Gail Anderson

Dr. Gail Anderson


Research Focus & Metrics

Academic Career Length

28Years (1999-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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14 September 2010 in Journal of Forensic Sciences
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GAGail Anderson
Gail Anderson

29 May 2004 in International journal of legal medicine
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Journal Article
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GAGail Anderson
Gail Anderson
NHN. R. Hobischak
N. R. Hobischak

20 October 2014 in PLOS ONE
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GAGail Anderson
Gail Anderson
LBLynne S. Bell
Lynne S. Bell
Decomposition and faunal colonization of a carcass in the terrestrial environment has been well studied, but knowledge of decomposition in the marine environment is based almost entirely on anecdotal reports. Three pig carcasses were deployed in Saanich Inlet, BC, over 3 years utilizing Ocean Network Canada’s VENUS observatory. Each carcass was deployed in late summer/early fall at 99 m under a remotely controlled camera and observed several times a day. Dissolved oxygen, temperature, salinity, density and pressure were continuously measured. Carcass 1 was immediately colonized by Munida quadrispina, Pandalus platyceros and Metacarcinus magister, rapidly scavenged then dragged from view by Day 22. Artifacts specific to each of the crustaceans’ feeding patterns were observed. Carcass 2 was scavenged in a similar fashion. Exposed tissue became covered by Orchomenella obtusa (Family Lysianassidae) which removed all the internal tissues rapidly. Carcass 3 attracted only a few M. quadrispina, remaining intact, developing a thick filamentous sulphur bacterial mat, until Day 92, when it was skeletonized by crustacea. The major difference between the deployments was dissolved oxygen levels. The first two carcasses were placed when oxygen levels were tolerable, becoming more anoxic. This allowed larger crustacea to feed. However, Carcass 3 was deployed when the water was already extremely anoxic, which prevented larger crustacea from accessing the carcass. The smaller M. quadrispina were unable to break the skin alone. The larger crustacea returned when the Inlet was re-oxygenated in spring. Oxygen levels, therefore, drive the biota in this area, although most crustacea endured stressful levels of oxygen to access the carcasses for much of the time. These data will be valuable in forensic investigations involving submerged bodies, indicating types of water conditions to which the body has been exposed, identifying post-mortem artifacts and providing realistic expectations for recovery divers and families of the deceased.

25 March 2021 in Insects
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ZKZanthe Kotze
Zanthe Kotze
SASylvain Aimar
Sylvain Aimar
Jens AmendtJens Amendt
Jens Amendt
GAGail Anderson
Gail Anderson
LBLuc Bourguignon
Luc Bourguignon
JTJeffrey Tomberlin
Jeffrey Tomberlin
Forensic practitioners analyzing entomological evidence are faced with numerous challenges when presenting their findings to law practitioners, particularly in terms of terminology used to describe insect age, what this means for colonization time of remains, and the limitations to estimates made. Due to varying legal requirements in different countries, there is no standard format for the entomological case report prepared, nor any guidelines as to the sections that are required, optional or unnecessary in a case report. The authors herein propose sections that should be considered when drafting an entomological case report. The criteria under which entomological evidence is analyzed are discussed, as well as the limitations for each criterion. The concept of a global, standardized entomological case report is impossible to achieve due to national legislative differences, but the authors here propose a basic template which can be adapted and changed according to the needs of the practitioner. Furthermore, while the discussion is fairly detailed, capturing all differences between nations could not be accomplished, and those initiating casework for the first time are encouraged to engage other practicing forensic entomologists or professional associations within their own nation or region, to ensure a complete report is generated that meets lab or national requirements, prior to generating a finalized report.

1 March 2016 in PLOS ONE
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GAGail Anderson
Gail Anderson
LBLynne S. Bell
Lynne S. Bell
Pig carcasses, as human proxies, were placed on the seabed at a depth of 300 m, in the Strait of Georgia and observed continuously by a remotely operated camera and instruments. Two carcasses were deployed in spring and two in fall utilizing Ocean Network Canada’s Victoria Experimental Network under the Sea (formerly VENUS) observatory. A trial experiment showed that bluntnose sixgill sharks could rapidly devour a carcass so a platform was designed which held two matched carcasses, one fully exposed, the other covered in a barred cage to protect it from sharks, while still allowing invertebrates and smaller vertebrates access. The carcasses were deployed under a frame which supported a video camera, and instruments which recorded oxygen, temperature, salinity, density, pressure, conductivity, sound speed and turbidity at per minute intervals. The spring exposed carcass was briefly fed upon by sharks, but they were inefficient feeders and lost interest after a few bites. Immediately after deployment, all carcasses, in both spring and fall, were very rapidly covered in vast numbers of lyssianassid amphipods. These skeletonized the carcasses by Day 3 in fall and Day 4 in spring. A dramatic, very localized drop in dissolved oxygen levels occurred in fall, exactly coinciding with the presence of the amphipods. Oxygen levels returned to normal once the amphipods dispersed. Either the physical presence of the amphipods or the sudden draw down of oxygen during their tenure, excluded other fauna. The amphipods fed from the inside out, removing the skin last. After the amphipods had receded, other fauna colonized such as spot shrimp and a few Dungeness crabs but by this time, all soft tissue had been removed. The amphipod activity caused major bioturbation in the local area and possible oxygen depletion. The spring deployment carcasses became covered in silt and a black film formed on them and on the silt above them whereas the fall bones remained uncovered and hence continued to be attractive to large numbers of spot shrimp. The carcass remains were recovered after 166 and 134 days respectively for further study.

1 January 2008 in Canadian Society of Forensic Science Journal
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Journal Article
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JKJ.A. Kelly
J.A. Kelly
TLT.C. Van Der Linde
T.C. Van Der Linde
GAGail Anderson
Gail Anderson
Clothing and wrapping of a carcass creates an environment which may influence natural decomposition and arthropod succession. Six pig carcasses were divided into three sample groups, each with a clothed carcass wrapped in a sheet and a carcass wrapped but with no clothes. These were sampled daily, or after five and ten days. An additional two pig carcasses, one with no clothes or wrapping, the other with clothes and no wrapping, were also sampled daily as controls. There was a delay in oviposition on the exposed and wrapped carcasses of five and nine days, respectively. During the extended active stage of the decomposition process, there was not a clear successional pattern, possibly due to the lack of competition between the arthropods. Overall the wrapped carcasses retained a higher mass than the exposed carcasses, as they remained moist for a longer period of time. The Diptera species breeding on the carcasses included the Calliphoridae, Lucilia spp., Chrysomya chloropyga and Calliphora vicina, and Sarcophagidae spp. The Coleoptera community was dominated by adult Dermestes maculatus (Dermestidae) and Necrobia rufipes (Cleridae) which were present on the carcasses throughout the trial. During the more advanced stages of decomposition, Thanathopilus micans (Silphidae) larvae, succeeded by D. maculatus larvae, were present.