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Review

Optimising Nutrition for Sustainable Pig Production: Strategies to Quantify and Mitigate Environmental Impact

1
School of Agriculture and Food Science, University College Dublin, Belfield, D04 W6F6 Dublin, Ireland
2
School of Veterinary Medicine, University College Dublin, Belfield, D04 W6F6 Dublin, Ireland
*
Author to whom correspondence should be addressed.
Animals 2025, 15(10), 1403; https://doi.org/10.3390/ani15101403
Submission received: 31 March 2025 / Revised: 24 April 2025 / Accepted: 7 May 2025 / Published: 13 May 2025

Simple Summary

Pig farming plays an important role in global food production but faces growing challenges, including rising input costs, environmental pollution, and increasing pressure on natural resources. Life cycle assessment is a useful tool for measuring the environmental impact of food systems and identifying where emissions originate. Feed and manure are the two main sources of emissions in pig farming. Widely used ingredients like soybean meal are linked to deforestation and biodiversity loss in some regions. In cooler climates, locally grown faba beans offer a more sustainable alternative, though their inclusion requires careful management due to its nutritional limitations. Maintaining feed quality is also crucial, as post-harvest losses and contamination can impact productivity and animal health. Preserving grain with organic acids offers a safe, energy-efficient alternative to traditional grain drying, reducing fossil fuel use while maintaining feed safety. Other dietary strategies, such as lowering protein levels, adjusting fibre sources, using feed additives, and supplementing sow diets, can improve digestion, reduce waste, and minimise environmental pollution. Together, these strategies can offer practical, science-based solutions for making pig farming more sustainable and efficient.

Abstract

The intensifying global demand for food presents significant challenges for sustainable pig production, particularly in the context of escalating input costs, environmental degradation, and resource scarcity. Life cycle assessment provides a comprehensive framework for quantifying environmental impacts and identifying production hotspots within pig production systems. Feed production and manure management are consistently identified as major contributors, emphasising the need for targeted interventions. Although soybean meal remains a key protein source, its association with deforestation and biodiversity loss is driving an interest in more sustainable alternatives. In temperate climates, faba beans offer a promising, locally sourced option, though their wider adoption is limited by amino acid imbalances and anti-nutritional factors. Grain preservation is another critical consideration, as post-harvest losses and fungal contamination compromise feed quality and animal health. Organic acid preservation has emerged as an energy-efficient, cost-effective alternative to industrial drying, improving storage stability and reducing fossil fuel dependence. Additional nutritional strategies, including dietary crude protein reduction, carbohydrate source modification, feed additive inclusion, and maternal nutritional interventions, can enhance nutrient utilisation, intestinal health, and herd resilience while mitigating environmental impact. This review explores practical feed-based strategies to support sustainable, resilient, and resource-efficient pig production and contribute to global food security.

1. Introduction

The increasing global demand for food, driven by population growth, longer life expectancy, and improving living standards, presents significant challenges for sustainable agriculture. By 2050, food demand is projected to rise by up to 50% [1,2], placing pressure on agricultural systems to enhance productivity while minimising environmental impact [3]. This pressure is further intensified by climate change, urbanisation, and land use transformation, which constrain the availability of natural resources [4,5]. Both crop and livestock production face growing scrutiny due to their competing demands for land, water, and energy, as well as their contribution to air, water, and soil pollution [6,7]. Pig production plays a central role in global food security, accounting for approximately one-third of total meat consumption [8]. Pork remains a dietary staple, particularly in developing countries, providing high-quality protein and essential micronutrients [9,10]. However, modern pig production faces mounting economic, environmental, and health-related challenges, including high feed and energy costs, resource limitations, and emissions [11]. Additionally, concerns over antimicrobial resistance and feed safety emphasise the urgent need for more responsible production strategies [12,13].
Achieving sustainable pig production requires balancing environmental goals with economic viability, animal performance, and consumer expectations [14]. In this context, life cycle assessment (LCA) is a widely accepted tool for assessing the sustainability of complex systems such as agriculture and food production [15,16,17]. It provides a quantitative framework for evaluating environmental impacts across different production stages [18]. By identifying key environmental ‘hotspots’, LCA supports the development of targeted mitigation strategies to reduce emissions and improve resource efficiency. This holistic approach enables a comprehensive evaluation, making LCA widely applicable in swine production systems [19].
Feed represents the largest economic and environmental cost in pig production, making ingredient selection and formulation critical [19,20,21]. In addition to influencing animal health, welfare, and productivity, feed composition affects farm profitability and environmental impact, particularly with respect to greenhouse gas (GHG) emissions, land use, fossil energy demand, and water quality [22,23]. In swine diets, cereal grains are the primary energy source, while soybean meal (SBM) remains the main protein source. However, SBM production is linked to major environmental and economic issues including deforestation, biodiversity loss, land degradation, transport-related emissions, and reliance on international trade [24,25]. In response, faba beans have received growing attention across Europe as regionally adapted, sustainable alternatives to imported soybean [25,26]. Nevertheless, nutritional limitations, inconsistent supply, and preservation challenges hinder their widespread adoption [27].
With over one-third of global food production lost post-harvest [28,29], improving grain preservation techniques is critical to ensuring feed safety and reducing waste. In temperate climates, the high moisture content of feed commodities increases their susceptibility to mould and mycotoxin contamination, an issue expected to intensify with climate change [30,31]. Industrial drying is the most conventional method used but it incurs high financial and environmental costs due to its reliance on fossil fuels [32,33,34,35]. Despite its widespread use, the environmental impact of grain drying is often overlooked, and more efficient alternatives remain underexplored.
Organic acid preservation has emerged as a cost-effective, energy-efficient alternative that maintains grain quality while reducing the reliance on energy-intensive drying [36,37,38]. Beyond preservation, dietary organic acids also support the reduction in in-feed antimicrobials [39]. Organic acids can enhance digestive function, modulate intestinal microbiota, reduce manure-related pollution, and improve growth performance in pigs, making them a valuable tool for sustainable production [40,41]. Other nutritional strategies, such as reducing crude protein (CP) levels, modifying carbohydrate sources, and using enzyme supplementation, have also shown potential to lower manure-related emissions and odorous compounds by improving nutrient digestibility and microbial balance [42,43]. In addition to direct dietary interventions, maternal nutrition is gaining recognition as a proactive approach to improve offspring health and environmental sustainability. Optimising sow diets during late gestation and lactation can improve piglet microbial colonisation and resilience, reducing post-weaning challenges and antimicrobial reliance [44]. Such interventions have the potential to induce lifetime improvements in digestive health, immune function, and overall production efficiency.
Both European Union (EU) and national policies are increasingly steering the transition towards more sustainable livestock systems by promoting innovation, emission reduction strategies, and improved resource management [45,46]. Science-based nutritional interventions can help producers meet regulatory requirements while maintaining economic viability. This review explores a set of practical, feed-related strategies, each targeting specific sustainability challenges within the pig production chain. Specifically, it focuses on nutritional approaches that reduce nutrient excretion, minimise odorous emissions, and support gut health; the potential of faba beans as sustainable alternatives to SBM; the dual role of organic acids as grain preservatives and functional feed additives; and the impact of maternal nutrition on offspring development and performance. Using an LCA perspective, this review identifies critical environmental hotspots and evaluates how targeted dietary interventions can mitigate these impacts, ultimately supporting a more environmentally and economically sustainable pig sector, as illustrated in Figure 1.

2. Life Cycle Assessment in Pig Production

LCA is a standardised methodology used to quantitatively evaluate the environmental impacts of a product across all stages of its life cycle, from raw material extraction to final disposal (cradle-to-grave) [18]. In pig production, LCA has been widely applied to assess GHG emissions, resource use, and other environmental pressures. It helps identify environmental hotspots, compare different feed or production systems, and informs decision making to develop more sustainable practices. As such, LCA is a valuable tool for improving the environmental performance of pig production systems [47,48,49,50,51,52,53].

2.1. Methodology

LCA follows internationally recognised standards, including ISO 14040 and ISO 14044 [54,55], and consists of four key phases. The first and arguably more important step is defining the goal and scope, which establishes the study’s objective, the system boundary, the allocation method, and the functional unit (the reference to which all inputs and outputs are scaled). In pig production, 1 kg of live weight at the farm gate is commonly used (Figure 1), although alternative functional units such as carcass weight or protein content have also been reported [56,57,58]. The second phase, life cycle inventory (LCI), involves compiling data on elementary flows such as feed, water, and energy use, as well as emissions, nutrient losses, and waste generation [59]. Where primary farm-level data are unavailable, secondary sources including the literature or databases (Ecoinvent, Agribalyse, and Agri-Footprint) may be used [60,61,62]. However, the variability in databases and data assumptions complicate comparability between studies [20]. The third phase, life cycle impact assessment (LCIA), translates or ‘calculates’ inventory data into impact categories, including global warming potential (GWP; also known as climate change), acidification potential (AP), and eutrophication potential (EP), among others [63]. This phase can be largely automated using software packages such as OpenLCA, GaBi, and SimaPro [64,65,66]. The interpretation is the final stage, which involves testing model sensitivity, identifying key hotspots, and providing recommendations or potential mitigation strategies based on the results obtained [67].

2.2. Challenges and Opportunities

Despite its value, the application of LCA in pig production faces several challenges that limit the comparability, transparency, and practical relevance of results [20]. A major issue is the inherent methodological flexibility of LCA. While this adaptability allows tailoring to specific goals, it also introduces variability in system boundaries and functional units [19,68]. For instance, some studies may adopt a cradle-to-farm-gate approach, while others extend to the slaughterhouse gate, leading to differing impact values that complicate cross-study comparisons [20]. Functional units also vary widely, ranging from 1 kg of live weight or carcass weight to 1 kg of pork cuts or even 1 tonne of pig, further reducing comparability [21].
Allocation methods for co-products such as manure, straw, or soybean oil also vary. Although ISO 14044 recommends system expansion as the preferred approach, it is often impractical in agriculture due to data and modelling constraints [69]. Consequently, many studies use allocations based on economic value, mass, or energy. Economic allocation is the most commonly used in swine LCAs, but nearly one-third of studies fail to report the method applied, undermining transparency and reproducibility [19].
The inconsistent treatment of land use change (LUC) is another challenge, particularly for high-impact ingredients like SBM. While climate change was the most frequently reported impact category across 74 pig LCAs, the handling of direct LUC (dLUC) was often unclear [19]. Only six studies reported dLUC separately, seven included it in results, and five explicitly excluded it. Most did not state whether LUC emissions were embedded in background datasets, creating uncertainty and a risk of over or underestimation. When included, dLUC raised climate change impacts by up to 6.5 kg CO2-eq/kg live weight, with one study reporting a 470% increase compared with LUC-excluded results [70]. Indirect LUC (iLUC) was even less commonly addressed, appearing in just four studies. These finding emphasise the need for transparent reporting of LUC assumptions to improve the credibility of results.
Data quality and availability remain additional persistent barriers. Primary farm-level data collection is often resource intensive, accounting for up to 80% of the total time and cost in conducting an LCA [71]. Although secondary datasets help address these gaps, they may not fully capture the regional or temporal variation in feed production, manure management, and farming practices, potentially compromising the reliability of the results.
Emerging tools such as artificial intelligence (AI) and machine learning have the potential to improve data processing, predictive modelling, and scenario analysis [72]. However, their integration into agricultural LCAs remains in its infancy and requires further validation to ensure accuracy and reproducibility. Similarly, geographic information systems (GIS) are also being explored to analyse spatial variations in nutrient runoff, land use, and air pollution, which could enable more region-specific mitigation strategies [73]. Additionally, social factors such as labour conditions and animal welfare have historically been underrepresented in LCA models; however, more recent studies have started integrating these aspects for a more holistic sustainability assessment [74,75]. Although these advancements may improve LCA applications in pig production, the inherent complexity and methodological inconsistencies remain challenges that must be addressed to ensure more robust, transparent, and actionable assessments.

2.3. Production Hotspots

The livestock sector is responsible for approximately 15% of global anthropogenic GHG emissions, with pork production accounting for around 9% of livestock-related emissions [76]. In the EU, agricultural GHG emissions primarily arise from enteric fermentation (45%), soil management (38%), and manure management (15%) [77]. Unlike ruminants, pigs produce relatively low emissions from enteric fermentation [78]. Instead, the most significant contributors to the environmental impacts of swine systems are feed and manure [19]. Therefore, optimising feed formulations and manure management are essential for reducing the sector’s environmental footprint [79,80].
Feed production alone accounts for more than 70% of the environmental impacts of the pig supply chain, driven by fertiliser and pesticide application, land use and LUC, energy-intensive processing, and the extensive transportation networks of globally sourced raw materials [19,21]. In particular, the environmental and economic burdens associated with SBM and grain preservation highlight the urgent need for more sustainable alternatives [81,82]. It was recently reported that feed-related changes implemented over the past two decades have reduced the GWP of pig production by 20–35% [19], demonstrating the substantial mitigation potential of feed-focused interventions.
Manure management is another major environmental hotspot, contributing to nitrogen and phosphorus losses, eutrophication, acidification, and ammonia volatilisation. Housing systems and manure storage conditions directly influence methane, ammonia, and nitrous oxide emissions, with flooring type, storage methods, and temperature playing key roles in emission rates [83]. While technologies such as slurry additives, anaerobic digestion, and low-emission slurry spreading offer promising mitigation options, this review focuses on nutritional strategies as a practical and preventive approach to reducing nutrient excretion, emissions, and manure odour at the source. Optimising feeding practices and diet composition can minimise nutrient excretion, lower emissions, and significantly improve air, water, and soil quality [84,85].

3. Nutritional Strategies for Enhancing Sustainability of Pig Production

3.1. Feed Formulation and Ingredient Sourcing

The composition of pig diets is primarily determined by ingredient availability, nutritional value, and economic feasibility, which vary by region and production system [86,87]. Modern feed mills employ mathematical optimisation techniques to formulate least-cost diets while ensuring nutrient balance for optimal growth and feed conversion efficiency [88]. However, recent volatility in raw material prices, geopolitical unpredictability, and increasing scrutiny of the environmental impact of imported feedstuffs have intensified the interest in alternative feed sources [25,26].
Cereal grains, such as maize, wheat, and barley, serve as the primary energy sources in pig diets. Maize is widely used due to its high starch content and digestibility. However, its production is resource intensive, requiring substantial irrigation, fertiliser inputs, and land area, contributing to GHG emissions, eutrophication, and soil degradation [89]. The cultivation of maize in temperate climates is limited by the cooler temperatures and shorter growing season. In addition, it often requires the use of plastic film for crop establishment which increases soil temperature and promotes early growth, further adding to its environmental footprint [90]. As a result, wheat and barley serve as viable alternatives. Wheat provides a more balanced amino acid profile than maize, which is important for the total protein intake of pigs [91]. Barley contains a higher fibre content, which, although beneficial for intestinal health, can inadvertently reduce energy digestibility [92]. Non-starch polysaccharides in wheat and barley, such as arabinoxylans and β-glucans, can lower feed efficiency due to their resistance to enzymatic breakdown [93]. Additionally, phosphorus in cereals is largely bound to phytate, which is poorly digested by pigs, increasing phosphorus excretion and environmental risks. To mitigate these issues, diets are commonly supplemented with exogenous enzymes, which improve digestibility [94], enhance mineral bioavailability and reduce the reliance on non-renewable resources [95].
Soybean meal remains the predominant protein source in pig diets due to its high digestibility, well-balanced amino acid profile, and consistent availability [96]. However, its reliance in Europe presents challenges, including price volatility, environmental degradation, and deforestation associated with large-scale cultivation in South America [97]. Given that feed accounts for the largest share of GHG emissions in pig production, the environmental footprint of SBM has become a key target for mitigation [25]. As concerns around imported feed ingredients intensify, interest is growing in sustainable protein alternatives that offer comparable nutritional value with a lower environmental impact. In response, a variety of novel feed sources such as food waste, insect meal, single-cell proteins, microalgae, and fermented substrates, have been evaluated [26,98,99]. While these options show potential for improving land use efficiency and supporting circular economy principles [25], barriers related to cost, feed safety, regulatory approval, and consumer acceptance limit their widespread adoption [100,101]. In contrast, there is a renewed interest in regionally adapted and agronomically feasible protein crops. Among these, grain legumes offer a practical and sustainable alternative to imported SBM. This review specifically highlights faba beans as a locally available option.
Feed formulation also plays a crucial role in optimising nutrient retention and minimising the environmental burden of manure management. Diet composition influences manure characteristics, influencing nutrient excretion, ammonia volatilisation, and odorous emissions [102]. Strategic modifications to dietary protein levels, carbohydrate sources, and the inclusion of feed additives can improve nutrient utilisation, thereby reducing excretion and minimising environmental impacts.

3.2. Nutritional Interventions for Minimising Nutrient Losses, Manure Emissions, and Odour

A key concern in intensive pig production is the inefficient utilisation of dietary nutrients, leading to its excessive excretion in manure. This contributes to ammonia and odorous compound emissions, as well as the eutrophication of water bodies [103]. To mitigate these challenges, precision feeding and nutritional strategies have been developed to optimise intestinal microbial populations, enhancing nutrient absorption while minimising waste output [104,105,106]. Approaches such as optimising dietary CP levels, altering carbohydrate sources, and integrating feed additives offer practical solutions for reducing emissions and improving sustainability in pig production [107]. These strategies not only decrease nutrient losses but enhance feed efficiency and support animal health, promoting a balance between animal welfare, environmental responsibility, and economic viability.
Swine manure has tremendous value as a natural fertiliser for crop production but must be managed to minimise GHG emissions and nutrient leaching [108]. A significant concern is the low nutrient retention efficiency in pigs. Research indicates that only 33% of ingested nitrogen and 37% of ingested phosphorus is retained, with the remainder contributing to environmental pollution [88,109]. Excess nitrogen and phosphorus are particularly problematic, as nitrogen volatilisation leads to ammonia emissions, while both nutrients lead to the eutrophication of water bodies. These environmental concerns necessitate nutritional strategies that enhance both nitrogen retention and phosphorus utilisation, reducing their excretion into the environment.
The ‘ideal protein’ concept, introduced by Cole [110], advocates for lowering dietary CP levels and supplementing with synthetic amino acids to improve nitrogen efficiency. This strategy has been effective in reducing nitrogen excretion without compromising animal performance, although it may increase feed costs due to amino acid supplementation requirements [111]. A reduction of 1% in dietary CP has been associated with a 9% decrease in nitrogen excretion, along with lower AP and EP in LCA models [112]. Similarly, reducing CP from 18.5% to 15.5% in growing pigs improved nitrogen and phosphorus retention, enhanced daily gain, and further reduced AP and EP impacts [113]. Reducing CP from 20% to 12% has also been shown to lower urine production by 25%, leading to a more favourable manure composition with a lower urine-to-faeces ratio [105,107]. Since excess urinary nitrogen is primarily excreted as urea, microbial urease in manure converts it to ammonia, contributing to air pollution [114]. Studies suggest for every 1% reduction in dietary CP, ammonia emissions may be reduced by 8–12%, making CP reduction an effective strategy for mitigating environmental impacts [115,116,117,118,119]. However, care must be taken when formulating low-CP diets, especially for younger pigs, to avoid amino acid deficiencies and ensure growth is not compromised [120,121]. Although reducing nitrogen excretion lowers ammonia emissions, its effect on odorous compounds is inconsistent. Some studies suggest that sulphur-containing amino acids contribute to offensive odours [122,123], increasing manure pH and promoting ammonia volatilisation [124,125]. While CP reduction clearly alters manure composition, its impact on gastrointestinal fermentation and odour production remains an area for further investigation.
Dietary carbohydrate composition also influences intestinal microbial populations, which can affect odorous emissions. For example, substituting wheat with barley can reduce proteolytic metabolites and manure odour due to the presence of β-glucans [126,127]. Similarly, oat-based diets promote beneficial gut bacteria such as Lactobacillus and Bifidobacterium, altering volatile fatty acid profiles and reducing manure odour emissions [128]. Incorporating fermentable carbohydrates is an effective strategy for modifying the microbiota and reducing manure emissions [129]. Studies have shown that supplementing finisher pig diets with sugar beet pulp increases faecal output while reducing ammonia emissions by stimulating microbial nitrogen incorporation [105]. This lowers manure pH, thereby reducing ammonia volatilisation and subsequently decreasing air pollution [104]. However, fermentation effects vary based on carbohydrate structure. Rapidly fermentable fibres promote volatile fatty acid production and microbial activity, whereas less fermentable fibres primarily increase faecal bulk [130].
The use of feed additives such as enzymes, organic acids, and probiotics can also reduce nutrient excretion and manure-related emissions. Enzyme supplementation improves nutrient digestibility and efficiency, reducing the need for higher protein and phosphorus levels in feed. Phytase increases phosphorus bioavailability, lowering inorganic phosphorus requirements and excretion [95]. Protease and carbohydrase enzymes also enhance protein digestion efficiency, decreasing nitrogen excretion and subsequent ammonia volatilisation [131,132,133,134]. Organic acids also influence nutrient digestibility and fermentation processes by enhancing enzymatic activity, improving protein digestibility, and promoting beneficial microbial populations [135,136,137,138], which will be further discussed in Section 3.6. This reduces the substrates available for microbial proteolysis, thereby minimising ammonia and odorous metabolite production [125,139,140]. Another alternative is the introduction of dietary lactic acid bacteria through Lactiplantibacillus plantarum supplementation, which has been reported to improve distal gut microbiota composition, reduce protein-derived odorous compounds, and lower manure emissions [141]. This aligns with the broader understanding that saccharolytic fermentation displaces proteolytic fermentation, reducing noxious gas production while improving gut health [142,143]. While challenges remain in balancing nutrient utilisation and cost effectiveness, ongoing research should apply LCA to evaluate the potential of dietary interventions to enhance environmental sustainability and animal productivity.

3.3. Integrating Faba Beans into Pig Diets: Opportunities and Challenges

In response to the plant protein shortage in Europe, grain legume cultivation has expanded considerably over the past 15 years [99]. Over the next decade, EU legume production is projected to increase by more than 80%, reflecting a strong shift towards sustainable protein sources [144]. These trends align with the European Green Deal objectives, which aim to promote regional food autonomy and reduced the reliance on imported soybean. Policy incentives supporting legume cultivation provide farmers with new income opportunities and encourage diversification in agricultural production [145]. This renewed emphasis, and indeed availability in grain legumes, presents a practical approach to enhancing sustainable protein sourcing in livestock diets [146,147,148,149].
Beyond their role in nutrition, grain legumes or pulses such as faba beans, peas, and lupins possess nitrogen-fixing properties, which enhance soil fertility and reduce the dependence on synthetic fertilisers [150,151]. Legumes also help decrease nitrate immobilisation during decomposition, making soil nutrients more readily available compared with cereals [152]. Research has shown that crops sown after grain legumes achieve higher yields with reduced fertiliser inputs [153], benefitting from the disruption of pest, disease, and weed cycles [154]. Unlike SBM, which is predominantly grown in tropical climates, legumes thrive in temperate regions, promoting circular economy principles and reducing transport-related emissions. However, some challenges remain, including variability in protein content, amino acid imbalances, and the presence of anti-nutritional factors (ANFs) [27]. Additionally, the high moisture content of pulses at harvest presents storage challenges, emphasising the need for effective preservation techniques to maintain nutritional integrity.
Faba beans (Vicia faba L.), also known as fava beans, field beans, horse beans, or broad beans, are the third most widely cultivated legume globally, after soybeans and peas [155]. Their increasing use in livestock feed is attributed to their high protein content (250–300 g/kg) and favourable amino acid profile [156,157]. Faba beans provide lysine and threonine levels comparable with SBM; however, they are deficient in sulphur-containing amino acids, such as methionine and cysteine, which may necessitate dietary supplementation depending on inclusion rates and overall feed formulation [158].
Furthermore, the various ANFs present in faba beans can impair digestion, reduce nutrient absorption, and affect pig performance. Among these, vicine and convicine are two pyrimidine glycosides which can interfere with red blood cell metabolism and negatively affect growth in pigs. However, the development of low-vicine and convicine cultivars is helping to mitigate these effects [27]. Faba beans also contain protease inhibitors, condensed tannins, and oligosaccharides. The Bowman–Birk inhibitor reduces protein digestibility by interfering with trypsin and chymotrypsin, leading to higher endogenous nitrogen losses [159,160]. Although these inhibitors are heat sensitive and largely inactivated through thermal processing, their presence limits the maximum inclusion rates of raw faba beans in pig diets [148]. Condensed tannins, primarily concentrated in the hulls of coloured flower faba bean varieties, can reduce palatability and protein digestibility by forming complexes with dietary proteins and digestive enzymes [161,162]. Although zero-tannin cultivars exist, they often exhibit poorer agronomic performance, including lower yield stability and reduced frost resistance [163]. Additionally, faba beans also contain high levels of non-digestible oligosaccharides, such as raffinose and stachyose, which are highly fermentable in monogastric animals [164]. While moderate fermentation supports intestinal health, excessive intake can lead to flatulence, loose faeces, or diarrhoea, particularly in younger pigs, thereby limiting their inclusion in early-stage diets [27]. Furthermore, the higher crude fibre content of legumes can lead to increased nutrient excretion, raising concerns related to ammonia emissions and manure management [118].
To reduce the impact of these ANFs and improve the nutritional value of faba beans, a variety of processing techniques have been developed. Dehulling is effective at removing tannin-rich outer layers, while soaking and thermal treatments (e.g., boiling, autoclaving, or roasting), can significantly reduce protease inhibitor and oligosaccharide content [27,165]. However, high-temperature treatments can degrade heat-liable amino acids or trigger Maillard reactions, negatively affecting amino acid availability. Extrusion, a widely used technique in feed processing, enhances protein availability and reduces oligosaccharides through the application of heat, pressure, and force [166]. Nevertheless, despite its potential to modify ANF content, extrusion does not necessarily translate into improved pig performance outcomes when applied to faba beans [37,167]. Germination and fermentation are also effective in breaking down complex compounds and increasing bioavailable protein fractions [168]. However, both methods require the careful control of microbial cultures and may pose implementation challenges at the commercial scale. Moreover, the efficacy of these processing techniques can vary with cultivar, initial bean composition, and the specific processing conditions applied.
Beyond genetic and processing considerations, environmental and agronomic factors such as soil quality, crop husbandry practices, and post-harvest processing also influence the nutritional value of faba beans. Industrial drying is often necessary to reduce moisture content and prevent spoilage during storage. However, drying is energy intensive and expensive, as discussed in Section 3.4 below. Additionally, dried beans can present handling and grinding challenges in feed mills, further affecting feed formulation efficiency. Organic acid preservation has emerged as a promising alternative to conventional drying, offering benefits for digestibility, storage stability, and overall feeding value. Recently, grower–finisher pigs offered organic acid-preserved faba beans exhibited higher feed intake and final body weight compared with those consuming conventional SBM-based diets [37]. Further research is needed to optimise these benefits, particularly by integrating LCA to quantify the environmental implications of substituting SBM with faba beans and replacing conventional drying with organic acid preservation.
While the integration of faba beans presents clear sustainability opportunities, potential trade-offs must be carefully managed. The displacement of conventional crops, variability in nutrient composition, and supply chain inconsistencies pose challenges that require attention. To enhance both performance and sustainability, technologies such as near-infrared spectroscopy (NIR) for real-time nutrient analysis and AI-driven feed formulation tools, are increasingly being utilised [72]. As research advances, faba beans hold strong potential as sustainable alternatives to SBM. However, future research should focus on optimising inclusion levels, improving processing technologies, and integrating LCA to comprehensively evaluate feed sustainability trade-offs. Addressing these challenges will be key to ensuring the successful adoption of faba beans as a viable, regionally produced protein source in pig production.

3.4. Importance of Grain Preservation for Feed Sustainability

While advances in plant genetics and agronomic practices have improved crop yields, corresponding efforts in grain preservation have lagged behind [169]. In fact, more than one-third of food produced worldwide is lost during the post-harvest phase due to inefficiencies in storage and preservation [33,170]. Poor post-harvest management not only compromises feed supply but also quality and contamination risks [171]. Thus, effective preservation strategies are essential for maximising production, reducing waste, and minimising resource inputs.
Preserving grain quality is also crucial for maintaining feed efficiency, nutritional integrity, and feed safety in swine nutrition. Effective preservation safeguards the physical, compositional, and sanitary attributes of grains, all of which influence their nutritional contribution to pig diets [172]. Physical properties such as grain size, hardness, and moisture content affect milling efficiency, storage stability, and digestibility; compositional factors including energy, protein, fibre, and mineral content determine nutrient availability; while sanitary conditions, particularly fungal contamination, are critical for feed safety [173].
Moisture control plays a key role in preservation, as high moisture levels promote fungal growth, spoilage, and nutrient degradation [174]. In Europe, cereals, legumes, and oilseeds must be stored below 14%, 15%, and 9% moisture content, respectively [175,176]. However, grains are often harvested at higher moisture levels, necessitating industrial drying to prevent degradation [173]. Fungal contamination remains a significant challenge, particularly under humid conditions. Field fungi, such as Fusarium spp., infect crops pre-harvest, while storage fungi, including Aspergillus and Penicillium spp., proliferate in improperly stored grains [177]. These fungi not only degrade grain quality but also produce mycotoxins, toxic compounds that impair livestock health and performance [178].
Pigs are particularly susceptible to mycotoxins due to their high cereal-based diets and limited detoxification capacity [179,180]. Aflatoxins (AF), produced from Aspergillus, cause hepatotoxic and immunosuppressive issues. Trichothecenes such as deoxynivalenol (DON), HT-2, and T-2 toxins, mainly from Fusarium, reduce feed intake, damage the gastrointestinal tract (GIT), and may cause vomiting [181,182]. Zearalenone (ZEN/ZEA), also from Fusarium, disrupts reproductive function due to its oestrogenic effects, while fumonisins impair liver and kidney function [183]. Ochratoxin A (OTA), produced from Aspergillus and Penicillium, is nephrotoxic and immunosuppressive, leading to long-term organ damage [184]. Although regulatory guidelines aim to mitigate mycotoxin risks in animal feed, enforcement and monitoring can vary by region [185]. Additionally, climate change is increasing the prevalence of toxin-producing fungi, thereby elevating the contamination risks [31,186].
Biological detoxification methods, including enzymatic degradation and probiotic interventions, offer innovative solutions for mycotoxin mitigation in pig feed. Enzymatic treatments targeting mycotoxin deactivation, such as esterases and oxidoreductases, promote feed safety by neutralising toxic compounds before ingestion [187,188]. Certain microbial strains, such as Lactobacillus, Bacillus, and Saccharomyces, have been shown to degrade mycotoxins or reduce their bioavailability in the GIT [189]. Advancements in mycotoxin-binding agents, including activated clays and yeast-derived products, also contribute to minimising mycotoxin exposure in pig diets [190]. These adsorbents effectively sequester mycotoxins in the GIT, preventing their absorption and subsequent toxic effects. However, their efficacy varies based on mycotoxin structure, diet composition, and intestinal health, emphasising the importance of feed formulation and preservation [191,192].
Industrial grain drying remains the primary method for preventing microbial growth and spoilage in storage, yet industrial dryers are energy intensive and heavily reliant on fossil fuels [32,33,34,35]. Drying lowers water activity, inhibiting microbial metabolism, but improper drying can lead to rehydration, uneven moisture distribution, and nutritional degradation [193,194]. Alternative drying methods, such as natural air drying, offer lower cost solutions but depend on suitable climatic conditions, which can slow drying and increase fungal and pest risks [195]. Solar-assisted drying provides a renewable energy alternative, reducing operational costs and environmental impacts; however, its effectiveness is also limited by weather variability as well as high infrastructure costs [196,197]. Hybrid solar drying systems, which incorporate auxiliary heat sources, may enhance drying efficiency [198] but further research is required to ensure cost effectiveness and consistent grain quality across varying environmental conditions. Given the environmental and logistical drawbacks of conventional drying methods, alternative preservation strategies are gaining interest. Among these alternatives, organic acids preservation has emerged as a promising strategy [199], which will be discussed in the following section.

3.5. The Potential of Organic Acids as Grain Preservatives in Sustainable Pig Production

Organic acids and their salts are commonly used food preservatives due to their antifungal and antibacterial properties. These compounds, such as propionic, formic, and lactic acids, disrupt microbial cell membranes, preventing spoilage and reducing the need for energy-intensive drying processes [36]. By lowering pH and suppressing fungal activity, these acids effectively inhibit mould growth, extend shelf life, and reduce contamination risks, making them a viable alternative to traditional drying methods [200,201]. Unlike drying, organic acid preservation does not rely on fossil fuel combustion, providing a more environmentally sustainable solution [34].
The process of preserving grain with organic acids is both straightforward and efficient. At harvest, the grain is transferred into a mixing auger or conveyor, where the acid is applied at a controlled concentration and mixed thoroughly to ensure uniform coverage before storage. This approach preserves grain quality and enables faster transfer into storage, easing pressure on harvest logistics and reducing operational costs. Although early concerns were raised regarding equipment corrosion, acid volatility, and feed palatability, these have been largely mitigated through stabilised formulations. Studies show that concentrated organic acids like acetic and formic acid can corrode stainless steel under certain conditions, particularly at high temperature and concentrations. However, buffered or salt-based formulations improve corrosion resistance by enhancing passivation and limiting metal ion diffusion. These stabilised blends maintain preservation efficacy while improving handling safety, equipment compatibility, and storage stability [41,202].
Beyond storage stability, recent studies have also demonstrated nutritional and performance benefits of organic acid-preserved grain in pig diets, as summarised in Table 1. Preserved grains exhibit higher digestible and metabolisable energy values, leading to improved feed intake and daily gain in pigs [36,203]. Interestingly, pigs consuming preserved grain outperformed those receiving the same acid blend as a direct additive [204], suggesting that the preservation process may enhance the bioavailability and functional efficacy of organic acids. These findings indicate that applying organic acids at harvest may offer greater nutritional advantages than direct supplementation by improving grain quality. One possible hypothesis is that organic acid application at harvest interacts with the grain while it is still biologically active, potentially modifying the structure of key components, such as starch and protein, in ways that enhance digestibility. Acidification at this early stage may also help retain functional compounds and inhibit microbial contamination during storage, contributing to a more favourable nutritional profile. In contrast, when organic acids are added at the feed manufacturing stage, they primarily act as acidifiers rather than influencing the grain’s intrinsic properties. While these mechanisms remain speculative, future studies incorporating microscopy, spectroscopy, or targeted biochemical assays could help clarify the structural and compositional changes induced by early organic acid application. Establishing such effects would provide important insight into the mode of action and long-term nutritional value of acid-preserved grain.
Besides nutritional advantages, organic acid-preserved grains positively influence intestinal health at key production stages. Weaned pigs consuming these grains exhibit enhanced nutrient digestibility and a higher abundance of beneficial bacteria such as Faecalibacterium, contributing to an enhanced gut microbial composition and a reduced reliance on in-feed antimicrobials [203,204,205,206]. More recently, a study investigating the lifetime effects of organic acid-preserved grain from creep feed to finisher diets found that pigs offered preserved grain had a higher daily gain, an improved feed efficiency from two weeks post-weaning, and a higher body weight from four weeks post-weaning. These pigs showed increased nutrient digestibility at four weeks post-weaning and at slaughter [207]. They also had a higher carcass weight and increased faecal abundance of Faecalibacterium at slaughter, suggesting that the preserved grain may help reduce the days to slaughter and maintain a more beneficial GIT microbiome throughout production. These findings emphasise the dual benefit of organic acid preservation in maintaining feed quality while enhancing lifetime health, resilience, and herd productivity.
Integrating advanced preservation techniques is key to improving grain storage efficiency and minimising environmental impacts. Organic acid preservation provides an opportunity to optimise storage conditions, maintain feed quality, and reduce reliance on fossil fuel drying methods. Future research should incorporate LCA to quantify the environmental trade-offs between different grain preservation methods. Addressing grain storage challenges is essential for ensuring a sustainable and cost-effective feed supply, reducing contamination risks, and supporting long-term productivity in swine production systems.

3.6. The Potential of Organic Acids as Functional Feed Additives in Sustainable Pig Nutrition

Amid ongoing environmental and economic pressures, maintaining herd health and productivity remains a critical challenge for the pig industry. The EU ban on zinc oxide and increasing restrictions on in-feed antimicrobials have intensified the urgent need for sustainable nutritional strategies to support animal resilience and reduce reliance on pharmaceutical interventions [12,208]. These shifts are particularly important given that poor health status not only compromises productivity but also increases the environmental footprint of pig production systems [209].
Beyond their preservative role, organic acids have emerged as multifunctional feed additives offering benefits beyond pathogen control. Their antimicrobial activity stems from their ability to penetrate microbial cell membranes in their undissociated form, disrupting cellular function and inhibiting pathogen growth [210,211,212]. In contrast to inorganic acids, organic acids are generally less corrosive and better suited for long-term dietary use, especially when used in buffered or salt forms at appropriate levels [213].
The functional properties of organic acids vary depending on their structure. Short-chain fatty acids (SCFA), including formic, acetic, propionic, and butyric acids, contribute to microbial balance and support epithelial integrity [40]. Medium-chain fatty acids (MCFA), like caprylic and capric acids, exert antimicrobial effects and serve as energy sources [214], while tricarboxylic acids (TCA), such as citric and fumaric acid, assist in metabolism and pH regulation [41]. Recent reviews have highlighted the potential of organic acids to improve intestinal health, nutrient digestibility, and growth performance while reducing nitrogen excretion and environmental emissions [215,216,217,218,219,220,221].

3.6.1. The Role of Organic Acids in Weaner Diets

Organic acids have been extensively studied across all stages of pig production, with their use being particularly prominent during the weaning transition. This critical period is characterised by abrupt dietary changes, immature gut and immune function, and heightened susceptibility to enteric infections [222]. During this time, organic acids contribute to piglet health and performance through several key mechanisms [223]. One of their primary roles is gastric acidification, which is vital in early life when endogenous hydrochloric acid secretion is underdeveloped [224,225]. Post-weaning dietary changes often elevate gastric pH, compromising the stomach’s antimicrobial efficiency and digestive efficiency [226]. Organic acids help restore low pH levels, thereby enhancing protein digestion and reinforcing defence mechanisms of the stomach [227,228].
In addition to acidification, organic acids help modulate the gut microbiota by promoting beneficial bacteria such as Lactobacillus and Bifidobacteria [229,230], while suppressing pH-sensitive pathogens like Escherichia and Salmonella [231]. Blended organic acid formulations are often more effective than single-acid supplements, supporting a more resilient microbial community [232]. These microbial shifts are frequently accompanied by reductions in Enterobacteriaceae populations and improvements in faecal consistency, both of which are indicators of enhanced gut health [233,234,235].
Organic acids also help alleviate the adverse effects of weaning on intestinal morphology. Weaning typically results in villous atrophy and crypt hyperplasia, which impair nutrient absorption [236,237]. Supplementation with organic acids has been shown to improve villus height and the villus height-to-crypt depth ratio, indicating enhanced epithelial function and nutrient uptake [238,239,240]. Furthermore, organic acids may improve feed palatability, encouraging intake when voluntary consumption is often reduced [217,233,241,242]. However, excessive inclusion rates may have the opposite effect, underscoring the importance of optimised formulations [243].

3.6.2. The Role of Organic Acids in Grower–Finisher Diets

Although most research has focused on weaned piglets, a growing body of evidence supports the efficacy of organic acids in grower–finisher pigs. As pigs mature, the GIT becomes more resilient, reducing susceptibility to dietary and environmental stressors. Nevertheless, organic acids continue to improve digestive efficiency and nutrient absorption during this later production stage [39,40]. In grower–finisher systems, key objectives include maximising growth rates, feed efficiency, and carcass quality while minimising environmental impact and production costs. Notably, European fattening units have been associated with up to ten times higher environmental impacts than weaning units [14], primarily due to the longer finishing period, higher feed intake, and increased manure output [51,244].
Organic acids in older pigs have been shown to enhance the digestibility of protein and amino acids, improve the absorption of key minerals such as calcium, phosphorus, magnesium, and zinc, and reduce nitrogen excretion [216,245,246]. These effects contribute to both better performance and lower nutrient losses, helping to reduce emissions associated with pig production [138]. While the gut microbiota in grower–finisher pigs is generally more stable than that of weaned piglets, organic acids can still promote beneficial microbial shifts that support digestive health and feed utilisation.
Fewer studies have evaluated the effects of organic acids on carcass characteristics or meat quality parameters [218,247]. However, emerging evidence suggests potential benefits, including reduced microbial shedding and improvements in food safety indicators [231,248,249]. These findings highlight the need for further investigation into their broader impacts, such as effects on meat pH, colour, tenderness, water holding capacity, and oxidative stability.
While responses may vary depending on acid type, inclusion level, diet composition, health status, and age, the current evidence supports the use of organic acids as a versatile nutritional strategy for enhancing digestive health, nutrient utilisation, and environmental sustainability across all stages of pig production. A comparative summary of their effects during the weaning, growing, and finishing stages is provided in Table 2.

3.6.3. The Role of Organic Acids in Sow Diets

There is a growing recognition of the critical role that maternal nutrition plays in shaping the development, health, and resilience of offspring both before and after weaning [262]. A sow’s diet can influence foetal growth, colostrum and milk composition, microbial transmission, and immune system development, all of which are essential for neonatal survival and long-term productivity [44,263]. While immediate improvements in piglet growth are not always observed, numerous studies report benefits emerging later in life, particularly during the late post-weaning and finishing stages [264,265]. Despite the logistical challenges of conducting longitudinal experiments, maternal dietary interventions hold significant potential for improving herd health, productivity, and sustainability. Among the various bioactive compounds explored in sow diets, including probiotics, prebiotics, algae, milk products, and yeast derivatives [266,267,268,269,270], dietary organic acids have emerged as a particularly promising strategy and are the focus of this review.
Organic acid supplementation during gestation and lactation has shown multiple benefits for maternal digestive function, immune modulation, and piglet development. These outcomes are particularly relevant during late gestation and lactation, when sows experience heightened nutrient demands [271]. Organic acids have been reported to improve nutrient digestibility, enhance colostrum and milk quality, and suppress pathogenic bacterial populations, making them valuable components for maternal feeding strategies [40]. For instance, citric acid supplementation during late gestation and lactation was found to improve CP, calcium, and phosphorus digestibility, enhancing overall nutrient utilisation [272]. Similarly, blends of organic acid increased dry matter, nitrogen, and gross energy digestibility during reproductive phases [273,274]. Improved nutrient absorption supports energy balance, prevents excessive tissue mobilisation during lactation, and reduces reproductive cycle delays, ultimately enhancing sow longevity and productivity [271].
Organic acids may also support sow metabolic health and lactation performance. Blends containing formic, propionic, and butyric acids, along with ammonium salts, have been shown to increase maternal feed intake, reduce the number of weak-born piglets, and improve litter weaning weight [275]. Furthermore, supplementation with SCFA and MCFA blends reduced body weight loss, enhanced milk production, and improved maternal energy balance [276]. Colostrum and milk not only provide energy and nutrients to piglets but also critical immunoglobulins (Ig), antimicrobial peptides, and prebiotic compounds, which help shape early immune responses and microbial colonisation [277,278]. Some studies have found that organic acids can increase the Ig concentrations in colostrum and milk [272,273], leading to improved piglet plasma Ig levels and reduced pre-weaning mortality [279]. However, these effects may vary based on acid type, inclusion rate, and sow parity, as summarised in Table 3.
Importantly, evidence suggests that maternal organic acid supplementation can influence microbial transfer pathways from sows to piglets. While some microbial exposure may occur in utero via amniotic fluid [280,281], most colonisation takes place postpartum through direct contact with maternal skin, mucosal surfaces, colostrum, milk, and faeces [282]. Since piglets naturally ingest sows faeces in the farrowing environment, modulating the sow’s gut microbiota provides a practical route to shaping early microbial seeding [283,284]. Organic acids have been shown to reduce Escherichia coli and increase Lactobacillus abundance in sow faeces during farrowing and lactation [273]. These microbial shifts not only enhance sow gut health but also support piglet immune maturation, nutrient absorption, and GIT integrity, which are critical for protection against infections during the challenging post-weaning phase [263,285].
Recent studies have explored advanced delivery methods for organic acids, such as tributyrin (a glycerol ester of butyric acid). Supplementation from day 100 of gestation shortened parturition duration, enhanced dry matter and fat digestibility, and increased milk fat and protein content by day 20 of lactation. Notably, piglets from supplemented sows exhibited reduced diarrhoea and higher plasma levels of IL-10, IL-6, and IgA, indicating improved immune function. Faecal microbial analysis revealed greater microbial diversity, with an increased abundance of Lactobacillaceae, Oscillospiraceae, and Christensenellaceae in sows, and a higher prevalence of Lactobacillaceae in piglets [286].
In a similar context, offering sows organic acid-preserved grain (65% propionic acid blend) from day 100 of gestation has recently been shown to deliver multifaceted benefits. Sows fed preserved grain showed increased digestibility of dry matter, nitrogen, neutral detergent fibre, and gross energy. At farrowing, their faecal microbiota had increased Oscillospiraceae and Christensenellaceae, both of which are associated with enhanced fibre fermentation and gut health [287,288]. Piglets born from these sows had healthier faecal scores during lactation, greater faecal Lactobacillus abundance at weaning, and superior post-weaning growth and feed efficiency through to slaughter compared with those from sows fed conventionally dried grain diets [289].
Collectively, these findings emphasise the value of organic acids in sow nutrition. Not only do they enhance maternal digestion and gut health, but they also modulate microbial transfer and improve piglet development. The positive effects observed with direct supplementation has laid the groundwork for more advanced delivery methods. Notably, organic acid preserved grain may offer a holistic strategy that can be extended beyond sows to include creep and finisher diets, supporting a cohesive, farm-wide model for enhancing productivity and sustainability. A selection of studies evaluating organic acids in sow diets and their impact on sow and offspring performance is summarised in Table 3.
Table 3. The effects of maternal dietary organic acid inclusion on sow and offspring gut health, digestive function, and growth performance.
Table 3. The effects of maternal dietary organic acid inclusion on sow and offspring gut health, digestive function, and growth performance.
Supplementation
Period
Organic Acid and
Inclusion Level
ParityLactation LengthMain Effects on SowMain Effects on OffspringRef.
48 days
(d90 of gestation)
Citric acid
(0.5, 1.0, or 1.5%)
3.824 days
  • No effect on ADFI or BW change during lactation.
  • 1.5% increased the CATTD of CP and Ca
  • 1.0 and 1.5% increased serum IgG, IgA, and IgM concentrations.
  • 1.5% increased CP, IgA, and IgM concentrations in colostrum and milk (d 14 post-partum).
  • No effect on total piglets born/weaned.
  • No effect on mortality, birth weight, or weaning weight.
[272]
41 days
(d95 of gestation)
Fumaric, citric, malic, caprylic, and capric acid blend (0.1 and 0.2%)4.021 days
  • No effect on ADFI, BW loss, or BF change during lactation or wean-to-oestrus interval.
  • 0.2% increased the CATTD of DM, N, and GE.
  • 0.2% increased plasma IgG at weaning.
  • 0.2% increased faecal Lactobacillus and reduced E.coli at farrowing and weaning.
  • No effect on total piglets born/weaned.
  • No effect on mortality, growth, or faecal scores during lactation.
  • 0.2% increased plasma immunoglobulin level.
[273]
70 days
(d73 of gestation)
Fumaric, citric, malic, caprylic and capric acid blend (0.1 and 0.2%)3.328 days
  • No effect on ADFI, BW loss, or BF change during lactation.
  • No effect on the CATTD of DM, N or GE.
  • Linear increase in faecal Lactobacillus at farrowing and weaning.
  • Linear decrease in faecal E.coli at weaning.
  • No effect on total piglets born/weaned, pre-weaning mortality, or faecal scores during lactation.
  • Linear increase in ADG and weaning weight.
  • Linear increase in faecal Lactobacillus and linear reduction in E.coli at weaning.
[274]
51 days
(d85 of gestation)
Formic, propionic, butyric acid and ammonium salt blend (0.25%)4.421 days
  • Increased ADFI during lactation however BW and BF were not recorded.
  • No effect on serum antioxidant status.
  • No effect on colostrum or milk composition.
  • No effect on total piglets born/weaned.
  • Reduced number of low-birth weight piglets (<0.7 kg) but no effect on mortality.
  • Increased litter weight/piglet BW at weaning.
[275]
29 days
(d107 of gestation)
Formic, acetic, lactic,
citric, propionic, sorbic, caprylic, capric and lauric acid blend (0.1 and 0.3%)
2.621 days
  • 0.3% increased ADFI and reduced BW and BF loss during lactation.
  • No effect on the wean-to-oestrus interval.
  • No effect on the faecal microbiota pre-farrowing or post-partum, but Clostridium perfringens was reduced on d 7 of lactation.
  • No effect on total born/weaned.
  • Reduced mummified piglets at birth.
  • Both levels increased piglet ADG during lactation and BW at weaning.
  • No effect on the faecal microbiota on d 7 post-partum or at weaning.
[276]
52 days
(d85 of gestation)
Sodium butyrate (0.1%)3.022 days
  • Increased ADFI during lactation.
  • Reduced wean-to-oestrus interval.
  • Increased fat, CP, IgA, IgG, and IgM concentration in colostrum.
  • Sow microbiota not analysed.
  • Reduced pre-weaning mortality, diarrhoea incidence, jejunal CD, and the expression of inflammatory cytokines in the colon at weaning.
  • Increased the expression of tight junction proteins in the colon at weaning.
  • Increased colonic microbial diversity and plasma IgA, IgG, and IgM concentrations at weaning.
[279]
35 days
(d100 of gestation)
Butyric
(Tributyrin 0.05%)
N/A21 days
  • Reduced total parturition time
  • No effect on ADFI or BF change during lactation.
  • Increased the CATTD of DM, GE, and EE.
  • No effect on colostrum or milk composition.
  • Increased faecal microbial diversity and the abundance of Lactobacillaceae, Oscillospiraceae and Christensenellaceae.
  • No effect on total piglets born/weaned, pre-weaning mortality, or growth during lactation.
  • Reduced diarrhoea incidence during lactation.
  • Increased microbial diversity and faecal Lactobacillus at weaning.
[286]
N/A
Entire cycle
K-diformate and formic acid (0.8 and 1.2%)3.428 days
  • Reduced BF loss during gestation.
  • Increased ADFI during lactation.
  • No effect on BW or BF change during lactation.
  • 1.2% inclusion increased CATTD of ash and EE.
  • K-diformate tended to increase milk fat.
  • No effect on total piglets born/weaned.
  • Increased birth and weaning weight.
[290]
32 days
(d108 of gestation)
Citric and sorbic acid blend (0.05 or 0.1%)1.525 days
  • No effect on ADFI or BF change during lactation or wean-to-estrus interval.
  • Linear tendency to reduce lactation BW loss.
  • 0.05 and 0.1% increased the CATTD of DM.
  • No effect on total piglets born/weaned.
  • No effect on pre-weaning mortality.
  • 0.1% increased piglet ADG and reduced diarrhoea incidence during lactation.
  • 0.1% increased offspring weaning weight.
[291]
Late gestationSodium butyrate
(0.05% or 0.1%)
3.6N/A
  • No effect on ADFI, BW loss, milk composition, or blood clinical chemistry during lactation.
  • IgG and IgA in colostrum tended to increase in supplemented sows.
  • No effect on total piglets born/weaned, pre-weaning mortality, or growth during lactation.
  • 0.1% increased ADFI, ADG, BW, and G:F increased in offspring PW.
[292]
26 days
(d110 of gestation)
Sorbic, formic, acetic,
lactic, propionic and MCFA blend (0.3%)
4.821 days
  • No effect on ADFI or BW loss during lactation.
  • Reduced BF loss during lactation.
  • No effect on weaning-to-oestrus interval.
  • Reduced faecal Streptococcus suis on d 7 post-partum.
  • No effect on total piglets born/weaned, or pre-weaning mortality.
  • Increased piglet ADG during lactation.
  • No effect on growth from weaning to d 35 PW.
  • Reduced Clostridium perfringens on d 7 PW.
[293]
40 days
(d100 of gestation)
Organic acid-preserved grain (65% propionic acid blend)3.226 days
  • No effect on ADFI, BW loss, or BF change during lactation.
  • Increased the CATTD of DM, OM, N, NDF, and GE.
  • Reduced faecal Proteobacteria and increased Oscillospiraceae and Christensenellaceae at farrowing.
  • No effect on total piglets born/weaned, pre-weaning mortality, or growth during lactation.
  • Reduced faecal scores during lactation.
  • Reduced faecal Proteobacteria on d 10 post-partum and increased Lactobacillus at weaning.
  • Increased ADG and FCR from weaning to slaughter.
[289]
ADFI, average daily feed intake; ADG, average daily gain; BF, back-fat thickness; BW, body weight; Ca, calcium; CATTD, coefficient of apparent total tract digestibility; CD, crypt depth; CP, crude protein; d, day; DM, dry matter; EE, ether extract; FCR, feed conversion ratio; GE, gross energy; G:F, gain-to-feed ratio; Ig, immunoglobulin; K, potassium; N, nitrogen; NDF, neutral detergent fibre; OA, organic acid; OM, organic matter; PW, post-weaning.

4. Conclusions

Sustainable pig production requires an integrated approach that balances productivity, herd health, and environmental responsibility. This review highlights the central role of nutrition-based strategies in achieving these goals, particularly through informed ingredient selection, sustainable preservation techniques, and targeted dietary interventions. Life cycle assessment consistently identifies feed production and manure management as major environmental hotspots in pig systems. Strategies such as replacing soybean meal with locally grown faba beans and substituting energy-intensive drying with organic acid preservation offer practical solutions to reduce greenhouse gas emissions and enhance feed system autonomy. Nutritional interventions that lower dietary crude protein, modify carbohydrate profiles, or include functional feed additives such as organic acids and exogenous enzymes have been shown to improve nutrient utilisation and reduce nitrogen losses, ammonia emissions, and odorous compounds. Among these, organic acids emerge as particularly versatile tools. Their dual role as grain preservatives and functional additives has been shown to improve storage stability, enhance digestive efficiency, support beneficial microbiota, and reduce enteric pathogen load across all production stages. These benefits are especially relevant considering increasing restrictions on in-feed antimicrobials and the ban on zinc oxide. Notably, maternal supplementation with organic acids during late gestation and lactation represents a promising nutritional strategy. The studies reviewed here indicate that this approach can enhance maternal digestibility, modulate sow microbiota, and confer lasting benefits to offspring by supporting microbial colonisation, gut development, and growth performance. This reinforces the value of holistic nutritional management to support long-term productivity and resilience.
Despite these advances, several research gaps remain. A greater integration of life cycle assessment with nutritional trials is needed to better quantify the environmental trade-offs and synergies of feed innovations. Further development and processing of legume-based protein sources such as faba beans is needed to improve digestibility, lower nutritional limitations, and support their wider use as alternatives to soybean meal. Continued work is needed to better understand the mode of action of organic acid-preserved grain. Proposed mechanisms such as enhanced nutrient preservation and increased starch and protein availability require further investigation and validation. Research is also needed to optimise the use of organic acids across all production stages, particularly in older pigs. This includes refining inclusion rates, delivery methods, and acid combinations tailored to animal age, health status, and diet composition. Finally, while maternal organic acid supplementation has shown promising results, its long-term effects on gut development, immune programming, and lifetime growth trajectories remain an area of active investigation and considerable interest. By aligning nutritional innovation with practical application, the industry can move towards a more resilient, environmentally responsible model that ensures long-term food security and economic stability.

Author Contributions

Conceptualisation, S.M., T.S. and J.V.O.; writing—original draft preparation, S.M.; writing—review and editing, S.M., T.S. and J.V.O.; supervision and funding acquisition, J.V.O. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by Science Foundation Ireland (BiOrbic Centre, Dublin, Ireland) and Adesco Nutricines (Waterford, Ireland), grant number 16/RC/3889.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. van Dijk, M.; Morley, T.; Rau, M.L.; Saghai, Y. A Meta-Analysis of Projected Global Food Demand and Population at Risk of Hunger for the Period 2010–2050. Nat. Food 2021, 2, 494–501. [Google Scholar] [CrossRef] [PubMed]
  2. Falcon, W.P.; Naylor, R.L.; Shankar, N.D. Rethinking Global Food Demand for 2050. Popul. Dev. Rev. 2022, 48, 921–957. [Google Scholar] [CrossRef]
  3. Vastolo, A.; Serrapica, F.; Cavallini, D.; Fusaro, I.; Atzori, A.S.; Todaro, M. Editorial: Alternative and Novel Livestock Feed: Reducing Environmental Impact. Front. Vet. Sci. 2024, 11, 1441905. [Google Scholar] [CrossRef]
  4. Praveen, B.; Sharma, P. A Review of Literature on Climate Change and Its Impacts on Agriculture Productivity. J. Public Aff. 2019, 19, e1960. [Google Scholar] [CrossRef]
  5. Güneralp, B.; Reba, M.; Hales, B.U.; Wentz, E.A.; Seto, K.C. Trends in Urban Land Expansion, Density, and Land Transitions from 1970 to 2010: A Global Synthesis. Environ. Res. Lett. 2020, 15, 044015. [Google Scholar] [CrossRef]
  6. de Vries, M.; de Boer, I.J.M. Comparing Environmental Impacts for Livestock Products: A Review of Life Cycle Assessments. Livest. Sci. 2010, 128, 1–11. [Google Scholar] [CrossRef]
  7. Aziz, T.; Maqsood, M.A.; Kanwal, S.; Hussain, S.; Ahmad, H.R.; Sabir, M. Fertilizers and Environment: Issues and Challenges. In Crop Production and Global Environmental Issues; Hakeem, K.R., Ed.; Springer International Publishing: Cham, Switzerland, 2015; pp. 575–598. ISBN 978-3-319-23161-7. [Google Scholar]
  8. FAO. Meat Market Review: Emerging Trends and Outlook in 2024; FAO: Rome, Italy, 2024. [Google Scholar]
  9. Pereira, P.M.D.C.C.; Vicente, A.F.D.R.B. Meat Nutritional Composition and Nutritive Role in the Human Diet. Meat Sci. 2013, 93, 586–592. [Google Scholar] [CrossRef]
  10. Ahmad, R.S.; Imran, A.; Hussain, M.B. Nutritional Composition of Meat. In Meat Science and Nutrition; Arshad, M.S., Ed.; InTech: London, UK, 2018; ISBN 978-1-78984-233-3. [Google Scholar]
  11. Dutt, T. Commercial Pig Farming Scenario, Challenges, and Prospects. In Commercial Pig Farming; Elsevier: Amsterdam, The Netherlands, 2025; pp. 1–14. ISBN 978-0-443-23769-0. [Google Scholar]
  12. Diana, A.; Snijders, S.; Rieple, A.; Boyle, L.A. Why Do Irish Pig Farmers Use Medications? Barriers for Effective Reduction of Antimicrobials in Irish Pig Production. Ir. Vet. J. 2021, 74, 12. [Google Scholar] [CrossRef]
  13. Bartlett, H.; Balmford, A.; Wood, J.L.N.; Holmes, M.A. Identifying Ways of Producing Pigs More Sustainably: Tradeoffs and Co-Benefits in Land and Antimicrobial Use. Sci. Rep. 2023, 13, 2840. [Google Scholar] [CrossRef]
  14. Pexas, G.; Kyriazakis, I. Hotspots and Bottlenecks for the Enhancement of the Environmental Sustainability of Pig Systems, with Emphasis on European Pig Systems. Porc. Health Manag. 2023, 9, 53. [Google Scholar] [CrossRef]
  15. Yan, M.-J.; Humphreys, J.; Holden, N.M. Evaluation of Process and Input–Output-Based Life-Cycle Assessment of Irish Milk Production. J. Agric. Sci. 2013, 151, 701–713. [Google Scholar] [CrossRef]
  16. Herron, J.; Curran, T.P.; Moloney, A.P.; McGee, M.; O’Riordan, E.G.; O’Brien, D. Life Cycle Assessment of Pasture-Based Suckler Steer Weanling-to-Beef Production Systems: Effect of Breed and Slaughter Age. Animal 2021, 15, 100247. [Google Scholar] [CrossRef]
  17. O’Brien, D.; Lanigan, G.; Tresise, M.; Wynn, S.; Kealy, J.; Ryan, P.; Spink, J. A Life Cycle Assessment Model of Irish Grain Cropping Systems Focused on Carbon Footprint. Ir. J. Agric. Food Res. 2025, 64, 1–21. [Google Scholar] [CrossRef]
  18. Guinee, J.B. Handbook on Life Cycle Assessment Operational Guide to the ISO Standards. Int. J. Life Cycle Assess. 2002, 7, 311–313. [Google Scholar] [CrossRef]
  19. Gislason, S.; Birkved, M.; Maresca, A. A Systematic Literature Review of Life Cycle Assessments on Primary Pig Production: Impacts, Comparisons, and Mitigation Areas. Sustain. Prod. Consum. 2023, 42, 44–62. [Google Scholar] [CrossRef]
  20. McAuliffe, G.A.; Chapman, D.V.; Sage, C.L. A Thematic Review of Life Cycle Assessment (LCA) Applied to Pig Production. Environ. Impact Assess. Rev. 2016, 56, 12–22. [Google Scholar] [CrossRef]
  21. Andretta, I.; Hickmann, F.M.W.; Remus, A.; Franceschi, C.H.; Mariani, A.B.; Orso, C.; Kipper, M.; Létourneau-Montminy, M.-P.; Pomar, C. Environmental Impacts of Pig and Poultry Production: Insights From a Systematic Review. Front. Vet. Sci. 2021, 8, 750733. [Google Scholar] [CrossRef]
  22. Makkar, H.P.S.; Ankers, P. Towards Sustainable Animal Diets: A Survey-Based Study. Anim. Feed Sci. Technol. 2014, 198, 309–322. [Google Scholar] [CrossRef]
  23. de Quelen, F.; Brossard, L.; Wilfart, A.; Dourmad, J.-Y.; Garcia-Launay, F. Eco-Friendly Feed Formulation and On-Farm Feed Production as Ways to Reduce the Environmental Impacts of Pig Production Without Consequences on Animal Performance. Front. Vet. Sci. 2021, 8, 689012. [Google Scholar] [CrossRef]
  24. Gollnow, F.; Hissa, L.D.B.V.; Rufin, P.; Lakes, T. Property-Level Direct and Indirect Deforestation for Soybean Production in the Amazon Region of Mato Grosso, Brazil. Land Use Policy 2018, 78, 377–385. [Google Scholar] [CrossRef]
  25. Pexas, G.; Doherty, B.; Kyriazakis, I. The Future of Protein Sources in Livestock Feeds: Implications for Sustainability and Food Safety. Front. Sustain. Food Syst. 2023, 7, 1188467. [Google Scholar] [CrossRef]
  26. Lestingi, A. Alternative and Sustainable Protein Sources in Pig Diet: A Review. Animals 2024, 14, 310. [Google Scholar] [CrossRef] [PubMed]
  27. Jezierny, D.; Mosenthin, R.; Bauer, E. The Use of Grain Legumes as a Protein Source in Pig Nutrition: A Review. Anim. Feed Sci. Technol. 2010, 157, 111–128. [Google Scholar] [CrossRef]
  28. Bradford, K.J.; Dahal, P.; Van Asbrouck, J.; Kunusoth, K.; Bello, P.; Thompson, J.; Wu, F. The Dry Chain: Reducing Postharvest Losses and Improving Food Safety in Humid Climates. In Food Industry Wastes; Elsevier: Amsterdam, The Netherlands, 2020; pp. 375–389. ISBN 978-0-12-817121-9. [Google Scholar]
  29. Wang, X.; Dou, Z.; Feng, S.; Zhang, Y.; Ma, L.; Zou, C.; Bai, Z.; Lakshmanan, P.; Shi, X.; Liu, D.; et al. Global Food Nutrients Analysis Reveals Alarming Gaps and Daunting Challenges. Nat. Food 2023, 4, 1007–1017. [Google Scholar] [CrossRef]
  30. Kolawole, O.; Siri-Anusornsak, W.; Petchkongkaew, A.; Elliott, C. A Systematic Review of Global Occurrence of Emerging Mycotoxins in Crops and Animal Feeds, and Their Toxicity in Livestock. Emerg. Contam. 2024, 10, 100305. [Google Scholar] [CrossRef]
  31. Hossain, A.; Farhad, M.; Aonti, A.J.; Kabir, P.; Hossain, M.; Ahmed, B.; Haq, I.; Azim, J. Cereals Production under Changing Climate. In Challenges and Solutions of Climate Impact on Agriculture; Elsevier: Amsterdam, The Netherlands, 2025; pp. 63–83. ISBN 978-0-443-23707-2. [Google Scholar]
  32. Menon, A.; Stojceska, V.; Tassou, S.A. A Systematic Review on the Recent Advances of the Energy Efficiency Improvements in Non-Conventional Food Drying Technologies. Trends Food Sci. Technol. 2020, 100, 67–76. [Google Scholar] [CrossRef]
  33. Chojnacka, K.; Mikula, K.; Izydorczyk, G.; Skrzypczak, D.; Witek-Krowiak, A.; Moustakas, K.; Ludwig, W.; Kułażyński, M. Improvements in Drying Technologies—Efficient Solutions for Cleaner Production with Higher Energy Efficiency and Reduced Emission. J. Clean. Prod. 2021, 320, 128706. [Google Scholar] [CrossRef]
  34. Ibrahim, A.; Amer, A.; Elsebaee, I.; Sabahe, A.; Amer, M.A. Applied Insight: Studying Reducing the Carbon Footprint of the Drying Process and Its Environmental Impact and Financial Return. Front. Bioeng. Biotechnol. 2024, 12, 1355133. [Google Scholar] [CrossRef]
  35. Mondal, H.T.; Sarker, S.H. Comprehensive Energy Analysis and Environmental Sustainability of Industrial Grain Drying. Renew. Sustain. Energy Rev. 2024, 199, 114442. [Google Scholar] [CrossRef]
  36. Xu, X.; Wang, H.L.; Li, P.; Zeng, Z.K.; Tian, Q.Y.; Piao, X.S.; Kuang, E.Y.W. A Comparison of the Nutritional Value of Organic-Acid Preserved Corn and Heat-Dried Corn for Pigs. Anim. Feed Sci. Technol. 2016, 214, 95–103. [Google Scholar] [CrossRef]
  37. Torres-Pitarch, A.; Perez-Vendrell, A.M.; Manzanilla, E.G.; Gardiner, G.E.; Ryan, T.; O Doherty, J.V.; Torrallardona, D.; Lawlor, P.G. Effect of Raw and Extruded Propionic Acid-Treated Field Beans on Energy and Crude Protein Digestibility (In-Vitro and In-Vivo), Growth and Carcass Quality in Grow-Finisher Pigs. Animals 2021, 11, 3080. [Google Scholar] [CrossRef] [PubMed]
  38. Konieczka, P.; Józefiak, D.; Kinsner, M.; Smulikowska, S. Effects of High-Moisture Corn Preserved with Organic Acids Combined with Rapeseed Meal and Peas on Performance and Gut Microbiota Activity of Broiler Chickens. Anim. Feed Sci. Technol. 2021, 280, 115063. [Google Scholar] [CrossRef]
  39. Wang, H.; Long, W.; Chadwick, D.; Zhang, X.; Zhang, S.; Piao, X.; Hou, Y. Dietary Acidifiers as an Alternative to Antibiotics for Promoting Pig Growth Performance: A Systematic Review and Meta-Analysis. Anim. Feed Sci. Technol. 2022, 289, 115320. [Google Scholar] [CrossRef]
  40. Suiryanrayna, M.V.A.N.; Ramana, J.V. A Review of the Effects of Dietary Organic Acids Fed to Swine. J. Anim. Sci. Biotechnol. 2015, 6, 45. [Google Scholar] [CrossRef]
  41. Tugnoli, B.; Giovagnoni, G.; Piva, A.; Grilli, E. From Acidifiers to Intestinal Health Enhancers: How Organic Acids Can Improve Growth Efficiency of Pigs. Animals 2020, 10, 134. [Google Scholar] [CrossRef]
  42. Ball, M.E.E.; Smyth, S.; Beattie, V.E.; McCracken, K.J.; McCormack, U.; Muns, R.; Gordon, F.J.; Bradford, R.; Reid, L.A.; Magowan, E. The Environmental Impact of Lowering Dietary Crude Protein in Finishing Pig Diets—The Effect on Ammonia, Odour and Slurry Production. Sustainability 2022, 14, 12016. [Google Scholar] [CrossRef]
  43. Hossain, M.; Cho, S.B.; Kim, I.H. Strategies for Reducing Noxious Gas Emissions in Pig Production: A Comprehensive Review on the Role of Feed Additives. J. Anim. Sci. Technol. 2024, 66, 237–250. [Google Scholar] [CrossRef] [PubMed]
  44. Gormley, A.; Jang, K.B.; Garavito-Duarte, Y.; Deng, Z.; Kim, S.W. Impacts of Maternal Nutrition on Sow Performance and Potential Positive Effects on Piglet Performance. Animals 2024, 14, 1858. [Google Scholar] [CrossRef]
  45. Firoiu, D.; Ionescu, G.H.; Cismaș, C.M.; Costin, M.P.; Cismaș, L.M.; Ciobanu, Ș.C.F. Sustainable Production and Consumption in EU Member States: Achieving the 2030 Sustainable Development Goals (SDG 12). Sustainability 2025, 17, 1537. [Google Scholar] [CrossRef]
  46. Kabato, W.; Getnet, G.T.; Sinore, T.; Nemeth, A.; Molnár, Z. Towards Climate-Smart Agriculture: Strategies for Sustainable Agricultural Production, Food Security, and Greenhouse Gas Reduction. Agronomy 2025, 15, 565. [Google Scholar] [CrossRef]
  47. Mosnier, E.; Van Der Werf, H.M.G.; Boissy, J.; Dourmad, J.-Y. Evaluation of the Environmental Implications of the Incorporation of Feed-Use Amino Acids in the Manufacturing of Pig and Broiler Feeds Using Life Cycle Assessment. Animal 2011, 5, 1972–1983. [Google Scholar] [CrossRef] [PubMed]
  48. Reckmann, K.; Traulsen, I.; Krieter, J. Environmental Impact Assessment—Methodology with Special Emphasis on European Pork Production. J. Environ. Manag. 2012, 107, 102–109. [Google Scholar] [CrossRef]
  49. Dourmad, J.Y.; Ryschawy, J.; Trousson, T.; Bonneau, M.; Gonzàlez, J.; Houwers, H.W.J.; Hviid, M.; Zimmer, C.; Nguyen, T.L.T.; Morgensen, L. Evaluating Environmental Impacts of Contrasting Pig Farming Systems with Life Cycle Assessment. Animal 2014, 8, 2027–2037. [Google Scholar] [CrossRef]
  50. McAuliffe, G.A.; Takahashi, T.; Mogensen, L.; Hermansen, J.E.; Sage, C.L.; Chapman, D.V.; Lee, M.R.F. Environmental Trade-Offs of Pig Production Systems under Varied Operational Efficiencies. J. Clean. Prod. 2017, 165, 1163–1173. [Google Scholar] [CrossRef]
  51. Noya, I.; Villanueva-Rey, P.; González-García, S.; Fernandez, M.D.; Rodriguez, M.R.; Moreira, M.T. Life Cycle Assessment of Pig Production: A Case Study in Galicia. J. Clean. Prod. 2017, 142, 4327–4338. [Google Scholar] [CrossRef]
  52. Van Grinsven, H.J.M.; Van Eerdt, M.M.; Westhoek, H.; Kruitwagen, S. Benchmarking Eco-Efficiency and Footprints of Dutch Agriculture in European Context and Implications for Policies for Climate and Environment. Front. Sustain. Food Syst. 2019, 3, 13. [Google Scholar] [CrossRef]
  53. Ottosen, M.; Mackenzie, S.G.; Filipe, J.A.N.; Misiura, M.M.; Kyriazakis, I. Changes in the Environmental Impacts of Pig Production Systems in Great Britain over the Last 18 Years. Agric. Syst. 2021, 189, 103063. [Google Scholar] [CrossRef]
  54. ISO 14040; Environmental Management—Life Cycle Assessment—Principles and Framework. International Organization for Standardization: Geneva, Switzerland, 2006.
  55. ISO 14044; Environmental Management—Life Cycle Assessment—Requirements and Guidelines. International Organization for Standardization: Geneva, Switzerland, 2006.
  56. Heller, M.C.; Keoleian, G.A.; Willett, W.C. Toward a Life Cycle-Based, Diet-Level Framework for Food Environmental Impact and Nutritional Quality Assessment: A Critical Review. Environ. Sci. Technol. 2013, 47, 12632–12647. [Google Scholar] [CrossRef] [PubMed]
  57. Sonesson, U.; Davis, J.; Flysjö, A.; Gustavsson, J.; Witthöft, C. Protein Quality as Functional Unit—A Methodological Framework for Inclusion in Life Cycle Assessment of Food. J. Clean. Prod. 2017, 140, 470–478. [Google Scholar] [CrossRef]
  58. McAuliffe, G.A.; Takahashi, T.; Lee, M.R.F. Applications of Nutritional Functional Units in Commodity-Level Life Cycle Assessment (LCA) of Agri-Food Systems. Int. J. Life Cycle Assess. 2020, 25, 208–221. [Google Scholar] [CrossRef]
  59. Finnveden, G.; Hauschild, M.Z.; Ekvall, T.; Guinée, J.; Heijungs, R.; Hellweg, S.; Koehler, A.; Pennington, D.; Suh, S. Recent Developments in Life Cycle Assessment. J. Environ. Manag. 2009, 91, 1–21. [Google Scholar] [CrossRef] [PubMed]
  60. Colomb, V.; Ait Amar, S.; Mens, C.B.; Gac, A.; Gaillard, G.; Koch, P.; Mousset, J.; Salou, T.; Tailleur, A.; Van Der Werf, H.M.G. AGRIBALYSE®, the French LCI Database for Agricultural Products: High Quality Data for Producers and Environmental Labelling. OCL 2015, 22, D104. [Google Scholar] [CrossRef]
  61. Wernet, G.; Bauer, C.; Steubing, B.; Reinhard, J.; Moreno-Ruiz, E.; Weidema, B. The Ecoinvent Database Version 3 (Part I): Overview and Methodology. Int. J. Life Cycle Assess. 2016, 21, 1218–1230. [Google Scholar] [CrossRef]
  62. Durlinger, B.; Koukouna, E.; Broekema, R.; van Paassen, M.; Scholten, J. Agri-Footprint 3.0; Blonk Consultants: Gouda, The Netherlands, 2017. [Google Scholar]
  63. Babinszky, L.; Verstegen, M.W.A.; Hendriks, W.H. Challenges in the 21st Century in Pig and Poultry Nutrition and the Future of Animal Nutrition. In Poultry and Pig Nutrition; Hendriks, W.H., Verstegen, M.W.A., Babinszky, L., Eds.; Brill|Wageningen Academic: Wageningen, The Netherlands, 2019; pp. 17–37. ISBN 978-90-8686-333-4. [Google Scholar]
  64. Starostka-Patyk, M. New Products Design Decision Making Support by SimaPro Software on the Base of Defective Products Management. Procedia Comput. Sci. 2015, 65, 1066–1074. [Google Scholar] [CrossRef]
  65. Abu, R.; Ab Aziz, M.A.; Che Hassan, C.H.; Noor, Z.Z.; Abd Jalil, R. Life Cycle Assessment Analyzing with Gabi Software for Food Waste Management Using Windrow and Hybrid Composting Technologies. J. Teknol. 2021, 83, 95–108. [Google Scholar] [CrossRef]
  66. Pamu, Y.; Kumar, V.S.S.; Shakir, M.A.; Ubbana, H. Life Cycle Assessment of a Building Using Open-LCA Software. Mater. Today Proc. 2022, 52, 1968–1978. [Google Scholar] [CrossRef]
  67. Brentrup, F.; Küsters, J.; Kuhlmann, H.; Lammel, J. Environmental Impact Assessment of Agricultural Production Systems Using the Life Cycle Assessment Methodology. Eur. J. Agron. 2004, 20, 247–264. [Google Scholar] [CrossRef]
  68. Toniolo, S.; Borsoi, L.; Camana, D. Life Cycle Assessment: Methods, Limitations, and Illustrations. In Methods in Sustainability Science; Elsevier: Amsterdam, The Netherlands, 2021; pp. 105–118. ISBN 978-0-12-823987-2. [Google Scholar]
  69. Dominguez Aldama, D.; Grassauer, F.; Zhu, Y.; Ardestani-Jaafari, A.; Pelletier, N. Allocation Methods in Life Cycle Assessments (LCAs) of Agri-Food Co-Products and Food Waste Valorization Systems: Systematic Review and Recommendations. J. Clean. Prod. 2023, 421, 138488. [Google Scholar] [CrossRef]
  70. Kebreab, E.; Liedke, A.; Caro, D.; Deimling, S.; Binder, M.; Finkbeiner, M. Environmental Impact of Using Specialty Feed Ingredients in Swine and Poultry Production: A Life Cycle Assessment1. J. Anim. Sci. 2016, 94, 2664–2681. [Google Scholar] [CrossRef]
  71. Miah, J.H.; Griffiths, A.; McNeill, R.; Halvorson, S.; Schenker, U.; Espinoza-Orias, N.; Morse, S.; Yang, A.; Sadhukhan, J. A Framework for Increasing the Availability of Life Cycle Inventory Data Based on the Role of Multinational Companies. Int. J. Life Cycle Assess. 2018, 23, 1744–1760. [Google Scholar] [CrossRef]
  72. Brossard, L.; Van Milgen, J.; Dourmad, J.-Y.; Gaillard, C. Smart Pig Nutrition in the Digital Era. In Smart Livestock Nutrition; Kyriazakis, I., Ed.; Smart Animal Production; Springer International Publishing: Cham, Switzerland, 2023; Volume 1, pp. 169–199. ISBN 978-3-031-22583-3. [Google Scholar]
  73. Poore, J.; Nemecek, T. Reducing Food’s Environmental Impacts through Producers and Consumers. Science 2018, 360, 987–992. [Google Scholar] [CrossRef] [PubMed]
  74. Olsen, J.V.; Andersen, H.M.-L.; Kristensen, T.; Schlægelberger, S.V.; Udesen, F.; Christensen, T.; Sandøe, P. Multidimensional Sustainability Assessment of Pig Production Systems at Herd Level—The Case of Denmark. Livest. Sci. 2023, 270, 105208. [Google Scholar] [CrossRef]
  75. Savian, M.; Da Penha Simon, C.; Holden, N.M. Evaluating Environmental, Economic, and Social Aspects of an Intensive Pig Production Farm in the South of Brazil: A Case Study. Int. J. Life Cycle Assess. 2023, 28, 1544–1560. [Google Scholar] [CrossRef]
  76. Gerber, P.J.; Steinfeld, H.; Henderson, B.; Mottet, A.; Opio, C.; Dijkman, J.; Falcucci, A.; Tempio, G. Tackling Climate Change through Livestock: A Global Assessment of Emissions and Mitigation Opportunities.; Food and Agriculture Organization of the United Nations: Rome, Italy, 2013; ISBN 92-5-107920-X. [Google Scholar]
  77. Mielcarek-Bocheńska, P.; Rzeźnik, W. Greenhouse Gas Emissions from Agriculture in EU Countries—State and Perspectives. Atmosphere 2021, 12, 1396. [Google Scholar] [CrossRef]
  78. Zervas, G.; Tsiplakou, E. An Assessment of GHG Emissions from Small Ruminants in Comparison with GHG Emissions from Large Ruminants and Monogastric Livestock. Atmos. Environ. 2012, 49, 13–23. [Google Scholar] [CrossRef]
  79. Ferket, P.R.; Van Heugten, E.; Van Kempen, T.A.T.G.; Angel, R. Nutritional Strategies to Reduce Environmental Emissions from Nonruminants. J. Anim. Sci. 2002, 80, E168–E182. [Google Scholar] [CrossRef]
  80. Andretta, I.; Hauschild, L.; Kipper, M.; Pires, P.G.S.; Pomar, C. Environmental Impacts of Precision Feeding Programs Applied in Pig Production. Animal 2018, 12, 1990–1998. [Google Scholar] [CrossRef]
  81. Nguyen, T.L.T.; Hermansen, J.E.; Mogensen, L. Fossil Energy and GHG Saving Potentials of Pig Farming in the EU. Energy Policy 2010, 38, 2561–2571. [Google Scholar] [CrossRef]
  82. Castanheira, É.G.; Freire, F. Greenhouse Gas Assessment of Soybean Production: Implications of Land Use Change and Different Cultivation Systems. J. Clean. Prod. 2013, 54, 49–60. [Google Scholar] [CrossRef]
  83. Pexas, G.; Mackenzie, S.G.; Wallace, M.; Kyriazakis, I. Environmental Impacts of Housing Conditions and Manure Management in European Pig Production Systems through a Life Cycle Perspective: A Case Study in Denmark. J. Clean. Prod. 2020, 253, 120005. [Google Scholar] [CrossRef]
  84. Cadero, A.; Aubry, A.; Brun, F.; Dourmad, J.Y.; Salaün, Y.; Garcia-Launay, F. Global Sensitivity Analysis of a Pig Fattening Unit Model Simulating Technico-Economic Performance and Environmental Impacts. Agric. Syst. 2018, 165, 221–229. [Google Scholar] [CrossRef]
  85. Meda, B.; Belloir, P.; Nancy, A.; Wilfart, A. Improving Environmental Sustainability of Poultry Production Using Innovative Feeding Strategies. In Proceedings of the 22nd European Symposium on Poultry Nutrition, Gdańsk, Poland, 10–13 June 2019. [Google Scholar]
  86. Niemi, J.K.; Sevón-Aimonen, M.-L.; Pietola, K.; Stalder, K.J. The Value of Precision Feeding Technologies for Grow–Finish Swine. Livest. Sci. 2010, 129, 13–23. [Google Scholar] [CrossRef]
  87. Lindberg, J.E. Review: Nutrient and Energy Supply in Monogastric Food Producing Animals with Reduced Environmental and Climatic Footprint and Improved Gut Health. Animal 2023, 17, 100832. [Google Scholar] [CrossRef] [PubMed]
  88. Lautrou, M.; Cappelaere, L.; Létourneau Montminy, M.-P. Phosphorus and Nitrogen Nutrition in Swine Production. Anim. Front. 2022, 12, 23–29. [Google Scholar] [CrossRef]
  89. Stein, H.H.; Lagos, L.V.; Casas, G.A. Nutritional Value of Feed Ingredients of Plant Origin Fed to Pigs. Anim. Feed Sci. Technol. 2016, 218, 33–69. [Google Scholar] [CrossRef]
  90. Igiebor, F.A.; Uwuigiaren, N.J. Influence of Soil Microplastic Contamination on Maize (Zea Mays) Development and Microbial Dynamics. Discov. Environ. 2024, 2, 122. [Google Scholar] [CrossRef]
  91. Myrie, S.B.; Bertolo, R.F.; Sauer, W.C.; Ball, R.O. Effect of Common Antinutritive Factors and Fibrous Feedstuffs in Pig Diets on Amino Acid Digestibilities with Special Emphasis on Threonine. J. Anim. Sci. 2008, 86, 609–619. [Google Scholar] [CrossRef]
  92. Bach Knudsen, K.E.; Nørskov, N.P.; Bolvig, A.K.; Hedemann, M.S.; Laerke, H.N. Dietary Fibers and Associated Phytochemicals in Cereals. Mol. Nutr. Food Res. 2017, 61, 1600518. [Google Scholar] [CrossRef]
  93. Kiarie, E.; Walsh, M.C.; Nyachoti, C.M. Performance, Digestive Function, and Mucosal Responses to Selected Feed Additives for Pigs. J. Anim. Sci. 2016, 94, 169–180. [Google Scholar] [CrossRef]
  94. Dersjant-Li, Y.; Awati, A.; Schulze, H.; Partridge, G. Phytase in Non-ruminant Animal Nutrition: A Critical Review on Phytase Activities in the Gastrointestinal Tract and Influencing Factors. J. Sci. Food Agric. 2015, 95, 878–896. [Google Scholar] [CrossRef]
  95. Symeou, V.; Leinonen, I.; Kyriazakis, I. Modelling Phosphorus Intake, Digestion, Retention and Excretion in Growing and Finishing Pigs: Model Description. Animal 2014, 8, 1612–1621. [Google Scholar] [CrossRef] [PubMed]
  96. Nahashon, S.; Kilonzo-Nthenge, A. Soybean in Monogastric Nutrition: Modifications to Add Value and Disease Prevention Properties. In Soybean–Bio-Active Compounds; El-Shemy, H., Ed.; InTech: London, UK, 2013; ISBN 978-953-51-0977-8. [Google Scholar]
  97. Semper-Pascual, A.; Decarre, J.; Baumann, M.; Busso, J.M.; Camino, M.; Gómez-Valencia, B.; Kuemmerle, T. Biodiversity Loss in Deforestation Frontiers: Linking Occupancy Modelling and Physiological Stress Indicators to Understand Local Extinctions. Biol. Conserv. 2019, 236, 281–288. [Google Scholar] [CrossRef]
  98. Salomone, R.; Saija, G.; Mondello, G.; Giannetto, A.; Fasulo, S.; Savastano, D. Environmental Impact of Food Waste Bioconversion by Insects: Application of Life Cycle Assessment to Process Using Hermetia Illucens. J. Clean. Prod. 2017, 140, 890–905. [Google Scholar] [CrossRef]
  99. Parrini, S.; Aquilani, C.; Pugliese, C.; Bozzi, R.; Sirtori, F. Soybean Replacement by Alternative Protein Sources in Pig Nutrition and Its Effect on Meat Quality. Animals 2023, 13, 494. [Google Scholar] [CrossRef]
  100. Malila, Y.; Owolabi, I.O.; Chotanaphuti, T.; Sakdibhornssup, N.; Elliott, C.T.; Visessanguan, W.; Karoonuthaisiri, N.; Petchkongkaew, A. Current Challenges of Alternative Proteins as Future Foods. NPJ Sci. Food 2024, 8, 53. [Google Scholar] [CrossRef] [PubMed]
  101. Traynor, A.; Burns, D.T.; Wu, D.; Karoonuthaisiri, N.; Petchkongkaew, A.; Elliott, C.T. An Analysis of Emerging Food Safety and Fraud Risks of Novel Insect Proteins within Complex Supply Chains. NPJ Sci. Food 2024, 8, 7. [Google Scholar] [CrossRef]
  102. Trabue, S.L.; Kerr, B.J.; Scoggin, K.D.; Andersen, D.; Van Weelden, M. Swine Diets Impact Manure Characteristics and Gas Emissions: Part I Protein Level. Sci. Total Environ. 2021, 755, 142528. [Google Scholar] [CrossRef]
  103. Vonderohe, C.E.; Brizgys, L.A.; Richert, J.A.; Radcliffe, J.S. Swine Production: How Sustainable Is Sustainability? Anim. Front. 2022, 12, 7–17. [Google Scholar] [CrossRef] [PubMed]
  104. Aarnink, A.J.A.; Verstegen, M.W.A. Nutrition, Key Factor to Reduce Environmental Load from Pig Production. Livest. Sci. 2007, 109, 194–203. [Google Scholar] [CrossRef]
  105. Lynch, M.B.; O’Shea, C.J.; Sweeney, T.; Callan, J.J.; O’Doherty, J.V. Effect of Crude Protein Concentration and Sugar-Beet Pulp on Nutrient Digestibility, Nitrogen Excretion, Intestinal Fermentation and Manure Ammonia and Odour Emissions from Finisher Pigs. Animal 2008, 2, 425–434. [Google Scholar] [CrossRef]
  106. O’Shea, C.J.; Gahan, D.A.; Lynch, M.B.; Callan, J.J.; O’Doherty, J.V. Effect of β-Glucan Source and Exogenous Enzyme Supplementation on Intestinal Fermentation and Manure Odour and Ammonia Emissions from Finisher Boars. Livest. Sci. 2010, 134, 194–197. [Google Scholar] [CrossRef]
  107. Carpenter, D.; O’Mara, F.P.; O’Doherty, J.V. The Effect of Dietary Crude Protein Concentration on Growth Performance, Carcass Composition and Nitrogen Excretion in Entire Grower-Finisher Pigs. Ir. J. Agric. Food Res. 2004, 43, 227–236. [Google Scholar]
  108. McCutcheon, G.; Quinn, A.J. Pig Manure: A Valuable Fertiliser, 2nd ed.; Teagasc: Carlow, Ireland, 2020. [Google Scholar]
  109. Dourmad, J.Y.; Guingand, N.; Latimier, P.; Sève, B. Nitrogen and Phosphorus Consumption, Utilisation and Losses in Pig Production: France. Livest. Prod. Sci. 1999, 58, 199–211. [Google Scholar] [CrossRef]
  110. Cole, D.J.A. Amino Acid Nutrition of the Pig. In Recent Advances in Animal Nutrition; Butterworths: London, UK, 1978; pp. 71–95. [Google Scholar]
  111. Pomar, C.; Andretta, I.; Remus, A. Feeding Strategies to Reduce Nutrient Losses and Improve the Sustainability of Growing Pigs. Front. Vet. Sci. 2021, 8, 742220. [Google Scholar] [CrossRef] [PubMed]
  112. Monteiro, A.N.T.R.; Dourmad, J.-Y.; Pozza, P.C. Life Cycle Assessment as a Tool to Evaluate the Impact of Reducing Crude Protein in Pig Diets. Ciênc. Rural 2017, 47. [Google Scholar] [CrossRef]
  113. Esteves, L.A.C.; Monteiro, A.N.T.R.; Sitanaka, N.Y.; Oliveira, P.C.; Castilha, L.D.; Paula, V.R.C.; Pozza, P.C. The Reduction of Crude Protein with the Supplementation of Amino Acids in the Diet Reduces the Environmental Impact of Growing Pigs Production Evaluated through Life Cycle Assessment. Sustainability 2021, 13, 4815. [Google Scholar] [CrossRef]
  114. Mobley, H.L.; Hausinger, R.P. Microbial Ureases: Significance, Regulation, and Molecular Characterization. Microbiol. Rev. 1989, 53, 85–108. [Google Scholar] [CrossRef]
  115. Canh, T.T.; Aarnink, A.J.A.; Schutte, J.B.; Sutton, A.; Langhout, D.J.; Verstegen, M.W.A. Dietary Protein Affects Nitrogen Excretion and Ammonia Emission from Slurry of Growing–Finishing Pigs. Livest. Prod. Sci. 1998, 56, 181–191. [Google Scholar] [CrossRef]
  116. Lynch, M.B.; Sweeney, T.; Callan, B.; Flynn, J.J.; O’Doherty, J.V. The Effect of High and Low Dietary Crude Protein and Inulin Supplementation on Nutrient Digestibility, Nitrogen Excretion, Intestinal Microflora and Manure Ammonia Emissions from Finisher Pigs. Animal 2007, 1, 1112–1121. [Google Scholar] [CrossRef]
  117. Monteiro, A.N.T.R.; Bertol, T.M.; De Oliveira, P.A.V.; Dourmad, J.-Y.; Coldebella, A.; Kessler, A.M. The Impact of Feeding Growing-Finishing Pigs with Reduced Dietary Protein Levels on Performance, Carcass Traits, Meat Quality and Environmental Impacts. Livest. Sci. 2017, 198, 162–169. [Google Scholar] [CrossRef]
  118. Trabue, S.L.; Kerr, B.J.; Scoggin, K.D.; Andersen, D.; Van Weelden, M. Swine Diets Impact Manure Characteristics and Gas Emissions: Part II Protein Source. Sci. Total Environ. 2021, 763, 144207. [Google Scholar] [CrossRef] [PubMed]
  119. Le Dinh, P.; Van Der Peet-Schwering, C.; Ogink, N.; Aarnink, A. Effect of Diet Composition on Excreta Composition and Ammonia Emissions from Growing-Finishing Pigs. Animals 2022, 12, 229. [Google Scholar] [CrossRef] [PubMed]
  120. Peng, X.; Hu, L.; Liu, Y.; Yan, C.; Fang, Z.F.; Lin, Y.; Xu, S.Y.; Li, J.; Wu, C.M.; Chen, D.W.; et al. Effects of Low-Protein Diets Supplemented with Indispensable Amino Acids on Growth Performance, Intestinal Morphology and Immunological Parameters in 13 to 35 Kg Pigs. Animal 2016, 10, 1812–1820. [Google Scholar] [CrossRef]
  121. Rattigan, R.; Sweeney, T.; Maher, S.; Ryan, M.T.; Thornton, K.; O’Doherty, J.V. Effects of Reducing Dietary Crude Protein Concentration and Supplementation with Either Laminarin or Zinc Oxide on the Growth Performance and Intestinal Health of Newly Weaned Pigs. Anim. Feed Sci. Technol. 2020, 270, 114693. [Google Scholar] [CrossRef]
  122. Le, P.D.; Aarnink, A.J.A.; Jongbloed, A.W. Odour and Ammonia Emission from Pig Manure as Affected by Dietary Crude Protein Level. Livest. Sci. 2009, 121, 267–274. [Google Scholar] [CrossRef]
  123. Poulsen, H.V.; Canibe, N.; Finster, K.; Jensen, B.B. Concentration of Volatile Sulphur-Containing Compounds along the Gastrointestinal Tract of Pigs Fed a High-Sulphur or a Low-Sulphur Diet. Livest. Sci. 2010, 133, 128–131. [Google Scholar] [CrossRef]
  124. O’Connell, J.M.; Callan, J.J.; O’Doherty, J.V. The Effect of Dietary Crude Protein Level, Cereal Type and Exogenous Enzyme Supplementation on Nutrient Digestibility, Nitrogen Excretion, Faecal Volatile Fatty Acid Concentration and Ammonia Emissions from Pigs. Anim. Feed Sci. Technol. 2006, 127, 73–88. [Google Scholar] [CrossRef]
  125. Murphy, D.P.; O’Doherty, J.V.; Boland, T.M.; O’Shea, C.J.; Callan, J.J.; Pierce, K.M.; Lynch, M.B. The Effect of Benzoic Acid Concentration on Nitrogen Metabolism, Manure Ammonia and Odour Emissions in Finishing Pigs. Anim. Feed Sci. Technol. 2011, 163, 194–199. [Google Scholar] [CrossRef]
  126. Garry, B.P.; Fogarty, M.; Curran, T.P.; O’Connell, M.J.; O’Doherty, J.V. The Effect of Cereal Type and Enzyme Addition on Pig Performance, Intestinal Microflora, and Ammonia and Odour Emissions. Animal 2007, 1, 751–757. [Google Scholar] [CrossRef]
  127. Lynch, M.B.; Sweeney, T.; Callan, J.J.; O’Doherty, J.V. Effects of Increasing the Intake of Dietary β-Glucans by Exchanging Wheat for Barley on Nutrient Digestibility, Nitrogen Excretion, Intestinal Microflora, Volatile Fatty Acid Concentration and Manure Ammonia Emissions in Finishing Pigs. Animal 2007, 1, 812–819. [Google Scholar] [CrossRef]
  128. O’Shea, C.J.; Sweeney, T.; Lynch, M.B.; Gahan, D.A.; Callan, J.J.; O’Doherty, J.V. Effect of -Glucans Contained in Barley- and Oat-Based Diets and Exogenous Enzyme Supplementation on Gastrointestinal Fermentation of Finisher Pigs and Subsequent Manure Odor and Ammonia Emissions. J. Anim. Sci. 2010, 88, 1411–1420. [Google Scholar] [CrossRef]
  129. Jha, R.; Leterme, P. Feed Ingredients Differing in Fermentable Fibre and Indigestible Protein Content Affect Fermentation Metabolites and Faecal Nitrogen Excretion in Growing Pigs. Animal 2012, 6, 603–611. [Google Scholar] [CrossRef] [PubMed]
  130. Wilfart, A.; Montagne, L.; Simmins, P.H.; Van Milgen, J.; Noblet, J. Sites of Nutrient Digestion in Growing Pigs: Effect of Dietary Fiber. J. Anim. Sci. 2007, 85, 976–983. [Google Scholar] [CrossRef]
  131. Guggenbuhl, P.; Waché, Y.; Wilson, J.W. Effects of Dietary Supplementation with a Protease on the Apparent Ileal Digestibility of the Weaned Piglet. J. Anim. Sci. 2012, 90, 152–154. [Google Scholar] [CrossRef] [PubMed]
  132. Mc Alpine, P.O.; O’Shea, C.J.; Varley, P.F.; Solan, P.; Curran, T.; O’Doherty, J.V. The Effect of Protease and Nonstarch Polysaccharide Enzymes on Manure Odor and Ammonia Emissions from Finisher Pigs. J. Anim. Sci. 2012, 90, 369–371. [Google Scholar] [CrossRef]
  133. O’Shea, C.J.; Mc Alpine, P.O.; Solan, P.; Curran, T.; Varley, P.F.; Walsh, A.M.; Doherty, J.V.O. The Effect of Protease and Xylanase Enzymes on Growth Performance, Nutrient Digestibility, and Manure Odour in Grower–Finisher Pigs. Anim. Feed Sci. Technol. 2014, 189, 88–97. [Google Scholar] [CrossRef]
  134. Torres-Pitarch, A.; Manzanilla, E.G.; Gardiner, G.E.; O’Doherty, J.V.; Lawlor, P.G. Systematic Review and Meta-Analysis of the Effect of Feed Enzymes on Growth and Nutrient Digestibility in Grow-Finisher Pigs: Effect of Enzyme Type and Cereal Source. Anim. Feed Sci. Technol. 2019, 251, 153–165. [Google Scholar] [CrossRef]
  135. Partanen, K.; Jalava, T.; Valaja, J.; Perttilä, S.; Siljander-Rasi, H.; Lindeberg, H. Effect of Dietary Carbadox or Formic Acid and Fibre Level on Ileal and Faecal Nutrient Digestibility and Microbial Metabolite Concentrations in Ileal Digesta of the Pig. Anim. Feed Sci. Technol. 2001, 93, 137–155. [Google Scholar] [CrossRef]
  136. Biagi, G.; Piva, A. In Vitro Effects of Some Organic Acids on Swine Cecal Microflora. Ital. J. Anim. Sci. 2007, 6, 361–374. [Google Scholar] [CrossRef]
  137. Partanen, K.; Jalava, T.; Valaja, J. Effects of a Dietary Organic Acid Mixture and of Dietary Fibre Levels on Ileal and Faecal Nutrient Apparent Digestibility, Bacterial Nitrogen Flow, Microbial Metabolite Concentrations and Rate of Passage in the Digestive Tract of Pigs. Animal 2007, 1, 389–401. [Google Scholar] [CrossRef]
  138. Hossain, M.M.; Jayaraman, B.; Kim, S.C.; Lee, K.Y.; Kim, I.H.; Nyachoti, C.M. Effects of a Matrix-Coated Organic Acids and Medium-Chain Fatty Acids Blend on Performance, and in Vitro Fecal Noxious Gas Emissions in Growing Pigs Fed in-Feed Antibiotic-Free Diets. Can. J. Anim. Sci. 2018, 98, 433–442. [Google Scholar] [CrossRef]
  139. Eriksen, J.; Adamsen, A.P.S.; Nørgaard, J.V.; Poulsen, H.D.; Jensen, B.B.; Petersen, S.O. Emissions of Sulfur-Containing Odorants, Ammonia, and Methane from Pig Slurry: Effects of Dietary Methionine and Benzoic Acid. J. Environ. Qual. 2010, 39, 1097–1107. [Google Scholar] [CrossRef]
  140. Yoo, S.B.; Song, Y.S.; Seo, S.; Kim, S.W.; Kim, B.G. Effects of Benzoic Acid in Pig Diets on Nitrogen Utilization, Urinary pH, Slurry pH, and Odorous Compounds. Anim. Biosci. 2024, 37, 2137–2144. [Google Scholar] [CrossRef] [PubMed]
  141. O’Shea, C.J.; Sweeney, T.; Bahar, B.; Ryan, M.T.; Thornton, K.; O’Doherty, J.V. Indices of Gastrointestinal Fermentation and Manure Emissions of Growing-Finishing Pigs as Influenced through Singular or Combined Consumption of Lactobacillus Plantarum and Inulin. J. Anim. Sci. 2012, 90, 3848–3857. [Google Scholar] [CrossRef] [PubMed]
  142. O’Shea, C.J.; Lynch, M.B.; Sweeney, T.; Gahan, D.A.; Callan, J.J.; O’Doherty, J.V. Comparison of a Wheat-Based Diet Supplemented with Purified β-Glucans, with an Oat-Based Diet on Nutrient Digestibility, Nitrogen Utilization, Distal Gastrointestinal Tract Composition, and Manure Odor and Ammonia Emissions from Finishing Pigs. J. Anim. Sci. 2011, 89, 438–447. [Google Scholar] [CrossRef]
  143. Gilbert, M.S.; Ijssennagger, N.; Kies, A.K.; Van Mil, S.W.C. Protein Fermentation in the Gut; Implications for Intestinal Dysfunction in Humans, Pigs, and Poultry. Am. J. Physiol.-Gastrointest. Liver Physiol. 2018, 315, G159–G170. [Google Scholar] [CrossRef]
  144. OECD; FAO. OECD-FAO Agricultural Outlook 2024-2033; OECD-FAO Agricultural Outlook; OECD: Paris, France, 2024; ISBN 978-92-64-72259-0. [Google Scholar]
  145. DAFM. Protein Aid Scheme; Department of Agriculture, Food and the Marine: Dublin, Ireland, 2023. [Google Scholar]
  146. Prandini, A.; Sigolo, S.; Morlacchini, M.; Cerioli, C.; Masoero, F. Pea (Pisum Sativum) and Faba Bean (Vicia faba L.) Seeds as Protein Sources in Growing-Finishing Heavy Pig Diets: Effect on Growth Performance, Carcass Characteristics and on Fresh and Seasoned Parma Ham Quality. Ital. J. Anim. Sci. 2011, 10, e45. [Google Scholar] [CrossRef]
  147. Smith, L.A.; Houdijk, J.G.M.; Homer, D.; Kyriazakis, I. Effects of Dietary Inclusion of Pea and Faba Bean as a Replacement for Soybean Meal on Grower and Finisher Pig Performance and Carcass Quality. J. Anim. Sci. 2013, 91, 3733–3741. [Google Scholar] [CrossRef]
  148. White, G.A.; Smith, L.A.; Houdijk, J.G.M.; Homer, D.; Kyriazakis, I.; Wiseman, J. Replacement of Soya Bean Meal with Peas and Faba Beans in Growing/Finishing Pig Diets: Effect on Performance, Carcass Composition and Nutrient Excretion. Anim. Feed Sci. Technol. 2015, 209, 202–210. [Google Scholar] [CrossRef]
  149. Cherif, C.; Hassanat, F.; Claveau, S.; Girard, J.; Gervais, R.; Benchaar, C. Faba Bean (Vicia faba) Inclusion in Dairy Cow Diets: Effect on Nutrient Digestion, Rumen Fermentation, Nitrogen Utilization, Methane Production, and Milk Performance. J. Dairy Sci. 2018, 101, 8916–8928. [Google Scholar] [CrossRef]
  150. Zahran, H.H. Rhizobium-Legume Symbiosis and Nitrogen Fixation under Severe Conditions and in an Arid Climate. Microbiol. Mol. Biol. Rev. 1999, 63, 968–989. [Google Scholar] [CrossRef] [PubMed]
  151. Neugschwandtner, R.; Ziegler, K.; Kriegner, S.; Wagentristl, H.; Kaul, H.-P. Nitrogen Yield and Nitrogen Fixation of Winter Faba Beans. Acta Agric. Scand. Sect. B—Soil Plant Sci. 2015, 65, 658–666. [Google Scholar] [CrossRef]
  152. Da Silva, J.P.; Teixeira, R.D.S.; Da Silva, I.R.; Soares, E.M.B.; Lima, A.M.N. Decomposition and Nutrient Release from Legume and Non-legume Residues in a Tropical Soil. Eur. J. Soil Sci. 2022, 73. [Google Scholar] [CrossRef]
  153. Bedoussac, L.; Journet, E.-P.; Hauggaard-Nielsen, H.; Naudin, C.; Corre-Hellou, G.; Jensen, E.S.; Prieur, L.; Justes, E. Ecological Principles Underlying the Increase of Productivity Achieved by Cereal-Grain Legume Intercrops in Organic Farming. A Review. Agron. Sustain. Dev. 2015, 35, 911–935. [Google Scholar] [CrossRef]
  154. Kocira, A.; Staniak, M.; Tomaszewska, M.; Kornas, R.; Cymerman, J.; Panasiewicz, K.; Lipińska, H. Legume Cover Crops as One of the Elements of Strategic Weed Management and Soil Quality Improvement. A Review. Agriculture 2020, 10, 394. [Google Scholar] [CrossRef]
  155. Rahate, K.A.; Madhumita, M.; Prabhakar, P.K. Nutritional Composition, Anti-Nutritional Factors, Pretreatments-Cum-Processing Impact and Food Formulation Potential of Faba Bean (Vicia faba L.): A Comprehensive Review. LWT 2021, 138, 110796. [Google Scholar] [CrossRef]
  156. Sauvant, D.; Perez, J.; Tran, G. Tables of Composition and Nutritional Value of Feed Materials: Pigs, Poultry, Cattle, Sheep, Goats, Rabbits, Horses and Fish; Wageningen Academic Publishers: Amsterdam, The Netherlands, 2004; ISBN 90-8686-668-9. [Google Scholar]
  157. Stein, H.H.; Sève, B.; Fuller, M.F.; Moughan, P.J.; De Lange, C.F.M. Invited Review: Amino Acid Bioavailability and Digestibility in Pig Feed Ingredients: Terminology and Application. J. Anim. Sci. 2007, 85, 172–180. [Google Scholar] [CrossRef]
  158. Carbas, B.; Machado, N.; Pathania, S.; Brites, C.; Rosa, E.A.; Barros, A.I. Potential of Legumes: Nutritional Value, Bioactive Properties, Innovative Food Products, and Application of Eco-Friendly Tools for Their Assessment. Food Rev. Int. 2023, 39, 160–188. [Google Scholar] [CrossRef]
  159. Pusztai, A.; Bardocz, S.; Martín-Cabrejas, M.A. The Mode of Action of ANFs on the Gastrointestinal Tract and Its Microflora. In Recent Advances of Research in Antinutritional Factors in Legume Seeds and Oilseeds; Wageningen Academic Publishers: Wageningen, The Netherlands, 2004; pp. 87–100. [Google Scholar]
  160. Mayer Labba, I.-C.; Frøkiær, H.; Sandberg, A.-S. Nutritional and Antinutritional Composition of Fava Bean (Vicia faba L., Var. Minor) Cultivars. Food Res. Int. 2021, 140, 110038. [Google Scholar] [CrossRef]
  161. Hagerman, A.E.; Butler, L.G. Condensed Tannin Purification and Characterization of Tannin-Associated Proteins. J. Agric. Food Chem. 1980, 28, 947–952. [Google Scholar] [CrossRef]
  162. Ivarsson, E.; Neil, M. Variations in Nutritional and Antinutritional Contents among Faba Bean Cultivars and Effects on Growth Performance of Weaner Pigs. Livest. Sci. 2018, 212, 14–21. [Google Scholar] [CrossRef]
  163. Henriquez, B.; Olson, M.A.; Hoy, C.F.; Jackson, M.; Wouda, T. Frost Tolerance of Faba Bean Cultivars (Vicia faba L.) in Central Alberta. Can. J. Plant Sci. 2017, 98, 509–514. [Google Scholar] [CrossRef]
  164. Houdijk, J.G.M.; Hartemink, R.; Verstegen, M.W.A.; Bosch, M. Effects of Dietary Non-Digestible Oligosaccharides on Microbial Characteristics of Ileal Chyme and Faeces in Weaner Pigs. Arch. Für Tierernaehrung 2002, 56, 297–307. [Google Scholar] [CrossRef] [PubMed]
  165. Alonso, R.; Aguirre, A.; Marzo, F. Effects of Extrusion and Traditional Processing Methods on Antinutrients and in Vitro Digestibility of Protein and Starch in Faba and Kidney Beans. Food Chem. 2000, 68, 159–165. [Google Scholar] [CrossRef]
  166. Sun, T.; Lærke, H.N.; Jørgensen, H.; Knudsen, K.E.B. The Effect of Extrusion Cooking of Different Starch Sources on the in Vitro and in Vivo Digestibility in Growing Pigs. Anim. Feed Sci. Technol. 2006, 131, 67–86. [Google Scholar] [CrossRef]
  167. O’Doherty, J.V.; McKeon, M.P. A Note on the Nutritive Value of Extruded and Raw Beans for Growing and Finishing Pigs. Ir. J. Agric. Food Res. 2001, 40, 97–104. [Google Scholar]
  168. King, J.; Leong, S.Y.; Alpos, M.; Johnson, C.; McLeod, S.; Peng, M.; Sutton, K.; Oey, I. Role of Food Processing and Incorporating Legumes in Food Products to Increase Protein Intake and Enhance Satiety. Trends Food Sci. Technol. 2024, 147, 104466. [Google Scholar] [CrossRef]
  169. Bala, B.K. Principles of Storage. In Drying and Storage of Cereal Grains; Wiley: Hoboken, NJ, USA, 2016; pp. 215–221. ISBN 978-1-119-12423-8. [Google Scholar]
  170. Barrozo, M.A.S.; Mujumdar, A.; Freire, J.T. Air-Drying of Seeds: A Review. Dry. Technol. 2014, 32, 1127–1141. [Google Scholar] [CrossRef]
  171. Los, A.; Ziuzina, D.; Bourke, P. Current and Future Technologies for Microbiological Decontamination of Cereal Grains: Decontamination Methods of Cereal Grains. J. Food Sci. 2018, 83, 1484–1493. [Google Scholar] [CrossRef]
  172. Ziegler, V.; Paraginski, R.T.; Ferreira, C.D. Grain Storage Systems and Effects of Moisture, Temperature and Time on Grain Quality—A Review. J. Stored Prod. Res. 2021, 91, 101770. [Google Scholar] [CrossRef]
  173. Fleurat-Lessard, F. STORED GRAIN|Physico-Chemical Treatment. In Encyclopedia of Grain Science; Elsevier: Amsterdam, The Netherlands, 2004; pp. 254–263. ISBN 978-0-12-765490-4. [Google Scholar]
  174. Jouany, J.P. Methods for Preventing, Decontaminating and Minimizing the Toxicity of Mycotoxins in Feeds. Anim. Feed Sci. Technol. 2007, 137, 342–362. [Google Scholar] [CrossRef]
  175. Jimoh, K.A.; Hashim, N.; Shamsudin, R.; Man, H.C.; Jahari, M.; Onwude, D.I. Recent Advances in the Drying Process of Grains. Food Eng. Rev. 2023, 15, 548–576. [Google Scholar] [CrossRef]
  176. Baidhe, E.; Clementson, C.L. A Review of the Application of Modeling and Simulation to Drying Systems for Improved Grain and Seed Quality. Comput. Electron. Agric. 2024, 222, 109094. [Google Scholar] [CrossRef]
  177. Maciorowski, K.G.; Herrera, P.; Jones, F.T.; Pillai, S.D.; Ricke, S.C. Effects on Poultry and Livestock of Feed Contamination with Bacteria and Fungi. Anim. Feed Sci. Technol. 2007, 133, 109–136. [Google Scholar] [CrossRef]
  178. Bryden, W.L. Mycotoxin Contamination of the Feed Supply Chain: Implications for Animal Productivity and Feed Security. Anim. Feed Sci. Technol. 2012, 173, 134–158. [Google Scholar] [CrossRef]
  179. Yang, C.; Song, G.; Lim, W. Effects of Mycotoxin-Contaminated Feed on Farm Animals. J. Hazard. Mater. 2020, 389, 122087. [Google Scholar] [CrossRef]
  180. Summers, K.L. Chapter 10 Mycotoxins and Swine Gut Health. In Environmental Effects on Gut Health in Production Animals; Wageningen Academic: Leiden, The Netherlands, 2024; pp. 198–212. ISBN 978-90-04-69546-7. [Google Scholar]
  181. Pierron, A.; Alassane-Kpembi, I.; Oswald, I.P. Impact of Mycotoxin on Immune Response and Consequences for Pig Health. Anim. Nutr. 2016, 2, 63–68. [Google Scholar] [CrossRef] [PubMed]
  182. Meneely, J.; Greer, B.; Kolawole, O.; Elliott, C. T-2 and HT-2 Toxins: Toxicity, Occurrence and Analysis: A Review. Toxins 2023, 15, 481. [Google Scholar] [CrossRef]
  183. Minervini, F.; Dell’Aquila, M.E. Zearalenone and Reproductive Function in Farm Animals. Int. J. Mol. Sci. 2008, 9, 2570–2584. [Google Scholar] [CrossRef]
  184. Denli, M.; Perez, J. Ochratoxins in Feed, a Risk for Animal and Human Health: Control Strategies. Toxins 2010, 2, 1065–1077. [Google Scholar] [CrossRef]
  185. Gruber-Dorninger, C.; Jenkins, T.; Schatzmayr, G. Global Mycotoxin Occurrence in Feed: A Ten-Year Survey. Toxins 2019, 11, 375. [Google Scholar] [CrossRef] [PubMed]
  186. Medina, Á.; González-Jartín, J.M.; Sainz, M.J. Impact of Global Warming on Mycotoxins. Curr. Opin. Food Sci. 2017, 18, 76–81. [Google Scholar] [CrossRef]
  187. Kabak, B.; Dobson, A.D.W. Mycotoxins in Spices and Herbs–An Update. Crit. Rev. Food Sci. Nutr. 2017, 57, 18–34. [Google Scholar] [CrossRef]
  188. Manubolu, M.; Goodla, L.; Pathakoti, K.; Malmlöf, K. Enzymes as Direct Decontaminating Agents—Mycotoxins. In Enzymes in Human and Animal Nutrition; Elsevier: Amsterdam, The Netherlands, 2018; pp. 313–330. ISBN 978-0-12-805419-2. [Google Scholar]
  189. Ji, C.; Fan, Y.; Zhao, L. Review on Biological Degradation of Mycotoxins. Anim. Nutr. 2016, 2, 127–133. [Google Scholar] [CrossRef]
  190. Clarke, L.C.; Sweeney, T.; Curley, E.; Duffy, S.K.; Vigors, S.; Rajauria, G.; O’Doherty, J.V. Mycotoxin Binder Increases Growth Performance, Nutrient Digestibility and Digestive Health of Finisher Pigs Offered Wheat Based Diets Grown under Different Agronomical Conditions. Anim. Feed Sci. Technol. 2018, 240, 52–65. [Google Scholar] [CrossRef]
  191. Kolosova, A.; Stroka, J. Substances for Reduction of the Contamination of Feed by Mycotoxins: A Review. World Mycotoxin J. 2011, 4, 225–256. [Google Scholar] [CrossRef]
  192. Elliott, C.T.; Connolly, L.; Kolawole, O. Potential Adverse Effects on Animal Health and Performance Caused by the Addition of Mineral Adsorbents to Feeds to Reduce Mycotoxin Exposure. Mycotoxin Res. 2020, 36, 115–126. [Google Scholar] [CrossRef]
  193. Jokiniemi, H.T.; Ahokas, J.M. Drying Process Optimisation in a Mixed-Flow Batch Grain Dryer. Biosyst. Eng. 2014, 121, 209–220. [Google Scholar] [CrossRef]
  194. Zhang, F.; Adeola, O. Techniques for Evaluating Digestibility of Energy, Amino Acids, Phosphorus, and Calcium in Feed Ingredients for Pigs. Anim. Nutr. 2017, 3, 344–352. [Google Scholar] [CrossRef]
  195. Sharma, V.; Chandel, S.S. Performance and Degradation Analysis for Long Term Reliability of Solar Photovoltaic Systems: A Review. Renew. Sustain. Energy Rev. 2013, 27, 753–767. [Google Scholar] [CrossRef]
  196. EL-Mesery, H.S.; EL-Seesy, A.I.; Hu, Z.; Li, Y. Recent Developments in Solar Drying Technology of Food and Agricultural Products: A Review. Renew. Sustain. Energy Rev. 2022, 157, 112070. [Google Scholar] [CrossRef]
  197. Olivkar, P.R.; Katekar, V.P.; Deshmukh, S.S.; Palatkar, S.V. Effect of Sensible Heat Storage Materials on the Thermal Performance of Solar Air Heaters: State-of-the-Art Review. Renew. Sustain. Energy Rev. 2022, 157, 112085. [Google Scholar] [CrossRef]
  198. Panigrahi, S.S.; Luthra, K.; Singh, C.B.; Atungulu, G.; Corscadden, K. On-Farm Grain Drying System Sustainability: Current Energy and Carbon Footprint Assessment with Potential Reform Measures. Sustain. Energy Technol. Assess. 2023, 60, 103430. [Google Scholar] [CrossRef]
  199. Koyuncu, S.; Andersson, M.G.; Löfström, C.; Skandamis, P.N.; Gounadaki, A.; Zentek, J.; Häggblom, P. Organic Acids for Control of Salmonella in Different Feed Materials. BMC Vet. Res. 2013, 9, 81. [Google Scholar] [CrossRef] [PubMed]
  200. Dijksterhuis, J.; Meijer, M.; Van Doorn, T.; Houbraken, J.; Bruinenberg, P. The Preservative Propionic Acid Differentially Affects Survival of Conidia and Germ Tubes of Feed Spoilage Fungi. Int. J. Food Microbiol. 2019, 306, 108258. [Google Scholar] [CrossRef]
  201. Schmidt, M.; Zannini, E.; Lynch, K.M.; Arendt, E.K. Novel Approaches for Chemical and Microbiological Shelf Life Extension of Cereal Crops. Crit. Rev. Food Sci. Nutr. 2019, 59, 3395–3419. [Google Scholar] [CrossRef]
  202. Abbas, A.; Adesina, A.Y.; Suleiman, R.K. Influence of Organic Acids and Related Organic Compounds on Corrosion Behavior of Stainless Steel—A Critical Review. Metals 2023, 13, 1479. [Google Scholar] [CrossRef]
  203. Maher, S.; Sweeney, T.; Kiernan, D.P.; Ryan, M.T.; Gath, V.; Vigors, S.; Connolly, K.R.; O’Doherty, J.V. Organic Acid Preservation of Cereal Grains Improves Grain Quality, Growth Performance, and Intestinal Health of Post-Weaned Pigs. Anim. Feed Sci. Technol. 2024, 316, 116078. [Google Scholar] [CrossRef]
  204. Connolly, K.R.; Sweeney, T.; Kiernan, D.P.; Round, A.; Ryan, M.T.; Gath, V.; Maher, S.; Vigors, S.; O’Doherty, J.V. The Role of Propionic Acid as a Feed Additive and Grain Preservative on Weanling Pig Performance and Digestive Health. Anim. Feed Sci. Technol. 2025, 321, 116237. [Google Scholar] [CrossRef]
  205. Connolly, K.R.; Sweeney, T.; Ryan, M.T.; Vigors, S.; O’Doherty, J.V. Impact of Reduced Dietary Crude Protein and Propionic Acid Preservation on Intestinal Health and Growth Performance in Post-Weaned Pigs. Animals 2025, 15, 702. [Google Scholar] [CrossRef]
  206. Connolly, K.R.; Sweeney, T.; Ryan, M.T.; Vigors, S.; O’Doherty, J.V. Effects of Butyric Acid Supplementation on the Gut Microbiome and Growth Performance of Weanling Pigs Fed a Low-Crude Protein, Propionic Acid-Preserved Grain Diet. Microorganisms 2025, 13, 689. [Google Scholar] [CrossRef] [PubMed]
  207. Maher, S.; Sweeney, T.; Vigors, S.; O’Doherty, J.V. Maternal and/or Direct Feeding of Organic Acid-Preserved Cereal Grains Improves Performance and Digestive Health of Pigs from Birth to Slaughter. Anim. Feed Sci. Technol. 2025, 323, 116295. [Google Scholar] [CrossRef]
  208. Bonetti, A.; Tugnoli, B.; Piva, A.; Grilli, E. Towards Zero Zinc Oxide: Feeding Strategies to Manage Post-Weaning Diarrhea in Piglets. Animals 2021, 11, 642. [Google Scholar] [CrossRef]
  209. Cadéro, A.; Aubry, A.; Dourmad, J.Y.; Salaün, Y.; Garcia-Launay, F. Effects of Interactions between Feeding Practices, Animal Health and Farm Infrastructure on Technical, Economic and Environmental Performances of a Pig-Fattening Unit. Animal 2020, 14, s348–s359. [Google Scholar] [CrossRef] [PubMed]
  210. Russell, J.B.; Diez-Gonzalez, F. The Effects of Fermentation Acids on Bacterial Growth. In Advances in Microbial Physiology; Elsevier: Amsterdam, The Netherlands, 1998; Volume 39, pp. 205–234. ISBN 978-0-12-027739-1. [Google Scholar]
  211. Brul, S.; Coote, P. Preservative Agents in Foods Mode of Action and Microbial Resistance Mechanisms. Int. J. Food Microbiol. 1999, 50, 1–17. [Google Scholar] [CrossRef]
  212. O’ Meara, F.M.; Gardiner, G.E.; O’ Doherty, J.V.; Lawlor, P.G. Effect of Dietary Inclusion of Benzoic Acid (VevoVitall®) on the Microbial Quality of Liquid Feed and the Growth and Carcass Quality of Grow-Finisher Pigs. Livest. Sci. 2020, 237, 104043. [Google Scholar] [CrossRef]
  213. Kim, Y.Y.; Kil, D.Y.; Oh, H.K.; Han, I.K. Acidifier as an Alternative Material to Antibiotics in Animal Feed. Asian-Australas. J. Anim. Sci. 2005, 18, 1048–1060. [Google Scholar] [CrossRef]
  214. Jackman, J.A.; Boyd, R.D.; Elrod, C.C. Medium-Chain Fatty Acids and Monoglycerides as Feed Additives for Pig Production: Towards Gut Health Improvement and Feed Pathogen Mitigation. J. Anim. Sci. Biotechnol. 2020, 11, 44. [Google Scholar] [CrossRef]
  215. Ferronato, G.; Prandini, A. Dietary Supplementation of Inorganic, Organic, and Fatty Acids in Pig: A Review. Animals 2020, 10, 1740. [Google Scholar] [CrossRef]
  216. Pearlin, B.V.; Muthuvel, S.; Govidasamy, P.; Villavan, M.; Alagawany, M.; Ragab Farag, M.; Dhama, K.; Gopi, M. Role of Acidifiers in Livestock Nutrition and Health: A Review. J. Anim. Physiol. Anim. Nutr. 2020, 104, 558–569. [Google Scholar] [CrossRef]
  217. Nowak, P.; Zaworska-Zakrzewska, A.; Frankiewicz, A.; Kasprowicz-Potocka, M. The Effects and Mechanisms of Acids on the Health of Piglets and Weaners—A Review. Ann. Anim. Sci. 2021, 21, 433–455. [Google Scholar] [CrossRef]
  218. Rathnayake, D.; Mun, H.S.; Dilawar, M.A.; Baek, K.S.; Yang, C.J. Time for a Paradigm Shift in Animal Nutrition Metabolic Pathway: Dietary Inclusion of Organic Acids on the Production Parameters, Nutrient Digestibility, and Meat Quality Traits of Swine and Broilers. Life 2021, 11, 476. [Google Scholar] [CrossRef]
  219. Rao, Z.-X.; Tokach, M.D.; Woodworth, J.C.; DeRouchey, J.M.; Goodband, R.D.; Gebhardt, J.T. Effects of Various Feed Additives on Finishing Pig Growth Performance and Carcass Characteristics: A Review. Animals 2023, 13, 200. [Google Scholar] [CrossRef] [PubMed]
  220. Connolly, K.R.; Sweeney, T.; O’Doherty, J.V. Sustainable Nutritional Strategies for Gut Health in Weaned Pigs: The Role of Reduced Dietary Crude Protein, Organic Acids and Butyrate Production. Animals 2024, 15, 66. [Google Scholar] [CrossRef]
  221. Nguyen, V.T.H.L.; Ho, T.T.; Le, N.A.T.; Ho, V.D. Acidifiers as Alternatives for Antibiotics Reduction and Gut Health Improvement for Poultry and Swine. In Veterinary Medicine and Science; Babinszky, L., Ed.; IntechOpen: London, UK, 2024; Volume 20, ISBN 978-1-83769-081-7. [Google Scholar]
  222. Heo, J.M.; Opapeju, F.O.; Pluske, J.R.; Kim, J.C.; Hampson, D.J.; Nyachoti, C.M. Gastrointestinal Health and Function in Weaned Pigs: A Review of Feeding Strategies to Control Post-Weaning Diarrhoea without Using in-Feed Antimicrobial Compounds: Feeding Strategies without Using in-Feed Antibiotics. J. Anim. Physiol. Anim. Nutr. 2013, 97, 207–237. [Google Scholar] [CrossRef] [PubMed]
  223. Tung, C.M.; Pettigrew, J.E. Critical Review of Acidifiers; National Pork Board: Des Moines, IA, USA, 2006. [Google Scholar]
  224. Grecco, H.A.T.; Amorim, A.B.; Saleh, M.A.D.; Tse, M.L.P.; Telles, F.G.; Miassi, G.M.; Pimenta, G.M.; Berto, D.A. Evaluation of Growth Performance and Gastro-Intestinal Parameters on the Response of Weaned Piglets to Dietary Organic Acids. An. Acad. Bras. Ciênc. 2018, 90, 401–414. [Google Scholar] [CrossRef]
  225. Hansen, C.F.; Riis, A.L.; Bresson, S.; Højbjerg, O.; Jensen, B.B. Feeding Organic Acids Enhances the Barrier Function against Pathogenic Bacteria of the Piglet Stomach. Livest. Sci. 2007, 108, 206–209. [Google Scholar] [CrossRef]
  226. Pieper, R.; Villodre Tudela, C.; Taciak, M.; Bindelle, J.; Pérez, J.F.; Zentek, J. Health Relevance of Intestinal Protein Fermentation in Young Pigs. Anim. Health Res. Rev. 2016, 17, 137–147. [Google Scholar] [CrossRef]
  227. Paulicks, B.R.; Roth, F.X.; Kirchgessner, M. Effects of Potassium Diformate (Formi® LHS) in Combination with Different Grains and Energy Densities in the Feed on Growth Performance of Weaned Piglets. J. Anim. Physiol. Anim. Nutr. 2000, 84, 102–111. [Google Scholar] [CrossRef]
  228. Liu, Y.; Espinosa, C.D.; Abelilla, J.J.; Casas, G.A.; Lagos, L.V.; Lee, S.A.; Kwon, W.B.; Mathai, J.K.; Navarro, D.M.D.L.; Jaworski, N.W.; et al. Non-Antibiotic Feed Additives in Diets for Pigs: A Review. Anim. Nutr. 2018, 4, 113–125. [Google Scholar] [CrossRef]
  229. Kuang, Y.; Wang, Y.; Zhang, Y.; Song, Y.; Zhang, X.; Lin, Y.; Che, L.; Xu, S.; Wu, D.; Xue, B.; et al. Effects of Dietary Combinations of Organic Acids and Medium Chain Fatty Acids as a Replacement of Zinc Oxide on Growth, Digestibility and Immunity of Weaned Pigs. Anim. Feed Sci. Technol. 2015, 208, 145–157. [Google Scholar] [CrossRef]
  230. Lee, J.; Kim, J.W.; Hall, H.; Nyachoti, C.M. Effect of Dietary Organic Acids Supplementation on Growth Performance, Nutrient Digestibility, and Gut Morphology in Weaned Pigs. Can. J. Anim. Sci. 2022, 102, 255–265. [Google Scholar] [CrossRef]
  231. Walia, K.; Argüello, H.; Lynch, H.; Leonard, F.C.; Grant, J.; Yearsley, D.; Kelly, S.; Duffy, G.; Gardiner, G.E.; Lawlor, P.G. Effect of Strategic Administration of an Encapsulated Blend of Formic Acid, Citric Acid, and Essential Oils on Salmonella Carriage, Seroprevalence, and Growth of Finishing Pigs. Prev. Vet. Med. 2017, 137, 28–35. [Google Scholar] [CrossRef] [PubMed]
  232. Nguyen, D.H.; Seok, W.J.; Kim, I.H. Organic Acids Mixture as a Dietary Additive for Pigs—A Review. Animals 2020, 10, 952. [Google Scholar] [CrossRef]
  233. Tsiloyiannis, V.K.; Kyriakis, S.C.; Vlemmas, J.; Sarris, K. The Effect of Organic Acids on the Control of Porcine Post-Weaning Diarrhoea. Res. Vet. Sci. 2001, 70, 287–293. [Google Scholar] [CrossRef]
  234. Lei, X.J.; Park, J.W.; Baek, D.H.; Kim, J.K.; Kim, I.H. Feeding the Blend of Organic Acids and Medium Chain Fatty Acids Reduces the Diarrhea in Piglets Orally Challenged with Enterotoxigenic Escherichia Coli K88. Anim. Feed Sci. Technol. 2017, 224, 46–51. [Google Scholar] [CrossRef]
  235. Pluske, J.R.; Turpin, D.L.; Sahibzada, S.; Pineda, L.; Han, Y.; Collins, A. Impacts of Feeding Organic Acid-Based Feed Additives on Diarrhea, Performance, and Fecal Microbiome Characteristics of Pigs after Weaning Challenged with an Enterotoxigenic Strain of Escherichia Coli. Transl. Anim. Sci. 2021, 5, txab212. [Google Scholar] [CrossRef]
  236. Pluske, J.R.; Hampson, D.J.; Williams, I.H. Factors Influencing the Structure and Function of the Small Intestine in the Weaned Pig: A Review. Livest. Prod. Sci. 1997, 51, 215–236. [Google Scholar] [CrossRef]
  237. Lallès, J.-P.; Boudry, G.; Favier, C.; Le Floc’h, N.; Luron, I.; Montagne, L.; Oswald, I.P.; Pié, S.; Piel, C.; Sève, B. Gut Function and Dysfunction in Young Pigs: Physiology. Anim. Res. 2004, 53, 301–316. [Google Scholar] [CrossRef]
  238. Wen, Z.-S.; Lu, J.-J.; Zou, X.-T. Effects of Sodium Butyrate on the Intestinal Morphology and DNA-Binding Activity of Intestinal Nuclear Factor-κB in Weanling Pigs. J. Anim. Vet. Adv. 2012, 11, 814–821. [Google Scholar] [CrossRef]
  239. Diao, H.; Gao, Z.; Yu, B.; Zheng, P.; He, J.; Yu, J.; Huang, Z.; Chen, D.; Mao, X. Effects of Benzoic Acid (VevoVitall®) on the Performance and Jejunal Digestive Physiology in Young Pigs. J. Anim. Sci. Biotechnol. 2016, 7, 32. [Google Scholar] [CrossRef] [PubMed]
  240. Long, S.F.; Xu, Y.T.; Pan, L.; Wang, Q.Q.; Wang, C.L.; Wu, J.Y.; Wu, Y.Y.; Han, Y.M.; Yun, C.H.; Piao, X.S. Mixed Organic Acids as Antibiotic Substitutes Improve Performance, Serum Immunity, Intestinal Morphology and Microbiota for Weaned Piglets. Anim. Feed Sci. Technol. 2018, 235, 23–32. [Google Scholar] [CrossRef]
  241. Luise, D.; Motta, V.; Salvarani, C.; Chiappelli, M.; Fusco, L.; Bertocchi, M.; Mazzoni, M.; Maiorano, G.; Costa, L.N.; Van Milgen, J.; et al. Long-Term Administration of Formic Acid to Weaners: Influence on Intestinal Microbiota, Immunity Parameters and Growth Performance. Anim. Feed Sci. Technol. 2017, 232, 160–168. [Google Scholar] [CrossRef]
  242. Wensley, M.R.; Tokach, M.D.; Woodworth, J.C.; Goodband, R.D.; Gebhardt, J.T.; DeRouchey, J.M.; McKilligan, D. Maintaining Continuity of Nutrient Intake after Weaning. II. Review of Post-Weaning Strategies. Transl. Anim. Sci. 2021, 5, txab022. [Google Scholar] [CrossRef] [PubMed]
  243. Kholif, A.E.; Gouda, G.A.; Olafadehan, O.A.; Sallam, S.M.; Anele, U.Y. Acidifiers and Organic Acids in Livestock Nutrition and Health. In Organic Feed Additives for Livestock; Elsevier: Amsterdam, The Netherlands, 2025; pp. 43–56. ISBN 978-0-443-13510-1. [Google Scholar]
  244. Ottosen, M.; Mackenzie, S.G.; Wallace, M.; Kyriazakis, I. A Method to Estimate the Environmental Impacts from Genetic Change in Pig Production Systems. Int. J. Life Cycle Assess. 2020, 25, 523–537. [Google Scholar] [CrossRef]
  245. Mosenthin, R.; Sauer, W.C.; Ahrens, F.; De Lange, C.F.M.; Bornholdt, U. Effect of Dietary Supplements of Propionic Acid, Siliceous Earth or a Combination of These on the Energy, Protein and Amino Acid Digestibilities and Concentrations of Microbial Metabolites in the Digestive Tract of Growing Pigs. Anim. Feed Sci. Technol. 1992, 37, 245–255. [Google Scholar] [CrossRef]
  246. Mroz, Z.; Jongbloed, A.W.; Partanen, K.H.; Vreman, K.; Kemme, P.A.; Kogut, J. The Effects of Calcium Benzoate in Diets with or without Organic Acids on Dietary Buffering Capacity, Apparent Digestibility, Retention of Nutrients, and Manure Characteristics in Swine. J. Anim. Sci. 2000, 78, 2622. [Google Scholar] [CrossRef]
  247. Nhara, R.B.; Marume, U.; Nantapo, C.W.T. Potential of Organic Acids, Essential Oils and Their Blends in Pig Diets as Alternatives to Antibiotic Growth Promoters. Animals 2024, 14, 762. [Google Scholar] [CrossRef]
  248. Nkosi, D.V.; Bekker, J.L.; Hoffman, L.C. The Use of Organic Acids (Lactic and Acetic) as a Microbial Decontaminant during the Slaughter of Meat Animal Species: A Review. Foods 2021, 10, 2293. [Google Scholar] [CrossRef]
  249. Barcenilla, C.; Ducic, M.; López, M.; Prieto, M.; Álvarez-Ordóñez, A. Application of Lactic Acid Bacteria for the Biopreservation of Meat Products: A Systematic Review. Meat Sci. 2022, 183, 108661. [Google Scholar] [CrossRef]
  250. Li, Z.; Yi, G.; Yin, J.; Sun, P.; Li, D.; Knight, C. Effects of Organic Acids on Growth Performance, Gastrointestinal pH, Intestinal Microbial Populations and Immune Responses of Weaned Pigs. Asian-Australas. J. Anim. Sci. 2008, 21, 252–261. [Google Scholar] [CrossRef]
  251. Ahmed, S.T.; Hwang, J.A.; Hoon, J.; Mun, H.S.; Yang, C.J. Comparison of Single and Blend Acidifiers as Alternative to Antibiotics on Growth Performance, Fecal Microflora, and Humoral Immunity in Weaned Piglets. Asian-Australas. J. Anim. Sci. 2014, 27, 93–100. [Google Scholar] [CrossRef] [PubMed]
  252. Han, Y.S.; Tang, C.H.; Zhao, Q.Y.; Zhan, T.F.; Zhang, K.; Han, Y.M.; Zhang, J.M. Effects of Dietary Supplementation with Combinations of Organic and Medium Chain Fatty Acids as Replacements for Chlortetracycline on Growth Performance, Serum Immunity, and Fecal Microbiota of Weaned Piglets. Livest. Sci. 2018, 216, 210–218. [Google Scholar] [CrossRef]
  253. Li, S.; Zheng, J.; Deng, K.; Chen, L.; Zhao, X.L.; Jiang, X.M.; Fang, Z.F.; Che, L.Q.; Xu, S.Y.; Feng, B.; et al. Supplementation with Organic Acids Showing Different Effects on Growth Performance, Gut Morphology and Microbiota of Weaned Pigs Fed with Highly or Less Digestible Diets. J. Anim. Sci. 2018, 96, 3302–3318. [Google Scholar] [CrossRef] [PubMed]
  254. de Groot, N.; Fariñas, F.; Cabrera-Gómez, C.G.; Pallares, F.J.; Ramis, G. Blend of Organic Acids Improves Gut Morphology and Affects Inflammation Response in Piglets after Weaning. Front. Anim. Sci. 2024, 5, 1308514. [Google Scholar] [CrossRef]
  255. Xu, Y.T.; Liu, L.; Long, S.F.; Pan, L.; Piao, X.S. Effect of Organic Acids and Essential Oils on Performance, Intestinal Health and Digestive Enzyme Activities of Weaned Pigs. Anim. Feed Sci. Technol. 2018, 235, 110–119. [Google Scholar] [CrossRef]
  256. Yang, Y.; Lee, K.Y.; Kim, I.H. Effects of Dietary Protected Organic Acids on Growth Performance, Nutrient Digestibility, Fecal Microflora, Diarrhea Score, and Fecal Gas Emission in Weanling Pigs. Can. J. Anim. Sci. 2019, 99, 514–520. [Google Scholar] [CrossRef]
  257. Xiang, X.-D.; Deng, Z.-C.; Wang, Y.-W.; Sun, H.; Wang, L.; Han, Y.-M.; Wu, Y.-Y.; Liu, J.-G.; Sun, L.-H. Organic Acids Improve Growth Performance with Potential Regulation of Redox Homeostasis, Immunity, and Microflora in Intestines of Weaned Piglets. Antioxidants 2021, 10, 1665. [Google Scholar] [CrossRef]
  258. Upadhaya, S.D.; Lee, K.Y.; Kim, I.H. Influence of Protected Organic Acid Blends and Diets with Different Nutrient Densities on Growth Performance, Nutrient Digestibility and Faecal Noxious Gas Emission in Growing Pigs. Veter. Med. 2014, 59, 491–497. [Google Scholar] [CrossRef]
  259. Upadhaya, S.D.; Lee, K.Y.; Kim, I.H. Effect of Protected Organic Acid Blends on Growth Performance, Nutrient Digestibility and Faecal Micro Flora in Growing Pigs. J. Appl. Anim. Res. 2016, 44, 238–242. [Google Scholar] [CrossRef]
  260. Upadhaya, S.D.; Lee, K.Y.; Kim, I.H. Protected Organic Acid Blends as an Alternative to Antibiotics in Finishing Pigs. Asian-Australas. J. Anim. Sci. 2014, 27, 1600–1607. [Google Scholar] [CrossRef] [PubMed]
  261. Gaffield, K.N.; Becker, G.J.; Smallfield, J.L.; DeRouchey, J.M.; Tokach, M.D.; Woodworth, J.C.; Goodband, R.D.; Lohrmann, T.; Lückstädt, C.; Menegat, M.B.; et al. Evaluating Increasing Levels of Sodium Diformate in Diets for Nursery and Finishing Pigs on Growth Performance, Fecal Dry Matter, and Carcass Characteristics. Transl. Anim. Sci. 2024, 8, txae085. [Google Scholar] [CrossRef]
  262. Kiernan, D.P.; O’Doherty, J.V.; Ryan, M.T.; Sweeney, T. Effects of Maternal Probiotics and Piglet Dietary Tryptophan Level on Gastric Function Pre- and Post-Weaning. Agriculture 2025, 15, 310. [Google Scholar] [CrossRef]
  263. Blavi, L.; Solà-Oriol, D.; Llonch, P.; López-Vergé, S.; Martín-Orúe, S.M.; Pérez, J.F. Management and Feeding Strategies in Early Life to Increase Piglet Performance and Welfare around Weaning: A Review. Animals 2021, 11, 302. [Google Scholar] [CrossRef]
  264. Lu, H.; Su, S.; Ajuwon, K.M. Butyrate Supplementation to Gestating Sows and Piglets Induces Muscle and Adipose Tissue Oxidative Genes and Improves Growth Performance. J. Anim. Sci. 2012, 90, 430–432. [Google Scholar] [CrossRef] [PubMed]
  265. Crespo-Piazuelo, D.; Gardiner, G.E.; Ranjitkar, S.; Bouwhuis, M.A.; Ham, R.; Phelan, J.P.; Marsh, A.; Lawlor, P.G. Maternal Supplementation with Bacillus Altitudinis Spores Improves Porcine Offspring Growth Performance and Carcass Weight. Br. J. Nutr. 2022, 127, 403–420. [Google Scholar] [CrossRef]
  266. Heim, G.; Sweeney, T.; O’Shea, C.J.; Doyle, D.N.; O’Doherty, J.V. Effect of Maternal Supplementation with Seaweed Extracts on Growth Performance and Aspects of Gastrointestinal Health of Newly Weaned Piglets after Challenge with Enterotoxigenic Escherichia Coli K88. Br. J. Nutr. 2014, 112, 1955–1965. [Google Scholar] [CrossRef] [PubMed]
  267. Dowley, A.; O’Doherty, J.V.; Mukhopadhya, A.; Conway, E.; Vigors, S.; Maher, S.; Ryan, M.T.; Sweeney, T. Maternal Supplementation with a Casein Hydrolysate and Yeast Beta-Glucan from Late Gestation through Lactation Improves Gastrointestinal Health of Piglets at Weaning. Sci. Rep. 2022, 12, 17407. [Google Scholar] [CrossRef]
  268. Rooney, H.B.; O’Driscoll, K.; O’Doherty, J.V.; Lawlor, P.G. Effect of L-Carnitine Supplementation and Sugar Beet Pulp Inclusion in Gilt Gestation Diets on Gilt Live Weight, Lactation Feed Intake, and Offspring Growth from Birth to Slaughter. J. Anim. Sci. 2019, 97, 4208–4218. [Google Scholar] [CrossRef]
  269. Kiernan, D.P.; O’Doherty, J.V.; Sweeney, T. The Effect of Prebiotic Supplements on the Gastrointestinal Microbiota and Associated Health Parameters in Pigs. Animals 2023, 13, 3012. [Google Scholar] [CrossRef]
  270. Jenkins, A.K.; DeRouchey, J.M.; Gebhardt, J.T.; Tokach, M.D.; Woodworth, J.C.; Goodband, R.D.; Loughmiller, J.A.; Kremer, B.T. Effect of Yeast Probiotics in Lactation and Yeast Cell Wall Prebiotic and Bacillus Subtilis Probiotic in Nursery on Lifetime Growth Performance, Immune Response, and Carcass Characteristics. J. Anim. Sci. 2024, 102, skae320. [Google Scholar] [CrossRef] [PubMed]
  271. Tokach, M.D.; Menegat, M.B.; Gourley, K.M.; Goodband, R.D. Review: Nutrient Requirements of the Modern High-Producing Lactating Sow, with an Emphasis on Amino Acid Requirements. Animal 2019, 13, 2967–2977. [Google Scholar] [CrossRef] [PubMed]
  272. Liu, S.T.; Hou, W.X.; Cheng, S.Y.; Shi, B.M.; Shan, A.S. Effects of Dietary Citric Acid on Performance, Digestibility of Calcium and Phosphorus, Milk Composition and Immunoglobulin in Sows during Late Gestation and Lactation. Anim. Feed Sci. Technol. 2014, 191, 67–75. [Google Scholar] [CrossRef]
  273. Devi, S.M.; Lee, K.Y.; Kim, I.H. Analysis of the Effect of Dietary Protected Organic Acid Blend on Lactating Sows and Their Piglets. Rev. Bras. Zootec. 2016, 45, 39–47. [Google Scholar] [CrossRef]
  274. Lan, R.; Kim, I. Effects of Organic Acid and Medium Chain Fatty Acid Blends on the Performance of Sows and Their Piglets. Anim. Sci. J. 2018, 89, 1673–1679. [Google Scholar] [CrossRef] [PubMed]
  275. Chen, J.; Guo, J.; Guan, W.; Song, J.-J.; Deng, Z.-X.; Cheng, L.; Deng, Y.-L.; Chen, F.; Zhang, S.-H.; Zhang, Y.-Z.; et al. Effect of Pad-Fan Cooling and Dietary Organic Acid Supplementation during Late Gestation and Lactation on Reproductive Performance and Antioxidant Status of Multiparous Sows in Hot Weather. Trop. Anim. Health Prod. 2018, 50, 973–982. [Google Scholar] [CrossRef]
  276. Sampath, V.; Park, J.H.; Pineda, L.; Han, Y.; Kim, I.H. Impact of Synergistic Blend of Organic Acids on the Performance of Late Gestating Sows and Their Offspring. Ital. J. Anim. Sci. 2022, 21, 1334–1342. [Google Scholar] [CrossRef]
  277. Devillers, N.; Le Dividich, J.; Prunier, A. Influence of Colostrum Intake on Piglet Survival and Immunity. Animal 2011, 5, 1605–1612. [Google Scholar] [CrossRef]
  278. Liu, H.; Zeng, X.; Zhang, G.; Hou, C.; Li, N.; Yu, H.; Shang, L.; Zhang, X.; Trevisi, P.; Yang, F.; et al. Maternal Milk and Fecal Microbes Guide the Spatiotemporal Development of Mucosa-Associated Microbiota and Barrier Function in the Porcine Neonatal Gut. BMC Biol. 2019, 17, 106. [Google Scholar] [CrossRef]
  279. Chen, J.; Xu, Q.; Li, Y.; Tang, Z.; Sun, W.; Zhang, X.; Sun, J.; Sun, Z. Comparative Effects of Dietary Supplementations with Sodium Butyrate, Medium-Chain Fatty Acids, and n-3 Polyunsaturated Fatty Acids in Late Pregnancy and Lactation on the Reproductive Performance of Sows and Growth Performance of Suckling Piglets. J. Anim. Sci. 2019, 97, 4256–4267. [Google Scholar] [CrossRef]
  280. Leblois, J.; Massart, S.; Li, B.; Wavreille, J.; Bindelle, J.; Everaert, N. Modulation of Piglets’ Microbiota: Differential Effects by a High Wheat Bran Maternal Diet during Gestation and Lactation. Sci. Rep. 2017, 7, 7426. [Google Scholar] [CrossRef] [PubMed]
  281. Kiernan, D.P.; O’Doherty, J.V.; Sweeney, T. The Effect of Maternal Probiotic or Synbiotic Supplementation on Sow and Offspring Gastrointestinal Microbiota, Health, and Performance. Animals 2023, 13, 2996. [Google Scholar] [CrossRef] [PubMed]
  282. Law, K.; Lozinski, B.; Torres, I.; Davison, S.; Hilbrands, A.; Nelson, E.; Parra-Suescun, J.; Johnston, L.; Gomez, A. Disinfection of Maternal Environments Is Associated with Piglet Microbiome Composition from Birth to Weaning. mSphere 2021, 6, e00663-21. [Google Scholar] [CrossRef]
  283. Chen, X.; Xu, J.; Ren, E.; Su, Y.; Zhu, W. Co-Occurrence of Early Gut Colonization in Neonatal Piglets with Microbiota in the Maternal and Surrounding Delivery Environments. Anaerobe 2018, 49, 30–40. [Google Scholar] [CrossRef] [PubMed]
  284. Zhou, H.; Yu, B.; Sun, J.; Chen, H.; Liu, Z.; Ge, L.; Chen, D. Comparison of Maternal and Neonatal Gut Microbial Community and Function in a Porcine Model. Anim. Biotechnol. 2023, 34, 2972–2978. [Google Scholar] [CrossRef]
  285. Huting, A.M.S.; Middelkoop, A.; Guan, X.; Molist, F. Using Nutritional Strategies to Shape the Gastro-Intestinal Tracts of Suckling and Weaned Piglets. Animals 2021, 11, 402. [Google Scholar] [CrossRef]
  286. Lin, Y.; Li, D.; Ma, Z.; Che, L.; Feng, B.; Fang, Z.; Xu, S.; Zhuo, Y.; Li, J.; Hua, L.; et al. Maternal Tributyrin Supplementation in Late Pregnancy and Lactation Improves Offspring Immunity, Gut Microbiota, and Diarrhea Rate in a Sow Model. Front. Microbiol. 2023, 14, 1142174. [Google Scholar] [CrossRef]
  287. Yang, H.; Huang, X.; Fang, S.; Xin, W.; Huang, L.; Chen, C. Uncovering the Composition of Microbial Community Structure and Metagenomics among Three Gut Locations in Pigs with Distinct Fatness. Sci. Rep. 2016, 6, 27427. [Google Scholar] [CrossRef]
  288. Kropp, C.; Le Corf, K.; Relizani, K.; Tambosco, K.; Martinez, C.; Chain, F.; Rawadi, G.; Langella, P.; Claus, S.P.; Martin, R. The Keystone Commensal Bacterium Christensenella Minuta DSM 22607 Displays Anti-Inflammatory Properties Both In Vitro and In Vivo. Sci. Rep. 2021, 11, 11494. [Google Scholar] [CrossRef]
  289. Maher, S.; Sweeney, T.; Vigors, S.; McDonald, M.; O’Doherty, J.V. Effects of Organic Acid-Preserved Cereal Grains in Sow Diets during Late Gestation and Lactation on the Performance and Faecal Microbiota of Sows and Their Offspring. J. Anim. Sci. Biotechnol. 2025, 16, 43. [Google Scholar] [CrossRef]
  290. Øverland, M.; Bikker, P.; Fledderus, J. Potassium Diformate in the Diet of Reproducing Sows: Effect on Performance of Sows and Litters. Livest. Sci. 2009, 122, 241–247. [Google Scholar] [CrossRef]
  291. Balasubramanian, B.; Park, J.W.; Kim, I.H. Evaluation of the Effectiveness of Supplementing Micro-Encapsulated Organic Acids and Essential Oils in Diets for Sows and Suckling Piglets. Ital. J. Anim. Sci. 2016, 15, 626–633. [Google Scholar] [CrossRef]
  292. Jang, Y.D.; Lindemann, M.D.; Monegue, H.J.; Monegue, J.S. The Effect of Coated Sodium Butyrate Supplementation in Sow and Nursery Diets on Lactation Performance and Nursery Pig Growth Performance. Livest. Sci. 2017, 195, 13–20. [Google Scholar] [CrossRef]
  293. Villagómez-Estrada, S.; Melo-Durán, D.; Van Kuijk, S.; Pérez, J.F.; Solà-Oriol, D. Specialized Feed-Additive Blends of Short- and Medium-Chain Fatty Acids Improve Sow and Pig Performance During Nursery and Post-Weaning Phase. Animals 2024, 14, 3692. [Google Scholar] [CrossRef]
Figure 1. Schematic overview of the pig production chain from crop production to the farm gate, illustrating environmental hotspots and opportunities for intervention. Sustainable strategies include the use of regionally grown faba beans as alternatives to imported soybean, using organic acids for energy-efficient grain preservation, and applying targeted nutritional strategies to enhance gut health, feed efficiency, and nutrient management on farm. These interventions aim to lower greenhouse gas emissions, imported feed dependence, and nutrient losses across the system.
Figure 1. Schematic overview of the pig production chain from crop production to the farm gate, illustrating environmental hotspots and opportunities for intervention. Sustainable strategies include the use of regionally grown faba beans as alternatives to imported soybean, using organic acids for energy-efficient grain preservation, and applying targeted nutritional strategies to enhance gut health, feed efficiency, and nutrient management on farm. These interventions aim to lower greenhouse gas emissions, imported feed dependence, and nutrient losses across the system.
Animals 15 01403 g001
Table 1. The effects of organic acid-preserved grain on intestinal health, digestive function, and growth performance of pigs.
Table 1. The effects of organic acid-preserved grain on intestinal health, digestive function, and growth performance of pigs.
Production StageOrganic AcidEffects on Intestinal Health and Digestive FunctionEffects on Growth PerformanceRef.
Exp. 1 and 2: Growing Exp. 3: WeaningOrganic acid-preserved grain (57% formic acid blend)
  • Exp 1: Increased the diet DE and ME content.
  • Exp. 2: No effect on the CAID of amino acids or CP.
  • Exp. 3: No effect on the CATTD of DM, OM, GE, N, EE, P or Ca.
  • Exp. 3: Increased ADFI and ADG during d 0–28 PW and final BW on d 28 PW.
[36]
Weaning (7–22 kg)Organic acid-preserved grain (65% propionic acid blend)
  • Reduced faecal scores and diarrhoea incidence during d 0–21 PW.
  • Increased the CATTD of DM, OM, N, NDF, and GE on d 21 PW.
  • Increased the CAID of DM, OM, N, and GE on d 35 PW.
  • Reduced ileal Streptococcus and increased colonic Faecalibacterium on d 35 PW.
  • Reduced colonic BCFA on d 35 PW.
  • Increased ADFI and ADG during d 0–35 PW and final BW on d 35 PW.
  • Preserved grain outperformed pigs supplemented with ZnO after d 21 PW.
[203]
Weaning (7–21 kg)Organic acid-preserved grain (65% propionic acid blend)
  • Reduced ileal Escherichia and increased ileal and colonic Faecalibacterium on d 10 PW.
  • Increased colonic propionate on d 10 PW.
  • Increased ADFI and ADG during d 0–35 PW and final BW on d 35 PW.
[204]
Weaning (7–24 kg)Organic acid-preserved grain (65% propionic acid blend)
  • Increased ileal Lactobacillus and colonic Faecalibacterium and Prevotella on d 8 PW.
  • Preserved grain increased the CATTD of N in low CP diets (17%) on d 30 PW.
  • No effect on ADFI but improved FCR during d 0–35 PW and increased final BW on d 35 PW.
[205]
Weaning (7–23 kg)Organic acid-preserved grain (65% propionic acid blend)
  • Increased duodenal VH on d 8 PW and tended to increase jejunal VH:CD.
  • Increased the CATTD of DM, OM, N, and GE on d 30 PW.
  • Increased colonic Prevotellaceae on d 8 PW.
  • Increased ADFI during d 15–35 PW and improved FCR during d 0–35 PW.
[206]
Suckling to Slaughter (3–120 kg)Organic acid-preserved grain (65% propionic acid blend)
  • Increased the CATTD of DM, OM, N, and GE on d 30 PW and at slaughter.
  • Increased faecal microbial diversity at weaning and d 30 PW, and increased Faecalibacterium at slaughter.
  • No effect on ADFI, but increased ADG to slaughter, improved G:F from d 14 PW, higher BW from d 30 PW, and heavier carcass weight at slaughter.
[207]
ADFI, average daily feed intake; ADG, average daily gain; BCFA, branched-chain fatty acids; BW, body weight; Ca, calcium; CAID, coefficient of apparent ileal digestibility; CATTD, coefficient of apparent total tract digestibility; CP, crude protein; d, day; DM, dry matter; EE, ether extract; FCR, feed conversion ratio; GE, gross energy; G:F, gain-to-feed ratio; N, nitrogen; NDF, neutral detergent fibre; OM, organic matter; P, phosphorus; PW, post-weaning; VH, villus height; VH:CD, villus height-crypt depth ratio.
Table 2. The effects of dietary organic acid inclusion on intestinal health, digestive function, and growth performance of pigs.
Table 2. The effects of dietary organic acid inclusion on intestinal health, digestive function, and growth performance of pigs.
Production StageOrganic Acid and Inclusion LevelEffects on Intestinal Health and Digestive FunctionEffects on Growth PerformanceRef.
Weaning (7–26 kg)
  • OA1 (fumaric acid; 0.8–0.2%)
  • OA2 (Ca-formate, Ca-lactate, capric acid and caprylic acid blend; 0.3–0.2%)
  • Combination (OA1 + OA2)
  • No effect on duodenal morphology or gastric, jejunal, ileal, cecal, or rectal pH on d 14 PW.
  • OA1 reduced jejunal villus height and cecal E. coli counts on day 14 PW.
  • OA2 increased the relative weight of the large intestine on d 14 PW.
  • No synergistic effect of combination.
  • No effect on ADFI, ADG, or FCR during d 0–42 PW.
[224]
Weaning (9–18 kg)Ca-formate, Ca-lactate, lauric, myristic, and capric acid and citric acid blend (0.3%)
  • Upregulated the expression of jejunal amino acid transporters (EAAT3, CAT2).
  • Increased plasma IgG concentrations.
  • Increased the CAID of most amino acids.
  • Increased ileal and rectal Lactobacillus populations.
  • Increased ADFI, ADG, FCR, and final BW during d 0–28 PW.
[229]
Weaning (8–32 kg)
  • OA1 (formic and propionic acid blend; 0.1%)
  • OA2 (formic, propionic and butyric acid blend; 0.2%)
  • OA2 increased VH in the ileum, while both OA increased jejunal VH:CD on d 35 PW.
  • No effect on CATTD of DM, GE, or CP during d 14 or d 35 PW.
  • OA increased faecal Bifidobacteria on d 14 PW.
  • No effect on ADFI, ADG, or BW during d 0–35 PW.
  • OA1 tended to improve G:F overall.
[230]
Weaning (6–12 kg)Fumaric, citric, malic, caprylic and capric acids blend (0.2% or 0.4%)
  • Both levels reduced diarrhoea incidence during d 0–7, 7–14, and 14–21 PW.
  • Both levels increased ADFI, ADG, G:F, and final BW before and after E. coli K88 challenge.
[234]
Weaning (6–13 kg)Sodium butyrate (0.05 and 0.1%)
  • 0.1% increased villus height in the duodenum, jejunum and ileum and reduced jejunal crypt depth on d 21 PW.
  • 0.1% reduced duodenal/ileal, and colonic E. coli and duodenal/ileal Clostridium.
  • 0.05% had no effect on performance.
  • 0.1% increased ADFI, ADG, and G:F during d 0–21 PW and final BW on d 21 PW.
[238]
Weaning (9–20 kg)
  • OA1 (blend of formic, acetic and propionic acids combined with MCFA; 0.3%)
  • OA2 (phenolic compound, slow release C12, target release butyrate, MCFA and OA blend; 0.2%)
  • OA reduced diarrhoea incidence during d 0–14 PW and d 0–28 PW.
  • OA1 increased serum IgM during d 0–14 PW.
  • OA2 reduced jejunal CD, while both OA increased jejunal and ileal VH:CD on day 28 PW.
  • OA1 increased the CATTD of DM, NDF and ADF during d 14–28 PW.
  • OA2 increased the CATTD of NDF, ADF, and P during d 0–14 PW and EE, and P during d 14–28 PW.
  • OA reduced faecal E. coli populations on d 28 PW.
  • OA increased total faecal VFA concentrations, including higher acetic, propionic, and butyric acid on d 28 PW.
  • OA1 improved FCR during d 0–28 PW.
  • OA2 increased ADG during both d 0–14 and d 14–28 and improved FCR during d 0–28 PW.
[240]
Weaning (7–28 kg)Formic acid (0.14 or 0.64%)
  • No effect on gastric mucosa thickness, the number of parietal cells, or stomach weights on d 42 PW.
  • 0.64% increased jejunal microbial diversity on d 42 PW.
  • Both levels tended to increase ADFI and FCR and increased ADG during d 0–21 PW.
[241]
Weaning (8–18 kg)Butryic, fumaric and benzoic acid blend (0.5 and 1.0%)
  • No effect on digesta pH.
  • Tended to have higher duodenal and ileal Lactobacillus populations and lower ileal E. coli.
  • Increased ADG and FCR when challenged with E. coli K88.
[250]
Weaning (8–16 kg)
  • OA1 (citric acid; 0.5%)
  • OA2 (formic, propionic, lactic, and phosphoric acids; 0.4%)
  • OA1 increased serum IgG on d 28 PW.
  • OA reduced faecal Salmonella and E. coli populations on d 21 and 28 PW.
  • OA increased faecal Lactobacillus populations on d 14, 21 and 28 PW.
  • OA1 reduced ADFI, increased G:F but had no effect on ADG during d 0–28 PW.
  • OA2 reduced ADFI, ADG and G:F.
[251]
Weaning (8–13 kg)
  • OA1 (phenolic compound, slow release C12, target release butyrate, MCFA and OA blend; 0.2%)
  • OA2 (OA1 (0.2–0.4%) + formic, acetic, lactic, propionic, citric and sorbic acids and salt blend (0.6–0.4%)
  • No effect on diarrhoea incidence.
  • OA increased serum IgG on d 14 PW and IgA on d 28 PW.
  • OA increased total antioxidant capacity on d 14 and 28 PW.
  • No effect on faecal microbial diversity.
  • OA increased the faecal abundance of Firmicutes and reduced Proteobacteria
  • OA increased the abundance of Lactobacillus and Faecalibacterium.
  • OA1 had no effect on ADFI, ADG, FCR or final BW during d 0–28 PW.
  • OA2 improved overall ADG and FCR and final BW on d 28 PW.
[252]
Exp. 1: Weaning
(7–24 kg)
  • OA1 (phenolic compound, slow release C12, target release butyrate, MCFA, and OA blend; 0.2%)
  • OA2 (formic, acetic and propionic acids and MCFA blend; 0.3%)
  • Combination (OA1 + OA2)
  • OA1 and OA2 reduced diarrhoea index during d 15–17 PW.
  • No effect on gastric, jejunal, or colonic digesta pH.
  • OA2 increased duodenal VH d 28 PW.
  • OA1 increased caecal acetic and propionic acid concentrations on d 28 PW.
  • All OA increased colonic acetic, propionic and butyrate concentrations.
  • OA1 and OA2 increased colonic Lactobacillus, while OA2 also reduced colonic E. coli.
  • No effect on ADFI, ADG, FCR or BW during d 0–42 PW.
[253]
Exp. 2: Weaning
(7–24 kg)
  • OA1 (phenolic compound, slow release C12, target release butyrate, MCFA, and OA blend; 0.2%)
  • OA3 (formic acid blend; 0.3%)
  • Combination (OA1 + OA2)
  • All OA reduced diarrhoea index during d 0–7, 7–14, 14–21, and 0–28 PW.
  • No effect on gastric, duodenal, jejunal, ileal, or colonic digesta pH on d 49 PW.
  • Combination increased ileal VH and acetic and propionic acid concentrations.
  • OA1 and OA3 increased microbial diversity.
  • Combination increased the abundance of Prevotella in the colon.
  • OA had improved ADG and FCR during d 43–49 PW.
Weaning (6–20 kg)Sorbic, benzoic, butyric, capric, caprylic, and lauric acid blend (0.2%)
  • Increased ileal VH:CD on d 15 PW.
  • Tended to increase jejunal and ileal VH on d 30 PW.
  • Increased ileal VH on d 45 PW.
  • Increased BW on day 30 and 45 PW.
  • Tended to increase ADG during d 0–45 PW.
[254]
Weaning (9–20 kg)Benzoic acid, Ca-formate,
fumaric acid blend (0.15%)
  • Tended to reduce faecal scores during d 14–21 PW.
  • No effect on gastric, duodenal, jejunal, ileal, cecal, colonic or rectal pH.
  • Increased duodenal VH.
  • Increased the CATTD of CP, EE, Ca, and P on d 28 PW.
  • No effect on duodenal, jejunal, or ileal trypsin or chymotrypsin activity.
  • Increased faecal Lactobacillus populations on d 28 PW.
  • Increased ADG during d 14–28 and d 0–28 PW but no effect on ADFI or G:F.
[255]
Weaning (7–25 kg)Fumaric, citric, malic, caprylic and capric acids blend (0.1% or 0.2%)
  • Linear reduction in faecal scores.
  • Increased the CATTD of DM and GE and tended to increase N.
  • Increased faecal Lactobacillus populations and reduced E. coli and Salmonella.
  • Tended to increase faecal Bifidobacterium and reduce Clostridium perfringens.
  • Reduced faecal ammonia.
  • No effect on ADFI but improved ADG and G:F during d 0–42 PW.
[256]
Weaning (5–24 kg)
  • OA1 (formic, acetic acid and ammonium formate blend; 0.2%)
  • OA2 (formic acid, acetic, sorbic, propionic, lactic and citric acids, ammonium formate blend; 0.2%)
  • OA2 reduced diarrhoea incidence during d 0–14, d 14–49, and d 0–49 PW.
  • OA2 tended to reduce CD and increase VH:CD in the duodenum on d 49 PW.
  • No effect on jejunum lipase, amylase or protease activity on d 14 or d 49 PW.
  • OA1 increased ADFI and ADG during d 0–14 PW and tended to increase ADG during d 0–49 PW.
  • OA2 had no effect on ADFI, ADG, or FCR overall.
[257]
Growing (19–28 kg)Benzoic acid (0.5%)
  • Tended to reduce jejunal pH.
  • Increased trypsin, lipase, and amylase activity in the jejunum after 14 days.
  • Reduced CD and increased VH:CD in the jejunum.
  • Increased the CATTD of DM, GE, CP, and EE.
  • Increased ADFI, ADG and BW after 14 days.
[239]
Growing (23–50 kg)Fumaric, citric, malic, caprylic and capric acid blend
(0.1% or 0.2%)
  • No effect on the CATTD of DM, N, or GE, or faecal ammonia during week 6.
  • Increased ADG during the 6-week period.
[258]
Growing (23–54 kg)Fumaric, citric, malic, caprylic and capric acid blend
(0.1%, 0.2% or 0.4%)
  • No effect on the CATTD of DM, N, or GE during week 6.
  • 0.2% increased faecal Lactobacillus but no effect on faecal E. coli during week 6 in any group.
  • 0.2% increased ADG, and G:F during the 6-week period.
[259]
Finishing (48–93 kg)Fumaric, citric, malic, caprylic and capric acid blend (0.2%)
  • Reduced faecal pH, ammonia, and acetic acid concentrations.
  • Increased the CATTD of DM, GE, CP and EE in groups without dietary antibiotic supplementation.
  • Improved G:F over 6 weeks without dietary antibiotic supplementation.
  • Negative effect on G:F in antibiotic supplemented group.
[138]
Finishing (50–117 kg)Fumaric, citric, malic, caprylic and capric acid blend (0.1% or 0.2%)
  • No effect on blood serum parameters during week 6 or 12.
  • Linear increase in the CATTD of DM, N, and GE during week 12.
  • Linear reduction in faecal ammonia contents during week 6 and 12.
  • Linear increase in faecal Lactobacillus populations during week 6 and reduced faecal E. coli during week 6 and 12.
  • Linear increase in ADG during weeks 0–6, weeks 6–12, and overall.
  • No effect on meat quality parameters (pH, water holding capacity, colour, or drip loss).
[260]
Exp. 1: Weaning
(6–22 kg)
Exp 2: Grow-Finishing
(24–140 kg)
Sodium diformate
Exp 1: (0.4%, 0.6%, 0.8%, 1% or 1.2%)
Exp 2: (0.25%, 0.5%, or 0.75%)
Exp 1:
  • No effect on faecal DM on d 9 PW.
  • Linear reduction in faecal DM on d 24 PW.
  • Exp 1: Linear increase in G:F during d 0–24 PW.
  • Exp 2: Linear increase in ADG and ADFI from d 60–93 and 93–117. Linear increase in G:F during d 93–117.
  • Exp 2: No effect on carcass characteristics
[261]
ADFI, average daily feed intake; ADG, average daily gain; BCFA, branched-chain fatty acids; BW, body weight; Ca, calcium; CAID, coefficient of apparent ileal digestibility; CATTD, coefficient of apparent total tract digestibility; CD, crypt depth; CP, crude protein; d, day; DM, dry matter; EE, ether extract; FCR, feed conversion ratio; GE, gross energy; G:F, gain-to-feed ratio; Ig, immunoglobulin; N, nitrogen; NDF, neutral detergent fibre; OA, organic acid; OM, organic matter; P, phosphorus; PW, post-weaning; VH, villus height; VH:CD, villus height-crypt depth ratio.
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Maher, S.; Sweeney, T.; O’Doherty, J.V. Optimising Nutrition for Sustainable Pig Production: Strategies to Quantify and Mitigate Environmental Impact. Animals 2025, 15, 1403. https://doi.org/10.3390/ani15101403

AMA Style

Maher S, Sweeney T, O’Doherty JV. Optimising Nutrition for Sustainable Pig Production: Strategies to Quantify and Mitigate Environmental Impact. Animals. 2025; 15(10):1403. https://doi.org/10.3390/ani15101403

Chicago/Turabian Style

Maher, Shane, Torres Sweeney, and John V. O’Doherty. 2025. "Optimising Nutrition for Sustainable Pig Production: Strategies to Quantify and Mitigate Environmental Impact" Animals 15, no. 10: 1403. https://doi.org/10.3390/ani15101403

APA Style

Maher, S., Sweeney, T., & O’Doherty, J. V. (2025). Optimising Nutrition for Sustainable Pig Production: Strategies to Quantify and Mitigate Environmental Impact. Animals, 15(10), 1403. https://doi.org/10.3390/ani15101403

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