Next Article in Journal
Tooth Cementum Annulation: A Literature Review
Next Article in Special Issue
A Controlled Experiment to Test the Efficacy of Ground-Penetrating Radar in the Search for Clandestine Burials in Poland
Previous Article in Journal
Dismemberment as a Method of Body Disposal in Spanish Forensic Cases
Previous Article in Special Issue
Soil Colour and Plant-Wax Markers: Application in Forensic Investigations under Urban Subtropical Environments
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Forensic Sciences
Volume 2
Issue 3
10.3390/forensicsci2030037
forensicsci-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Preliminary Taphonomical Comparison of the Decomposition Process in Simple Burials, Traditional Tombs and Aerated Tombs in an Urban Cemetery in Northern Italy

by
Edda Emanuela Guareschi
1,2,* and
Paola Annarosa Magni
1,3
1
Medical, Molecular and Forensic Sciences Department, Murdoch University, Murdoch 6150, WA, Australia
2
School of Medicine, The University of Notre Dame Australia, Fremantle 6160, WA, Australia
3
Singapore Centre for Research in Innovation, Productivity and Technology (SCRIPT), Murdoch University, Singapore 188306, Singapore
*
Author to whom correspondence should be addressed.
Forensic Sci. 2022, 2(3), 505-515; https://doi.org/10.3390/forensicsci2030037
Submission received: 17 June 2022 / Revised: 11 July 2022 / Accepted: 15 July 2022 / Published: 19 July 2022
(This article belongs to the Special Issue Forensic Geoscience and Death Investigations)
Browse Figures
Versions Notes

Abstract

:
In densely populated countries like Italy, cremation is promoted for the final disposition of the dead. However, many families still choose inhumation or entombment. In ordinary (traditional) tombs, bodies skeletonize slowly and partially, and often need a second disposal after the exhumation. The aim of this study was to experimentally test the functionality of a new type of tomb, defined as “aerated”. Aerated tombs feature an aerating system, absorbing materials and a purifying filter, which collectively maintain ventilation, process putrefactive fluids and gases and neutralize odors. In an experimental cemetery area with pristine soil, limbs of piglets were wrapped in cotton sheets and were either inhumed, placed in ordinary tombs or placed in aerated tombs. Following exhumation after planned time intervals (1, 3, 6, 9, 12, 18, 24 months), all samples were macro- and microscopically examined. The inhumed samples were completely skeletonized by 9 months after burial, and after 12 months showed initial bioerosion in bone Haversian canals. The traditionally entombed samples developed progressive adipocere formation, whereas the samples disposed in aerated tombs became mummified. Despite this outcome, aerated tombs represent a more energy-effective, environmentally-friendly and economical choice when compared to ordinary tombs. A mummified body is lighter and drier than a body entombed traditionally and, as such, it is easier to exhume and quicker to cremate. Overall, in the absence of alternative burials, aerated tombs are more suitable than ordinary tombs for the final disposition of the dead in cemeteries with limited space. The results of this experiment add to the knowledge of taphonomical processes in temperate climates and urban environments, potentially benefitting the forensic and medico-legal community.

1. Introduction

In densely populated countries, where the space available for cemeteries is limited, cremation is actively promoted for the final disposition of the dead. In Italy, cremation has been constantly increasing in the last 20 years, from 10% in 2007 [1] to 33.22% in 2020 [2]. This trend has also been accelerated by the need of handling a large number of deceased in a short period of time, due to the COVID-19 pandemic [3,4,5]. However, many families still choose inhumation (burial in the ground), or entombment (placement in a tomb or mausoleum), for practical reasons (e.g., the logistics of the crematorium), tribal traditions or religious and cultural beliefs. In a 2019 estimate for the Italian territory, this resulted in 18.82% of inhumations and 50.50% of entombments [2]. In order to maximize the space available in existing cemeteries, the Italian law requires periodic exhumations after 10 to 20 years, depending on the location [6]. However, while inhumed bodies can reach complete skeletonization in such time, allowing an easy relocation of the skeletal remains to ossuaries, after the same amount of time entombed bodies are generally not ready to be transferred. Even after 40 years since entombment, these remains can be still found only partially skeletonized, partially articulated and immersed in putrefactive sludge [7], with possibly extensive adipocere of soft tissues and corification of the skin layers [8]. In these cases, a further disposal of the body is required, either by cremation or inhumation, before the transfer to the ossuary. This practice is associated with sensitive issues, such as the cost of a second disposal, the necessity of space in cemeteries and the distress of the families involved [7]. In the last 20 years, the entombment in a new type of tomb defined as “aerated” [9,10] has been proposed as an alternative to inhumation or to the ordinary (traditional and sealed) entombment, with the aim of promoting the rapid skeletonization of the body, minimizing public health hazards and lowering the costs of further disposals, while respecting the established exhumation turnover.
Aerated tombs can be newly built or adapted from ordinary tombs. Through an aerating system with a purifying filter, these tombs achieve the double purpose of maintaining the ventilation within the tomb and of processing the putrefactive fluids and gases separately. This system targets the two main disadvantages of sealed tombs: (1) the ineffective skeletonization of bodies due to lack of ventilation; and (2) the leakage of fluids and gases during decomposition, which promotes the formation of adipocere [11]. In aerated tombs, fluids are absorbed by Enzisalm® (Ceabis), a biodegrading biological powder placed on the bottom of the coffin. Enzisalm® is composed of microorganisms and their specific nutrients, and promotes decomposition by metabolizing organic matter. Furthermore, Hydro-Gel® (Ceabis), another powder with gelifying and biocide action, is placed in the plastic collecting tray under the coffin, to absorb fluids and neutralize odors. Gases generated by decomposition are purified by an activated carbon filter. The structure of an aerated tomb is outlined in Figure 1. The first countries legalizing the use of aerated tombs in cemeteries were France, with the regulation NF P 98-049:1994 [12] and Spain, with the Decree 2263/1974 (20th of July) and autonomous regulations [13]. In the Italian region where this study was conducted (Emilia Romagna, north of Italy), aerated tombs were legalized in 2006 [14].
The aim of this study, carried out between 2011 and 2013 in Parma, Italy, was to test the safety and the functionality of aerated tombs for the first time, by characterizing the associated decomposition process and by comparing the decomposition rate with the one observed in inhumations and ordinary tombs in the environment of a northern Italian cemetery. Aerated tombs have been in use for about 20 years in the cemeteries of a few European countries, such as Italy, France and Spain, with the aim of achieving a more efficient, faster and cleaner decomposition of bodies. However, the aimed results have never been tested by research. The obtained results provide important information regarding the human decomposition process and the taphonomy in cemetery settings. Beside the main scope of testing aerated tombs, the obtained data will benefit forensic sciences by adding clues to the estimation of the time since death (Post-Mortem Interval, PMI) and the modification of bodies after death in medico-legal investigations regarding exhumed bodies and illegal burials [15,16].

2. Materials and Methods

The experiment took place between February 2011 and February 2013 in the cemetery “La Villetta” in Parma (northern Italy, 44°79′00″ N 10°31′43″ W), in a fenced area where the soil had never been previously used for burials. The fencing was necessary to prevent the accidental trespassing of the public. The use of cemetery areas for scientific studies was in accordance with the Italian legislation [6]. According to the Köppen-Geiger climate classification, the climate of Parma is Cfa, that is temperate, humid and with hot summers. The mean annual temperature is 13.70 °C (56.66 °F) and precipitation is 888.00 mm (34.96 in).
For the purpose of the experiment, lower limbs of swines (Sus scrofa domesticus Erxleben, n = 21, weighing between 420 g to 1430 g) deceased by natural causes in a local pig farm were used. In Italy, the current legislation does not allow the use of human cadavers for experimental purposes, and swines are considered the best proxy to human bodies for taphonomical studies [17]. Each limb was wrapped in biodegradable sheets (cotton) to mimic the presence of clothes [18]. In order to replicate inhumation, limb samples (n = 7) were individually placed in small pinewood coffins buried in the ground at a depth of 1.5 m; ordinary entombment was instead replicated by individually placing the samples (n = 7) in small zinc coffins, which were then sealed inside a stone tomb. The remaining samples (n = 7) were individually placed in small wooden coffins, which were then lined inside an aerated tomb, complete of all its components. The limited space available for the experiment in a public urban cemetery required the use of limbs, instead of complete bodies, and the allocation of a relatively small number of samples.
One sample for each of the disposal types was exhumed at planned time intervals of 1, 3, 6, 9, 12, 18 and 24 months, and codified as I (inhumation), OT (ordinary tomb) and AT (aerated tomb). Macroscopical parameters such as weight loss and an empirical estimation of decomposition were assessed at the time of exhumation. Microscopical analyses, such as microbiology on soft tissues, and histology on bone, were also performed at the time of exhumation. Microbiology was conducted in three different types of culture media, i.e., in atmosphere of CO2 at 37 °C for aerobic bacteria growth, in anaerobiosis at 37 °C for anaerobic bacteria growth, and in incubation at 25 °C for 10 days for yeasts, molds and fungal growth [19,20]. The staining techniques applied to histology on bone were Haematoxylin-Eosin, PAS (periodic-reactive Schiff acid) and Gomori-Grocott [21]. Each sample was observed and analyzed for the presence of insects and other arthropods, following the approved guidelines for collection and storage of necrophagous fauna available in the forensic entomology literature [22,23].

3. Data Analysis

Data obtained from the three types of sample disposals were subjected to statistical multivariate analysis. Contingency tables considered the type of disposal of the samples (inhumation, entombment in an ordinary tomb, entombment in an aerated tomb) and the outcome of decomposition (skeletonization, adipocere, mummification) over time (1, 3, 6, 9, 12, 18 and 24 months). The level of significance was set at p < 0.05. Calculations were performed using IBM® SPSS® Statistics 28 statistical analysis software.

4. Results

At the macroscopical observation, the inhumed samples followed the stages of putrefaction, that is, the typical pattern of decomposition. All the seven buried samples were completely skeletonized and disarticulated within 9 months since their deposition in the soil. On the contrary, the samples in both the ordinary and aerated tombs consistently maintained their overall morphology over time, until the last exhumation after 24 months. Traditionally entombed samples retained the moisture of soft tissues and showed the progressive formation of adipocere. In aerated tombs, samples shrank in size and became dry. The results of macroscopical observations are summarized in Table 1 and Figure 2.
Overall, in this quantitative, observational, longitudinal and prospective research, performed in an artificial setting, the statistical analysis of numerical data supported the hypothesis that aerated tombs were more functional than ordinary tombs for the decomposition of bodies in cemeteries. A total of 100% of the buried samples were completely skeletonized within 9 months after burial. In 18 and 24 months the samples placed in ordinary tombs only lost 48% and 47%, respectively, of their initial weight, showing a stabilization of the decomposition process from 18 months after the disposal onward. In 6 months, the samples placed in aerated tombs showed a loss of about one-third of the initial weight (34%), which reached slightly more than two-thirds (68%) by 9 months.
The microbiological analyses performed on soft tissues revealed a consistent presence of aerobic and anaerobic bacteria, with only anaerobic bacterial species (Clostridium spp.) present in ordinary entombments after 6 months. In all types of disposals (100%), the colonization by fungi and yeasts appeared to decrease over time, while molds increased. Bone histology confirmed the fast decomposition of soft tissues in inhumed samples, with preservation of bone microstructure and patterns of initial bioerosion in Haversian canals after 12 months. Bioerosion was not detected in bone samples from either ordinary or aerated tombs where, conversely, soft tissues such as bone marrow, connective and striated muscle remained visible throughout the whole duration of the experiment (24 months). Samples from aerated tombs exhibited a better microstructural preservation, with a clearer characterization of cells. The detailed results of microbiological and histological analyses are summarized in Table 2.
With regards to the entomological analyses, while at least specimens of coffin flies (Diptera: Phoridae), house flies (Diptera: Muscidae), beetles and mites typically present in tombs and burial environments were expected [24,25], negative results were obtained both at a macroscopical and microscopical observation.

5. Discussion

This study tested for the first time the safety and the functionality of aerated tombs, in comparison with inhumations and ordinary entombments. The results obtained are of interest for cemetery management purposes, but can also be useful for forensic investigations involving the estimation of the PMI of buried and entombed remains in urban cemetery settings. This research demonstrates that the decomposition process in aerated tombs leads to the mummification of the experimental samples. Progressive stages of the mummification process were identified and linked to the increasing amount of time passed since the start of the observations. The continuous drying, and the consequent shrinking, of the samples was generated by the presence of air, an essential and defining feature of aerated tombs, which promoted both the efficient evaporation of fluids and the colonization by diverse bacterial species, aerobic and anaerobic, which persisted throughout the experiment. The rapid loss of moisture and weight experienced by the samples continued until 12 months (78%), after which it slowed down and stabilized. The stabilization of the decomposition process is a typical characteristic of the mummification process [8,26,27,28]. In fact, samples that spent 12 and 24 months in the aerated tombs lost 82% and 85% of their initial weight, respectively. Having reached close-to-complete mummification, the last aerated tomb sample showed, at 24 months, scattered remnants of soft tissues attached to bone, such as bone marrow, connective and striated muscle, which microstructure was recognizable histologically and allowed the occasional clear identification of cells.
In accordance with previous studies [7,29,30,31], inhumation, notoriously associated with the drainage of water and fluids, the access of scavengers and the availability of oxygen [32,33], was confirmed as the environment characterized by the fastest decomposition, with complete skeletonization and disarticulation of the sample by 9 months after burial. The high aerobic and anaerobic microbiological activity promoted the fast breakdown of organic matter, and was also supported by the identification of initial patterns of bioerosion [34,35,36] in bone Haversian canals from 12 months onwards. In similar accordance with previous studies [7,11,37], entombment in ordinary tombs reaffirmed the trend towards the pervasive formation of adipocere, with no microstructure of soft tissues histologically recognizable after 12 months. Contrarily to both inhumation and aerated tombs, ordinary tombs feature a double coffin and act as closed systems, with virtually no exchange with the external environment, and create a humid microclimate that, in the absence of evaporation, causes slow weight loss. In fact, 48% and 47% of the initial samples’ weight were still present after 18 and 24 months, respectively. Finally, the consumption of air oxygen within 6 months led to the disappearance of fungi and aerobic bacterial species, thus only anaerobic bacterial species were detected.
Around the world, inhumation is still the most traditional of the post-mortem disposals [38,39], although presenting multiple disadvantages and being arguably eco-friendly. The requirements of a coffin with linings to accommodate the body, the purchase of a land plot and the need of funerary services (e.g., for the handling of the coffin) make it expensive. Moreover, cemetery land space is needed and potentially noxious substances, such as embalming chemicals, metals, cytotoxic drugs and infectious agents are left to seep into the ground for years [40,41,42]. This translates into the creation of necrosols, a type of urban soil [43,44], characterized by distinctive structure, stratigraphy and geochemistry. Necrosols present an increase in the contents of organic carbon, total nitrogen, phosphorus (defined as an indicator of anthropogenic impact) [45,46] and Zn, which can persist for thousands of years [47], and all concur in the production of an alkaline trend. Litter from grave artefacts, such as hardwood, nails, textiles and concrete, is widespread, and scattered human bones are easily found in necrosols [47,48,49]. This poses a threat to public health by the potential contamination of water sources, and makes any requalification of the urban spaces (e.g., parks) difficult [40,50]. Environmentally wise alternatives to inhumation or entombment are “green-burial” methods, such as water cremation [39,51] and human-composting, also known as natural organic reduction [52,53,54]. The environmental impact of these burials is much lighter than the traditional cremation by incineration [55] and achieves a final transformation of the body in a very short time (from 4 h in water cremation to 30 days in human composting), saving costs and space when compared to traditional cremation. Nowadays, green burials are available in an extremely limited number of countries, such as the US, Australia and South Africa.
When cremation is not the choice, either of the deceased (e.g., in their will) or of grieving families, green burials are not available and inhumation is not feasible, usually for the shortage of space in cemeteries, aerated tombs are a valid alternative to ordinary tombs for the final disposition of the dead. Despite the apparent favoring of mummification, aerated tombs represent a more energy-effective, environmentally-friendly and economical choice when compared to ordinary tombs. This study proves that, at the time of exhumation, the mummified body retrieved from an aerated tomb is comparatively lighter and drier than a traditionally entombed body, which often turns to adipocere. The exhumation of a mummified body is more hygienic and practical, the exhumations turnover can be more frequent, and the following cremation process requires less energy, with an overall decreased impact on the environment. Furthermore, it is highly likely that a mummified body exhumed from an aerated tomb in the context of a medicolegal investigation, e.g., for a posthumous identification, could yield usable genetic material, such as nuclear and/or mitochondrial DNA [56,57,58].

6. Conclusions

Preliminary comparison between different type of tombs shows that aerated tombs achieve better results than ordinary tombs in the decomposition of bodies. As a consequence, aerated tombs allow more frequent, practical and hygienic exhumations, as well as faster post-exhumation cremations. However, due to the limited numbers of samples, a variation of the obtained results can be reasonably expected if the experiment is repeated on a larger scale.
In countries affected by the shortage of space in, and for, urban cemeteries, a growing issue that requires careful management due to the sensitive nature of the topic, aerated tombs should be preferred to ordinary tombs when inhumation, cremation by incineration or other alternative final dispositions of the dead are not feasible.

7. Limitations of the Study and Future Directions

This study originated by research initially aimed to achieve a technical report to address a sensitive issue, associated with moral, ethical, financial, social and political implications. Hence, the small space allocated for the setup of an experimental area inside the public urban cemetery grounds limited the number of replicas. Moreover, the microbiological analyses were preliminary, and solely aimed to detect aerobic and/or anaerobic species. Finally, technical refinements of aerated tombs that might potentially overcome the mummification trend were not discussed, as they would fall beyond the journal’s forensic topic. From a taphonomic point of view, the mummification of bodies in aerated tombs could be reduced or eliminated with the aid of further studies (e.g., prospective and longitudinal on bodies disposed in aerated tombs in the present, with an established exhumation interval), by refining the deposition procedures (e.g., optimizing the added amount of biodegrading biological powder) and by improving the technology of the tomb structure. Future studies should consider larger experimental areas, as well as cemeteries in other locations, to compare the efficiency of aerated tombs in different climates.

Author Contributions

Conceptualization, Investigation, Methodology, Data Curation, Writing—Original Draft Preparation, E.E.G.; Methodology, Data Curation, Writing—Review and Editing, P.A.M. All authors have read and agreed to the published version of the manuscript.

Funding

No funds were received to perform and publish this research.

Institutional Review Board Statement

Ethical review and approval were waived for this study due to the absence of any specific requirement in the Italian legislation at the time of the study (2011-2013).

Informed Consent Statement

Not applicable.

Data Availability Statement

Not required at the time of the study (2011–2013). However, the authors declare that no animal was sacrificed for this study.

Acknowledgments

The authors wish to thank Paola Colla, then President of ADE S.p.A., and the cemetery director, Roberto Burchielli, for authorizing the study on the cemetery premises. The authors also wish to acknowledge the professional contributions of microbiologist Laura Zerbini, forensic pathologist Franklyn R.W. Van de Goot, Giuseppe Battistini and the operational staff of the cemetery “La Villetta” in Parma, Italy.

Conflicts of Interest

The authors declare that they have no conflict of interests.

References

  1. AA.VV. Cremazione: Italia divisa in due. Corr. Della Sera 2008, 2008, 8–9. [Google Scholar]
  2. AA.VV. Available online: https://www.funerali.org (accessed on 13 June 2022).
  3. Gonçalves, L.R.; Roberto, M.M.; Braga, A.P.A.; Barozzi, G.B.; Canizela, G.S.; de Souza Gigeck, L.; de Souza, L.R.; Marin-Morales, M.A. Another casualty of the SARS-CoV-2 pandemic—the environmental impact. Environ. Sci. Pollut. Res. 2022, 29, 1696–1711. [Google Scholar] [CrossRef]
  4. Ussai, S.; Armocida, B.; Formenti, B.; Palestra, F.; Calvi, M.; Missoni, E. Hazard Prevention, Death and Dignity During COVID-19 Pandemic in Italy. Front. Public Health 2020, 8, 509. [Google Scholar] [CrossRef]
  5. Calmon, M. Considerations of coronavirus (COVID-19) impact and the management of the dead in Brazil. Forensic Sci. Int. Rep. 2020, 2, 100110. [Google Scholar] [CrossRef]
  6. AA.VV. Regolamento di Polizia Mortuaria, ex DPR 10 Settembre 1990, n. 285. Gazzetta Ufficiale della Repubblica Italiana. 1990. Available online: http://www.tuttosuicimiteri.it/wp-content/files/RPM-285-circolare-24-1993-AGGIORNAMENTO-2017.pdf (accessed on 13 June 2022).
  7. Guareschi, E.E.; Dadour, I.R.; Magni, P.A. Taphonomic Examination of Inhumed and Entombed Remains in Parma Cemeteries, Italy. Glob. J. Forensic Sci. Med. 2019, 1, 1–8. [Google Scholar] [CrossRef]
  8. Collini, F.; Andreola, S.A.; Gentile, G.; Marchesi, M.; Muccino, E.; Zoja, R. Preservation of histological structure of cells in human skin presenting mummification and corification processes by Sandison’s rehydrating solution. Forensic Sci. Int. 2014, 244, 207–212. [Google Scholar] [CrossRef]
  9. Fogli, D. La città dei morti: Percezione della complessità gestionale dei cimiteri italiani moderni. L’evoluzione del cimitero in Italia. Nuova Antigone 1999. [Google Scholar]
  10. AA.VV. Development of an Advanced Burial Technology Integrating Biological Systems for Air Purifiaction and Enhanced Biodecomposition Leading to Reduced Harmful Emissions into the Environment. Available online: https://cordis.europa.eu/project/id/ENV4970690/it (accessed on 13 June 2022).
  11. Magni, P.A.; Lawn, J.; Guareschi, E.E. A practical review of adipocere: Key findings, case studies and operational considerations from crime scene to autopsy. J. Forensic Leg. Med. 2020, 78, 102109. [Google Scholar] [CrossRef]
  12. Un nouveau document pour décrypter la marque NF pour la qualité des caveaux autonomes préfabriqués en béton. Reson. Funer. 2009.
  13. Decreto 2263/1974, de 20 de Julio, por el Que se Aprueba el Reglamento de Policía Sanitaria Mortuoria. 1974. Available online: https://www.boe.es/eli/es/d/1974/07/20/2263/dof/spa/pdf (accessed on 13 June 2022).
  14. AA.VV. Regolamento in Materia di Piani Cimiteriali Comunali e di Inumazione e Tumulazione, Previsto Dall’art. 2, Comma 2, Della Legge Regionale N. 19/2004. 2006. Available online: https://demetra.regione.emilia-romagna.it/al/articolo?urn=er:assemblealegislativa:regolamento:2006;4 (accessed on 13 June 2022).
  15. Ferrándiz, F.; Robben, A.C.G.M.; Wilson, R.A. Necropolitics: Mass Graves and Exhumations in the Age of Human Rights; University of Pennsylvania Press: Philadelphia, PA, USA, 2015. [Google Scholar]
  16. Pokines, J.T.; L’Abbé, E.N.; Symes, S.A. Manual of Forensic Taphonomy, 2nd ed.; CRC Press: Boca Raton, FL, USA, 2021. [Google Scholar] [CrossRef]
  17. Schoenly, K.G.; Hall, R.D. Testing Reliability of Animal Models in Research and Training Programs in Forensic Entomology, Part II, Final Report; US Department of Justice: Rockville, MD, USA, 2002. [Google Scholar]
  18. Teo, C.H.; Hing, H.L.; Hamzah, N.H.; Hamzah, S. The Effect of Different Coverings on Total Body Score Development of Buried Carcasses. Malays. J. Med. Sci. 2021, 28, 103–112. [Google Scholar] [CrossRef]
  19. Willey, J.M.; Sherwood, L.M.; Woolverton, C.J.; Prescott, L.M. Prescott, Harley, and Klein’s Microbiology, 7th ed.; McGraw-Hill Higher Education: New York, NY, USA, 2008. [Google Scholar]
  20. Maier, R.M.; Gerba, C.P.; Pepper, I.L. Environmental Microbiology; Academic Press: London, UK; San Diego, CA, USA, 2000. [Google Scholar]
  21. Suvarna, S.K.; Layton, C.; Bancroft, J.D. Bancroft’s Theory and Practice of Histological Techniques, 7th ed.; Churchill Livingstone Elsevier: Oxford, UK, 2013. [Google Scholar]
  22. Amendt, J.; Amendt, J.; Campobasso, C.P.; Campobasso, C.P.; Gaudry, E.; Gaudry, E.; Reiter, C.; Reiter, C.; LeBlanc, H.N.; LeBlanc, H.N.; et al. Best practice in forensic entomology—standards and guidelines. Int. J. Leg. Med. 2007, 121, 90–104. [Google Scholar] [CrossRef]
  23. Sanford, M.R.; Byrd, J.H.; Tomberlin, J.K.; Wallace, J.R. Entomological evidence collections methods-American Board of Forensic Entomology approved protocols. In Forensic Entomology—The Utility of Arthropods in Legal Investigation; Byrd, J.H., Tomberlin, J.K., Eds.; CRC Press: Boca Raton, FL, USA, 2020; pp. 63–86. [Google Scholar]
  24. Gaudry, E. The insect colonization of buried remains. In Current Concepts in Forensic Entomology; Amendt, J., Goff, M.L., Campobasso, C.P., Grassberger, M., Eds.; Springer: Berlin/Heidelberg, Germany, 2010; pp. 273–312. [Google Scholar]
  25. Perotti, M.A.; Braig, H.R. Acarology in crimino-legal investigations. The human acarofauna during life and death. In Forensic Entomology—The Utility of Arthropods in Legal Investigation; Byrd, J.H., Tomberlin, J.K., Eds.; CRC Press: Boca Raton, FL, USA, 2020; pp. 461–474. [Google Scholar]
  26. Aturaliya, S.; Lukasewycz, A. Experimental forensic and bioanthropological aspects of soft tissue taphonomy: 1. Factors influencing postmortem tissue desiccation rate. J. Forensic Sci. 1999, 44, 893. [Google Scholar] [CrossRef]
  27. Saukko, P.J.A.; Knight, B.A. Knight’s Forensic Pathology, 4th ed.; CRC Press: Boca Raton, FL, USA, 2016. [Google Scholar]
  28. Veiga, P. Studying Mummies and Human Remains: Some Current Developments and Issues. J. Wash. Acad. Sci. 2012, 98, 1–21. [Google Scholar]
  29. Vass, A.A. Beyond the grave-understanding human decomposition. Microbiol. Today 2001, 28, 190–192. [Google Scholar]
  30. Haglund, W.D.; Sorg, M. Forensic Taphonomy: The Postmortem Fate of human Remains; CRC Press: Boca Raton, FL, USA, 1997. [Google Scholar]
  31. Haglund, W.D.; Sorg, M. Advances in Forensic Taphonomy (Method, Theory and Archaeological Perspectives); CRC Press: Boca Raton, FL, USA, 2002. [Google Scholar]
  32. Galloway, A.; Birkby, W.H.; Jones, A.M.; Henry, T.E.; Parks, B.O. Decay rates of human remains in an arid environment. J. Forensic Sci. 1989, 34, 607–616. [Google Scholar] [CrossRef]
  33. Turner, B.; Wiltshire, P. Experimental validation of forensic evidence: A study of the decomposition of buried pigs in a heavy clay soil. Forensic Sci. Int. 1999, 101, 113–122. [Google Scholar] [CrossRef]
  34. Turner-Walker, G. Early bioerosion in skeletal tissues: Persistence through deep time. Neues Jahrb. Für Geol. Und Paläontologie - Abh. 2012, 265, 165–183. [Google Scholar] [CrossRef]
  35. Booth, T.J. An Investigation Into the Relationship Between Funerary Treatment and Bacterial Bioerosion in European Archaeological Human Bone. Archaeometry 2016, 58, 484–499. [Google Scholar] [CrossRef]
  36. Kendall, C.; Eriksen, A.M.H.; Kontopoulos, I.; Collins, M.J.; Turner-Walker, G. Diagenesis of archaeological bone and tooth. Palaeogeogr. Palaeoclimatol. Palaeoecol. 2018, 491, 21–37. [Google Scholar] [CrossRef] [Green Version]
  37. Ubelaker, D.H.; Zarenko, K.M. Adipocere: What is known after over two centuries of research. Forensic Sci. Int. 2011, 208, 167–172. [Google Scholar] [CrossRef]
  38. Thody, C.E. A Study of The Relationships Between Environments and Human Death Practices; University of Nebraska-Lincoln: Lincoln, NE, USA, 2020. [Google Scholar]
  39. Slabbert, M.; Labuschaigne, M. Aquamation: Legal nail in burial and cremation’s coffin? De Jure Law J. 2021, 54, 359–369. [Google Scholar] [CrossRef]
  40. Vélez, S.; Cardona Gallo, S.A.; Monsalve, T.; Quiroz, M.L.; Castañeda, D.; Terrazas, A.; Sedov, S. Estudio de Necrosoles y suelos de cementerio. Dyna 2019, 86, 337–345. [Google Scholar] [CrossRef] [Green Version]
  41. Żychowski, J.; Bryndal, T. Impact of cemeteries on groundwater contamination by bacteria and viruses—A review. J. Water Health 2014, 13, 285–301. [Google Scholar] [CrossRef]
  42. Całkosiński, I.; Płoneczka-Janeczko, K.; Ostapska, M.; Dudek, K.; Gamian, A.; Rypuła, K. Microbiological Analysis of Necrosols Collected from Urban Cemeteries in Poland. BioMed Res. Int. 2015, 2015, 169573. [Google Scholar] [CrossRef] [Green Version]
  43. Majgier, L.; Rahmonov, O. Selected Chemical Properties of Necrosols from the Abandoned Cemeteries Słabowo and Szymonka (Great Mazurian Lakes District). Bull. Geography. Phys. Geogr. Ser. 2012, 5, 43–55. [Google Scholar] [CrossRef] [Green Version]
  44. Graf, A. Flora und vegetation der Friedhofe in Berlin (West). Verh. Des Berl. Bot. Ver. 1986, 5, 209–210. [Google Scholar]
  45. Majgier, L.; Rahmonov, O.; Bednarek, R. Features of abandoned cemetery soils on sandy substrates in Northern Poland. Eurasian Soil Sci. 2014, 47, 621–629. [Google Scholar] [CrossRef]
  46. Jarvis, D.R. Nitrogen levels in long bones from coffin burials interred for periods of 26–90 years. Forensic Sci. Int. 1997, 85, 199–208. [Google Scholar] [CrossRef]
  47. Asare, M.O.; Šmejda, L.; Horák, J.; Holodňák, P.; Černý, M.; Pavlů, V.; Hejcman, M. Human burials can affect soil elemental composition for millennia—analysis of necrosols from the Corded Ware Culture graveyard in the Czech Republic. Archaeol. Anthropol. Sci. 2020, 12, 255. [Google Scholar] [CrossRef]
  48. Bednarek, R.; Jankowski, M.; Kwiatkowska, A.; Markiewicz, M.; Świtoniak, M. The Diversity of Phosphorus in Soils within the Complex in Kałdus Settlement and its Surroundings; Chudziak, W., Ed.; Polish Society of Soil Science: Warsaw, Poland, 2004; pp. 199–208. [Google Scholar]
  49. Amuno, S.A.; Amuno, M.M. Geochemical Assessment of Two Excavated Mass Graves in Rwanda: A Pilot Study. Soil Sediment Contam. Int. J. 2014, 23, 144–165. [Google Scholar] [CrossRef]
  50. Jonker, C.; Olivier, J. Mineral contamination from cemetery soils: Case study of Zandfontein Cemetery, South Africa. Int. J. Environ. Res. Public Health 2012, 9, 511–520. [Google Scholar] [CrossRef]
  51. Olson, P.R. Flush and Bone: Funeralizing Alkaline Hydrolysis in the United States. Sci. Technol. Hum. Values 2014, 39, 666–693. [Google Scholar] [CrossRef]
  52. Ghosh, P. Human compost funerals ‘better for environment’. BBC News, 16 February 2020. [Google Scholar]
  53. Devault-Weaver, W. The Architecture of Human Composting; University of Washington: Washington, DC, USA, 2020. [Google Scholar]
  54. Alfus, K.M. Better Homes and Scattered Gardens: Why Iowa Should Legalize “Human Composting” as a Method of Final Disposition. Iowa L. Rev. 2020, 106, 325–362. [Google Scholar]
  55. Mari, M.; Domingo, J.L. Toxic emissions from crematories: A review. Environ. Int. 2010, 36, 131–137. [Google Scholar] [CrossRef]
  56. Watson, T. Mummy DNA unravels ancient Egyptians’ ancestry. Nature 2017, 546, 17. [Google Scholar] [CrossRef] [Green Version]
  57. van den Berge, M.; Wiskerke, D.; Gerretsen, R.R.R.; Tabak, J.; Sijen, T. DNA and RNA profiling of excavated human remains with varying postmortem intervals. Int. J. Leg. Med. 2016, 130, 1471–1480. [Google Scholar] [CrossRef]
  58. Guareschi, E.E. A specific identification from mixed skeletal remains in a cemetery setting. In Forensic Pathology Case Studies, 1st ed.; Academic Press: Cambridge, MA, USA; Elsevier: Amsterdam, The Netherlands, 2021; pp. 47–56. [Google Scholar]
Forensicsci 02 00037 g001 550
Figure 1. Structural outline of an aerated tomb. Enzisalm® (Ceabis) is placed on the bottom of the coffin to absorb decomposition fluids. Hydro-Gel® (Ceabis) is placed in the collecting tray under the coffin to absorb fluids and neutralize odors. Decomposition gases are purified by the activated carbon filter (top right).
Figure 1. Structural outline of an aerated tomb. Enzisalm® (Ceabis) is placed on the bottom of the coffin to absorb decomposition fluids. Hydro-Gel® (Ceabis) is placed in the collecting tray under the coffin to absorb fluids and neutralize odors. Decomposition gases are purified by the activated carbon filter (top right).
Forensicsci 02 00037 g001
Forensicsci 02 00037 g002 550
Figure 2. Decrease of the samples’ weight over time, following the loss of soft tissues until the complete skeletonization. The buried samples were completely skeletonized within 9 months and were assigned a “0” weight value. The samples placed in ordinary tombs lost 48% and 47% of their initial weight in 18 and 24 months, respectively. The samples placed in aerated tombs showed a loss of about one-third of their initial weight (34%) in 6 months, and slightly more than two-thirds (68%) by 9 months.
Figure 2. Decrease of the samples’ weight over time, following the loss of soft tissues until the complete skeletonization. The buried samples were completely skeletonized within 9 months and were assigned a “0” weight value. The samples placed in ordinary tombs lost 48% and 47% of their initial weight in 18 and 24 months, respectively. The samples placed in aerated tombs showed a loss of about one-third of their initial weight (34%) in 6 months, and slightly more than two-thirds (68%) by 9 months.
Forensicsci 02 00037 g002
Table
Table 1. Results of the macroscopical observations: weight of each sample at the time of disposal (February 2011) and at the time of exhumation (after 1, 3, 6, 9, 12, 18 and 24 months), with the percentage of weight loss starting from 100%. Samples which had lost all soft tissues (complete skeletonization) were assigned a “0” weight value. Weights have been rounded to the closest whole number.
Table 1. Results of the macroscopical observations: weight of each sample at the time of disposal (February 2011) and at the time of exhumation (after 1, 3, 6, 9, 12, 18 and 24 months), with the percentage of weight loss starting from 100%. Samples which had lost all soft tissues (complete skeletonization) were assigned a “0” weight value. Weights have been rounded to the closest whole number.
Type of DisposalPeriod of Disposal
(Months)		Weight at the Time of Disposal (g)Weight at the Time of Exhumation (g)Weight Loss (%) a
Inhumation (I)177071693
31430110077
677039051
96500 b100 b
127800 b100 b
187500 b100 b
2410400 b100 b
Ordinary tomb
(OT)		149048699
31320118089
673057078
973050068
1270042060
1893045048
24138065047
Aerated tomb
(AT)		157054495
360046578
650033066
942013332
1265014622
18116021418
24106016015
a Starting from 100% at the time of disposal. b Completely skeletonized samples were assigned a “0” weight value.
Table
Table 2. Details of the results of microbiological analyses on soft tissues and bone histology.
Table 2. Details of the results of microbiological analyses on soft tissues and bone histology.
Type of DisposalPeriod of Disposal
(months)		Presence of Bacteria aPresence of Fungi bBone PreservationSoft Tissue Preservation
Inhumation (I)1AnBF, M, YPreservedResidues of bone marrow
3AB/AnBF, M, YPreservedNo
6AB/AnBNonePreservedNo
9AB/AnBF, M, YPreservedNo
12AB/AnBF, M, YBioerosion (Haversian canals)No
18AB/AnBMoldsBioerosion (Haversian canals)Rare remnants of bone marrow and cartilage
24AB/AnBMoldsBioerosion (Haversian canals)Rare remnants of bone marrow and cartilage
Ordinary tomb
(OT)		1AB/AnBF, M, YPreservedResidues of bone marrow
3AB/AnBF, M, YPreservedRare residues of bone marrow
6AnBNonePreservedRare residues of bone marrow
9AnB
(Clostridium spp.)		NonePreservedRare residues of bone marrow
12AnB
(Clostridium spp.)		Molds, yeastsPreservedRare residues of bone marrow
18AnBMoldsPreservedNo
24AnB
(Clostridium spp.)		MoldsPreservedNo
Aerated tomb
(AT)		1AB/AnBF, M, YPreservedRemnants of bone marrow, connective and striated muscular tissue
3AB/AnBF, M, YPreservedRare remnants of bone marrow, connective and striated muscular tissue
6AB/AnBMoldsPreservedRare remnants of bone marrow, connective and striated muscular tissue
9AB/AnBNonePreservedRare remnants of bone marrow, connective and striated muscular tissue
12AB/AnB
(Bacillus spp., Coccus spp.)		MoldsPreservedRare remnants of bone marrow, connective and striate muscular tissue
18AB/AnBMoldsPreservedRare remnants of bone marrow, connective and striated muscular tissue
24AB/AnBFungi, moldsPreservedRare remnants of bone marrow, connective and striated muscular tissue
a aerobic bacteria (AB) and anaerobic bacteria (AnB), b fungi (F), molds (M), yeasts (Y).
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Guareschi, E.E.; Magni, P.A. Preliminary Taphonomical Comparison of the Decomposition Process in Simple Burials, Traditional Tombs and Aerated Tombs in an Urban Cemetery in Northern Italy. Forensic Sci. 2022, 2, 505-515. https://doi.org/10.3390/forensicsci2030037

AMA Style

Guareschi EE, Magni PA. Preliminary Taphonomical Comparison of the Decomposition Process in Simple Burials, Traditional Tombs and Aerated Tombs in an Urban Cemetery in Northern Italy. Forensic Sciences. 2022; 2(3):505-515. https://doi.org/10.3390/forensicsci2030037

Chicago/Turabian Style

Guareschi, Edda Emanuela, and Paola Annarosa Magni. 2022. "Preliminary Taphonomical Comparison of the Decomposition Process in Simple Burials, Traditional Tombs and Aerated Tombs in an Urban Cemetery in Northern Italy" Forensic Sciences 2, no. 3: 505-515. https://doi.org/10.3390/forensicsci2030037

Article Metrics

Back to TopTop