SYSTEMATIC REVIEW article

Front. Vet. Sci., 27 October 2021

Sec. Animal Nutrition and Metabolism

Volume 8 - 2021 | https://doi.org/10.3389/fvets.2021.750733

Environmental Impacts of Pig and Poultry Production: Insights From a Systematic Review

  • 1. Department of Animal Science, Universidade Federal do Rio Grande do Sul, Porto Alegre, Brazil

  • 2. Département des Sciences Animales, Faculté des Sciences de l'Agriculture et de l'Alimentation, Université Laval, Québec, QC, Canada

  • 3. Sherbrooke Research and Development Centre, Agriculture and Agri-Food Canada, Sherbrooke, QC, Canada

  • 4. Elanco Animal Health, São Paulo, Brazil

Abstract

Pig and poultry production systems have reached high-performance levels over the last few decades. However, there is still room for improvement when it comes to their environmental sustainability. This issue is even more relevant due to the growing demand for food demand since this surplus food production needs to be met at an affordable cost with minimum impact on the environment. This study presents a systematic review of peer-reviewed manuscripts that investigated the environmental impacts associated with pig and poultry production. For this purpose, independent reviews were performed and two databases were constructed, one for each production system. Previous studies published in peer-reviewed journals were considered for the databases if the method of life cycle assessment (LCA) was applied to pig (pork meat) or poultry (broiler meat or table eggs) production to estimate at least the potential effects of climate change, measured as CO2-eq. Studies considering the cradle-to-farm gate were considered, as well as those evaluating processes up to the slaughterhouse or processor gate. The pig database comprised 55 studies, while 30 publications were selected for the poultry database. These studies confirmed feeding (which includes the crop cultivation phase, manufacturing processes, and transportation) as the main contributor to the environmental impact associated with pig and poultry production systems. Several studies evaluated feeding strategies, which were indicated as viable alternatives to mitigate the environmental footprint associated with both production chains. In this study, precision feeding techniques are highlighted given their applicability to modern pig and poultry farming. These novel feeding strategies are good examples of innovative strategies needed to break paradigms, improve resource-use efficiency, and effectively move the current productive scenario toward more sustainable livestock systems.

Introduction

The increasing demand for food is an important challenge that society will face in the coming decades. The growing population will need more resources, leading to a relevant increase in food demand. The productive sector (including agriculture and livestock) needs to support the growing demands for food, however, without compromising the ability of the future generations to also meet their requirements. In other words, environmentally sustainable agri-food systems are mandatory requirements for a world with increasing urbanization and growing food demands.

In this context, the benefits of agri-food sectors for society need to be maximized (), which can be achieved by improving the efficiency in which the resources are applied in the production chains. The current production methods will need to adapt to these new challenges (limited resources, increased production), with most surplus food production being supplied by innovative agri-food systems ().

Pig and poultry production systems have reached high-performance levels over the last few decades. Together, these sectors provide a large amount of affordable and nutritious food, especially high-quality protein, contributing to food security worldwide. However, there is still room for improvement when it comes to their environmental sustainability. Feeding pigs and poultry requires tremendous amounts of feed resources, with several studies indicating it as an important source of environmental impact (). In addition, pigs and broilers excrete annually large amounts of nitrogen and phosphorus to the environment, which conditions the production sustainability of these chains ().

Conventionally, the impacts of pig and poultry production have been assessed by methodologies that used an “animal basis” approach (e.g., studies focusing on reducing nutrient excretion). These are very important studies; however, few mitigation strategies have focused on the efficiency of resource use, which is critical in a global context. Considering the relevance of the topic, it is important to investigate feeding practices that mitigate the environmental impacts associated with the entire production system. Thus, we carried out a systematic review to summarize, analyze, and compare studies that used life cycle assessment (LCA) to evaluate the environmental impacts associated with pig and poultry production systems.

Materials and Methods

This systematic review was based on structured and elaborated research performed using online search methods. The search strategy was planned and carried out to identify as many studies as possible on the subject. Papers were rigorously selected and those focusing on feeding practices were further evaluated.

Independent searches were performed for pig and poultry production systems. The strategy “PICo” was applied to build the research question by identifying “Population” (database 1: “pig”; database 2: “poultry”), “Interest” (“life cycle assessment”), and “Context” (“climate change”) for both searches. Alternative terms for population and interest were listed using synonymous words in English to compose the final search strategy. Context was applied later (through full-text reads) to avoid missing any study in which the response was not mentioned among the main terms (title, abstract, and keywords). The final search terms were:

Database 1:

(pig OR pigs OR swine) AND (“life cycle assessment” OR “life cycle” OR “carbon emission” OR “carbon footprint” OR “greenhouse gas*” OR “global warming” OR LCA)

Database 2:

(poultry OR broiler*OR chicken*OR hen) AND (“life cycle assessment” OR “life cycle” OR “carbon emission” OR “carbon footprint” OR “greenhouse gas*” OR “global warming” OR LCA).

The search was conducted in March 2020, considering only original peer-reviewed studies published in scientific journals available in PubMed, Scopus, and Web of Science. A snowball approach using forward (e.g., databases) and backward research methods (e.g., direct journal search, reference lists, studies listed in previously published reviews) was performed to increase the chance of including as many relevant studies as possible. No limitations on the geographic origin or year of publication were applied in both searches.

Each database was exported to the reference software (EndNote X9, Philadelphia, PA) used to organize references and manage part of the study selection. Duplicate references were identified and excluded. Studies were critically evaluated regarding their relevance and quality by examining titles and abstracts, followed by a complete review of the LCA study. Two reviewers performed a critical evaluation of the study eligibility. A study was not considered in the final database (removed) after mutual agreement, with a third reviewer reassessing studies that differed in terms of eligibility.

The selection criteria were stated as (i) original papers published in peer-reviewed journals, (ii) environmental impact evaluated using the LCA methodology; (iii) evaluation of pig (pork meat) or poultry (broiler meat or table eggs) production systems; (iv) scopes including cradle-to-farm, to the slaughterhouse, or to processor gate; (v) estimation of at least the potential impact of climate change, in CO2-eq. The quality of selected studies was further evaluated and information relevant to describe the proposed theoretical model was transferred to the pig and poultry spreadsheets. Finally, cross-study comparisons were performed considering the subject, scope, and main results observed.

Results

Studies Focusing on Pig Production

The research process until obtaining the final pig database is described in Figure 1A. Articles obtained by online searches (4,237 references) were critically evaluated and successive exclusions were performed. The main exclusions (more related to methodological aspects of the original studies) were performed when assessing the full-text, when 36 references were eliminated (criterium i and ii: 15 publications; criterium iii: 2 publications; criterium iv: 13 publications; and criterium v: 6 publications). The final list of 55 selected studies is described in Table 1.

Figure 1

Table 1

CodeStudyCountryFunctional unitClimate change potentiala, CO2-eq
1Basset-Mens and van der Werf ()France1 kg of live weight2.30–3.97 kg
2Eriksson et al. ()Sweden1 kg of live weight gain1.36–1.51 kg
3Basset-Mens et al. ()France1 kg of live weight2.30 kg
4Basset-Mens et al. ()France1 t of pig0.88–1.39 t
5Liang et al. ()Japan1 kg of carcass weight5.02 kg
6Halberg et al. ()Denmark1 kg of live weight2.80–3.30 kg
7Halberg et al. ()United States1 t live weight pig2.47–3.33 kg
8Aramyan et al. ()Europe, several countries1 kg of slaughter weight2.55–2.97 kg
9Bonesmo et al. ()Norway1 kg of carcass weight2.65 kg
10Devers et al. ()United Kingdom1 kg of cut pork2.55–4.5 kg
11Dolman et al. ()Netherlands100 kg of live weight473–637 kg
12Stone et al. ()United States1 pig (118kg)398.20 kg
13De Moraes et al. ()World, several countries1 kg of live weight pig5.36–5.57 kg
14Luo et al. ()China1 farm (1,956 units of 500 kg each)5,611–5,714 t
15Ogino et al. ()Japan1 kg of meat after dressing7.12–7.12 kg
16Reckmann et al. ()Germany1 market pig346–370 kg
17Dourmad et al. ()Europe, several countries1 kg of slaughter weight3.20–3.25 kg
18Jacobsen et al. ()Belgium1 kg of live weight pig2.25–3.47 kg
19Sasu-Boakye et al. ()Sweden1 kg of deboned pork5.70 kg
20Cherubini et al. ()Brazil1 kg carcass weight2.10–2.20 kg
21Cherubini et al. ()Brazil1 t of swine carcass3.11–3.55 t
22González-García et al. ()Portugal30 kg of weight gain (finishing phase)67.15–76.02 kg
23Mackenzie et al. ()Canada1 kg of meat (carcass weight)3.34 kg
24Reckmann and Krieter ()Germany1 kg of carcass weight2.81 kg
25van Zanten et al. ()Netherlands1 kg of slaughter weight3.09–3.36 kg
26Wang et al. ()China1 kg of live weight pig2.50 kg
27Groen et al. ()Netherlands1,000 pigs9.08E+04 kg
28Kebreab et al. (31)Europe, North, and South America1 kg of live weight2.61 kg
29Lamnatou et al. (32)Spain1 t of live weight pig1.98–2.46 t
30Mackenzie et al. (33)Canada1 kg of meat (live or carcass weight)3.2–5.5 kg
31Monteiro et al. (34)Brazil and France1 market pig (105 kg)336–460 kg
32Noya et al. (35)Spain1 kg of carcass weight1.95–2.55 kg
33Pirlo et al. (36)Italy1 kg of weight gain (fattening phase)2.27–3.00 kg
34Sagastume Gutiérrez et al. (37)Cuba1 kg of live-weight pig6.70 kg
35Wang et al. (38)China1 kg of carcass pork8.70 kg
36Ali et al. (39)Brazil1 kg of cut pork10.3 kg
37Bava et al. (40)Italy1 kg of live weight gain3.3 kg
38Li et al. (41)China1 pig (120kg)1,019 kg
39Monteiro et al. (42)Brazil1 market pig2.29–3.19 kg
40Noya et al. (43)Spain1 kg of live weight pig1.13–1.96 kg
41Noya et al. (44)Spain1 kg of live weight pig2.69–5.81kg
42Six et al. (45)Belgium1 market pig248.53 kg
43Andretta et al. (46)Brazil1 kg of weight gain (fattening phase)2.57–2.67 kg
44Rudolph et al. (47)Europe, several countries1 kg of cut pork4.96 kg
45Arrieta and González (48)Argentina100 kg live weight pig342 kg
46Monteiro et al. (49)Brazil100 g of pork0.46 kg
47Monteiro et al. (50)Europe, several countries1 t live weight pig1.78–2.36 t
48Ottosen et al. (51)Denmark1 t live weight pig1.47–2.71 t
49Reyes et al. (52)Cuba1 t of live weight pig0.89–0.94 t
50Anestis et al. (53)Greece1 kg of weight gain (nursery phase)1.76–2.45 kg
51Cadero et al. (54)France1 kg of live weight pig5.07–9.35 kg
52Garcia-Gudino et al. (55)Spain1 kg of live weight pig4.18 kg
53Horrillo and Gaspar (56)Spain1 kg of live weight pig6.87–9.65 kg
54Monteiro et al. (57)Brazil1 kg of live weight pig3.85–4.15 kg
55Pexas et al. (58)Denmark1 kg of live weight gain2.16–2.48 kg

Summary of the LCA studies on pig production in terms of location, functional unit, and climate change potential.

a

Original results were preserved, however, some conversions were needed for the purpose of having the same weight unit as the functional unit.

The first LCA study identified in the pig database was published in 2005. Considering the entire database, 26 journals reported publications, with 16 papers being published in Journal of Cleaner Production and 5 papers in Animal. Production scenarios located in Brazil (which was considered in eight studies), Spain (considered in six studies), France (considered in five studies), and China (considered in four studies) were assessed in the selected papers, as illustrated in Figure 2A. The frequency of studied countries is highly related to the location of the main research groups. However, it is important to highlight that the order of most studied countries is not in complete agreement with the pork production ranking (led by China). Another important aspect related to the geographical characteristics of the papers is that five studies were developed by researchers from countries different than the one (or at least one of the regions) considered in the simulations, with Brazil or South America being studied in three of them.

Figure 2

A scope described as cradle-to-farm gate was used in the majority of the studies, which means that all phases comprised from the crop cultivation (and its inputs/outputs) up to the animal rearing phase were considered in these projects. The impacts associated with slaughtering and processing were considered in nine publications only.

Climate change was the focus of our study. However, the LCA studies also reported other impact categories (Figure 3A). From those variables, the most prevalent were eutrophication and acidification, followed by the use of energy and land.

Figure 3

The main subjects under evaluation in the studies focusing on pig production are presented in Table 2. The characterization of pig production in the region or country was the main objective in 18 studies. Another important objective in the studies was the comparison of production systems (including organic or alternative housing systems), which was the main subject in nine papers.

Table 2

CodeMain study subjectScope final boundary
1Production systemsAt farm gate
2Feed choiceAt farm gate
3Implications of uncertainty and variabilityAt farm gate
4Production systemsAt farm gate
5Production in JapanAt farm gate
6Production systems (organic)At farm gate
7Production systemsAt farm gate
8Production system in EuropeAt farm gate
9Production in NorwayAt farm gate
10Production in Western Cape and FlandersDelivered to the distribution center
11Production systemsAt farm gate
12Production in the United StatesAt farm gate
13Immunological castrationAt farm gate
14Manure managementAt farm gate
15Low-protein diet supplemented with amino acidsAt slaughterhouse gate
16Production in GermanyAt farm gate
17Production systemsAt slaughterhouse gate
18Production in FlandersAt farm gate
19Protein sources for feed productionAt pork cutting gate
20Manure managementAt farm gate
21Feed composition for finishing pigsAt slaughterhouse gate
22Production in PortugalAt farm gate
23Production in CanadaAt the slaughterhouse gate
24Farm performanceAt farm gate
25Replacing soybean meal with rapeseed mealAt slaughterhouse gate
26Production in North ChinaAt farm gate
27Sensitivity analysisAt farm gate
28Specialty feed ingredientsAt farm gate
29Production in SpainAt farm gate
30Utilizing co-products as feedAt farm gate
31Protein source, feeding programs (including precision feeding), amino acids inclusionAt farm gate
32Production in CataloniaAt farm gate
33Production in Italy (heavy pig)At farm gate
34Manure managementAt farm gate
35Husbandry on different scaleAt slaughterhouse gate
36Using co-products in the diets of finishing pigsAt slaughterhouse gate
37Production system in Italy (heavy pig)At farm gate
38Crop-swine integrated systemAt farm gate
39Reduced dietary protein levelsAt farm gate
40Production in CataloniaAt farm gate
41Production in GaliciaAt farm gate
42Supply chain managementAt farm gate
43Precision feedingAt farm gate
44Production systems (organic)At pork cutting gate
45Production in ArgentinaAt farm gate
46Individual data of performance and excretionAt retail gate
47European local breedsAt farm gate
48Altering genetic components of individual traitsAt farm gate
49Production system in CubaAt farm gate
50Dietary modification for fattening pigsAt farm gate
51Feeding practices, animal health, and farm infrastructureAt farm gate
52Production in SpainAt farm gate
53AgroecosystemsAt farm gate
54Source of performance and excretion dataAt farm gate
55Housing conditions and manure managementAt farm gate

Summary of the LCA studies on pig production in terms of main subject under analysis and scope boundary.

Changes in feeding practices (diet composition or feeding programs) were studied in 25% of the papers. The relative participation of feed production (which includes each ingredient's life cycle, fabrication, and transport) varied from 31 to 76% of the overall greenhouse gas (GHG) emissions in the pig database (Figure 4A). Despite the importance of feeding to the total pig production impact, the diet composition used in the inventory was described by the minority of the papers. Only 38% of the papers described the ingredient formulas, while only 29% of the studies showed any description for dietary nutritional composition, limited sometimes to crude protein. In addition, the environmental impacts related to the production of individual ingredients were presented in only 9% of the papers. The proportion of total impact associated with feed was highlighted in most of the studies. However, the impact of feed production (considering as a functional unit; e.g., 1 ton of feed) was presented in only 15% of the publications. These data would be of great value for further investigations on feeding practices that may mitigate the potential environmental impact of pig production. In addition, more information on feeding practices would allow a better comparison among studies, as great variability exists between the final results (impact of pig production) presented by the studies even for the same functional unit.

Figure 4

As previously stated, crop production is a major contributor to the overall impacts of the pig production chain. The globalization of feed ingredient markets is relevant to LCA studies because it disconnects commodity production from its use/consumption. In a context in which most of the ingredients used for feed production are internationally traded, it is important to highlight that the impacts associated with a certain product are virtually shared with several countries involved in the international trade. The most frequent example of this intercontinental sharing was the use of soybean imported from South America, mainly from Brazil, in European countries. Considering the pig database, 49% of the studies mentioned the use of Brazilian soybean. For that reason, several papers also mentioned the inclusion of overseas transport during the inventory characterization.

Studies Focusing on Poultry Production

The research process until obtaining the final poultry database is described in Figure 1B. Articles obtained by online searches (6,502 references) were critically evaluated, which resulted in several exclusions. Seventeen references were excluded when assessing the full-text (criterium i and ii: 2 publications; criterium iii: 1 publication; criterium iv: 7 publications; and criterium v: 7 publications). The final list of 30 selected studies is described in Table 3.

Table 3

CodeStudyCountryFocusFunctional unitClimate change potentiala, CO2-eq
1Bennett et al. (59)ArgentinaMeat1 kg (body weight) of broilerNA
2Mollenhorst et al. (60)NetherlandsEgg1 kg of eggs3.9–4.6 kg
3Pelletier (61)United StatesMeat1 t (live weight) of broiler1.40 t
4Leinonen et al. (62)United KingdomMeat1 t of expected carcass4.41–5.66 t
5Leinonen et al. (63)United KingdomEgg1 t of marketable eggs2.92–3.45 t
6Leinonen et al. (64)United KingdomMeat/Egg1 t of expected carcass weight3.54–4.39 t
7Pelletier et al. (65)United StatesEgg1 t of marketable eggs2.95–3.46 t
8Thévenot et al. (66)Reunion Island (France)Meat1 t of produced eggs4.20–6.10 t
9González-García et al. (67)PortugalMeat1 t of produced eggs4.32–6.45 t
10Leinonen et al. (68)United KingdomMeat/Egg1 t of liquid eggs4.95–7.48 t
11Prudêncio da Silva et al. (69)Brazil, FranceMeat1 t of whole chickens packed2.49 t
12Taylor et al. (70)United KingdomEgg1 kg (live weight) of broiler1.62 kg
13Ghasempour and Ahmadi (71)IranEgg1 kg of chicken meat packed2.46 kg
14Kalhor et al. (72)IranMeat1 t of expected carcass weight4.22–4.42 t
15Kebreab et al. (31)Europe, North, and South AmericaMeat1 t of marketable eggs2.83–2.92 t
16Leinonen et al. (73)United KingdomMeat1 t (live weight) of broiler1.45–2.70 t
17Cesari et al. (74)ItalyMeat1 t of packaged chicken1.95–4.02 t
18Giannenas et al. (75)GreeceMeat1 dozen eggs1.9–2.5 kg
19Mainali et al. (76)BangladeshEgg1 kg of expected carcass4.07 kg
20Payandeh et al. (77)IranMeat1 t (live weight) of broiler1.39–3.25 t
21Pelletier (78)CanadaEgg1 t of packed meat2.93–5.36 t
22Pishgar-Komleh et al. (79)IranMeat1 t (live weight) of broiler1.12–1.34 t
23Wiedemann et al. (80)AustraliaMeat1 kg (live weight) of broiler3.03–3.84 kg
24Abín et al. (81)SpainEgg1 kg of carcass5.52 kg
25Skunca et al. (82)SerbiaMeat1 t of expected carcass weight2.76 t
26Arrieta and González (48)ArgentinaMeat1 kg (live weight) of broiler1.63–4.21 kg
27Duarte da Silva Lima et al. (83)BrazilMeat10,000 eggs1.74 t
28Ramedani et al. (84)IranMeat1 t (live weight) of broiler5.00–5.78 t
29van Hal et al. (85)NetherlandsEgg1 t of produced eggs1.37–2.44 t
30Estrada-González et al. (86)MexicoEgg1,000 broilers17.36–20.25 t

Summary of the LCA studies on poultry production in terms of location, focus, functional unit and climate change potential.

a

Original results were preserved, however, some conversions were needed for the purpose of having the same weight unit as the functional unit.

The first study identified in the poultry database was published in 2006. Considering the entire database, 13 journals reported publications, with 10 papers being published in Journal of Cleaner Production and 5 papers in Poultry Science. Broiler production was evaluated in 18 studies, eggs were the main product evaluated in 10 studies, and both products were assessed in two papers. Production scenarios located in the United Kingdom and Iran (which were considered in 6 studies each); followed by Argentina, Brazil, France, Netherlands, and the USA, which were considered in two studies each; as illustrated in Figure 2B.

Likewise to the pig database, the scope described as cradle-to-farm gate was used in most studies focusing on poultry production. Impacts associated with slaughtering and processing were considered in 10 publications. Besides climate change, studies presented other impact categories (Figure 3B), such as acidification, eutrophication, and the use of energy and land. The characterization of the meat or egg production in the region or country was the main objective in 15 studies (Table 4).

Table 4

CodeMain study subjectFocusScope final boundary
1Conventional and genetically modified maizeMeatAt processing plant door
2Production systemsEggAt farm gate
3Production system in the United StatesMeatAt farm gate
4Production system in the United KingdomMeatAt farm gate
5Production system in the United KingdomEggAt farm gate
6Alternative protein cropsMeat/EggAt farm gate
7Production system in the United StatesEggAt farm gate
8Accounting for farm diversityMeatAt farm gate
9Production system in PortugalMeatAt shell egg processor facilities
10Welfare-enhancing system changesMeat/EggAt breaker facilities
11Large and small-scale production in Brazil and FranceMeatAt processor door
12Production systems (free-range)EggAt farm gate
13Production system in IranEggAt processor door
14Production system in IranMeatAt farm gate
15Specialty feed ingredientsMeatAt farm gate
16Genetic changesMeatAt farm gate
17Production system in ItalyMeatAt processor gate
18Protease and replacement of soybean mealMeatAt farm gate
19Litter managementEggAt farm gate
20Mitigating environmental impacts by data envelopment analysisMeatAt farm gate
21Production system in Canada and housing systemsEggAt processor door
22Production system in IranMeatAt farm gate
23Production system in AustraliaMeatAt farm gate
24Production system in SpainEggAt slaughterhouse gate
25Chicken meat chainMeatAt farm gate
26Production system in ArgentinaMeatAt farm gate
27Production system in BrazilMeatAt farm gate
28Comparing ostrich and chicken productionMeatAt farm gate
29Feed-food competitionEggAt processor door
30Production system in MexicoEggAt farm gate

Summary of the LCA studies on poultry production in terms of main subject under analysis and scope boundary.

Three papers described the environmental impacts of replacing ingredients in feed formulas, while one paper described the impacts of dietary supplementation with protease. Feeding was highlighted as the major source of environmental impact in most studies, accounting for 28–82% of the overall impact of climate change (Figure 4B). Despite the importance of feeding to the total impact, the diet composition used in the inventory was not described in most studies. Only 13% of the papers described the ingredient formulas, while only 10% of the studies showed any description for dietary nutritional composition. In addition, the environmental impacts related to the production of individual ingredients were presented in only 13% of the papers, with the impact of feed production (considering as a functional unit; e.g., 1 ton of feed) being presented in only 20% of the publications. The use of Brazilian soybean was reported by 30% of the studies, highlighting the importance of international trade also for the environmental impact of poultry production.

Discussion

The availability of peer-reviewed publications using LCA to assess the environmental impacts of pig and poultry production systems has increased over the years (Figure 5). The first studies of each database were published in close years for both pig (2005) and poultry (2006) production chains. However, the availability of studies focusing on pig production evolved greatly in the following years, mainly after 2014. In most research areas, the number of studies on poultry production is great than the number of publications available in a comparable topic in pigs. However, the opposite was found in this systematic review, probably due to the higher risk and concern with the environmental impacts of pig production compared to poultry systems.

Figure 5

The interest in using LCA to investigate the sustainability of a given production originates from its capability to quantify and evaluate the resources consumed and the emissions released at each phase needed for its production (). Concerns about food safety and climate change have greatly increased in recent years. In response, the livestock industry must then reduce the utilization of resources by increasing its efficiency while reducing its environmental impact.

The impacts estimated for both production systems varied greatly across studies, mainly due to the heterogeneity of functional units and the amplitude of the considered life-cycle scopes. However, other attributes may also be listed as sources of variability when comparing publications. In particular, this heterogeneity may be related to the production systems under analysis (, 62, 63), as well as to regional characteristics (31, 69). The conditions considered for housing (58), farm size (38, 79), level of intensification (), and manure management () are also reported as important factors determining the final impact associated to the product. When focusing on animal aspects, some welfare (68) and genetic traits (50, 51, 73), as well as sanitary aspects (54) were reported.

Feed production was highlighted in several papers due to its relevant contribution to the total environmental impact. This phase was simulated including each ingredient's life cycle, fabrication, and transportation to the feed mill or to the farm in most studies. The reported contribution of the feed production phase relative to the overall GHG emissions varied from 31 to 76% in the pig database. In the poultry database, it accounted for 28–82% of the total climate change impact. Regardless of the exact environmental impact attributed to the feeding phase, almost all studies identified feeding as the production factor having the greatest environmental impact. These findings support the hypothesis that eco-friendly feeding practices can mitigate the environmental impacts of pig and poultry production.

Importance of Rearing System Scenarios

Even though a comparison between organic and conventional systems will not be deeply reviewed, it is important to highlight that several studies indicated the production system as one of the important aspects determining the relative contribution of feeding to the overall environmental impact (due to the feed ingredient composition, number of feeding phases, among others). Conventional production systems were considered in most simulations (i.e., conventional feed ingredients). However, some studies evaluated the environmental impacts of adopting alternative production systems (e.g., organic, free-range, certified labels). According to Leinonen et al. (62, 63), the global warming impact necessary to obtain a given functional unit of feed (e.g., 1 ton) can be low in organic farms in comparison to conventional farms. However, a higher feed amount is generally necessary for organic farms than in conventional production systems to obtain the same functional unit. Several reasons are indicated in the papers, as the impairment in feed conversion ratio, an increase in feed consumption, or even waste of feed or products. Thus, when the total cycle is analyzed, a greater global warming potential impact may be associated with feeding animals in organic than in conventional systems (, 62, 63).

The environmental impacts of a given rearing system are highly correlated with animal performance, especially feed efficiency (, 87). Thus, technologies that improve animal performance usually have great potential to mitigate life cycle environmental impacts. In this particular aspect, some technologies were assessed in the reviewed studies. Immunological castration and feed additives are some of these factors (, 31, 53, 75), but probably many more aspects still need to be evaluated in future research.

Another important factor evaluated in some studies was the impact of innovative practices during the cultivation or processing of feed ingredients. The use of maize genetically modified (59), different processing methods for soybean (48), or crop-animal integrated systems (41) were evaluated, and impacts in the final product (i.e., functional unit) were reported.

Importance of Feeding Scenarios

The use of alternative feed ingredients is an important strategy in livestock systems. Some studies presented environmental advantages when using co-products in the assessed feeds (, 33, 39). Other papers indicated that these advantages may be related to the calculation method, with favorable results being reported only when the impacts were not co-allocated between the main and the co-products (35, 88). The environmental cost to obtain co-products cannot be ignored in the LCA analysis, and this should be probably further evaluated in future research. Another limitation to be considered when comparing studies are the different ingredient choices given the difficulties in data acquisition, especially for local or limited ingredients as well as the great variability among processes used to obtain co-products (64, 88).

The distance between feedstuff production location and their place of use is an important argument in favor of using ingredient choice (or replacement) as a strategy to mitigate environmental impacts. Feed ingredients are products with cross-border flows, which are a consequence of globalization. Reducing the distance from producers to consumers means fewer transportation needs, and consequently fewer costs and emissions. Using this argument, several studies were developed proposing the use of locally grown ingredients instead of products cultivated in different countries or even continents (, 43, 64). This is particularly important for local protein-ingredients that replace imported soybean and soybean meal (64). However, the use of local ingredients must not impair feed conversion (, 66). Otherwise, the advantages may be lost caused by increased demand for feed to reach the same final weight.

Feed composition in terms of ingredients is also a way to reduce the excretion of nutrients and, consequently, manure composition. For that reason, the choice of ingredients needs to be made always with caution, focusing on the origin, but also on the nutritional quality of the product. Nitrogen excretion in manure is highly correlated with diet formulation. If an increase in nitrogen losses in the manure is related to a given ingredient choice, it is expected that this modification will lead to higher GHG emissions and probably other major consequences too (65). In this context, strategies that mitigate nutrient excretion, such as enzyme supplementation (75), synthetic amino acid partially replacing protein crops, or the use of low-protein diets (, 42, 57), can potentially mitigate the environmental impacts of both pig and poultry production. The modification of the feed formulation method (89) and the adoption of precision feeding techniques (46, 90) are also very important and innovative tools. Due to its relevance for future animal production, precision feeding will be further discussed in the next section, with a focus on pig production.

Precision Feeding as an Eco-Friendly Strategy to Mitigate the Environmental Impacts of Pig Production

Feeding is a major source of environmental impacts, as previously discussed. When correctly applied, precision feeding is an efficient tool to decrease production and environmental costs (91). Pigs and poultry are usually fed according to group requirements, disregarding individual particularities. This means that all animals receive the same feed for an extended period, with part of the population receiving nutrients above their requirements (92). The animals that receive nutrients above their needs excrete this excess. An increased protein intake decreases protein efficiency utilization, resulting in larger nitrogen excretions (93). In many pig commercial systems, the nitrogen retention in conventional phase-feeding programs will rarely exceed 35%, being that the efficiency of nitrogen utilization used in many LCA studies (94). However, nitrogen efficiency varies depending on age, sanitary status, and crude protein levels (95, 96).

Precision feeding consists in providing the right amount of feed with the right balance composition to each animal at the right time. Thus, precision feeding can be defined as the technology that provides each animal the nutrients tailored to meet in real-time the animal requirements (91). Nitrogen and phosphorus excretions can be decreased by 40% and consequently reduce production costs by 10% when using an individual precision feeding program (93, 97).

In this context, precision feeding can improve the sustainability of pig production systems. Automatic feeding stations allow pigs to be fed individually with a diet whose composition is appropriate to their growth potential (91). This strategy is an important pattern shift in animal nutrition because at this point nutritional requirements are no longer consider static, but as dynamic processes that develop differently for each individual.

The use of precision feeding instead of conventional group feeding systems already demonstrated several benefits. The increased nutrient-use efficiency and the consequent reduction in the excretion of polluting substances to the environment, improving the overall sustainability of the production system, are the main advantages presented by this feeding system (91). In addition, studies have shown that it is possible to considerably reduce soybean meal and dicalcium phosphate in diet formulations compared to conventional programs. In validation studies (93, 97), individual feeding allowed a reduction in lysine intake by up to 26%, and nitrogen and phosphorus excretion by 30 and 14%, respectively, without affecting the productive pig performance.

Environmental Impacts of Applying Precision Feeding Techniques

Before applying precision feeding techniques, it is necessary to study the environmental impacts of adopting these techniques. An LCA study performed by Andretta et al. (46) intends to estimate the environmental impact of precision feeding techniques applied to pig production. Once again, in Brazilian scenarios, feeding was the largest source of environmental impact. In addition, the study showed that replacing conventional group feeding with daily group feeding (nutrient supply adjusted daily to meet the group requirements) could decrease the potential impact of eutrophication by 4% and acidification by 3%. The mitigation was even greater (up to 6% for the potential impact of climate change and 5% for eutrophication and acidification) when the program was applied to each animal individually (pigs received diets daily tailored to their requirements).

The study also highlighted a reduction over time in the potential impact of climate change associated with pig feed production related to reducing the expected dietary nutrient levels. In the simulated population, reducing the dietary standardized ileal digestible lysine level by one percentage point led to a reduction of up to 194.7 kg of CO2-eq per ton of feed, depending on the simulated scenario. Certainly, the main advantage of this method was the improved nutrient use efficiency. In other words, the same amount of product was produced using fewer resources. Monteiro et al. (34) performed a similar study considering Brazilian and French scenarios with simulated data (the previous study used data collected in vivo). In their study, a precision feeding system that fed pigs individually was able to reduce the impact of climate change by 7%.

Future Challenges

Animals are exposed to several conditions during their lives and these factors may impact directly their nutrient requirements (98). For example, sanitary challenges affect the way amino acids are used by the animal because the nutrients that would be used for protein deposition are directed to cope with the immune system (98). Sanitary challenges also impact the growth performance of pigs and broilers (99), reducing feed efficiency and consequently increasing the environmental impact associated with this production (). Cadero et al. (54) reported a significant effect of impaired health status on the carbon footprint of pig production. This is only one of several topics that need to be more evaluated in the future, especially in a scenario with reduced use of antibiotics in animal production.

Several studies on the environmental impact of animal production have been published, but only a few have worked using precision feeding programs or considering sanitary challenges. More studies must be carried out to better understand their environmental impact on modern pig and poultry production. Despite all the variability found in livestock, precision systems can foster some eco-friendly solutions by the possibility of managing animals as an individual, having their diets tailored based on real-time data.

Important Aspects to Be Considered When Applying LCA to Animal Science

LCA is a well-known and established method to evaluate environmental impacts, particularly for complex production chains as those in the livestock sector. However, LCA has its limitation like any other scientific method. Some of these limitations have been described by Finkbeiner et al. (100). Some of these gaps may apply in the studies described in this systematic review.

One important limitation observed in the studies was the assessment of water use. Many studies did not include this impact category or they did not consider water consumption (water not returned to the system), which is very relevant for agriculture (100, 101).

The great variability in functional units is certainly another important limitation to be highlighted. The unit choice is a challenging task because it impacts directly on the results and is also related to the objective and scope (100). However, the variability among studies is a great limitation when comparing results since transformations are sometimes not possible or precise (e.g., results expressed for 1 ton of live pig are difficult to compare to those expressed for 1 ton of carcass because there are more processes included and sometimes the carcass yield is not fully known).

In addition, impacts on human health are probably insufficiently covered in LCA studies dealing with pig and poultry production. Soil contamination, noise, and odors are some of these impacts that are not commonly addressed in LCA studies. Additionally, the LCA method fails to consider other aspects, such as biodiversity, welfare, and social aspects (100). The positive impact of specific activities may be also disregarded.

Finally, the choice of a single scenario to represent the reality of an entire production chain is another important limitation of some reviewed LCA studies. The issue related to data gathering was previously highlighted (102). A single model (e.g., data collected in a single scenario) are not able to describe the pig and poultry production systems worldwide, and neither probably across regions. Even in integrated systems that are characterized by a higher level of uniformity, it is possible to observe a different performance in each producer (for the same genetic type, with the same feed, and similar management practices). Thus, variability is something that needs to be considered in future LCA studies.

Conclusion

This systematic review confirmed feeding as the largest source of environmental impact associated with pig and poultry production systems. This supports the hypothesis that novel feeding techniques may mitigate the environmental footprint associated with both production chains. Precision feeding is highlighted as a way to optimize nutrient-use efficiency and, for that reason, as a promising tool toward more sustainable animal production systems. It is still a challenging task to properly consider and compare the variability among LCA studies. Despite these issues, LCA is a comprehensive way to assess sustainability from a global perspective and its application on pig and poultry production systems is very encouraged in future research.

Publisher's Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Statements

Data availability statement

The raw data supporting the conclusions of this article will be made available by the authors upon request.

Author contributions

AR, CF, CO, MK, and IA searched articles for the systematic review and interpreted results. IA interpreted results, prepared figures, and tables, and wrote the first draft of the manuscript. M-PL-M and CP were involved in the interpretation and discussion of results. FH and AM contributed to manuscript revision, read, and drafted the final version of the manuscript. All authors read and approved the final version of the manuscript.

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

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Summary

Keywords

sustainability, swine, broilers, environment, livestock, climate change, laying hens, precision feeding

Citation

Andretta I, Hickmann FMW, Remus A, Franceschi CH, Mariani AB, Orso C, Kipper M, Létourneau-Montminy M-P and Pomar C (2021) Environmental Impacts of Pig and Poultry Production: Insights From a Systematic Review. Front. Vet. Sci. 8:750733. doi: 10.3389/fvets.2021.750733

Received

31 July 2021

Accepted

23 September 2021

Published

27 October 2021

Volume

8 - 2021

Edited by

Emma Fàbrega Romans, Institute of Agrifood Research and Technology (IRTA), Spain

Reviewed by

Siaka Seriba Diarra, University of the South Pacific, Fiji; Peter John White, The University of Sydney, Australia

Updates

Copyright

*Correspondence: Ines Andretta Aline Remus

This article was submitted to Animal Nutrition and Metabolism, a section of the journal Frontiers in Veterinary Science

Disclaimer

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

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