SEGH Articles

# Michael Watts elected SEGH President

10 October 2017
Dr Michael Watts was recently elected SEGH President, following a handover from Dr Chaosheng Zhang. Michael has been involved in the SEGH for nearly 15 years as a member of the European board and active on the International board via his role in redesigning the website since 2010.

Dr Michael Watts was recently elected SEGH President, following a handover from Dr Chaosheng Zhang. Michael has been involved in the SEGH for nearly 15 years as a member of the European board and active on the International board via his role in redesigning the website since 2010.

Dr Michael Watts is the Head of Inorganic Geochemistry at the British Geological Survey. He has a team of geochemists and analytical chemists, supporting a suite of geochemistry laboratories and leading on environmental geochemistry projects in the UK and overseas, particularly in Africa. These projects involve investigations that span pollutant pathways from source through to human biomonitoring and ecological hazard assessment; micronutrient pathways from soil-crop-diet-health, with both aspects seeking better knowledge of geochemical controls on mobility/biovailability of micronutrients and potentially harmful elements through to measures of health status. Activities often link with industry, overseas governments, regulatory bodies or academia, in particular through a joint Centre for Environmental Geochemistry with the University of Nottingham.

We take the opportunity to ask a few questions of Michael to gain an insight into his experience as an environmental scientist, member of SEGH and his hopes for the future of SEGH.

What are your hopes for the future of SEGH and how do you intend to lead the SEGH forward as the new President?

Firstly, I would like to thank Dr Chaosheng Zhang for his steering of SEGH through a period of significant change, including revision and acceptance by the international board for the revised constitution and strategy to make SEGH ‘fit for purpose’ for the future.

SEGH faces many challenges, namely competition from numerous societies, financial constraints for members, maintaining representation for members equitably across each region and financial pressures to remain relevant e.g. maintaining web interaction, communications and relevancy to PhD students and early career scientists. Young scientists will be increasingly discerning in choosing which societies to become involved in and spend their money on subscriptions. The SEGH board will need to constantly question what the member is gaining.  This will need to include better communication with members, whether through web interaction, web articles or the like, which has been particularly poor in recent years. This could become part of the terms of reference that board members sign up to and agree to actively participate and drive SEGH forward, seek out new opportunities, gauge the current themes relevant to SEGH and encourage young scientists to join SEGH. Some ideas under discussion have included a form of fellowship for the mentoring of members, which should form part of a wider consultation with the membership.

SEGH is at the cusp of consolidating on its reach across the regions, with good knowledge of web traffic driving emphasis on developing and renewing sections.  For example, a section for Africa will be developed in the next year leading up to the conference in Victoria Falls in July 2018. Whilst web traffic has increased significantly in Africa, this has also been the case in the Indian sub-continent which needs further attention for the Asia/Pacific section.  Interaction via the web and membership numbers has fallen away in Southern America, which will need to be addressed by the Americas regional section.  European membership and web traffic has remained strong and diversified in recent years. We will still need to maintain our efforts in this area, particularly eastern and southern Europe which has experienced financial instability in recent years.  Innovative ideas will be required, whether this is via web communications, hosting of small local symposia or online groups, with an emphasis on keeping costs down to ensure affordability for members. SEGH has been successful in running conferences each year that bring together early, mid and late career scientists to share their research and experience.  SEGH has been very good at fostering new talent, but how could we do this better with an increasingly interconnected world?  Should we be considering other platforms to supplement and reinforce the traditional conference schedule? This is a point where we need to engage with members for fresh ideas.

What do you think are the major scientific issues facing the society’s areas of research and could SEGH take a lead role in these?

The major theme for SEGH is still the interdisciplinary nature of the society in linking through from environmental studies to the health of humans, animals, wildlife and wider ecological contexts. There has been patchy success over the years and perhaps SEGH will continue to struggle to link directly with medical practitioners. However, there are examples of inter-disciplinary research linked through epidemiologists, public/animal health professionals and regulatory bodies. Further efforts are required to draw in members from these areas, but also improve the relevancy of research by drawing in socio-economic skills to better demonstrate pathways to impact to justify research expenditure. SEGH has a unique platform to link such disciplines. SEGH also has the potential to facilitate members in working through Official Development Assistance programmes targeting the United Nations Strategic Development Goals (SDG), of which there are 17(http://www.segh.net/articles/geology_for_global_development_gfgd/ ), the majority of which SEGH members research most likely overlaps. Enormous sums of money are being spent to target the SDG’s, SEGH has a potential role to play in ensuring funds are spent wisely, researchers are connected for funding proposals for sustainable development opportunities.  We have seen a little more diversity of the use of technologies in research particularly at Brussels 2015, such as biomarker research. A future challenge will be for the transfer of technologies ‘fit for purpose’ for researchers in Lower Middle income Countries (LMIC) who often only lack technical capacity to engage equally in international research programmes, rather than samples disappearing to the so-called developed world for data outputs.

During your scientific career, how was your membership of SEGH benefited you personally? What do you are the advantages of early – mid – late career scientists joining SEGH?

I joined SEGH in 2002/03 and attended my first conference in Glasgow where I was buttonholed at the bar to see if I would be interested in joining the SEGH board as ‘new blood’. Both as a member attending meetings and as a board member I have made like-minded friends, many of whom in the early days provided some form of mentorship, linking me with appropriate researchers who were also trying to work in the gap between environment and health sciences. Some of these links progressed through to funded projects and publications, helping me to get my research career kick-started. Certainly having independent and outside research links via SEGH has helped my career at BGS, but has also enriched my understanding of inter-disciplinary research. I think this continues to be the case for mid and late career scientists, with SEGH providing a friendly environment to reinforce relationships and develop new links as scientific research questions and priorities evolve. I am probably in the mid-career phase and seeing students present research is also very rewarding, students and early career scientists are generally where the cutting edge research is taking place as they have the time to focus before other responsibilities start to soak up time. As already mentioned, as long as I have been involved, SEGH has placed emphasis on giving young and new scientists an opportunity to present their research. This is not always the case at other meetings and is an aspect of SEGH we should strive to protect.

By Dr Daniel Middleton

SEGH webmaster

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## Science in theNews

Latest on-line papers from the SEGH journal: Environmental Geochemistry and Health

• Distribution of metal(loid)s in particle size fraction in urban soil and street dust: influence of population density 2020-01-18

### Abstract

Assessment of street dust is an invaluable approach for monitoring atmospheric pollution. Little information is available on the size distribution of contaminants in street dusts and urban soils, and it is not known how the population density would influence them. This research was carried out to assess the size distribution of trace metal(loid)s in street dust and urban soil, and to understand how population density might influence the size-resolved concentration of metal(loid)s. Three urban areas with a high, medium and low population density and a natural area were selected and urban soil and street dust sampled. They were fractionated into 8 size fractions: 2000–850, 850–180, 180–106, 106–50, 50–20, 20–10, 10–2, and < 2 µm. The concentration of Pb, Zn, Cu, Cd, Cr, Ni, As, and Fe was determined, and enrichment factor and grain size fraction loadings were computed. The results indicated that the concentration of Pb, Zn, Cu, Cd, and Cr was highly size dependent, particularly for particles < 100 µm, especially for street dust. Low concentrations of Ni and As in street dust and urban soil were size and population density independent. Higher size dependency of the metals concentration and the higher degree of elemental enrichment in the street dust fractions than the urban soils indicate higher contribution of human-induced pollution to the dust. Findings also confirm the inevitability of size fractionation when soils or dusts are environmentally assessed, particularly in moderately to highly polluted areas. Otherwise, higher concentrations of certain pollutants in fine-sized particles might be overlooked leading to inappropriate decisions for environmental remediation.

• Soil–plant system and potential human health risk of Chinese cabbage and oregano growing in soils from Mn- and Fe-abandoned mines: microcosm assay 2020-01-17

### Abstract

In Portugal, many abandoned mines are often close to agricultural areas and might be used for plant food cultivation. Soils in the vicinity of two Mn- and Fe-abandoned mines (Ferragudo and Rosalgar, SW of Portugal) were collected to cultivate two different food species (Brassica rapa subsp. pekinensis (Lour.) Hanelt and Origanum vulgare L.). Chemical characterization of the soil–plant system and potential risk of adverse effects for human health posed by plants associated with soil contamination, based on the estimation of hazard quotient (HQ), were assessed in a microcosm assay under greenhouse conditions. In both soils, the average total concentrations of Fe and Mn were above the normal values for soils in the region and their concentration in shoots of both species was very high. Brassica rapa subsp. pekinensis grew better in Ferragudo than in Rosalgar soils, and it behaved as an excluder of Cu, Mn, Fe, S and Zn in both soils. The HQ for Cu, Fe, Mn and Zn in the studied species grown on both soils was lower than unit indicating that its consumption is safe. The high Mn tolerance found in both species might be due in part to the high contents of Fe in the soil available fraction that might contribute to an antagonism effect in the uptake and translocation of Mn. The obtained results emphasize the need of further studies with different food crops before cultivation in the studied soils to assess health risks associated with high metal intake.

• Concentration, fractionation, and ecological risk assessment of heavy metals and phosphorus in surface sediments from lakes in N. Greece 2020-01-13

### Abstract

The presence of phosphorus (P) and heavy metals (HMs) in surface sediments originating from lakes Volvi, Kerkini, and Doirani (N. Greece), as well as their fractionation patterns, were investigated. No statistically significant differences in total P content were observed among the studied lakes, but notable differences were observed among sampling periods. HM contents in all lakes presented a consistent trend, i.e., Mn > Cr > Zn > Pb > Ni > Cu > Cd, while the highest concentrations were recorded in Lake Kerkini. Most of the HMs exceeded probable effect level value indicating a probable biological effect, while Ni in many cases even exceeded threshold effects level, suggesting severe toxic effects. P was dominantly bound to metal oxides, while a significant shift toward the labile fractions was observed during the spring period. The sum of potentially bioavailable HM fractions followed a downward trend of Mn > Cr > Pb > Zn > Cu > Ni > Cd for most lakes. The geoaccumulation index Igeo values of Cr, Cu, Mn, Ni, and Zn in all lakes characterized the sediments as “unpolluted,” while many sediments in lakes Volvi and Kerkini were characterized as “moderately to heavily polluted” with regard to Cd. The descending order of potential ecological risk $$E_{\text{r}}^{i}$$ was Cd > Pb > Cu > Ni > Cr > Zn > Mn for all the studied lakes. Ni and Cr presented the highest toxic risk index values in all lake sediments. Finally, the role of mineralogical divergences among lake sediments on the contamination degree was signified.