Sustainability and Quality Aspects of Different Table Egg Production Systems: A Literature Review
Abstract
:1. Introduction
2. Materials and Methods
3. Results
3.1. Egg Quality Issues
3.2. Environmental Issues
3.3. Animal Welfare, Animal Health and Food Safety Issues
3.4. Production Efficiency and Economic Issues
4. Discussion and Conclusions
Author Contributions
Funding
Conflicts of Interest
References
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Research Objectives |
(1) To identify the effects of different housing systems on the quality aspect of egg production. (2) To identify the effects of different housing systems on the environmental issues of egg production. (3) To identify the effects of different housing systems on the animal welfare, animal health and food safety aspects of egg production. (4) To identify the effects of different housing systems on the production efficiency and economic aspects of egg production. (5) To compare these patterns with consumer preferences. |
Initial Inclusion Criteria |
Documents available in Google Scholar, in Web of Science, in Scopus and materials collected for years by authors of this study. |
Setting the Inclusion Criteria |
(1) keywords: egg housing; non-cage egg production; alternative egg production; egg housing environment; environmental effect table egg in the different production system; ammonia contamination in eggs production; egg production emission; bacteriological contamination of eggshell; physical contamination of eggshell; eggs dioxin different housing system; contamination on eggshell; eggs contamination alternative system; antibiotic in egg production; antibiotic-free egg production; effect of housing system on egg quality; cleanliness of eggshell; the interior quality of eggshell; effect of eggshell quality; content of table hen eggs; laying hen housing productivity; production cost of eggs in the different housing system; consumer preferences eggs; consumer preference eggshell colour; housing system consumer preference; health awareness egg consumption; egg sustainability; (2) relevant documents from the bibliography of selected papers; (3) timeframe: 2010–2020; (4) geographical limitation: Europe, North America; (5) housing systems: cage housing (conventional and/or enriched/furnished cage) vs. non-cage housing (aviary and/or barn and/or free-range and/or organic); non-cage housing vs. non-cage housing; |
Applying the Exclusion Criteria |
After the reading of title and abstracts, only documents that were focused on (1) the sustainability issues and quality aspects of egg production in various housing systems and (2) egg consumer preferences were selected. |
Content Analysis |
In-depth analysis and classification of papers by key topics. Overview and compare findings of selected papers. |
Critical Discussion and Conclusion |
Studies | Analyzed Housing System | Evaluated Egg Quality Traits | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
EW | SI | ESC | EST | ESS | AH/W | HU | YW | YC | C/N | SC | ||
Minelli et al. (2007) [64] | CC, O | √ | - | - | - | - | -/√ | √ | √ | √ | √ | - |
Matt et al. (2009) [65] | CC, O | - | - | - | - | - | - | - | - | - | √ | - |
Yenice et al. (2016) [55] | Cage, FR | √ | √ | - | √ | √ | √/- | √ | - | √ | √ | - |
Anderson (2011) [49] | Cage, FR | - | - | - | - | - | - | - | - | - | √ | - |
Küçükyılmaz et al. (2012) [66] | CC, O | √ | √ | - | √ | √ | √/- | √ | - | √ | √ | - |
Kralik et al. (2013) [63] | Cage, FR | √ | √ | - | √ | √ | √√ | √ | √ | √ | - | - |
Jones et al. (2014) [67] | CC, EC, AV/B | √ | - | - | - | √ | √/- | √ | - | - | - | - |
Samiullah and Chousalkar (2014) [68] | CC, FR | √ | - | - | √ | √ | √/- | √ | - | √ | - | - |
Yang et al. (2014) [69] | Cage, FR | √ | √ | - | √ | √ | √/- | - | - | √ | - | - |
Ferrante et al. (2015) [70] | AV/B, O | √ | - | - | - | - | -/√ | - | √ | - | - | √ |
Englmaierová et al. (2017) [60] | CC, EC, AV/B | √ | √ | - | √ | √ | √ | √ | - | - | - | - |
Yilmaz Dikmen et al. (2017) [71] | CC, EC, FR | √ | √ | √ | √ | - | -/√ | √ | √ | √ | - | - |
Perić et al. (2016) [54] | CC, FR | √ | √ | √ | √ | √ | √/- | √ | - | √ | √ | √ |
Sokolowicz et al. (2018) [72] | B, FR, O | √ | √ | √ | √ | √ | √/- | √ | √ | √ | - | - |
Sokolowicz et al. (2018) [73] | AV/B, FR, O | √ | √ | √ | √ | √ | √/- | √ | √ | √ | √ | - |
Vlčková et al. (2018) [57] | EC, FR | √ | - | - | √ | √ | -/- | - | - | - | - | - |
Zita et al. (2018) [56] | Cage, B | √ | √ | √ | √ | √ | -/- | √ | - | √ | - | - |
Galic et al. (2019) [61] | EC, AV/B, FR | √ | √ | - | √ | - | -/√ | - | √ | - | - | - |
Kraus et al. (2019) [58] | EC, B | √ | √ | √ | √ | √ | -/√ | √ | √ | - | - | - |
Vlčková et al. (2019) [74] | EC, FR | √ | - | - | - | - | - | √ | - | - | - | - |
Ghanima et al. (2020) [75] | Cage, B | √ | - | - | √ | - | - | √ | - | - | √ | - |
Popova et al. (2020) [76] | Alternative with pasture, B | √ | √ | - | √ | - | √/√ | √ | √ | - | √ | - |
Studies | Analyzed Housing System | Evaluated Environmental Factors | ||||
---|---|---|---|---|---|---|
GHGE CO2/CH4/N2O | AE NH3/SO2 | PO4/NO3 | PM | NRU E/L/W/N | ||
Whyte (2002) [87] | Cage, B | -/-/- | √/- | -/- | √ | -/-/-/- |
Bessei et al. (2011) [88] | CC, EC, AV, B, FR | √/√/√ | √/- | -/- | - | -/√/-/√ |
Xin et al. (2011) [89] | cage, non-cage | √/√/√ | √/- | -/- | √ | √/√/-/- |
Dekker et al. (2011) [90] | CC, B, FR, O | √/√/√ | √/√ | -/- | - | √/√/√/√ |
Shepherd et al. (2015) [91] | CC, EC, AV | √/√/- | √/- | -/- | √ | -/-/-/√ |
Zhao et al. (2015) [92] | CC, EC, AV | √/√/√ | √/- | -/- | √ | -/-/-/- |
van Asselt et al. (2015) [93] | EC, B, FR, O | √/-/- | √/√ | √/√ | √ | √/√/√/√ |
Pelletier (2017) [94] | CC, EC, B, FR, O | √/-/- | -/√ | √/- | - | √/√/-/√ |
Studies | Main Findings |
---|---|
Whyte (2002) [87] | Exposure to particulate matter and ammonia concentration is higher in B than in cage systems. |
Bessei et al. (2011) [88] | The resource use and harmful gas emission per hen unit are steadily growing from CC, through small group housing to B. |
Xin et al. (2011) [89] | The treatment or presence of hen manure may pose significant environmental load on the quality of air and water. In addition, processing the manure has a relatively high energy demand. The air quality (ammonia and dust) is usually lower in non-caged systems than in cage housing. The resources use of egg production (feed, energy and land) is less efficient in non-caged systems than in cage housing, which leads to a larger carbon footprint. |
Dekker et al. (2011) [90] | Based on an LCA analysis, it is projected that a ban on CC in the European Union increases the global warming potential, land occupation and acidification potential per kg of egg produced. Resource use and emissions change negatively from cage housing to non-cage systems. Of non-cage technologies, O systems have the lowest global warming potential, energy use, fossil phosphorus use, and nitrogen and phosphorus surplus, whereas land occupation and nitrogen and phosphorus deficit are lowest for B systems. |
Shepherd et al. (2015) [91] | The highest house-level ammonia emissions were observed in the AV housing, followed by CC and EC. House-level methane emissions were similar for all houses. The particulate matter concentration was the highest in the AV housing, while similar results were obtained in the CC and EC. The manure storage accounts for 60-70% of the farm’s ammonia output. |
Zhao et al. (2015) [92] | Comparing the CC, EC and AV housing systems, air quality (ammonia and particulate matter concentration) is the worst in the AV housing system. |
van Asselt et al. (2015) [93] | In the Netherlands, comparing the EC, AV, FR and O systems using a scoring method, EC was the best system according to the environmental dimension of sustainability. |
Pelletier (2017) [94] | Among five housing technologies considered (CC, EC, free run, FR, O), both the life cycle inventory and impact assessment results suggested quite similar levels of performance between the non-organic systems. In case of O production, lower research use and emission intensity was found. |
Studies | Analyzed Housing System | Evaluated Animal Welfare, Animal Health and Food Safety Factors | |||||||
---|---|---|---|---|---|---|---|---|---|
H/F/B | I/C | D/P | FP/C | M | PP | MO/AB | D/R | ||
Tauson (2002) [101] | EC, AV | √ | - | - | √ | - | - | - | - |
Kijlstra (2004) [102] | FR, O | - | - | - | - | - | - | - | √ |
Tauson (2005) [100] | CC, EC, AV, B, FR, O | √ | √ | √ | √ | √ | - | - | - |
Rodenburg et al. (2008) [103] | EC, AV/B | √ | √ | - | - | √ | - | - | - |
de Reu et al. (2008) [104] | CC, EC, AV | - | - | - | - | - | - | √ | - |
Vučemilo et al. (2010) [105] | CC, AV | - | - | - | - | - | - | √ | - |
Sherwin et al. (2010) [106] | CC, EC, B, FR | - | √ | - | - | - | - | - | - |
Bessei et al. (2011) [88] | CC, EC, AV, B, FR | √ | √ | √ | √ | - | - | - | - |
Lay et al. (2011) [107] | CC, EC, AV/B, FR | √ | √ | √ | - | - | √ | - | - |
de Vylder (2011) [108] | CC, EC, AV, B | - | - | - | - | - | - | √ | - |
Holt et al. (2011) [109] | EC, AV, B, FR, O | - | - | - | - | - | - | √ | √ |
Englmaierová et al. (2014) [60] | CC, EC, AV, B | - | - | - | - | - | - | √ | - |
Parisi et al. (2015) [110] | CC, FR | - | - | - | - | - | - | √ | - |
Jones et al. (2015) [111] | CC, EC, AV | - | - | - | - | - | - | √ | - |
Cotter (2015) [112] | CC, EC, AV | - | - | - | - | - | √ | - | - |
van Asselt et al. (2015) [93] | EC, B, FR, O | √ | √ | √ | √ | √ | - | √ | √ |
Cepero and Hernándiz (2015) [53] | CC, EC, AV, B, FR, O | - | - | - | - | - | - | √ | √ |
Zhao et al. (2016) [113] | CC, EC, AV | - | - | - | - | - | - | √ | - |
Stadig et al. (2016) [114] | CC, EC, AV, B, FR | √ | √ | √ | √ | √ | - | - | - |
Hatcher and Jones (2017) [115] | cage, non-cage | √ | √ | √ | √ | - | - | - | - |
Galvão et al. (2018) [116] | CC, FR | - | - | - | - | - | - | √ | - |
Vlčkova et al. (2018) [57] | EC, FR | - | - | - | - | - | - | √ | - |
Gast et al. (2019) [117] | CC, EC | - | - | - | - | - | - | √ | - |
Fulton (2019) [118] | CC, EC, AV | - | √ | √ | - | √ | - | - | - |
Studies | Main Findings |
---|---|
Kijlstra (2004) [102] | The dioxin level is higher in eggs from FR and O housing than in caged eggs. |
Tauson (2005) [100] | The main issues related to housing in larger groups: misplaced eggs, increased feed intake, air quality (ammonia and dust levels), catching of spent hens, parasitic infection and feather pecking. |
Rodenburg et al. (2008) [103] | Birds are more active and their bones are stronger in non-cage housing than in EC. The mortality rate, the frequency of bone fractures and the particulate matter concentration in the air are lower in the case of EC. |
Vučemilo et al. (2010) [105] | Alternative production systems are more favorable from the aspect of animal welfare and behavioral requirements; however, they are dissatisfactory in terms of pollutants in the air and hygiene, as they can represent a greater risk of horizontal contamination of the egg content. |
Sherwin et al. (2010) [106] | Hens in B systems have the highest prevalence of old fractures, emaciation, poor plumage condition, abnormal egg calcification, and the highest corticosterone. Vent pecking was most common in FR flocks. The lowest prevalence of problems occurred in hens in EC. |
Bessei et al. (2011) [88] | In B housing, the litter makes it possible for birds to bathe in dust and to peck in the dirt; however, intestinal parasites are a threat. Increasing the group size in EC and B increases space, which possibly leads to increased risk of bone fracture, feather pecking and cannibalism. |
Lay et al. (2011) [107] | Mortality is generally lower in EC than in CC, and mortality can reach unacceptably high levels in non-cage systems. EC may reduce the risk of bone breakage compared with CC or non-cage systems. Hens in CC and EC have less bumblefoot and footpad dermatitis than more extensively housed hens, but claw health is worse in CC than in all other systems. |
de Vylder (2011) [108] | Increased bird-to-bird Salmonella Enteritidis transmission was detected in the AV and floor system compared with cage systems. Contamination with Salmonella Enteritidis is more common in eggs produced in AV, compared to cage systems and B. |
Englmaierová et al. (2014) [60] | The bacterial contamination of the eggshell fluctuates more in alternative housing systems than in the case of the cage. |
Parisi et al. (2015) [110] | FR eggs have greater microbiological contamination on the eggshell surface than eggs produced in CC. |
Jones et al. (2015) [111] | Particulate matter also affects the microbiology of the environment and eggs. In non-cage systems, floor eggs have the greatest opportunity for exposure to high levels of microorganisms and human pathogens. During the management of housing systems, it is important to reduce and control the amount of aerobes and coliforms, as well as the level of Salmonella and Campylobacter spp. in the B system. |
Cotter (2015) [112] | Physiological measures did not show differences in stress between CC, EC and AV systems. |
van Asselt et al. (2015) [93] | In the Netherlands, comparing the EC, AV, FR and O systems using a scoring method, FR was the best system according to the social dimension (food safety, animal welfare, and human welfare) of sustainability. |
Zhao et al. (2016) [113] | Based on the comparison of the CC, EC and AV housing systems, the highest airborne total bacteria concentrations were observed in the AV system. However, airborne total bacteria concentrations were higher in all three housing systems than the level recommended for the human environment. |
Stadig et al. (2016) [114] | Belgian egg farmers currently using cage systems were more satisfied with hen health than farmers with non-cage systems. According to Belgian farmers who shifted to non-cage systems from CC, feather pecking, cannibalism, smothering and mortality were perceived to be higher in non-cage systems compared to CC. |
Hatcher and Jones (2017) [115] | The risk of the emergence and spreading of infectious diseases, as well as feather pecking, is the lowest in non-cage systems. |
Galvão et al. (2018) [116] | CC systems have better hygiene and sanitary status than FR systems. |
Vlčkova et al. (2018) [57] | The numbers of Escherichia coli and Enterococcus and the total number of microorganisms were higher in FR eggs compared to EC eggs. |
Gast et al. (2019) [117] | S. Enteritidis deposition inside eggs can vary between genetic lines of infected laying hens, but housing these hens in two different systems did not affect the production of contaminated eggs. |
Fulton (2019) [118] | The mortality, keel bone fractures and other skeletal abnormalities were greatest for AV compared with CC and EC. EC housing is better for the health and welfare of layers than CC or AV housing. |
Housing Systems | Average Cost (%) in Different Studies | |||||
---|---|---|---|---|---|---|
Netherlands (2007–2008) [90] | USA (2011) [126] | USA (2011) [133] | France (2012) [134] | Hungary (2012–2015) [135] | EU (2015, 2017) [125,136] | |
Conventional cage | 100 | 100 | 100 | 100 | no data | 100 |
Furnished cage | no data | no data | 113 | no data | 100 | 106 |
Barn/aviary | 112–115 | 140 | 136 | 113 | 139 | 123 |
Free-range | 115–117 | no data | no data | 128 | no data | no data |
Organic | 185 | no data | no data | 213 | no data | no data |
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Molnár, S.; Szőllősi, L. Sustainability and Quality Aspects of Different Table Egg Production Systems: A Literature Review. Sustainability 2020, 12, 7884. https://doi.org/10.3390/su12197884
Molnár S, Szőllősi L. Sustainability and Quality Aspects of Different Table Egg Production Systems: A Literature Review. Sustainability. 2020; 12(19):7884. https://doi.org/10.3390/su12197884
Chicago/Turabian StyleMolnár, Szilvia, and László Szőllősi. 2020. "Sustainability and Quality Aspects of Different Table Egg Production Systems: A Literature Review" Sustainability 12, no. 19: 7884. https://doi.org/10.3390/su12197884
APA StyleMolnár, S., & Szőllősi, L. (2020). Sustainability and Quality Aspects of Different Table Egg Production Systems: A Literature Review. Sustainability, 12(19), 7884. https://doi.org/10.3390/su12197884