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Erschienen in: International Journal of Legal Medicine 2/2020

Open Access 17.06.2019 | Review

Pigs vs people: the use of pigs as analogues for humans in forensic entomology and taphonomy research

Erschienen in: International Journal of Legal Medicine | Ausgabe 2/2020

Abstract

Most studies of decomposition in forensic entomology and taphonomy have used non-human cadavers. Following the recommendation of using domestic pig cadavers as analogues for humans in forensic entomology in the 1980s, pigs became the most frequently used model cadavers in forensic sciences. They have shaped our understanding of how large vertebrate cadavers decompose in, for example, various environments, seasons and after various ante- or postmortem cadaver modifications. They have also been used to demonstrate the feasibility of several new or well-established forensic techniques. The advent of outdoor human taphonomy facilities enabled experimental comparisons of decomposition between pig and human cadavers. Recent comparisons challenged the pig-as-analogue claim in entomology and taphonomy research. In this review, we discuss in a broad methodological context the advantages and disadvantages of pig and human cadavers for forensic research and rebut the critique of pigs as analogues for humans. We conclude that experiments using human cadaver analogues (i.e. pig carcasses) are easier to replicate and more practical for controlling confounding factors than studies based solely on humans and, therefore, are likely to remain our primary epistemic source of forensic knowledge for the immediate future. We supplement these considerations with new guidelines for model cadaver choice in forensic science research.
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“We are unlikely to ever know everything about every organism. Therefore, we should agree on some convenient organism(s) to study in great depth, so that we can use the experience of the past (in that organism) to build on in the future. This will lead to a body of knowledge in that ‘model system’ that allows us to design appropriate studies of nonmodel systems to answer important questions about their biology” [1].
“Model species are usually easy to rear, observe, or otherwise experimentally manipulate. They therefore allow knowledge to be built up rapidly and efficiently, because confounding factors are known and thus can be controlled in subsequent experiments” [2].

Introduction

While collaborating with medical examiners in the late 1800s, French entomologist Pierre Mégnin [3] advanced the first formal definition and testable mechanism of ecological succession and recognized the predictability of carrion-arthropod succession and resource partitioning in human corpses and their application in forensic analysis [4, 5]. These investigations gave birth to the twin disciplines of carrion ecology and forensic entomology. Subsequently, most studies of vertebrate decomposition used non-human carcasses ranging in size from amphibians to elephants (Table 1). Payne innovatively used pig cadavers in his ground-breaking ecological experiments on decomposition [68]. Wider interest in forensic entomology and taphonomy arose in the mid-1980s, and such studies initially focussed on pigs or rabbits (Table 1). By the late 1980s, the domestic pig was being recommended as an analogue for humans in forensic entomology research and training workshops [911]. Starting in the early 1990s, field studies and statistical models were proposed to test different aspects of the pig-as-analogue claim in forensic entomology [1214].
Table 1
Selected cadaver studies in carrion ecology, forensic entomology and taphonomy. References to this table are listed in Electronic Supplementary Material
Author(s)
Date of publication
Locality
Animal model
Major research focus
Chapman and Sankey [1]
1955
England
Rabbits
Arthropod inventory; habitats
Bornemissza [2]
1957
Australia
Guinea pig
Arthropod inventory; succession
Reed [3]
1958
USA
Dogs
Arthropod inventory; succession
Payne [4]
1965
USA
Pigs
Surface decomposition; insect access
Payne et al. [5]
1968
USA
Pigs
Underground decomposition
Payne and King [6]
1972
USA
Pigs
Water decomposition
Nabagło [7]
1973
Poland
Bank voles
Surface/underground decomposition; insect inventory; succession; seasons
Cornaby [8]
1974
Costa Rica
Lizards, toads
Arthropod inventory; succession; habitats
Johnson [9]
1975
USA
Small mammals
Arthropod inventory; succession; seasons
Smith [10]
1975
England
Fox
Arthropod inventory; succession
Coe [11]
1978
Kenya
Elephants
Surface decomposition; insect inventory
McKinnerney [12]
1978
USA
Rabbits
Arthropod inventory; succession; scavenging
Jiron and Cartin [13]
1981
Costa Rica
Dogs
Arthropod inventory; succession
Abell et al. [14]
1982
USA
Turtles
Arthropod inventory; succession
Rodriguez and Bass [15]
1983
USA
Humans
Insect inventory; succession
Schoenly and Reid [16]
1983
USA
Various mammals
Cadaver mass; insect inventory
Lord and Burger [17]
1984
USA
Gulls
Arthropod inventory; succession; seasons; habitats; scavenging
Rodriguez and Bass [18]
1985
USA
Humans
Underground decomposition
Early and Goff [19]
1986
Hawaii
Cats
Surface decomposition; arthropod inventory; succession
Micozzi [20]
1986
USA
Rats
Freezing; wounds
Braack [21]
1986
South Africa
Impala
Insect inventory
Peschke et al. [22]
1987
Germany
Rabbits
Insect inventory; succession; habitats; seasons
Tullis and Goff [23]
1987
Hawaii
Pig
Surface decomposition; arthropod inventory; succession
Blacklith and Blacklith [24]
1990
Ireland
Birds, mice
Insect inventory; habitats
Kentner and Streit [25]
1990
Germany
Rats
Insect inventory; succession; habitats
Hewadikaram and Goff [26]
1991
Hawaii
Pigs
Cadaver mass
Vass et al. [27]
1992
USA
Humans
Compounds released into soil during decomposition
Shean et al. [28]
1993
USA
Pigs
Sun exposure
Anderson and VanLaerhoven [29]
1996
Canada
Pigs
Insect inventory; succession
Tantawi et al. [30]
1996
Egypt
Rabbits
Insect inventory; succession; seasons
Keiper et al. [31]
1997
USA
Rats
Water decomposition; habitats; arthropod inventory
Richards and Goff [32]
1997
Hawaii
Pigs
Arthropod inventory; succession; habitats
Avila and Goff [33]
1998
Hawaii
Pigs
Burnt cadaver decomposition; habitats; succession
Komar and Beattie [34, 35]
1998
Canada
Pigs
Cadaver mass; habitats; clothing; post-mortem artefacts
Tomberlin and Adler [36]
1998
USA
Rats
Water decomposition; insect inventory; seasons; habitats
Bourel et al. [37]
1999
France
Rabbits
Insect inventory; succession; habitats
DeJong and Chadwick [38]
1999
USA
Rabbits
Insect inventory; succession; habitats
Turner and Wiltshire [39]
1999
England
Pigs
Underground decomposition
VanLaerhoven and Anderson [40]
1999
Canada
Pigs
Underground decomposition; insect inventory; succession; habitats
Carvalho et al. [41]
2000
Brazil
Pigs, humans
Insect inventory
Davis and Goff [42]
2000
Hawaii
Pigs
Intertidal habitats; succession
Shalaby et al. [43]
2000
Hawaii
Pigs
Hanging cadaver decomposition; succession
Arnaldos et al. [44]
2001
Spain
Chickens
Insect inventory; succession
Carvalho and Linhares [45]
2001
Brazil
Pigs
Insect inventory; succession
Marchenko [46]
2001
Russia
Dogs, cats, rabbits, pigs
Decomposition in various scenarios; seasons; habitats; insect repellents; clothing, plant response to cadavers
Wolff et al. [47]
2001
Colombia
Pigs
Insect inventory; succession
Yan et al. [48]
2001
USA
Pigs
Adipocere formation
Centeno et al. [49]
2002
Argentina
Pigs
Insect inventory; seasons; habitats; succession
Hobischak and Anderson [50]
2002
Canada
Pigs
Water decomposition; habitat; arthropod inventory; succession
LeBlanc and Strongman [51]
2002
Canada
Pigs
Insect inventory; habitats
Archer and Elgar [52, 53]
2003
Australia
Pigs
Insect inventory; seasons; colonisation patterns
Bharti and Singh [54]
2003
India
Rabbits
Insect inventory; seasons; succession
Kočárek [55]
2003
Czech Republic
Rats
Insect inventory; seasons; habitats; succession
Shahid et al. [56]
2003
USA
Pigs
Arthropod saturation in human taphonomy facilities
Watson and Carlton [57–59]
2003, 2005
USA
Bear, deer, alligators, pigs
Insect inventory; seasons; succession; animal models comparison
Anderson and Hobischak [60]
2004
Canada
Pigs
Marine decomposition
Archer [61, 62]
2004
Australia
Pigs
Succession; seasons; annual variation; abiotic determinants of decomposition rate
Arnaldos et al. [63]
2004
Spain
Chickens
Insect inventory; seasons; succession
Grassberger and Frank [64]
2004
Austria
Pigs
Urban decomposition; insect inventory; succession
Tabor et al. [65, 66]
2004, 2005
USA
Pigs
Insect inventory; succession; seasons
Vass et al. [67]
2004
USA
Humans
Volatiles of decomposition
Anderson [68]
2005
Canada
Pigs
Arson and insect evidence
Moura et al. [69]
2005
Brazil
Rats
Succession mechanisms; seasons; habitats
Perez et al. [70]
2005
Colombia
Pigs
Urban decomposition; insect inventory; succession
Schoenly et al. [71]
2005
USA
Pigs
Arthropod saturation in human taphonomy facilities
Weitzel [72]
2005
Canada
Pigs
Underground decomposition; seasons
DeJong and Hoback [73]; DeJong et al. [74]
2006; 2011
USA
Rats
Investigator disturbance; insect inventory; succession
Hobischak et al. [75]
2006
Canada
Pigs
Sun exposure; insect inventory; succession
Joy et al. [76]
2006
USA
Pigs
Blow fly inventory; habitats; annual variation; maggot mass
Lang et al. [77]
2006
Australia
Possums
Insect inventory; colonisation patterns
Adlam and Simmons [78]
2007
UK
Rabbits
Repeated cadaver disturbance
Gruner et al. [79]
2007
USA
Pigs
Blow fly inventory; seasons; annual variation
Martinez et al. [80]
2007
Colombia
Pigs
Insect inventory; succession
O’Brien et al. [81]
2007
Australia
Pigs
Scavenging
Schoenly et al. [82]
2007
USA
Pigs, humans
Sampling techniques; human/pig comparison
Benninger et al. [83]
2008
Canada
Pigs
Compounds released into soil during decomposition
Eberhardt and Elliot [84]
2008
New Zealand
Pigs
Insect inventory; succession; habitats
Fiedler et al. [85]
2008
Germany
Pigs
Adult fly inventory; succession; habitats
Huntington et al. [86]
2008
USA
Pigs
Blow fly multigenerational colonisation
Matuszewski et al. [87]
2008
Poland
Pigs
Insect inventory; succession; habitats
Moretti et al. [88]
2008
Brazil
Mice, rats
Insect inventory; succession; seasons
Sharanowski et al. [89]
2008
Canada
Pigs
Insect inventory; succession; seasons; sun exposure
Ururahy-Rodrigues et al. [90]
2008
Brazil
Pigs
Post-mortem artefacts
Voss et al. [91]
2008
Australia
Pigs
Inside-car decomposition; colonisation patterns
Wang et al. [92]
2008
China
Pigs
Insect inventory; succession; seasons
Charabidze et al. [93]
2009
France
Rats, Mice
Insect repellents; colonisation patterns
Dekeirsschieter et al. [94]
2009
Belgium
Pigs
Volatiles of decomposition
Kalinová et al. [95]
2009
Czech Republic
Mice
Carrion beetle attractants
Kelly et al. [96, 97]
2009, 2011
South Africa
Pigs
Wounds; wrapping; clothing
Kjorlien et al. [98]
2009
Canada
Pigs
Scavenging; habitats; clothing
Nelder et al. [99]
2009
USA
Alligators
Succession
Özdemir and Sert [100]
2009
Turkey
Pigs
Insect inventory; succession; seasons
Pakosh and Rogers [101]
2009
Canada
Pigs (limbs)
Water decomposition;
Parmenter and MacMahon [102]
2009
USA
Various mammals and birds
Seasons; surface/underground decomposition; scavenging; nutrient cycling
Segura et al. [103]
2009
Colombia
Pigs
Insect inventory; succession
Van Belle et al. [104]
2009
Canada
Pigs
Compounds released into soil during decomposition; surface/underground decomposition
Voss et al. [105]
2009
Australia
Pigs
Insect inventory; succession; seasons; habitats
Bachmann and Simmons [106]
2010
UK
Rabbits
Underground decomposition; colonisation patterns
Battán Horenstein et al. [107–109]
2010, 2011, 2012
Argentina
Pigs
Insect inventory; succession; seasons; habitats
Bonacci et al. [110]
2010
Italy
Pigs
Insect inventory; seasons; succession
Carter et al. [111]
2010
Australia
Rats
Underground decomposition
Chin et al. [112]
2010
Malaysia
Pigs
Hanging cadaver decomposition
Cross and Simmons [113]
2010
UK
Pigs
Wounds
Matuszewski et al. [114–116]
2010, 2011
Poland
Pigs
Surface decomposition; insect inventory; seasons; habitats; succession
Michaud et al. [117]
2010
Canada
Pigs
Insect inventory; seasons; habitats
Reibe and Madea [118]
2010
Germany
Pigs
Colonisation patterns; habitats
Sabanoglu and Sert [119]
2010
Turkey
Pigs
Insect inventory; succession; seasons
Simmons et al. [120]
2010
UK
Rabbits
Insect access; surface/underground decomposition
Simmons et al. [121]
2010
UK
Pigs
Insect access; cadaver mass
Swann et al. [122, 123]
2010
Canada, Australia
Pigs
Compounds released during decomposition
Szpila et al. [124]
2010
USA, Poland
Pigs, rats
Colonisation of buried cadavers
Valdes-Perezgasga et al. [125]
2010
Mexico
Pigs
Insect inventory; succession
Ahmad et al. [126]
2011
Malaysia
Macaques
Wrapping
Anderson [127]
2011
Canada
Pigs
Indoor/outdoor decomposition
Anton et al. [128]
2011
Germany
Pigs
Insect inventory; succession; seasons
Barrios and Wolff [129]
2011
Colombia
Pigs
Water decomposition; arthropod inventory; succession; habitats
Bajerlein et al. [130]
2011
Poland
Pigs
Seasons; habitats; colonisation patterns
Bugajski et al. [131]
2011
USA
Pigs
Freezing
Cassar et al. [132]
2011
Australia
Pigs
Adipocere formation
DeVault et al. [133]
2011
USA
Mice
Scavenging
Dickson et al. [134]
2011
New Zealand
Pigs (heads)
Marine decomposition; bacterial succession
von Hoermann et al. [135]
2011
Germany
Pigs
Hide beetle attractants
Spicka et al. [136]
2011
USA
Pigs
Cadaver mass
Statheropoulos et al. [137]
2011
Greece
Pigs
Volatiles of decomposition
Voss et al. [138]
2011
Australia
Pigs
Clothing
Al-Mesbah et al. [139]
2012
Kuwait
Rabbits
Insect inventory; habitats; succession
Brasseur et al. [140]
2012
Belgium
Pigs
Volatiles of decomposition
Gruenthal et al. [141]
2012
UK
Pigs
Burnt cadaver decomposition
Martin-Vega and Baz [142, 143]
2012, 2013
Spain
Squids
Carrion and skin beetle inventory; seasons; habitats
Ortloff et al. [144]
2012
Chile
Pigs
Insect inventory; succession
Prado e Castro et al. [145, 146]
2012, 2013
Portugal
Pigs
Insect inventory; succession; seasons
Shelomi et al. [147]
2012
USA
Pigs
Insect repellents; blow fly colonisation patterns
Stadler et al. [148]
2012
Canada
Pigs
Volatiles of decomposition
Widya et al. [149]
2012
UK
Rabbits
Water decomposition; adipocere formation
Azwandi et al. [150]
2013
Malaysia
Rats, rabbits, macaques
Insect inventory; succession; rat/rabbit/monkey comparison
Barton et al. [151]
2013
Australia
Kangaroos
Carrion and biodiversity
Benbow et al. [152]
2013
USA
Pigs
Insect inventory; succession; seasons
Bygarski and LeBlanc [153]
2013
Canada
Pigs
Insect inventory; succession
Dekeirsschieter et al. [154]
2013
Belgium
Pigs
Rove beetle inventory; seasons
von Hoermann et al. [155]
2013
Germany
Pigs
Carrion beetle attractants
Hyde et al. [156]
2013
USA
Humans
Cadaver microbiome
Johansen et al. [157]
2013
Norway
Mice
Blow fly attractants
Johnson et al. [158]
2013
Australia
Pigs
Thermogenesis in cadavers
Lowe et al. [159]
2013
Canada
Pigs
Textiles degradation on buried cadavers
Matuszewski et al. [160]; Mądra et al. [161]
2013, 2014
Poland
Pigs
Insect inventory; habitats; seasons
Metcalf et al. [162]
2013
USA
Mice
Cadaver microbiome
Meyer et al. [163]
2013
USA
Pigs
Surface decomposition; seasons
Sutherland et al. [164]
2013
South Africa
Pigs
Cadaver mass
von der Luhe [165]
2013
Canada
Pigs
Compounds released into soil during decomposition
Abouzied [166]
2014
Saudi Arabia
Rabbits
Insect inventory; seasons; succession
Anderson and Bell [167]
2014
Canada
Pigs
Marine decomposition; arthropod inventory
Bhadra et al. [168]
2014
England
Pigs (heads)
Colonisation patterns
Caballero and León-Cortéz [169]
2014
Mexico
Pigs
Beetle inventory; succession; habitats
Corrêa et al. [170]
2014
Brazil
Rabbits
Beetle inventory; seasons
Farwig et al. [171]
2014
Germany
Mice
Biotic determinants of decomposition rate; seasons
Matuszewski et al. [172, 173]; Mądra et al. [174]
2014, 2016, 2015
Poland
Pigs
Cadaver mass; clothing; insect inventory; long-term decomposition
Mohr and Tomberlin [175, 176]
2014, 2015
USA
Pigs
Cadaver visitation by adult blow flies
Oliveira-Costa et al. [177]
2014
Brazil
Pigs
Succession on burnt cadavers
Pechal et al. [178]
2014
USA
Pigs
Delayed insect access; colonisation patterns; succession
Pechal et al. [179]
2014
USA
Pigs
Cadaver microbiome
Perrault et al. [180–182]
2014, 2015
Australia
Pigs
Volatiles of decomposition
Whitaker [183]
2014
USA
Pigs, humans
Pig/human comparison of blow fly colonisation
Young et al. [184]
2014
England
Deer
Scavenging
Zurawski et al. [185]
2014
USA
Pigs
Nocturnal blow fly oviposition
Agapiou et al. [186]
2015
Greece
Pigs
Volatiles of decomposition
Alexander et al. [187]
2015
USA
Humans
Residual odour of decomposition in the soil
Aubernon et al. [188]
2015
France
Rats
Blow fly development on contaminated cadaver
Baz et al. [189]
2015
Spain
Squids
Insect inventory; habitats
Card et al. [190]
2015
England
Pigs
Clothing
Farrell et al. [191]
2015
Australia
Pigs
Insect inventory
Hyde et al. [192]
2015
USA
Humans
Cadaver microbiome
Iancu et al. [193]
2015
Romania
Pigs
Insect and microbe inventory; succession
Iancu et al. [194]
2015
Romania
Pigs
Insect and microbe inventory; succession
Lynch-Aird et al. [195]
2015
England
Pigs
Hanging cadaver decomposition
Martin-Vega et al. [196]
2015
Spain
Squids
Clown beetle inventory; habitats
Paczkowski et al. [197]
2015
Germany
Pigs
Volatiles of decomposition
Roberts and Dabbs [198]
2015
USA
Pigs
Freezing
Rysavy and Goff [199]
2015
Hawaii
Pigs
Underground decomposition; insect inventory
Silahuddin et al. [200]
2015
Malaysia
Rabbits
Insect inventory; succession; habitats
Stadler et al. [201]
2015
Canada
Pigs
Volatiles of decomposition
Sukchit et al. [202]
2015
Thailand
Pigs
Insect inventory; habitats; succession; seasons; hanging; clothing
Szpila et al. [203]
2015
Poland
Pigs
Insect inventory; succession
Ueland et al. [204]
2015
Australia
Pigs
Textiles degradation on surface cadavers
Zanetti et al. [205, 206]
2015
Argentina
Pigs
Underground decomposition; beetle inventory; seasons
Zeariya et al. [207]
2015
Egypt
Rabbits, dogs
Insect inventory; succession; habitats
Anderson and Bell [208]
2016
Canada
Pigs
Marine decomposition; seasons
Cammack et al. [209]
2016
USA
Pigs
Concealment; seasons
Lyu et al. [210]
2016
China
Pigs
Beetle inventory
Mashaly [211]
2016
Egypt
Rabbits
Burnt cadaver decomposition; insect inventory; succession; habitats
Metcalf et al. [212]
2016
USA
Mice, Humans
Cadaver microbiome
Moffatt et al. [213]
2016
England
Pigs
Distribution of maggots length on carrion
Parry et al. [214]
2016
South Africa
Fishes
Fly inventory; habitats; seasons
Perez et al. [215]
2016
USA
Pigs
Distance between cadavers
Weidner et al. [216]
2016
USA
Pigs
Blow fly colonisation timing
Weiss et al. [217]
2016
USA
Pigs
Cadaver microbiome
Vasconcelos et al. [218]
2016
Brazil
Pigs
Fly inventory
Amendt et al. [219]
2017
Germany
Pigs
Thermal imaging of cadavers
Connor et al. [220]
2017
USA
Pigs, humans
Human/pig comparison
Fancher et al. [221]
2017
USA
Humans
Compounds released into soil during decomposition
Marais-Werner et al. [222]
2017
South Africa
Pigs
Underground decomposition
Martin-Vega et al. [223]
2017
Spain
Pigs
Colonisation patterns; seasons
Mashaly [224]
2017
Saudi Arabia
Rabbits
Beetle inventory; habitats; succession
McIntosh et al. [225]
2017
Australia
Pigs
Burnt cadaver decomposition; succession
Michaud and Moreau [226]
2017
Canada
Pigs
Succession mechanisms
Niederegger et al. [227]
2017
Germany
Pigs
Wounds
Pacheco et al. [228]
2017
Canada
Pigs
Blow fly colonisation patterns
Roberts et al. [229]
2017
USA
Humans
Cadaver mass
Scholl and Moffatt [230]
2017
England
Pigs
Dismemberment; concealment in plastic sacks
Wang et al. [231]
2017
China
Pigs, humans, rabbits
Human/pig/rabbit comparison; surface decomposition; succession;
Wang et al. [232]
2017
China
Pigs
Exposure daytime; succession;
Weidner et al. [233]
2017
USA
Pigs
Comparison of bait traps and cadaver inventories
Cruise et al. [234, 235]
2018
USA
Pigs
Insect inventory; succession; sampling techniques
Dautartas et al. [236]; Steadman et al. [237]
2018
USA
Pigs, humans, rabbits
Human/pig/rabbit comparison; surface decomposition; scavenging
Díaz-Aranda et al. [238]
2018
Spain
Pigs
Insect inventory; succession; seasons
Frątczak-Łagiewska and Matuszewski [239]
2018
Poland
Pigs
Silphid beetles; succession; seasons; habitats
von Hoermann et al. [240]
2018
Germany
Pigs
Carrion beetle inventory; habitats
Knobel et al. [241]
2018
Australia
Pigs, humans
Decomposition rates; odour profiles; human/pig comparison
Lee et al. [242]
2018
Australia
Pigs
Thermal imaging of cadavers
Lutz et al. [243]
2018
Canada
Pigs
Beetle colonisation and breeding on concealed carcasses
Mañas-Jordá et al. [244]
2018
Mexico
Pigs
Fly inventory; succession; habitats
Marais-Werner et al. [245]
2018
South Africa
Pigs
Surface/underground decomposition
Pérez-Marcos [246]
2018
Spain
Pigs, chickens
Fly inventory; pig/chicken comparison
Salimi et al. [247]
2018
Iran
Rabbits
Insect inventory; succession; seasons; habitats
Shayya [248]
2018
Lebanon
Pigs
Clown beetle inventory; succession; seasons; habitats
Singh et al. [249]
2018
USA
Humans
Arthropod and microbe inventory and succession in the soil below a cadaver
Spies et al. [250, 251]
2018
South Africa
Pigs
Scavenging
Szelecz et al. [252, 253]
2018
Switzerland
Pigs
Compounds released into soil during decomposition; clown beetle colonisation of hanging and surface cadavers
Examples of taphonomic studies have been cited from as far back as Leonardo da Vinci in the fifteenth century, but the field began to achieve formality in the 1940s [15]. In the 1970s, palaeoanthropology used taphonomy to interpret the deposition of hominid remains in fossil-rich sites, particularly to provide information about how the hominids lived and died [16, 17]. Integration of fossil-focused taphonomy with physical anthropology led to the differentiation of forensic taphonomy, which relied on extensive comparisons of palaeontological, archaeological and modern case studies [18]. The development of pigs as model organisms in forensic entomology provided a more experimental approach for forensic taphonomy and established some major patterns regarding vertebrate decomposition (Table 1, Fig. 1).
The advent of outdoor human taphonomy facilities (often mistermed “body farms” [19]) facilitated experimental studies using human cadavers. First amongst these was the University of Tennessee Anthropological Research Facility, while the first outside the USA was the Australian Facility for Taphonomic Experimental Research (AFTER) [19, 20]. At least eight facilities now exist, six in the USA, one in Australia and one in the Netherlands [2022]. The facilities have allowed experimental comparison of decomposition in human and non-human models under a variety of conditions [14, 23, 24]. Since then, debate has arisen over the relevance of taphonomic studies for forensics (e.g. [19, 25, 26]), and the proper associated experimental (and ethical) protocols [27, 28]. There is variation in the source populations contributing to taphonomy facilities; moreover, their source cadavers (usually elders dying of natural causes) systematically differ from cadavers involved in forensic scenarios (usually adults dying of unnatural causes). Therefore, for a variety of reasons, the findings from these facilities may be difficult to extrapolate to other human populations and to typical forensic cases.
Recent publications have raised the opportunity to consolidate what has been learned from animal models in decomposition studies, and to examine the implications of this knowledge for the design of field experiments in forensic entomology and taphonomy, specifically, whether animal carcasses can effectively substitute for human cadavers, which is the major aim of this review. Our major focus is research on principles concerning cadaver decomposition, including the associated arthropods and their succession. Therefore this paper does not extensively address topics related to the accuracy and precision of PMI estimation techniques developed in forensic entomology or taphonomy.

Lessons from pig cadavers

The use of animal models to advance knowledge dates back to the ancient Greek times with dogs and chicks used to study human anatomy, physiology and ontogeny [29]. Nowadays, animal models are used to study a large array of human related-issues, e.g. diseases [30], mental and neuropsychiatric disorders [31] or orthopaedic and dental implants [32]. In a similar way, our current understanding of animal decomposition is largely derived from experiments with non-human cadavers, with pig carcasses contributing overwhelmingly to this knowledge (Table 1). Payne’s [6] experimental work using piglets was a watershed event in carrion ecology for its impact and originality. After trying carrion from different vertebrate animals (amphibians, mammals, birds), Payne settled on domesticated pigs because he knew the time of their death, he could acquire them in large numbers of uniform age and mass, and their relatively hairless skin and lack of feathers made insect sampling easier than from alternative carcasses. In his experiments, Payne used cages with different mesh sizes to provide open and limited access to insects to document daily changes in carcass decay and dismemberment. He found that carcasses protected from insects mummified, remaining intact for months; whereas, carcasses exposed to insects lost 90% of their starting mass in just 6 days. This result showed that insect access is a key determinant of cadaver decay.
Inspired by Payne’s experimental protocol, forensic entomologists started using pig cadavers in studies focused on inventorying carrion-arthropod faunas and successional patterns, which have been described for a long list of countries and habitats (Table 1). Although the species involved varied between biogeographical regions, ecological guilds were consistent and functioned in a very consistent way (Table 1). Pigs have illustrated patterns of decomposition over timescales of days, seasons and years (Table 1). Seasonal components of variation in the insect community are relatively well understood and several quantitative models have been proposed to describe the ecological succession that occurs in the arthropod community on a cadaver (Table 1). Much of the early work followed the stage-based paradigm (e.g. [6]). Decay stages, named according to physiochemical changes seen in the cadaver, accompanied timetables of insect succession. Stage descriptions varied in both number and duration; moreover, the widely-held view was that the onset of each stage was marked by an abrupt change in the insect community, similar to Mégnin’s [3] notion of “squads”. Subsequent ecological and forensic studies found that succession in carrion largely follows a continuum of gradual changes [3335]. Despite these findings, the use of stages of decomposition is still frequent in the forensic literature [35].
More recently, pigs became model animals in experimental research of forensic entomology and taphonomy (Table 1). Pigs have influenced recent theoretical developments in carrion and succession ecology and shaped our understanding of how vertebrate cadavers decompose in various environments, including indoor, suspended, buried, epigeic, intertidal, marine and freshwater settings. A wide spectrum of habitats has been investigated (Table 1) and found to show some idiosyncratic variations on otherwise very general patterns (Fig. 1). Results of these studies indicate that temperature and access or abundance of carrion insects are key environmental determinants of cadaver decomposition, whereas cadaver mass is a key cadaver-related determinant (Table 1, Fig. 1). At least five general decomposition patterns may be currently discerned: decay driven by either vertebrate scavengers, microbes, burying beetles, blow flies or blow flies with silphid beetles, with distinct key determinants of decomposition rate in each of the patterns (Table 1, Fig. 1).
Human cadavers vary in many characteristics that influence decomposition, most of which have been investigated using pigs (Table 1). Pre- or postmortem modifications such as wounds, burning, wrapping, dismemberment, contamination, concealment and clothing may affect the colonisation process and eventually decomposition to varying degrees, depending on their intensity and context of action (Table 1). Some modifications do not affect the whole cadaver, leaving parts of it to be colonized by insects in their usual manner, while other modifications such as clothing have effects on insect colonisation or succession that are too small or too variable to have practical consequences for estimates of postmortem intervals (PMIs). Other modifications delay colonisation by insects but have little consequence once colonisation has occurred. The same modifications may however differently affect non-entomological processes, for example, clothing influences rate of cadaver cooling and therefore is considered important for some pathology-based methods for estimation of PMI, e.g. Henssge’s nomogram method [36]. Regarding insects, the implications of modification appear to be larger than the effect of the cadaver’s species.
In parallel, pig cadavers were used to test new forensic techniques or validate well-established ones (Table 2). They have provided proof-of-concept for techniques as simple as entomological sampling and as sophisticated as ground penetrating radar or thermal imaging to locate cadavers (Table 2). Many of these techniques have gone on to be applied to forensic investigations involving humans, demonstrating in this way the practicality of pigs as model cadavers.
Table 2
Forensic methods and techniques developed, refined or tested using pig cadavers. References to this table are listed in Electronic Supplementary Material
Method/technique
References
Pig cadaver use
Field protocol for experimental studies on PMI
Schoenly et al. [1, 2]
Tests of the protocol
Model organisms
Watson and Carlton [3, 4]
Comparisons of different animals
Schoenly et al. [2]; Wang et al. [5]; Connor et al. [6]; Dautartas et al. [7]
Comparisons of pigs and humans
Human-size insect trap for studying succession
Schoenly et al. [1]
Recorded trap microclimate and carrion-arthropod families caught by trap
Device for sampling cadaver-related aquatic insects
Vance et al. [8]
Tests of trap efficiency in catching aquatic insects
Degree-day index for decomposition related processes
Michaud and Moreau [9]
Development of the index and tests for its reliability
Reconstruction of temperature conditions
Hofer et al. [10]
Reliability of temperature recordings on a death scene
Temperature methods for insect pre-appearance interval (PAI)
Matuszewski [11, 12]
Development of PAI models; tests of the method
Matuszewski and Szafałowicz [13]; Archer [14]; Matuszewski et al. [15]
Development of PAI models
Matuszewski and Mądra 2015 [16]
Tests of the protocols for PAI field studies
Matuszewski and Mądra-Bielewicz [17]
Validation of PAI methods
Total body score
Myburgh et al. [18]
Validation of the method
Lynch-Aird et al. [19]
Development of TBS for hanging cadavers
Nawrocka et al. [20]
Inter-rater reliability of the TBS
Keough et al. [21]
Amendment of TBS for pig cadavers
Ribéreau-Gayon et al. [22]
Reliability of TBS based on cadaver pictures
PMI estimation based on insect succession
Michaud and Moreau [23]
Tests of predictability of insect occurrence based on degree-day accumulation
Michaud and Moreau [24]
Tests of sampling protocols for field studies
Perez et al. [25]
Evaluation of utility of insect taxa for derivation of confidence intervals about PMI estimate
Mohr and Tomberlin [26]
Tests of oocyte development of adult blow flies visiting cadaver as a PMI indicator
Perez et al. [27]
Tests of minimum inter-cadaver distances for forensic field studies
Matuszewski [28]
Tests of presence/absence of insect taxa as an approach for PMI estimation
Mądra-Bielewicz et al. [29]
Tests of insect sex and size as PMI indicators
Cruise et al. [30]
Tests of the protocols for cadaver field studies
PMI estimation based on insect development
VanLaerhoven [31]
Validation of methods
Reibe-Pal and Madea [32]
Comparison of methods
Weatherbee et al. [33]
Validation of methods
PMI estimation based on microbes
Pechal et al. [34]
Tests of usefulness of microbe succession for PMI estimation
Exposed cadavers searching
Amendt et al. [35]; Lee et al. [36]
Tests of thermal imaging techniques used from the air
Clandestine burial searching
Schultz et al. [37]; Schultz [38]; Salsarola et al. [39]
Tests of ground-penetrating radar
Submerged cadavers searching
Healy et al. [40]
Tests of side-scan sonar
Detection of gasoline in cadaver tissues
Pahor et al. [41]
Proof-of-concept tests

Are pigs an appropriate model for forensic entomology and taphonomy?

A comparison of the advantages and disadvantages of pig and human cadavers for experimental forensic entomology and taphonomy research (Table 3) indicates that pigs are usually superior to humans in such experiments. Most importantly, pig cadavers may easily be replicated in large numbers and at low cost, whereas access to human corpses is restricted to taphonomic facilities or medical examiner’s offices with all of their associated inherent difficulties. At taphonomic facilities, waiting times for receiving replicate bodies on multiple-donation days are unpredictable and uncontrollable [37], even if minimum criteria are met for accepting cadavers as “replicates” (i.e. death within 48 h of acquisition, intact, unautopsied, unembalmed and refrigerated). The difficulty in amassing replicate human cadavers allows little experimental control over key decomposition determinants such as cadaver mass. The unpredictable and uncontrollable variation inherent in cadaver availability may limit the value of observations in humans and invalidate the experiment, by producing statistically underpowered comparisons that are insufficient to detect significant differences and by enlarging the risk of confounding effects. In addition, the practical realities of working with human remains can limit the types of information that can be gleaned from and about them. Moreover, the continual association of the taphonomy facilities with human cadavers can itself present a challenge. Although a 1998 field study at the Tennessee facility found little evidence of cadaver enrichment effects on the surface-active entomofauna or decay rates using pig carcasses [38, 39], a recent study of soil parameters [40] demonstrated that the Tennessee site is contaminated with high levels of decomposition products, which may limit the interpretation of certain nutrient-based taphonomic results as no reliable baseline sample can be obtained within the facility.
Table 3
Advantages and disadvantages of domestic pig and human cadavers in forensic entomology and taphonomy research related to human decomposition [6, 911, 14, 23, 24, 44, 65]
 
Pig cadavers
Human cadavers
Cons
1. Dissimilar to human cadavers in some important aspects:
a. Body proportions
b. Gastrointestinal anatomy
c. Diet (more uniform, larger proportion of plant products)
2. More uniform than humans
3. Unacceptable in some cultures
1. Difficult to replicate:
a. Available in low numbers
b. Time and cause of death beyond researcher control (self-donation, age, disease incidence etc.)
c. Dissimilar to each other in:
• Mass
• Age, sex, ethnicity
• Antemortem pharmaceuticals use
• Body conditions (frozen/fresh, autopsied/non-autopsied, etc.)
2. Limitations of taphonomy facilities (body farms):
a. Small area, potential for insufficient inter-cadaver distances
b. Uniform abiotic conditions
c. Frequently non-natural conditions
d. Area saturated with cadavers
3. Limitations of casework (i.e. medical examiner samples):
a. Restricted to observation
b. Cannot control effects of routine processing of remains
c. Sometimes no information about death circumstances and the cadaver itself
4. Risk of sensationalized research
a. Complex ethical considerations/generally unacceptable
b. Potentially negative publicity
c. Potential for findings to be “oversold”
Pros
1. Similar to human cadavers in some important aspects:
a. Body mass range
b. Anatomy
c. Body composition
d. Skin coverage with hair
e. Gut microbiota
f. Gross processes of decay
2. Easy to replicate:
a. Cheap and available in large numbers
b. Time and cause of death controllable
c. Cadaver traits controllable
d. Possible to work with unfrozen cadavers
3. Less sensationalized research and relatively straightforward ethical considerations
1. No species-related differences
While, in many cases, researchers may be interested in how the decomposition process works in humans, the available human remains are either derived from inappropriate populations, cannot be linked to control samples or are too variable for robust experiments. Due to these practicalities, pig cadavers are usually the best choice available for most experimental purposes in forensic sciences. Moreover, pig cadavers may be used to compare treatments of relevance with forensic scenarios and to make inferences about human decomposition. If treatment A results in a slower decomposition than treatment B in pigs, in the absence of other information, we can reasonably assume a similar effect in humans, especially if it can be supported with other knowledge and logic. The possibility that a model animal and the humans that it models decompose differently does not make that model useless; it depends on the specific question being addressed. This conclusion has much wider applicability. For example, mouse cadavers were useful in demonstrating forensic applications of microbiology [41, 42]. Postmortem microbiome comparisons between different animals revealed the common appearance of some informative bacterial taxa across rodent, pig and human models [4143]. Another example is the use of rabbit cadavers to provide local carrion insect inventories (Table 1). When early cadaver colonizers (e.g. blow flies) are the focus, rabbits are as informative as pigs or humans, but when middle or late colonizers (e.g. beetles of Silphinae or Cleridae) are studied, rabbit cadavers are inappropriate, because such insects rarely colonize carcasses as small as rabbits [44, 45].
Comparative studies of pig and human cadavers revealed largely overlapping insect faunas [14, 44], with as much difference between individual pigs or humans as between pigs and humans [46]. Similarly, insect faunas compiled from human case studies (e.g. [47, 48]) largely resembled those from pig cadaver experiments (Table 1). Although alligator carrion revealed important faunal differences compared with large mammals (i.e. pigs, bears and deer), the latter group yielded highly similar insect community composition [49, 50]. These results indicate that, when compared across related cadaver taxa of similar size, carrion insects (i.e. necrophagous insects) show negligible preference for one cadaver taxon over another. Therefore, when pig cadavers are used to inventory local carrion-arthropod faunas, they appear to be as good as humans and are more practical (Table 3).
However, we suggest that pig cadavers larger than the recommended 20–30 kg domestic pigs [9, 10] should be used to compile full inventories of carrion entomofauna because smaller pigs yield an incomplete insect inventory (i.e. underrepresentation of middle or late colonizers [44, 45]). We therefore recommend cadavers a starting mass of at least 40 kg (and preferably 50–80 kg) as a standard to investigate local carrion-insect inventories. Smaller cadavers (piglets or rabbits) may be used in cases when early colonizers (e.g. blow flies) are the focus.
Most methods developed in forensic entomology or taphonomy are intended to be used with human cadavers. Therefore, at least their final validation should be performed with humans and preferably in real case scenarios. We are not aware, however, of any validation experiment in which performance of the forensic method developed using non-human cadavers has been evaluated using human cadavers. This is definitely an area for future experiments. Such research could enable forensic scientists to evaluate whether techniques based on data from human analogues (e.g. pig cadavers) are satisfactorily accurate when used in casework for human cadavers. As a result, we could distinguish techniques for which reference data could be amassed using human cadaver analogues and techniques for which human cadavers are necessary to get reference data. Nevertheless, analogues for humans, particularly large-bodied species, serve well in “proof-of-concept” studies (Table 2). Similarly, initial validation of forensic methods may be efficiently performed with pig cadavers (Table 2), particularly when different cadaver traits (e.g. mass) or environmental conditions (e.g. below/above ground) are to be compared.
All animals used in forensic entomology or taphonomy research are highly variable within species. This may lead to misinterpretation of experimental results, particularly when the experimental design of a study has weaknesses (see section 4 of this paper). However, the variation may also be advantageous, as it enables the researcher to choose the model best suited to the research. For example, if the scientific question obliges large replication, the experiment simply cannot be made with large pigs within standard research budgets, whereas piglets may be appropriate. If the researcher is interested in the thermal profile of decomposing remains, it may be more important to focus on the sunlight absorbance and mass of the model species than on its other traits. This argument may be extended to different animal models: experiments on initial colonisation patterns of blow flies may be more tractable using piglets or rabbits rather than adult pig or human cadavers. On the other hand, validation of the total body score (TBS) method for PMI estimation [51] needs humans or at least large pigs. Therefore, there is no universal model cadaver for research in forensic taphonomy or entomology, and the one that should be chosen depends on the scientific question and its experimental demands. This is an important point for the forensic science community to consider when designing experiments, analysing results or extrapolating conclusions.

Critique of the pig model as an analogue for human cadavers

Background

Use of domestic pigs in experimental forensic sciences has been challenged by recent comparisons of pig and human cadaver decomposition [23, 24]. One study [23] concluded that “pigs are not an adequate proxy for human decomposition studies”, and another [24] indicated that neither rabbits nor pigs “captured the pattern, rate, and variability of human decomposition”. Pigs may indeed decompose differently to humans, and therefore their experimental comparison is clearly worthwhile to forensic sciences. However, the intrinsic logistical difficulties associated with experiments involving human cadavers may impair such comparisons (Table 3), and therefore, questions arise about the validity of recent findings and conclusions. In the following sections, we discuss these questions and try to identify their consequences for the findings of the referenced experiments [23, 24] and the implications they have for the validity of the conclusion that pigs are inadequate analogues for humans in forensic research.
As we have discussed in section 3, all model organisms are highly variable intra-specifically. Biased sampling of this variation may lead to the misinterpretation of results of any model comparison. Both pigs and humans clearly exhibit variable sizes, pigmentation, hairiness, body mass index and other characteristics. Such factors may be confounded with treatments, and when they affect decomposition, they may make it impossible to assign results of a comparison between human and pig cadavers (or any other model) to a species effect (Fig. 2). As an example, if a study was conducted with male piglets and adult female humans only, it would not be possible to disentangle sex and age (or mass) effects from species effects. Therefore, sample selection within and between species is critical for such comparisons.

Experimental design

Confounded variables

Confounded variables make the outcome of an experiment ambiguous. Confounding effects arise when differences recorded in a response (dependent) variable as a putative result of experimental manipulation of explanatory (independent) variable(s) cannot be separated from other variables that may affect the response [52]. To confidently show that differences resulted from experimental manipulations, the groups under comparison should differ only in the manipulated variable(s), or more realistically, the groups should not differ systematically in any important variable other than the one under manipulation. Confounding variables should be controlled in the experimental design (and thus eliminated) or in its statistical analysis (and thus quantified). An important confounding variable likely to arise in pig and human comparisons is body mass.
Identifying differences in decomposition between species needs an experiment in which cadaver samples differ systematically only in the cadavers’ species. In the experiments of Dautartas et al. [24] and Connor et al. [23], samples of pig and human cadavers differed systematically in cadaver mass: the humans were systematically much larger than the pigs (Table 4). Although there are anecdotal observations suggesting low importance of adult human cadaver mass [53] and experimental findings supporting the claim that in a mass range of 73–159 kg (N = 12, nine cadavers over 100 kg, i.e. obese, adipose bodies) decomposition rate is not significantly related to human body mass [54], all rigorous studies revealed that in a forensically relevant mass range (10–90 kg) small pig cadavers decompose significantly faster than large ones [5559]. This difference appeared only in the case of insect-colonized carcasses [56] and has been suggested to result from less efficient active decay in larger cadavers, as a consequence of competition over carrion between different insect taxa [45, 59]. It is also related to surface-to-volume ratios, which reflect the surface area of the tissue where insects can feed, and to the size of the individual insect relative to that of the resource. Based on these patterns, it may be assumed that, when insects are present, smaller pig cadavers’ progress through the TBS scale at a faster rate than larger human cadavers. This seems to be the case (Figs. 3 and 4) with the studies of Dautartas et al. [24] and Connor et al. [23], making some of their results ambiguous and uninterpretable with respect to human–pig differences.
Table 4
Cadaver mass of pigs and humans used by Dautartas et al. [24] and Connor et al. [23]
 
Cadaver mass (kg)
 
Pigs
Difference between humans and pigs in mean cadaver mass
Humans
 
Mean
Range
V
Mean
Range
V
Dissimilarity score
(h−p)/(h+p)
Dautartas et al. [24]
Trial 1
64.6
60–68
4.8
13.2
77.8
72–84
6.1
0.093
Trial 2
49
40–59
14.1
25
74
53–107
30.8
0.203
Trial 3
50.6
47–57
8.5
24.8
75.4
57–85
15.1
0.197
Connor et al. [23]
35 (median)
25–64
n/a
≥ 45* (median)
n/a ( 80)*
n/a
n/a
0.391*
n/a not available
*Authors did not report mass of their human cadavers. They used adult humans and mention that “...over half the human sample was overweight or obese.”. According to “Anthropometric Reference Data for Children and Adults: United States, 2011-2014” [Fryar et al., 2016, Vital Health Stat 3] average body weight of adult females in USA was 76.4 kg and adult males 88.8 kg. Based on these data, we assume that the median mass of the human sample from Connor et al. [23] was no less than 80 kg, so the difference in median between pig and human sample was no less than 45 kg

Independence of replicates. Distance between cadavers

When cadavers are close to one other, they may cross-contaminate one another or “compete” for insect colonizers, or both, making them statistically non-independent [60, 61]. The cadaver that is more attractive to insects may mask the other, resulting in underrepresentation of insects and slower decomposition of the less attractive cadaver. In addition, dispersal of larvae becomes a potential mechanism to affect larval competition if the carcasses are located close to one another. If such effects are not taken into account (i.e., watching for larval dispersal, deploying drift fencing), small inter-cadaver distances are likely to alter species composition or decomposition rate, and lead to a lack of independence of experimental units, a basic assumption or requirement of most statistical tests.
In forensic entomology experiments, cadavers have usually been placed at least 50 m apart (Table 1) because there is empirical support that such a distance is sufficient to minimize cross-contamination by dispersing fly larvae [62, 63] and to ensure independence of cadavers [60]. In forensic taphonomy experiments, particularly with human cadavers, the distance has usually been much smaller, probably as a result of the smaller areas of human taphonomy research facilities where such experiments are located. Dautartas et al. [24] report that their cadavers were placed at least 3 m apart, and although Connor et al. [23] provide no information on the distance between their cadavers, the outdoor facility where the study was located has an area of about one acre [22], so we can assume their between-cadaver distances were less than 50 m. Such distances indicate that the cadavers used in both studies were not demonstrably independent in terms of the insect communities attending them. Little is known about the effect of small distance between cadavers on the pattern and rate of insect-mediated decomposition [60, 61]; therefore, relevant consequences of small between-cadaver distance on the results of the above studies are currently difficult to identify.

Inter-annual effects

Different years generally have different weather profiles leading to different insect richness and abundances and/or different insect pre-appearance intervals (PAI) (Table 1). These may result in substantial annual differences in decomposition rate.
In the experiments of Connor et al. [23], pig cadavers were exposed in September 2012 through August 2013 (12 pigs, one each month), while an extra five pigs were exposed on the same day as their 2nd through 6th human cadaver. The authors gave no specific dates of the human cadaver exposure (between September 2012 and December 2015). However, according to Wikipedia [22], they started to use human cadavers at their outdoor facility in November 2013. Therefore, most pigs were exposed in 2012 and 2013 and most humans probably in 2014 and 2015. If that was the case, there was a high level of treatment segregation and the species effect was confounded with an inter-annual effect. Consequently, the findings reported by Connor et al. [23] may be the result, at least in part, of differences in the biotic and abiotic determinants of decomposition in the different years of exposure rather than differences between cadaver species.

Subject variables

Subject variables are characteristics of individuals that are idiosyncratic and may affect the research variables, primarily by increasing their measured variances, sometimes referred to as “statistical noise”. Wherever possible, such variables should be controlled by selecting experimental subjects to minimize their effects, usually through matching the individuals as closely as possible. This is generally possible with pigs or rabbits but can be impractical with humans. For instance, the study of Connor et al. [23] exposed some human cadavers effectively fresh at the day of death but others after 53 days of postmortem refrigeration. Refrigeration affects bacterial communities that initiate decomposition, with consequences for the rate of decomposition and the attraction of insects [64], which must have resulted in amplifying variation in decomposition rates of humans in that study. This sort of consequence of working with human cadavers may predispose a study to generate misleading results.

Quantifying decomposition

The total body score (TBS) was originally developed as a point-based, semi-quantitative scale for scoring the decomposition of human cadavers [51]. It represents the total amount of accumulated decomposition identified from three body regions (head and neck, trunk, and limbs). The scale was modified for rabbit [25] and pig cadavers [65]. Keough et al. [65] observed significant differences between pig and human cadavers during early decomposition and proposed the amendment of the TBS scale for pig cadavers. The use of the same TBS scale to compare human and pig decomposition rate (e.g. [23, 24]) is incorrect. Given the differences observed between human and pig cadavers in gross morphological changes during decomposition [23, 24, 65], cross-species use of the same TBS scale is risky and should, ideally, be complemented with other measures of decomposition, such as daily or periodic weight loss (in %).

Statistical analysis and the presentation of results

Criticism is essential to the advancement of science but for a critique to be acceptable, its analysis must be robust. However, the analyses presented in Connor et al. [23] and Dautartas et al. [24] are inadequate to support their conclusions. In Connor et al. [23], the conclusion of a difference between human and pig cadavers is derived from a comparison of the slopes developed using linear mixed modelling. However, a simple look at the regression lines used to compare decomposition rates (see Fig. 4 in Connor et al. [23]) shows that the selected models are inadequate in terms of adjustment, leverage values and residuals. The figure also demonstrates that a statistical difference is found by the authors only because pigs were allowed to decompose for a longer period, as no human cadaver was scored at TBS values > 31. TBS values > 31 had a powerful leverage effect on the regression line because these scores were squared in the analysis. The analyses of Dautartas et al. [24] are also problematic because none of them accounts for repeated measurements on cadavers, resulting in temporal pseudoreplication, which is known to artificially decrease P values.
In addition, statistically detectable effects may be too small or too variable to have practical significance for estimates of PMIs [66]. Because cadavers are highly variable, not surprisingly, decomposition rates can be highly variable too. For this reason, when trends are reported, they should be accompanied by quantitative indications of variation (i.e. uncertainty). For instance, human and pig cadavers appeared to decompose differently in the study of Connor et al. [23], but when 95% confidence intervals are added to the trend lines (Fig. 4), the apparent differences disappear. The inclusion of those intervals would indicate that pigs of small size are adequate models for human decomposition unless the TBS is greater than 28, which is a different interpretation from the one originally drawn from that research.

Alternative model organisms

In some countries, pigs are not a realistic option for religious reasons, and other animal models are needed. Rabbits have been frequently used by forensic entomologists (Table 1), but obviously, they are too small to serve well for most forensic research. Carrion insect assemblages are distinctly less complex and persist for less time on small-sized cadavers compared with larger cadavers [44, 45]. Owing to their small size, the decomposition rate of rabbit cadavers is much faster than that of pig or human cadavers [24, 44]. Accordingly, the well-established importance of body size needs to be remembered when selecting alternatives, like sheep or goats, usually shorn to make insect sampling feasible and to reduce the potential impact of the fleece on decomposition, which is different from pig and human situations.

Recommendations

Previous papers suggested that a universal model cadaver for experimental field studies and training programs in forensic entomology would be a domestic pig weighing 20–30 kg of starting mass [9, 10]. No recommendation is currently available for taphonomy studies. However, a single and universal “model cadaver” for the forensic sciences is not useful. Different studies have different purposes, conditions and limitations. Therefore, more flexible guidelines on cadaver species and mass are needed (Table 5). A review of the guidelines proposed in this paper (Table 5) indicates that human cadavers appear necessary only in comparative studies involving other cadaver taxa and for final validation of forensic methods. In most cases, pig cadavers are an ideal choice, whereas other animal cadavers may be useful in supplemental or unavoidable (substitutional) cases. Moreover, researchers should usually use cadavers that are larger than the currently recommended size of 20–30 kg. Depending on the specific question of interest, other non-mass-related considerations may also be necessary.
Table 5
Guidelines for cadaver choice in forensic science research
Research type/subtype
Guidelines
Cadaver species
Cadaver mass
Experimental studies
Domestic pig, rabbit or rodents, depending on the objective of the study, human for model comparison experiments
Depending on study objective
Local insect inventory or succession studies, insect PAI studies
Early colonizers
Domestic pig, rabbit
No cadaver mass limitations
Early and middle colonizers
Domestic pig
 20 kg starting mass, preferably 20–40 kg
All colonizers
Domestic pig
 40 kg starting mass, preferably 50–80 kg
Tests of forensic methods
Proof-of-concept studies
Domestic pig, rabbit or rodents, depending on method tested
Depending on method tested
Initial validation studies
Domestic pig
10–40 kg as juvenile analogues, 50–80 kg as adult analogues
Final validation studies
Human
Preferably whole mass range

Conclusions

Pig cadavers have provided a comprehensive experimental foundation for empirical studies of decomposition in forensic entomology, taphonomy and ecology, and are likely to remain the analogue of choice in most such studies for the immediate future. A pivotal limitation to the value of human cadavers is an adequate supply of donated bodies, especially when a well-replicated experiment is required. Some of these limitations can be avoided by conducting observational studies with samples derived from death investigations (i.e. through collaboration with medical examiners), which will be limited by the samples available, and may not be appropriate for all types of scientific questions. Analogue models such as pigs are likely to remain logistically more tractable, being more readily available, more uniform in size and age and less ethically complex to deploy. Pigs are a sensible compromise between availability, cost, ethics and similarity to humans, and there is no better candidate at this time. At present, experiments using analogues are easier to replicate and make control of confounding factors more practicable than studies based solely on humans, and they can be validated by including human remains alongside the analogues (e.g. [14, 44]). Therefore, an adequate query is not whether we should abandon pig carcasses, but rather how pig carcasses and other animal models differ from human cadavers in certain aspects of their decomposition, for example, decomposition rate and patterns of colonisation by insects. Such research would put into perspective all the developments made possible over the past four decades by the use of human analogues (Table 1). Moreover, human cadavers are definitely limited resources for forensic sciences. Therefore, they should be invested to test hypotheses which were found to be forensically interesting for analogues, e.g. pig carcasses.
The need for robust replication and control are a direct consequence of both the inherent complexity of animal decomposition and the need for reliable forensic evidence in court. Our recommendations provide a quality assurance baseline for cadaver experiments. Indeed, simulated and reconstructed casework using pigs is an ideal test and cross-validation of conditions at a death scene (i.e. litigation research). Pig carcasses should be placed, if possible and acceptable, at or near the same site and time of year as the death scene and should serve as a reference for case analyses [67, 68].
A certain level of imprecision is inevitable even in superbly designed decomposition experiments, and court testimony will always need to draw cross-validation of decomposition-based estimates from other fields of science. Future decomposition studies will need to underpin their own importance with rigorous quality control measures [27, 28]. A means to this end have been outlined here, and many of the recommendations apply as much to research with human corpses as to any other animal species.

Acknowledgements

We thank David O. Carter (USA), Colin Moffatt (UK), Darryl J. de Ruiter (USA) and Amoret P. Whitaker (UK) for discussions and comments on earlier versions of the manuscript. Thanks are also extended to anonymous reviewers whose comments helped to improve the manuscript.
Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.

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Metadaten
Titel
Pigs vs people: the use of pigs as analogues for humans in forensic entomology and taphonomy research
Publikationsdatum
17.06.2019
Erschienen in
International Journal of Legal Medicine / Ausgabe 2/2020
Print ISSN: 0937-9827
Elektronische ISSN: 1437-1596
DOI
https://doi.org/10.1007/s00414-019-02074-5

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