Adam Michael Lewis

Mr. Adam Michael Lewis


Research Focus & Metrics

Academic Career Length

9Years (2018-Present)

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

Representative Publications

View All Publications
11 January 2018 in Toxins
Verified
Journal Article
Open access
PDF file
Andrew David TurnerAndrew David Turner
Andrew David Turner
MDMonika Dhanji-Rapkova
Monika Dhanji-Rapkova
AOAlison O’neill
Alison O’neill
LCLewis Coates
Lewis Coates
ALAdam Michael Lewis
Adam Michael Lewis
KLKaty Lewis
Katy Lewis
Cyanobacterial blooms in freshwater bodies in England are currently monitored reactively, with samples containing more than 20,000 cells/mL of potentially toxin-producing species by light microscopy resulting in action by the water body owner. Whilst significantly reducing the risk of microcystin exposure, there is little data describing the levels of these toxins present in cyanobacterial blooms. This study focused on the quantitative LC-MS/MS analysis of microcystins in freshwater samples, collected across England during 2016 and found to contain potentially toxin-producing cyanobacteria. More than 50% of samples contained quantifiable concentrations of microcystins, with approximately 13% exceeding the WHO medium health threshold of 20 μg/L. Toxic samples were confirmed over a nine-month period, with a clear increase in toxins during late summer, but with no apparent geographical patterns. No statistical relationships were found between total toxin concentrations and environmental parameters. Complex toxin profiles were determined and profile clusters were unrelated to cyanobacterial species, although a dominance of MC-RR was determined in water samples from sites associated with lower rainfall. 100% of samples with toxins above the 20 μg/L limit contained cell densities above 20,000 cells/mL or cyanobacterial scum, showing the current regime is suitable for public health. Conversely, with only 18% of cell density threshold samples having total microcystins above 20 μg/L, there is the potential for reactive water closures to unnecessarily impact upon the socio-economics of the local population. In the future, routine analysis of bloom samples by LC-MS/MS would provide a beneficial confirmatory approach to the current microscopic assessment, aiding both public health and the needs of water users and industry.

26 July 2018 in Journal of Phycology
Verified
Journal Article
Closed access
PDF file
ALAdam Michael Lewis
Adam Michael Lewis
LCLewis Nicholas Coates
Lewis Nicholas Coates
Andrew David TurnerAndrew David Turner
Andrew David Turner
LPLinda Percy
Linda Percy
JLJane Lewis
Jane Lewis

29 July 2020 in Marine Drugs
Verified
Journal Article
Open access
PDF file
KDKarl Dean
Karl Dean
RHRobert G Hatfield
Robert G Hatfield
VLVanessa Lee
Vanessa Lee
RARyan P Alexander
Ryan P Alexander
ALAdam Michael Lewis
Adam Michael Lewis
Andrew David TurnerAndrew David Turner
Andrew David Turner
In early 2018, a large easterly storm hit the East Anglian coast of the UK, colloquially known as the ‘Beast from the East’, which also resulted in mass strandings of benthic organisms. There were subsequent instances of dogs consuming such organisms, leading to illness and, in some cases, fatalities. Epidemiological investigations identified paralytic shellfish toxins (PSTs) as the cause, with toxins present in a range of species and concentrations exceeding 14,000 µg STX eq./kg in the sunstar Crossaster papposus. This study sought to better elucidate the geographic spread of any toxicity and identify any key organisms of concern. During the summers of 2018 and 2019, various species of benthic invertebrates were collected from demersal trawl surveys conducted across a variety of locations in the North Sea. An analysis of the benthic epifauna using two independent PST testing methods identified a ‘hot spot’ of toxic organisms in the Southern Bight, with a mean toxicity of 449 µg STX eq./kg. PSTs were quantified in sea chervil (Alcyonidium diaphanum), the first known detection in the phylum bryozoan, as well as eleven other new vectors (>50 µg STX eq./kg), namely the opisthobranch Scaphander lignarius, the starfish Anseropoda placenta, Asterias rubens, Luidia ciliaris, Astropecten irregularis and Stichastrella rosea, the brittlestar Ophiura ophiura, the crustaceans Atelecyclus rotundatus and Munida rugosa, the sea mouse Aphrodita aculeata, and the sea urchin Psammechinus miliaris. The two species that showed consistently high PST concentrations were C. papposus and A. diaphanum. Two toxic profiles were identified, with one dominated by dcSTX (decarbamoylsaxitoxin) associated with the majority of samples across the whole sampling region. The second profile occurred only in North-Eastern England and consisted of mostly STX (Saxitoxin) and GTX2 (gonyautoxin 2). Consequently, this study highlights widespread and variable levels of PSTs in the marine benthos, together with the first evidence for toxicity in a large number of new species. These findings highlight impacts to ‘One Health’, with the unexpected sources of toxins potentially creating risks to animal, human and environmental health, with further work required to assess the severity and geographical/temporal extent of these impacts.

1 February 2021 in Environmental Pollution
Verified
Journal Article
Open access
DCDolores Camacho-Muñoz
Dolores Camacho-Muñoz
JWJulia Waack
Julia Waack
Andrew David TurnerAndrew David Turner
Andrew David Turner
ALAdam Michael Lewis
Adam Michael Lewis
LLLinda A. Lawton
Linda A. Lawton
CEChristine Edwards
Christine Edwards
Freshwater cyanobacteria produce highly toxic secondary metabolites, which can be transported downstream by rivers and waterways into the sea. Estuarine and coastal aquaculture sites exposed to toxic cyanobacteria raise concerns that shellfish may accumulate and transfer cyanotoxins in the food web. This study aims to describe the competitive pattern of uptake and depuration of a wide range of microcystins (MC-LR, MC-LF, MC-LW, MC-LY, [Asp3]-MC-LR/[Dha7]-MC-LR, MC-HilR) and nodularins (NOD cyclic and linear) within the common blue mussel Mytilus edulis exposed to a combined culture of Microcystis aeruginosa and Nodularia spumigena into the coastal environment. Different distribution profiles of MCs/NODs in the experimental system were observed. The majority of MCs/NODs were present intracellularly which is representative of healthy cyanobacterial cultures, with MC-LR and NOD the most abundant analogues. Higher removal rate was observed for NOD (≈96%) compared to MCs (≈50%) from the water phase. Accumulation of toxins in M. edulis was fast, reaching up to 3.4 μg/g shellfish tissue four days after the end of the 3-days exposure period, with NOD (1.72 μg/g) and MC-LR (0.74 μg/g) as the dominant toxins, followed by MC-LF (0.35 μg/g) and MC-LW (0.31 μg/g). Following the end of the exposure period depuration was incomplete after 27 days (0.49 μg/g of MCs/NODs). MCs/NODs were also present in faecal material and extrapallial fluid after 24 h of exposure with MCs the main contributors to the total cyanotoxin load in faecal material and NOD in the extrapallial fluid. Maximum concentration of MCs/NODs accumulated in a typical portion of mussels (20 mussels, ≈4 g each) was beyond greater the acute, seasonal and lifetime tolerable daily intake. Even after 27 days of depuration, consuming mussels harvested during even short term harmful algae blooms in close proximity to shellfish beds might carry a high health risk, highlighting the need for testing.

1 November 2020 in Harmful Algae
Verified
Journal Article
Closed access
AGAlejandra B. Goya
Alejandra B. Goya
STSophie Tarnovius
Sophie Tarnovius
RHRobert G. Hatfield
Robert G. Hatfield
LCLewis Coates
Lewis Coates
ALAdam Michael Lewis
Adam Michael Lewis
Andrew David TurnerAndrew David Turner
Andrew David Turner

1 January 2022 in Harmful Algae
Verified
Journal Article
Closed access
ALAdam Michael Lewis
Adam Michael Lewis
KDKarl J. Dean
Karl J. Dean
DHDavid M. Hartnell
David M. Hartnell
LPLinda Percy
Linda Percy
Andrew David TurnerAndrew David Turner
Andrew David Turner
JLJane M. Lewis
Jane M. Lewis