch is defined as dietary starch that escapes digestion by host enzymes in the upper gastrointestinal tract because of protection provided by other polymers (RS1), particle structure (RS2), retrogradation (RS3) or chemical cross-linking (RS4). The starch-degrading enzyme systems from human gut symbionts that have been studied in detail for Bacteroides thetaiotaomicron, Eubacterium rectale and more recently Ruminococcus bromii, which is a keystone species for the breakdown of resistant starch in the human large intestine(Reference Ze, Ben David and Laverde-Gomez48). Unlike starch, pectins found in plant cell walls are structurally highly complex and are classified into homo-polygalacturonan, rhamnogalacturonan I and rhamnogalacturonan II(Reference Caffall and Mohnen49). Pectin degradation requires glycoside hydrolases, polysaccharide lyases and carbohydrate esterases bacterial activities(Reference Flint, Scott and Duncan42). Pectin may be degraded by Gram-negative Bacteroides species(Reference Salyers, Vercellotti and West23) and a few Gram-positive bacterial species have also been reported to ferment pectin or pectin breakdown products including Eubacterium eligens (Reference Lopez-Siles, Khan and Duncan26,Reference Chung, Meijerink and Zeuner50) which possesses anti-inflammatory activity by promoting the production of IL-10 by epithelial cells(Reference Chung, Walker and Vermeiren51).

Edible plants can contain several hundreds of phenolic compounds derived by the phenylpropanoid pathway, and based on their structures, these are classified predominantly into phenolic acids, flavonoids, stilbenes, lignans and tannins. On average about 1 g plant phenolics may be consumed daily depending on dietary intakes(Reference Nordström52). Phenolic compounds can exert dual effects on the gut microbiota as they can inhibit the growth of specific taxa whilst enhancing the growth of others whereby they can be metabolised into bioavailable substrates for the host. Food rich in phenolics, such as fruit, vegetables, cereals, tea and coffee, is associated with a range of health-promoting activities with a reduced risk of chronic disease(Reference Russell, Hoyles and Flint53). Aromatic amino acids such as tyrosine and phenylalanine are fermented to further phenolic compounds including cresol and phenol derivatives whilst tryptophan is fermented to indoles(Reference Smith and Macfarlane54). Further studies revealed that two abundant phenylpropanoid-derived compounds found in human faecal samples are phenylacetic acid and 4-hydroxylphenylacetic acid, and although they have the potential to be derived from diets rich in plant-based foods, these compounds can also be derived from the microbial fermentation of aromatic amino acids in the colon and are likely to be a major source of phenylpropanoid-derived metabolites in the colon(Reference Russell, Hoyles and Flint53).

Dietary protein

Approximately 3–18 g dietary protein enters the human large intestine every day(Reference Smith and Macfarlane54), which is diet-dependent. On a very low protein diet, this can range from 3 to 16 g/d on a vegan diet high in unprocessed cereals and grains. This can increase to 18 g/d on meat-rich diets(Reference Yao, Muir and Gibson55). High protein and low carbohydrate diets may aid weight loss given their impact on satiety(Reference Johnstone, Horgan and Murison56). Undigested protein reaching the large intestine may however lead to an increase of pathogenic microorganisms with an associated higher risk of metabolic diseases. High consumption of red meat, which in addition to being rich in protein, also contains haeme and has been associated with an elevated risk of developing colorectal cancer(Reference Kim, Coelho and Blachier57).

Dietary proteins are hydrolysed into peptides and amino acids by both host- and bacterial-derived proteases and peptidases(Reference Neis, Dejong and Rensen58,Reference Dai59) . The released peptides and amino acids can be further utilised by both gut bacteria and the host. Bacterial metabolism of extracellular amino acids is likely however to require specific transporters. Peptide and amino acid-fermenting bacteria include species that belong to the following genera: Bacteroides, Prevotella, Clostridium, Veillonella, Megasphaera, Acidaminococcus and Selenomonas (Fig. 1). Certain species possess highly active dipeptidyl peptidase and dipeptidase activities, suggesting that these bacteria might be important for protein digestion and amino absorption in the mammalian digestive tract. Most gut bacteria utilise amino acids and ammonia as their preferred nitrogen source, although for others such as certain Prevotella species peptides are the preferred nitrogen source(Reference McIntosh, Shingfield and Devillard60). Bacteroides species can secrete proteases with presumed activity near the brush border of absorptive cells and a high abundance of Bacteroides species may result in an excess of proteases, which may degrade maltase and surcase enzymes in the brush borders of enterocytes(Reference Smith and Macfarlane61).

Fig. 1. Protein metabolism by colonic bacteria.

The levels of proteins, peptides and amino acids are relatively high in the proximal colon and reduced in the distal colon. Regarding the large intestine, it appears that amino acids are not significantly absorbed by the colonic mucosa, but rather are intensively metabolised by the large intestinal microbiota(Reference Davila, Blachier and Gotteland62). This higher rate of bacterial protein fermentation has been related to high pH and low carbohydrate availability in the large intestine(Reference Macfarlane, Allison and Gibson63) resulting in the generation of a complex combination of metabolic end products including SCFA and the major acids in the colon are acetate, propionate and butyrate and the branched-chain fatty acids valerate, iso-butyrate and iso-valerate. In addition, microbial metabolism of amino acids will also result in the formation of ammonia and amines and the latter is produced by decarboxylation of amino acids. The amines mainly produced by the resident microbiota include cadaverine (a decarboxylation product of lysine) and agmatine (a decarboxylation product of arginine)(Reference Sánchez-Jiménez, Ruiz-Pérez and Urdiales64). These amines can have significant physiological effects and agmatine has been shown to influence metabolic functions including elevating tissue cyclic AMP levels, ultimately replicating the effects of energy restriction with respect to metabolic reprogramming and leading to reduced diet-induced weight gain(Reference Nissim, Horyn and Daikhin65).

Microbial metabolites

Although microbial cells are usually prevented from breaching barriers allowing access to host cells in the large intestine, smaller molecular weight microbial metabolites can cross this barrier by diffusion and active transport. The gut microbiota forms an array of primary and secondary metabolites which can be transported into colonocytes and exert beneficial or deleterious effects on these epithelial cells depending on their concentrations in the lumen. Certain metabolites have been postulated to have a role in a wide range of health conditions, including diabetes, atherosclerosis, kidney disease, inflammatory bowel disease and cancer(Reference Hughes, Magee and Bingham66). The gut anaerobes ferment dietary nutrients to form SCFA which include acetate, propionate, butyrate and gases including carbon dioxide and hydrogen. Some of the weak acidic metabolites including propionate and butyrate are likely to provide health benefits including appetite control, dampen inflammation, maintain gut and systemic health and modulate disease progression. Conversely, lactate which is generally considered as an intermediate fermentation product can result in acidosis unless this product is removed by bacterial cross-feeding(Reference Duncan, Louis and Flint67). Specialist gut microbial species can release and transform dietary plant phenolics and the spectrum of products formed may provide potent antioxidant and anti-inflammatory activities(Reference Russell, Hoyles and Flint53). Conversely, consumption of high animal protein and fat diets may lead to the formation of damaging microbial products including elevated levels of nitroso-compounds, hydrogen sulphide and trimethylamine(Reference Scott, Gratz and Sheridan4).

SCFA

Microbial fermentation in the large intestine results in the formation of a range of SCFA and the main acids detected in the large intestine are acetate, propionate and butyrate that make up about 90 % of acids in the colon and are usually detected in molar proportions of about 3:1:1 but this is dependent on diet and the composition of each individual's microbiota. Some minor SCFA including iso-butyrate and iso-valerate are formed by bacterial fermentation of branched-chain amino acids. The total level of SCFA is usually in the region of 60–180 mm depending on factors such as diet and gut transit(Reference David, Maurice and Carmody37,Reference Louis, Scott and Duncan68) . The majority of intestinal bacteria use the glycolytic pathway and the pentose phosphate pathway to harvest energy from carbohydrates, both pathways lead to the formation of pyruvate which is a key intermediate in SCFA formation(Reference Macfarlane and Macfarlane11). Although acetate reaches the highest concentration of any of the SCFA in faeces, it is known that many human faecal bacteria are net consumers of acetate in pure culture(Reference Barcenilla, Pryde and Martin69) including the dominant butyrate producers F. prausnitzii, Roseburia species and E. rectale (Reference Duncan, Hold and Harmsen70). Butyrate is generally believed to be synthesised via two main routes namely butyrate kinase or butyryl CoA:acetate CoA transferase routes(Reference Pryde, Duncan and Hold71). Butyrate is generally considered to provide a number of health benefits and is the preferred energy source for the colonocytes(Reference Louis and Flint3,Reference Hamer, Jonkers and Venema72,Reference Scheppach73) . Increased levels of butyrate have been associated with increased intestinal transit(Reference Lewis and Heaton74).

Propionate can stimulate the gut hormones, peptide YY and glucagon-like peptide-1, which increase satiety and thereby reducing energy intake and body weight gain in adults(Reference Tolhurst, Heffron and Lam75,Reference Chambers, Viardot and Psichas76) . A large group of the gut bacteria can generate propionate including the abundant Bacteroidetes phylum(Reference Yang, Martínez and Walter77). Propionate can be formed via three different metabolic routes and these are the acrylate, succinate and the propanediol pathways(Reference Louis, Duncan and McCrae78).

Amino acids utilised by gut anaerobes that can be metabolised to acetate include glycine, threonine, glutamate, lysine, ornithine and aspartate(Reference Smith and Macfarlane61). Threonine can give rise to all three major SCFA and with propionate mainly being produced from threonine(Reference Smith and Macfarlane61). Butyrate can be generated from the metabolism of threonine, glutamate and lysine. The latter can be used by species of Intestinimonas to form butyrate(Reference Bui, de Vos and Plugge79). The branched-chain amino acids namely valine, leucine and isoleucine give rise to the formation of the branched-chain fatty acids, iso-leucine, iso-valine and valine as has been reported for Anaerotignum species(Reference Ueki, Goto and Ohtaki80).

Hydrogen sulphide

Hydrogen can be formed by fermentative bacteria in the large intestine and in turn can be consumed by methanogens, acetogens and sulphate-reducing bacteria. These bacteria are likely to compete for hydrogen. The end product of sulphate reduction, hydrogen sulphide can be formed by bacterial species such as Desulfovibrio piger (Reference Marquet, Duncan and Chassard27) and can inhibit butyrate metabolism and is therefore highly toxic to the colonic mucosa(Reference Attene-Ramos, Wagner and Gaskins81). This bacterial metabolic product can also inhibit colonic smooth muscle contractility(Reference Yao, Muir and Gibson55). Hydrogen sulphide is produced by fermentation of sulphur-containing amino acids, such as methionine and cysteine which is also derived from the reduction of inorganic sulphate and sulphite additives, and the catabolism of intestinal sulphomucins.

Ammonia and other nitrogenous bacterial metabolites

Peptides and amino acids are metabolised by gut bacteria following deamination and decarboxylation to several metabolites including ammonia, polyamines, phenols and indoles. Ammonia is generally found at millimolar concentrations in the large intestine and concentrations increase from the ascending to the descending colon, which is consistent with a higher rate of protein metabolism in the distal compared to the proximal colon. The ammonia concentration in the large intestine is mainly a microbial metabolite associated with amino acid deamination and urea hydrolysis. Intestinal microbiota can use ammonia, and ammonia can also be absorbed by the epithelial cells. Urea hydrolysis in the intestinal lumen is performed via bacteria urease activities which are better understood in ruminants than in human subjects(Reference Wallace82). A reduction in urease activity will result in a reduction in blood ammonia levels which is beneficial to health as high levels of ammonia have been linked to encephalopathy(Reference Jin, Singh and Chung83). Nitrosamines are known carcinogens and can be detected in human faeces. Gastric formation of nitrosamines has been well described in human subjects and the involvement of the microbiota has been demonstrated by comparing germ-free and conventional rats(Reference Massey, Key and Mallett84). Several bacterial species are capable of nitrosamine production including species belonging to Proteobacteria(Reference Matsui, Nagai and Suzuki85,Reference Suzuki and Mitsuoka86) .

The bacterial deamination of aromatic amino acids leads to the production of phenolic compounds and tyrosine deamination mainly yields phenol and p-cresol. The main food sources of tyrosine are egg, cod, seaweed and cheese and an increase of the nutritional protein load in healthy individuals principally results in greater urinary excretion of p-cresol. An example of possible health impacts is that the tryptophan metabolite indole-3-propionic acid, which has been shown to be a potent anti-non-alcoholic steatohepatitis microbial metabolite in preclinical models(Reference Del Bo, Bernardi and Marino87).

Polyamines are biogenic amines involved in host cell growth and differentiation and are produced by bacterial metabolism of species belonging to several genera including Bacteroides, Lactobacillus, Veillonella, Bifidobacterium and Clostridium. These bacteria can produce polyamines including putrescine, cadaverine, tyramine and histamine following the metabolism of amino acids including arginine, ornithine, lysine, tyrosine, histidine and methionine(Reference Zhao, Xin and Xue88). Preclinical studies have shown that putrescine and spermidine in the colon are dependent on colonic microbiota(Reference Noack, Kleessen and Proll89) and that pectin fermentation by B. thetaiotaomicron and Fusobacterium varium stimulated polyamine production. Microbial synthesis of polyamines is considered as a therapeutic target(Reference Gerner and Meyskens90), but there is limited information from human intervention studies on the impact of diet.

Regular consumption of cooked or processed meat can increase the risk of colon cancer and heterocyclic amines, such as 2-amino-1-methyl-6-phenylimidazo [4,5-b] pyridine, are considered to be a contributing factor. There is some evidence that the gut microbiota and, in particular, the most abundant carcinogenic heterocyclic amine, 2-amino-1-methyl-6-phenylimidazo [4,5-b] pyridine, can be transformed by representatives of the phyla Firmicutes, Bacteroidetes and Proteobacteria(Reference Zhang, Lacroix and Wortmann91). Similarly, the genotoxicity of mutagen 2-amino-3-methylimidazo[4,5-f]quinoline was impacted on by the gut microbiota(Reference Kassie92).

Human dietary protein studies

High levels of proteins and peptides in the large intestine could lead to increased production of deleterious metabolites. Magee et al.(Reference Magee, Richardson and Hughes93) reported that when subjects were fed a high-protein diet, the levels of sulphide were elevated due to the bacterial fermentation of sulphur-containing amino acids. Butyrate concentrations and numbers of butyrate-producing bacteria are decreased in the large intestine as well in the faeces(Reference Duncan, Louis and Flint20). It is widely regarded that butyrate is the main energy source for colonic epithelial cell; thus, a decrease in butyrate concentration and an increase in concentrations of ammonia and sulphide may explain the detrimental effect of high protein diet on the large intestine (e.g. increased incidence of colon cancer).

Consumption of red meat is often considered to have negative health outcomes; however, it is perhaps important to take into consideration the intakes, levels of processing and other dietary factors. The consumption of high-quality red meat is poorly associated with diabetes risk and CHD for a serving of 100 g red meat daily. In contrast, higher risks were observed for processed meat consumption with an increased incidence of colorectal cancer (by 22 %), heart disease (by 42 %) and type 2 diabetes (by 19 %)(Reference Mozaffarian94,Reference Micha, Wallace and Mozaffarian95) . Moreover, there were no associations with stroke for any of the meat-type products. Processed meats tend to contain higher sodium levels which may worsen cardiovascular conditions over habitual intake. The links between red meat and poorer health outcomes may therefore be confounded by the effects of processing. Higher plant protein intake and a lower intake of some animal-based protein sources may contribute to the lower risk of disease associated with vegetarian diets. It maybe however that the benefits of high plant protein intakes are linked to other nutrients.

The protein intake of children in western countries is very high and the average protein intake in children between 4 and 6 years old is about 55 g/d. In infants where energy, protein and amino acid requirements are high, protein requirements are primarily met by intakes of human milk and infant formula. It is not clear if the protein requirements of older adults are higher than that of younger adults or are only higher in the frail elderly who are at risk of malnutrition because of acute or chronic illness.

Vegetarians exclude meat and fish from their diets and therefore there is a gradient of protein intake from meat eaters to vegans in western countries. In general, the adult population in western countries have a protein intake of about 1⋅3/kg/d which is about twice the estimated average requirement of 0⋅66 g/kg/d although a proportion of lacto-ovo-vegetarians may have protein intakes that do not meet their individual requirements.

It is often considered that amino acids may be inadequate in vegetarian diets although almost all plant-based foods contain all twenty amino acids, including the nine indispensable amino acids. The distribution profile of the amino acids however is less optimal in plant foods than in animal foods with lysine often being present in much lower than optimal proportions for human needs in grains. Also, the sulphur-containing amino acids, methionine and cysteine, are proportionally slightly lower in legumes than would be optimal for human needs. Mixing complementary protein sources within the same meal however may simply be a practical way to secure long-term adequacy when total protein intake is low.

Meat consumers were found to have the lowest fibre intake of <10 g daily and lower PUFA consumption. Inadequacies for folate intake were also reported. However, the corresponding intake of micronutrients was found to be the highest for this group for zinc, phosphorus and vitamin B12. Iron intake was found to be inadequate in the case of women. Vegetarians were found to comply with most dietary requirements and among the three groups and have a fibre intake of approximately 33 % greater than meat-eaters. Vegans however were found to have a fibre intake which was 75 % greater than the meat-eating group and had mineral and micronutrient intake values similar to those observed in vegetarians. For people consuming plant-based diets, further scientific evidence is required to determine if the protein intakes of vegetarian and vegan diets are adequate(Reference Agnoli, Baroni and Bertini96). The amino acid requirements are therefore considered to be adequately met for vegetarian diets although some inadequacies were observed in the Adventist study population data which may have likely risen from over dependence on a few protein sources(Reference Rizzo, Sabate and Jaceldo-Siegl97).

Ten different diets were compared and based on average consumption of various plant and animal products consumed, in a Swiss study. Diets high in animal products were found to be detrimental to health and the environment, although this model failed to consider micronutrient intake which may affect long-term population health.

Across the Nutri-Santé and Oxford EPIC studies(Reference Mariotti and Gardner98,Reference Gluba-Brzózka, Franczyk and Rysz99) , protein intake followed the expected trend of meat eaters > pescatarians > vegetarians > vegans. Furthermore, the drop in protein intake across each group was approximately 0⋅1 g/kg body weight (translating to about 1⋅2 % protein with meat eaters having an intake of about 1⋅2 g/kg body weight). It is common in high-income countries to have diets with a protein contribution >15 % in the daily energy requirement. Vegans who form the baseline for an animal-free diet were found to consume 0⋅99 g protein/kg body weight in previously published studies. Given the minimum protein requirement to initiate anabolism is 30 g daily for a 70 kg person (translating to about 10 % of energy intake or 0⋅8 g/kg body weight), protein intake appears to be adequate across all diets. The average contribution to energy from protein across various food groups is shown in Fig. 2.

Fig. 2. Relative contribution of protein to energy for a range of food group from FAOSTAT Database (2020)(Reference Gennari, Seid and Sorrenti118). Lines refer to the mean energy contribution of protein in plant- and animal-derived foods.

Food security

There is considerable interest in the impact of plant-based diets on the environment(Reference Sabaté, Sranacharoenpong and Harwatt100Reference Röös, Bajželj and Smith102). Current insecurities around food production stem from the inefficiencies of food distribution, poor intensification strategies, water use and waste management(Reference Fitton, Alexander and Arnell103Reference Mueller, Gerber and Johnston105). The allocation of resources towards protein production is currently centred towards animal husbandry as the relative price of animal produce is about ten times higher than most plant products. The Scottish land mass is predominantly marginal owing to its hilly terrain. Consequently, the nature of agriculture favours animal rearing rather than high-intensity cropping (Fig. 3). For sustaining a given population, about 0⋅2 ha of land is required per individual(Reference Myers106), which implies a land mass of 1⋅1 × 106 ha capable of high-intensity cropping. Existing capable land in Scotland is about 6 × 105 ha which is about 45 % lower than required. Animal husbandry is therefore important to ensure sustained food supply. Moreover, climatic conditions make it difficult to cultivate a variety of vegetables which are often imported from countries with favourable conditions.

Fig. 3. Protein production from Scottish agriculture (119,120) . Left panel accounts for protein from major animal- and plant-based produce. The right panel compares the land allocation for the animal- and plant-based agriculture and the corresponding production of protein from these sources, respectively.

The emissions associated with agriculture in Scotland are shown in Fig. 4. Greenhouse gas emissions of food production as a share of anthropogenic emissions are comparable to global averages. However, satisfying the indigenous nutritional requirement is mostly dependent on meat. In terms of carbon efficiency in Scotland, 1 kg protein produced from animal sources results in an emission of 102⋅4 kg CO2 eq. while plant protein results in 13⋅5 kg CO2 eq. The average food prices in Scotland are relatively higher than global averages(Reference Barton, Wrieden and Armstrong107), diversity in diet is low, dependency on imports is high, and consequently, food security and environmental impact of food production is significant.

Fig. 4. Scottish anthropogenic emissions(121).

The WHO healthy plate guideline aims to recommend foods which meet nutritional requirements as well as ensuring low greenhouse gas emissions. These recommendations do not account for real-world wastage of food in common households, which was estimated to contribute about 9 % of total household dietary emissions(Reference Xue, Liu and Parfitt108). Furthermore, the single largest contributor to dietary emissions comes from animal products and in particular red meat. In India, for example, the contribution from red meat consumption among non-vegetarians is negligible, and consequently leading to a dietary per capita emission of 757 kg CO2 eq. per annum compared to the WHO healthy diet (1288 kg CO2 eq.)(Reference Ritchie, Reay and Higgins109). This can be explained by the unique reliance on pulses, fish and poultry to obtain nutrition which saved about 20 % of emissions. Current research is aimed at meat replacements(Reference Joshi and Kumar110,Reference Multari, Stewart and Russell111) and reducing enteric emissions by altering diet and gut composition of ruminants(Reference Basarab, Beauchemin and Baron112,Reference Matthews, Crispie and Lewis113) , but sustainable long-term solutions are mostly directed towards locally sourced, low red-meat high plant diets(Reference Chen, Chaudhary and Mathys114). Climate change affects food availability either by directly disrupting crop growth through unfavourable conditions or through altering crop quality due to increased atmospheric CO2 levels(Reference Fernando, Panozzo and Tausz115). Smith and Myers(Reference Smith and Myers116) established a close linear relation between protein and mineral content in plant-based diets in low-income countries which is not observed in animal-based products where mineral composition is relatively independent of the protein content. Paradoxically, WHO-recommended diet to mitigate nutrient deficiency relies on supplementation using animal products which of course adds to emissions(Reference Ritchie, Reay and Higgins117).

Conclusions

Dietary protein is metabolised by proteases and peptidases in the human small intestine, and the released amino acids from dietary protein can be used for protein synthesis by gut microbes. This contributes to the nitrogen cycling and utilisation between the microbiota and host. Moreover, the undigested protein and amino acids are mainly fermented into various bacterial metabolites, such as SCFA, hydrogen sulphide, ammonia and other nitrogenous and aromatic metabolites. Some of these bacterial metabolites can be transported inside colonocytes and exert beneficial or deleterious effects. These effects might be attributed to the modulation of the intestinal barrier function and immune defence by the altered gut microbiota. Further studies will be necessary to elucidate the relationship between dietary protein and gut microbiota as well as the interaction of microbial function and host health. This becomes increasingly important with a changing agricultural landscape addressing sustainability in our food system and transition to a more circular economy.

Acknowledgements

We would like to thank Pat Bain for help in preparing Fig. 1.

Financial Support

The Rowett Institute is funded by the Scottish Government Rural ad Environmental Sciences and Analytical Services (SG-RESAS).

Conflict of Interest

None.

Authorship

The authors had joint responsibility for all aspects of preparation of the paper.

References

Walker, AW, Duncan, SH, Louis, P et al. (2014) Phylogeny, culturing, and metagenomics of the human gut microbiota. Trends Microbiol 22, 267274.CrossRefGoogle ScholarPubMed
Lapébie, P, Lombard, V, Drula, E et al. (2019) Bacteroidetes use thousands of enzyme combinations to break down glycans. Nat Commun 10, 2043.CrossRefGoogle ScholarPubMed
Louis, P & Flint, HJ (2017) Formation of propionate and butyrate by the human colonic microbiota. Environ Microbiol 19, 2941.CrossRefGoogle ScholarPubMed
Scott, KP, Gratz, SW, Sheridan, PO et al. (2013) The influence of diet on the gut microbiota. Pharma Res 69, 5260.CrossRefGoogle ScholarPubMed
Flint, HJ, Scott, KP, Louis, P et al. (2012) The role of the gut microbiota in nutrition and health. Nat Rev Gastroenterol Hepatol 9, 577589.CrossRefGoogle ScholarPubMed
Smith, P & Gregory, PJ (2013) Climate change and sustainable food production. Proc Nutr Soc 72, 2128.CrossRefGoogle ScholarPubMed
Goodrich, JK, Davenport, ER, Beaumont, M et al. (2016) Genetic determinants of the gut microbiome in UK twins. Cell Host Microbe 19, 731743.CrossRefGoogle ScholarPubMed
Wu, GD, Chen, J, Hoffmann, C et al. (2011) Linking long-term dietary patterns with gut microbial enterotypes. Science 334, 105108.CrossRefGoogle ScholarPubMed
Wang, YT, Mohammed, SD, Farmer, AD et al. (2015) Regional gastrointestinal transit and pH studied in 215 healthy volunteers using the wireless motility capsule: influence of age, gender, study country and testing protocol. Aliment Pharmacol Ther 42, 761772.CrossRefGoogle ScholarPubMed
Abuhelwa, AY, Foster, DJR & Upton, RN (2016) A quantitative review and meta-models of the variability and factors affecting oral drug absorption – part I: gastrointestinal pH. AAPS J 18, 13091321.CrossRefGoogle ScholarPubMed
Macfarlane, S & Macfarlane, GT (2003) Regulation of short-chain fatty acid production. Proc Nutr Soc 62, 6772.CrossRefGoogle ScholarPubMed
Johnson, AJ, Vangay, P, Al-Ghalith, GA et al. (2019) Daily sampling reveals personalized diet-microbiome associations in humans. Cell Host Microbe 25, 789802.e5.CrossRefGoogle ScholarPubMed
Cummings, JH & Macfarlane, GT (1991) The control and consequences of bacterial fermentation in the human colon. J Appl Bacteriol 70, 443459.CrossRefGoogle ScholarPubMed
Columpsi, P, Sacchi, P, Zuccaro, V et al. (2016) Beyond the gut bacterial microbiota: the gut virome. J Med Virol 88, 14671472.CrossRefGoogle ScholarPubMed
Hofer, U (2013) Variation in the gut virome. Nat Rev Microbiol 11, 596596.Google ScholarPubMed
Gouba, N, Raoult, D & Drancourt, M (2014) Eukaryote culturomics of the gut reveals new species. PLoS ONE 11, e106994.CrossRefGoogle Scholar
Zoetendal, EG, Raes, J, van den Bogert, B et al. (2012) The human small intestinal microbiota is driven by rapid uptake and conversion of simple carbohydrates. ISME J 6, 14151426.CrossRefGoogle ScholarPubMed
Bäckhed, F, Ley, RE, Sonnenburg, JL et al. (2005) Host-bacterial mutualism in the human intestine. Science 307, 19151920.CrossRefGoogle ScholarPubMed
Qin, J, Li, R, Raes, J et al. (2010) A human gut microbial gene catalogue established by metagenomic sequencing. Nature 464, 5965.CrossRefGoogle ScholarPubMed
Duncan, SH, Louis, P & Flint, HJ (2007) Cultivable bacterial diversity from the human colon. Lett Appl Microbiol 44, 343350.CrossRefGoogle ScholarPubMed
Derrien, M, Vaughan, EE, Plugge, CM et al. (2004) Akkermansia muciniphila gen. nov., sp. nov., a human intestinal mucin-degrading bacterium. Int J Syst Evol Microbiol 54, 14691476.CrossRefGoogle ScholarPubMed
Macy, JM & Probst, I (1979) The biology of gastrointestinal Bacteroides. Annu Rev Microbiol 33, 561594.CrossRefGoogle ScholarPubMed
Salyers, AA, Vercellotti, JR, West, SE et al. (1977) Fermentation of mucin and plant polysaccharides by strains of Bacteroides from the human colon. Appl Environ Microbiol 33, 319322.CrossRefGoogle ScholarPubMed
Neish, AS (2002) The gut microflora and intestinal epithelial cells: a continuing dialogue. Microbes Infect 4, 309317.CrossRefGoogle ScholarPubMed
Isolauri, E, Kirjavainen, PV & Salminen, S (2002) Probiotics: a role in the treatment of intestinal infection and inflammation? Gut 50(Suppl. 3), 5459.CrossRefGoogle ScholarPubMed
Lopez-Siles, M, Khan, TM, Duncan, SH et al. (2012) Cultured representatives of two major phylogroups of human colonic Faecalibacterium prausnitzii can utilize pectin, uronic acids, and host-derived substrates for growth. Appl Environ Microbiol 78, 420428.CrossRefGoogle ScholarPubMed
Marquet, P, Duncan, SH, Chassard, C et al. (2009) Lactate has the potential to promote hydrogen sulphide formation in the human colon. FEMS Microbiol Lett 299, 128134.CrossRefGoogle ScholarPubMed
O'Toole, PW & Jeffery, IB (2015) Gut microbiota and aging. Science 350, 12141215.CrossRefGoogle ScholarPubMed
Eckburg, PB, Bik, EM, Bernstein, CN et al. (2005) Diversity of the human intestinal microbial flora. Science 308, 16351638.CrossRefGoogle ScholarPubMed
Khan, MT, Duncan, SH, Stams, AJM et al. (2012) The gut anaerobe Faecalibacterium prausnitzii uses an extracellular electron shuttle to grow at oxic–anoxic interphases. ISME J 6, 15781585.CrossRefGoogle ScholarPubMed
Walker, AW, Duncan, SH, McWilliam Leitch, EC et al. (2005) Ph and peptide supply can radically alter bacterial populations and short-chain fatty acid ratios within microbial communities from the human colon. Appl Environ Microbiol 71, 36923700.CrossRefGoogle ScholarPubMed
Flint, HJ & Duncan, SH (2014) Bacteroides and Prevotella. In Encyclopedia of Food Microbiology, 2nd ed., pp. 203208 [Batt, CA and Tortorello, ML, editors]. [Internet]. Oxford: Academic Press. Available at http://www.sciencedirect.com/science/article/pii/B9780123847300000318.CrossRefGoogle Scholar
Flint, HJ (2020) Why Gut Microbes Matter: Understanding Our Microbiome. Cham: Springer International Publishing (Fascinating Life Sciences). Available at http://link.springer.com/10.1007/978-3-030-43246-1.CrossRefGoogle Scholar
Ridlon, JM, Harris, SC, Bhowmik, S et al. (2016) Consequences of bile salt biotransformations by intestinal bacteria. Gut Microbes 7, 2239.CrossRefGoogle ScholarPubMed
Dominguez-Bello, MG, Costello, EK, Contreras, M et al. (2010) Delivery mode shapes the acquisition and structure of the initial microbiota across multiple body habitats in newborns. Proc Natl Acad Sci 107, 1197111975.CrossRefGoogle ScholarPubMed
Duncan, SH & Flint, HJ (2013) Probiotics and prebiotics and health in ageing populations. Maturitas 75, 4450.CrossRefGoogle ScholarPubMed
David, LA, Maurice, CF, Carmody, RN et al. (2014) Diet rapidly and reproducibly alters the human gut microbiome. Nature 505, 559563.CrossRefGoogle ScholarPubMed
van Best, N, Rolle-Kampczyk, U, Schaap, FG et al. (2020) Bile acids drive the newborn's gut microbiota maturation. Nat Commun 11, [Epublication 23 July 2020].CrossRefGoogle ScholarPubMed
Timmerman, HM, Rutten, NBMM, Boekhorst, J et al. (2017) Intestinal colonisation patterns in breastfed and formula-fed infants during the first 12 weeks of life reveal sequential microbiota signatures. Sci Rep 7, [Epublication 21 August 2020].CrossRefGoogle ScholarPubMed
Vandenplas, Y, Carnielli, VP, Ksiazyk, J et al. (2020) Factors affecting early-life intestinal microbiota development. Nutrition 78, [Epublication 25 March 2020].CrossRefGoogle ScholarPubMed
Praveen, P, Jordan, F, Priami, C et al. (2015) The role of breast-feeding in infant immune system: a systems perspective on the intestinal microbiome. Microbiome 3, 41.CrossRefGoogle ScholarPubMed
Flint, HJ, Scott, KP, Duncan, SH et al. (2012) Microbial degradation of complex carbohydrates in the gut. Gut Microbes 3, 289306.CrossRefGoogle Scholar
Leeming, ER, Johnson, AJ, Spector, TD et al. (2019) Effect of diet on the gut microbiota: rethinking intervention duration. Nutrients 11, [Epublication 22 November 2020].CrossRefGoogle ScholarPubMed
Harmsen, HJM, Wildeboer-Veloo, ACM, Raangs, GC et al. (2000) Analysis of intestinal flora development in breast-fed and formula-fed infants by using molecular identification and detection methods. J Pediatr Gastroenterol Nutr 30, 6167.CrossRefGoogle ScholarPubMed
Jeffery, IB, Claesson, MJ, O'Toole, PW et al. (2012) Categorization of the gut microbiota: enterotypes or gradients? Nat Rev Microbiol 10, 591592.CrossRefGoogle ScholarPubMed
Booijink, CCGM, El-Aidy, S, Rajilić-Stojanović, M et al. (2010) High temporal and inter-individual variation detected in the human ileal microbiota. Environ Microbiol 12, 32133227.CrossRefGoogle ScholarPubMed
Soto-Martin, EC, Warnke, I, Farquharson, FM et al. (2020) Vitamin biosynthesis by human gut butyrate-producing bacteria and cross-feeding in synthetic microbial communities. mBio 11, (article no. e00886-20), 118.CrossRefGoogle ScholarPubMed
Ze, X, Ben David, Y, Laverde-Gomez, JA et al. (2015) Unique organization of extracellular amylases into amylosomes in the resistant starch-utilizing human colonic Firmicutes bacterium Ruminococcus bromii. mBio 6, e01058-15.CrossRefGoogle ScholarPubMed
Caffall, KH & Mohnen, D (2009) The structure, function, and biosynthesis of plant cell wall pectic polysaccharides. Pectin Struct Funct 344, 18791900.Google ScholarPubMed
Chung, WSF, Meijerink, M, Zeuner, B et al. (2017) Prebiotic potential of pectin and pectic oligosaccharides to promote anti-inflammatory commensal bacteria in the human colon. FEMS Microbiol Ecol 93, [Epublication 3 October 2017].CrossRefGoogle ScholarPubMed
Chung, WSF, Walker, AW, Vermeiren, J et al. (2018) Impact of carbohydrate substrate complexity on the diversity of the human colonic microbiota. FEMS Microbiol Ecol 95, [Epublication 9 October 2018].Google Scholar
Nordström, C (1972) Release of enteropeptidase and other brush-border enzymes from the small intestinal wall in the rat. Biochim Biophys Acta BBA – Enzymol 289, 367377.CrossRefGoogle ScholarPubMed
Russell, WR, Hoyles, L, Flint, HJ et al. (2013) Colonic bacterial metabolites and human health. Curr Opin Microbiol 16, 246254.CrossRefGoogle ScholarPubMed
Smith, EA & Macfarlane, GT (1997) Formation of phenolic and indolic compounds by anaerobic bacteria in the human large intestine. Microb Ecol 33, 180188.CrossRefGoogle ScholarPubMed
Yao, CK, Muir, JG & Gibson, PR (2016) Review article: insights into colonic protein fermentation, its modulation and potential health implications. Aliment Pharmacol Ther 43, 181196.CrossRefGoogle ScholarPubMed
Johnstone, AM, Horgan, GW, Murison, SD et al. (2008) Effects of a high-protein ketogenic diet on hunger, appetite, and weight loss in obese men feeding ad libitum. Am J Clin Nutr 87, 4455.CrossRefGoogle ScholarPubMed
Kim, E, Coelho, D & Blachier, F (2013) Review of the association between meat consumption and risk of colorectal cancer. Nutr Res 33, 983994.CrossRefGoogle ScholarPubMed
Neis, E, Dejong, C & Rensen, S (2015) The role of microbial amino acid metabolism in host metabolism. Nutrients 7, 29302946.CrossRefGoogle ScholarPubMed
Dai, Z-L (2011) Amino acid metabolism in intestinal bacteria: links between gut ecology and host health. Front Biosci 16, 17681786.CrossRefGoogle ScholarPubMed
McIntosh, FM, Shingfield, KJ, Devillard, E et al. (2009) Mechanism of conjugated linoleic acid and vaccenic acid formation in human faecal suspensions and pure cultures of intestinal bacteria. Microbiology 155, 285294.CrossRefGoogle ScholarPubMed
Smith, EA & Macfarlane, GT (1997) Dissimilatory amino acid metabolism in human colonic bacteria. Anaerobe 3, 327337.CrossRefGoogle ScholarPubMed
Davila, A-M, Blachier, F, Gotteland, M et al. (2013) Intestinal luminal nitrogen metabolism: role of the gut microbiota and consequences for the host. Pharmacol Res 68, 95107.CrossRefGoogle ScholarPubMed
Macfarlane, GT, Allison, C, Gibson, SAW et al. (1988) Contribution of the microflora to proteolysis in the human large intestine. J Appl Bacteriol 64, 3746.CrossRefGoogle ScholarPubMed
Sánchez-Jiménez, F, Ruiz-Pérez, MV, Urdiales, JL et al. (2013) Pharmacological potential of biogenic amine-polyamine interactions beyond neurotransmission: amine interplay beyond neurotransmission. Br J Pharmacol 170, 416.CrossRefGoogle Scholar
Nissim, I, Horyn, O, Daikhin, Y et al. (2014) The molecular and metabolic influence of long term agmatine consumption. J Biol Chem 289, 97109729.CrossRefGoogle ScholarPubMed
Hughes, R, Magee, EAM & Bingham, S (2000) Protein degradation in the large intestine. Curr Issues Intest Microbiol 1, 5158.Google ScholarPubMed
Duncan, SH, Louis, P & Flint, HJ (2004) Lactate-utilizing bacteria, isolated from human feces, that produce butyrate as a major fermentation product. Appl Environ Microbiol 70, 58105817.CrossRefGoogle ScholarPubMed
Louis, P, Scott, KP, Duncan, SH et al. (2007) Understanding the effects of diet on bacterial metabolism in the large intestine. J Appl Microbiol 102, 11971208.CrossRefGoogle ScholarPubMed
Barcenilla, A, Pryde, SE, Martin, JC et al. (2000) Phylogenetic relationships of butyrate-producing bacteria from the human gut. Appl Environ Microbiol 66, 16541661.CrossRefGoogle ScholarPubMed
Duncan, SH, Hold, GL, Harmsen, HJM et al. (2002) Growth requirements and fermentation products of Fusobacterium prausnitzii, and a proposal to reclassify it as Faecalibacterium prausnitzii gen. nov., comb. nov. Int J Syst Evol Microbiol 52, 21412146.Google Scholar
Pryde, SE, Duncan, SH, Hold, GL et al. (2002) The microbiology of butyrate formation in the human colon. FEMS Microbiol Lett 217, 133139.CrossRefGoogle ScholarPubMed
Hamer, HM, Jonkers, D, Venema, K et al. (2007) Review article: the role of butyrate on colonic function. Aliment Pharmacol Ther 27, 104119.CrossRefGoogle ScholarPubMed
Scheppach, W (1994) Effects of short chain fatty acids on gut morphology and function. Gut 35(1 Suppl.), S35S38.CrossRefGoogle ScholarPubMed
Lewis, SJ & Heaton, KW (1997) Increasing butyrate concentration in the distal colon by accelerating intestinal transit. Gut 41, 245251.CrossRefGoogle ScholarPubMed
Tolhurst, G, Heffron, H, Lam, YS et al. (2012) Short-chain fatty acids stimulate glucagon-like peptide-1 secretion via the G-protein-coupled receptor FFAR2. Diabetes 61, 364371.CrossRefGoogle ScholarPubMed
Chambers, ES, Viardot, A, Psichas, A et al. (2015) Effects of targeted delivery of propionate to the human colon on appetite regulation, body weight maintenance and adiposity in overweight adults. Gut 64, 17441754.CrossRefGoogle Scholar
Yang, J, Martínez, I, Walter, J et al. (2013) In vitro characterization of the impact of selected dietary fibers on fecal microbiota composition and short chain fatty acid production. Anaerobe 23, 7481.CrossRefGoogle ScholarPubMed
Louis, P, Duncan, SH, McCrae, SI et al. (2004) Restricted distribution of the butyrate kinase pathway among butyrate-producing bacteria from the human colon. J Bacteriol 186, 20992106.CrossRefGoogle ScholarPubMed
Bui, TPN, de Vos, WM & Plugge, CM (2014) Anaerostipes rhamnosivorans sp. Nov., a human intestinal, butyrate-forming bacterium. Int J Syst Evol Microbiol 64, 787793.CrossRefGoogle ScholarPubMed
Ueki, A, Goto, K, Ohtaki, Y et al. (2017) Description of Anaerotignum aminivorans Gen. Nov., sp. Nov., a strictly anaerobic, amino-acid-decomposing bacterium isolated from a methanogenic reactor, and reclassification of Clostridium propionicum, Clostridium neopropionicum and Clostridium lactatifermentans as species of the genus Anaerotignum. Int J Syst Evol Microbiol 67, 41464153.CrossRefGoogle ScholarPubMed
Attene-Ramos, MS, Wagner, ED, Gaskins, HR et al. (2007) Hydrogen sulfide induces direct radical-associated DNA damage. Mol Cancer Res 5, 455459.CrossRefGoogle ScholarPubMed
Wallace, RJ (1996) Ruminal microbial metabolism of peptides and amino acids. J Nutr 126(Suppl. 4), 1326S1334S.CrossRefGoogle ScholarPubMed
Jin, Y, Singh, P, Chung, H-J et al. (2018) Blood ammonia as a possible etiological agent for Alzheimer's disease. Nutrients 10, [Epublication 4 May 2018].CrossRefGoogle ScholarPubMed
Massey, RC, Key, PE, Mallett, AK et al. (1988) An investigation of the endogenous formation of apparent total N-nitroso compounds in conventional microflora and germ-free rats. Food Chem Toxicol 26, 595600.CrossRefGoogle ScholarPubMed
Matsui, M, Nagai, F, Suzuki, E et al. (1984) Structure-activity relationships of nitrosamines and nitramines which stimulate UDP-glucuronosyltransferase activities in vitro. Biochem Pharmacol 33, 26472651.CrossRefGoogle ScholarPubMed
Suzuki, K & Mitsuoka, T (1984) N-nitrosamine formation by intestinal bacteria. IARC Sci Publ 57, 275281.Google Scholar
Del Bo, C, Bernardi, S, Marino, M et al. (2019) Systematic review on polyphenol intake and health outcomes: Is there sufficient evidence to define a health-promoting polyphenol-rich dietary pattern? Nutrients 11, [Epublication 16 June 2017].Google ScholarPubMed
Zhao, Z-H, Xin, F-Z, Xue, Y et al. (2019) Indole-3-propionic acid inhibits gut dysbiosis and endotoxin leakage to attenuate steatohepatitis in rats. Exp Mol Med 51, 114.Google ScholarPubMed
Noack, J, Kleessen, B, Proll, J et al. (1998) Dietary guar gum and pectin stimulate intestinal microbial polyamine synthesis in rats. J Nutr 128, 13851391.CrossRefGoogle ScholarPubMed
Gerner, EW & Meyskens, FL (2009) Combination chemoprevention for colon cancer targeting polyamine synthesis and inflammation. Clin Cancer Res 15, 758761.CrossRefGoogle ScholarPubMed
Zhang, J, Lacroix, C, Wortmann, E et al. (2019) Gut microbial beta-glucuronidase and glycerol/diol dehydratase activity contribute to dietary heterocyclic amine biotransformation. BMC Microbiol 19, [Epublication 16 May 2019].CrossRefGoogle ScholarPubMed
Kassie, F (2001) Intestinal microflora plays a crucial role in the genotoxicity of the cooked food mutagen 2-amino-3-methylimidazo[4,5-f]quinoline (IQ). Carcinogenesis 22, 17211725.CrossRefGoogle Scholar
Magee, EA, Richardson, CJ, Hughes, R et al. (2000) Contribution of dietary protein to sulfide production in the large intestine: an in vitro and a controlled feeding study in humans. Am J Clin Nutr 72, 14881494.CrossRefGoogle Scholar
Mozaffarian, D (2016) Dietary and policy priorities for cardiovascular disease, diabetes and obesity. Circulation 133, 187225.CrossRefGoogle ScholarPubMed
Micha, R, Wallace, SK & Mozaffarian, D (2010) Red and processed meat consumption and risk of incident coronary heart disease, stroke, and diabetes mellitus: a systematic review and meta-analysis. Circulation 121, 22712283.CrossRefGoogle ScholarPubMed
Agnoli, C, Baroni, L, Bertini, I et al. (2017) Position paper on vegetarian diets from the working group of the Italian society of human nutrition. Nutr Metab Cardiovasc Dis 27, 10371052.CrossRefGoogle Scholar
Rizzo, NS, Sabate, J, Jaceldo-Siegl, K et al. (2011) Vegetarian dietary patterns are associated with a lower risk of metabolic syndrome: the Adventist health study 2. Diabetes Care 34, 12251227.CrossRefGoogle ScholarPubMed
Mariotti, F & Gardner, CD (2019) Dietary protein and amino acids in vegetarian diets – a review. Nutrients 11, 119.CrossRefGoogle ScholarPubMed
Gluba-Brzózka, A, Franczyk, B & Rysz, J (2017) Vegetarian diet in chronic kidney disease – a friend or foe. Nutrients 9, [Epublication 10 April 2017].CrossRefGoogle ScholarPubMed
Sabaté, J, Sranacharoenpong, K, Harwatt, H et al. (2015) The environmental cost of protein food choices. Public Health Nutr 18, 20672073.CrossRefGoogle ScholarPubMed
Hedenus, F, Wirsenius, S & Johansson, DJA (2014) The importance of reduced meat and dairy consumption for meeting stringent climate change targets. Clim Change 124, 7991.CrossRefGoogle Scholar
Röös, E, Bajželj, B, Smith, P et al. (2017) Protein futures for Western Europe: potential land use and climate impacts in 2050. Reg Environ Change 17, 367377.CrossRefGoogle Scholar
Fitton, N, Alexander, P, Arnell, N et al. (2019) The vulnerabilities of agricultural land and food production to future water scarcity. Glob Environ Change 58, 101944.CrossRefGoogle Scholar
Brears, RC (2015) The circular economy and the water-food nexus. Future Food: J Food Agric Soc 4, 7374.Google Scholar
Mueller, ND, Gerber, JS, Johnston, M et al. (2012) Closing yield gaps through nutrient and water management. Nature 490, 5457.CrossRefGoogle ScholarPubMed
Myers, N (2000) The new millennium: an ecology and an economy of hope. Curr Sci 78, 686693.Google Scholar
Barton, KL, Wrieden, WL, Armstrong, J et al. (2011) Energy density of the Scottish diet: analysis from the expenditure and food survey. Proc Nutr Soc 70, E26.CrossRefGoogle Scholar
Xue, L, Liu, G, Parfitt, J et al. (2017) Missing food, missing data? A critical review of global food losses and food waste data. Environ Sci Technol 51, 66186633.CrossRefGoogle Scholar
Ritchie, H, Reay, DS & Higgins, P (2018) Beyond calories: a holistic assessment of the global food system. Front Sustain Food Syst 2, [Epublication14 September 2018].CrossRefGoogle Scholar
Joshi, V & Kumar, S (2015) Meat analogues: plant based alternatives to meat products – a review. Int J Food Ferment Technol 5, 107.CrossRefGoogle Scholar
Multari, S, Stewart, D & Russell, WR (2015) Potential of fava bean as future protein supply to partially replace meat intake in the human diet. Compr Rev Food Sci Food Saf 14, 511522.CrossRefGoogle Scholar
Basarab, JA, Beauchemin, KA, Baron, VS et al. (2013) Reducing GHG emissions through genetic improvement for feed efficiency: effects on economically important traits and enteric methane production. Animal: Int J Anim Biosci 7(Suppl. 2), 303315.CrossRefGoogle ScholarPubMed
Matthews, C, Crispie, F, Lewis, E et al. (2019) The rumen microbiome: a crucial consideration when optimising milk and meat production and nitrogen utilisation efficiency. Gut Microbes 10, 115132.CrossRefGoogle ScholarPubMed
Chen, C, Chaudhary, A & Mathys, A (2019) Dietary change scenarios and implications for environmental, nutrition, human health and economic dimensions of food sustainability. Nutrients 11, [Epublication 16 April 2020].CrossRefGoogle ScholarPubMed
Fernando, N, Panozzo, J, Tausz, M et al. (2012) Rising atmospheric CO2 concentration affects mineral nutrient and protein concentration of wheat grain. Food Chem 133, 13071311.CrossRefGoogle Scholar
Smith, MR & Myers, SS (2018) Impact of anthropogenic CO2 emissions on global human nutrition. Nat Clim Change 8, 834839.CrossRefGoogle Scholar
Ritchie, H, Reay, DS & Higgins, P (2018) The impact of global dietary guidelines on climate change. Glob Environ Change 49, 4655.CrossRefGoogle Scholar
Gennari, P, Seid, Y, Sorrenti, S et al. (2020) FAOSTAT. Available at http://www.fao.org/faostat/en/#home.Google Scholar
Food Policy and Food Science Service (2016) Amino acid content of food and biological data on proteins. Food and Nutrition Series – Collection FAO. Available at http://www.fao.org/3/ac854t/AC854T00.htm.Google Scholar
UK Government (2018) Agriculture in the United Kingdom data sets. Available at https://www.gov.uk/government/statistical-data-sets/agriculture-in-the-united-kingdom.Google Scholar
Scottish Government (2020) Greenhouse Gas Emissions 2018: Estimates. Scottish Government Statistics. Available at https://www.gov.scot/publications/scottish-greenhouse-gas-emissions-2018/.Google Scholar
Figure 0

Fig. 1. Protein metabolism by colonic bacteria.

Figure 1

Fig. 2. Relative contribution of protein to energy for a range of food group from FAOSTAT Database (2020)(118). Lines refer to the mean energy contribution of protein in plant- and animal-derived foods.

Figure 2

Fig. 3. Protein production from Scottish agriculture (119,120). Left panel accounts for protein from major animal- and plant-based produce. The right panel compares the land allocation for the animal- and plant-based agriculture and the corresponding production of protein from these sources, respectively.

Figure 3

Fig. 4. Scottish anthropogenic emissions(121).