Spatial distribution and composition of mine dispersed trace metals in residential soil and house dust: Implications for exposure assessment and human health.

Trace metal exposure from environmental sources remains a persistent global problem, particularly in communities residing adjacent to metal extraction and processing industries. This study examines front yard soil and house dust from 62 residences throughout the Australian Ag-Pb-Zn mining city of Broken Hill to better understand spatial variability in metal distributions, compositions and exposures across an industrially polluted urban environment. X-ray fluorescence analysis of paired soil/dust samples indicated that geomean concentrations (mg/kg) of Cu (32/113), Zn (996/1852), As (24/34) and Pb (408/587) were higher in house dust while Ti (4239/3660) and Mn (1895/1101) were higher in outdoor soil. Ore associated metals and metalloids (Mn, Zn, As, Pb) in soil and house dust were positively correlated and declined in concentration away from mining areas, the primary source of metalliferous emissions in Broken Hill. The rate of decline was not equivalent between soil and house dust, with the indoor/outdoor concentration ratio increasing with distance from mining areas for Zn/Pb (geomean = 1.25/1.05 (<1 km); 2.14/1.52 (1-2 km); 2.54/2.04 (>2 km)). House dust and Broken Hill ore Pb isotopic compositions (206Pb/207Pb; 208Pb/207Pb) were more similar in homes nearest to mining areas than those further away (geomean apportioned ore Pb = 88% (<1 km); 76% (1-2 km); 66% (>2 km)), reflecting spatial shifts in the balance of sources contributing to indoor contamination. Incorporation of house dust Pb reduced overestimation of IEUBK modelled blood Pb concentrations compared to when only soil Pb was used. These findings demonstrate that even in contexts where the source and environmental burden of metals are relatively apparent, geochemical relationships and exposures between outdoor and indoor environments are not always predictable, nor easily disaggregated.

Environmental impacts of abrasive blasting of transmission towers in protected areas.

In Australia, and other parts of the world, tower infrastructure in electricity transmission networks are nearing the end of their asset life. In changing economic, political and regulatory environments Transmission Network Service Providers are implementing new approaches to asset management and reinvestment, such as refurbishment to extend the life of existing assets, instead of replacement. As part of these refurbishment efforts, abrasive blasting and recoating is being employed to remove corrosion and extend the life of steel electricity transmission towers. New controls and procedures have been developed to manage the most likely impacts associated with the abrasive blasting of transmission towers. However, little or no data have been available on the environmental impacts of abrasive blasting or the effectiveness of management procedures currently being used to mitigate potential adverse environmental impacts.We conducted an integrated study on the impacts of abrasive blasting, which brought together on-site research; modelling; and controlled laboratory trials. The study was undertaken during a transmission tower refurbishment project within the World Heritage listed Wet Tropics Region in Queensland, Australia. Measured metal deposition around towers due to blasting, was primarily as large particles (>PM10) at 12-30 m from the tower. Soil concentrations of metals were highest under towers, with a small number of samples showing elevated zinc at 12-30 m. The presence of spent abrasive media and dust on the geofabric material used under the towers and up to 15 m from the tower base, as part of control measures used to contain the abrasive products, indicates that deposition also occurs between 0 and 12 m from the tower.The potential impacts of the abrasive blasting technique on plants and invertebrates appear to be low. Five species of tropical rainforest tree seedlings exposed to abrasive blasting dust at worst-case levels had no negative impact on physiological performance or plant health. This research will assist Transmission Network Service Providers and other operators of corroded linear infrastructure to plan and implement mitigating management actions and procedures during abrasive blasting projects and assist regulators and the community to better understand the impacts of the practice.

Airborne ultrafine particles in a Pacific Island country: Characteristics, sources and implications for human exposure.

The Pacific Islands carry a perception of having clean air, yet emissions from transport and burning activities are of concern in regard to air quality and health. Ultrafine particle number concentrations (PNCs), one of the best metrics to demonstrate combustion emissions, have not been measured either in Suva or elsewhere in the Islands. This work provides insight into PNC variation across Suva and its relationship with particle mass (PM) concentration and composition. Measurements over a short monitoring campaign provide a vignette of conditions in Suva. Ambient PNCs were monitored for 8 day at a fixed location, and mobile PNC sampling for two days. These were compared with PM concentration (TSP, PM10, PM2.5, PM1) and are discussed in relation to black carbon (BC) content and PM2.5 sources, determined from elemental concentrations; for the October 2015 period and longer-term data. Whilst Suva City PM levels remained fairly low, PM2.5 = 10-12 µg m-3, mean PNC (1.64 ± 0.02 × 104 cm-3) was high compared to global data. PNCs were greater during mobile sampling, with means of 10.3 ± 1.4 × 104 cm-3 and 3.51 ± 0.07 × 104 cm-3 when travelling by bus and taxi, respectively. Emissions from road vehicles, shipping, diesel and open burning were identified as PM sources for the October 2015 period. Transport related ultrafine particle emissions had a significant impact on microscale ambient concentrations, with PNCs near roads being 1.5 to 2 times higher than nearby outdoor locations and peak PNCs occurring during peak traffic times. Further data, particularly on transport and wet-season exposures, are required to confirm results. Understanding PNC in Suva will assist in formulating effective air emissions control strategies, potentially reducing population exposure across the Islands and in developing countries with similar emission characteristics. Suva's PNC was high in comparison to global data; high exposures were related to transport and combustion emissions, which were also identified as significant PM2.5 sources.

Visualisation and quantification of heavy metal accessibility in smelter slags: The influence of morphology on availability.

The Imperial Smelting Furnace (ISF) for producing lead and zinc simultaneously has operated on four continents and in eleven countries from the 1950's. One of the process changes that the ISF introduced was the production of a finely granulated slag waste. Although this slag contained significant amounts of residual lead (Pb) and zinc (Zn), because of its glassy nature it was considered environmentally benign. From the Cockle Creek smelter near Boolaroo at the northern end of Lake Macquarie, NSW, Australia, it is estimated that around 2.1 million tonnes of the fine slag was distributed into the community and most remains where it was originally utilised. Residual tonnages of slag of this magnitude are common worldwide wherever the ISF operated. Studies of base metal smelting slags have concluded that mineralogical and morphological characteristics of the slag play a critical role in moderating environmental release of toxic elements. Scanning electron microscopy (SEM) and microanalysis of the ISF slags has shown that the Pb and associated elements are present as discrete nodules (∼6-22 µm) in the slag and that they are not associated with Zn which is contained in the glass slag phase. Using an automated SEM and analysis technique (QEMSCAN(®)) to "map" the mineralogical structure of the particles, it was possible to quantitatively determine the degree of access infiltrating fluids might have to the reaction surface of the Pb phases. The level of access decreases with increasing particle size, but in even the largest sized particles (-3350 + 2000 µm) nearly 80% of the Pb-containing phases were totally or partially accessible. These results provide evidence that the toxic elements in the slags are not contained by the glassy phase and will be vulnerable to leaching over time depending on their individual phase reactivity.

Preliminary findings of chemistry and bioaccessibility in base metal smelter slags.

Leaching of toxic metals from slag waste produced during smelting of Pb-Zn ores is generally considered to be negligible. A 1.4 million tonne stockpile of slag containing up to 2.5% Pb and other contaminants has accumulated on a smelter site at North Lake Macquarie, New South Wales, Australia, and it has also been freely used within the community for landscaping and drainage projects. It had been suggested that Pb in fine particles derived from the slags may be a potential contributor to the blood Pb of some children in this community, although there is conflicting evidence in the literature for such a hypothesis. Bioaccessibility of lead and selected metals derived from nine slag samples collected from areas of public open space was examined using a relatively simple in vitro gastric dissolution technique. Size analyses of the slag samples demonstrate that finely-sized material was present in the slags which could be ingested, especially by children. The finer-sized particles contain high levels of Pb (6,490-41,400 ppm), along with Cd and As. Pb bioaccessibility of the slags was high, averaging 45% for -250 microm material and 75% for particles in the size range -53+32 microm. Increasing bioaccessibility and Pb concentration showed an inverse relationship to particle size. Almost 100% of Pb would be bioaccessible in the smallest slag particles (<20 microm), which also contained very high Pb levels ranging from 50,000 to 80,000 ppm and thus constitute a potential health hazard for children.

An assessment of the effectiveness of lead pollution reduction strategies in North Lake Macquarie, NSW, Australia.

The North Lake Macquarie area of NSW, Australia, principally the suburbs of Boolaroo, Argenton and Speers Point, has been significantly polluted by lead emissions emanating from the Pasminco Metals Smelter (Cockle Creek). A lead accessibility reduction program has been carried out in North Lake Macquarie since 1991. The primary measure of success for the program is reduced blood lead levels, particularly in children. From 1991 to 2000 average child blood lead levels have decreased from 11 to 7.5 microg/dl. However, the lead accessibility reduction programs had failed to eliminate child blood lead levels that exceed the National Health and Medical Research Council maximum goal of 10 microg/dl, and a number of children still retain blood lead levels >25 microg/dl. Many factors have contributed to this failure, notably the continued presence of airborne high lead pollutants in ambient air, dusts and soil in residential areas. Significant reductions in lead mass emissions from 92 tonnes per annum (p.a.) in 1988 to approximately 15 tonnes p.a. to September 2000 have been achieved by the smelter operator. However, the reductions have been insufficient to ensure that ambient air quality consent conditions of 1 microg/m(3) are achieved in the residential areas surrounding the smelter. Sampling by the smelter operator also provides confirmation of continued deposition of high lead dusts in residential areas. The continued dust deposition places a high burden on the local community which must maintain obsessive levels of household cleanliness in order to minimise lead uptake from dusts deposited within the home and community. Evidence exists of institutional failure that may also have limited the success of the program. These failures include the use of inappropriate standards and non-approved techniques in remediation, lack of coordination between various arms of government and an unwillingness to enforce consent conditions. The smelter operator has also failed to proactively seek changes which would minimise community harm. It is suggested that for child blood lead levels to be further reduced it may be necessary to impose added restrictions on smelter emissions. Firstly, however, current emission requirements should be mandated and methodologies for remediation of historical lead depositions should also follow accepted standards and practices to maximise the benefits of the work to the affected community.