Magnetic trees and human health. In recent years, much awareness has been raised about the long-term negative health

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‘Magnetic trees’ and human health

In recent years, much awareness has been raised about the long-term negative health impacts of air pollution, with significant associations identified between air pollution levels and mortality (Elliot et al., 2008). Whilst these pollution/illness links are strongest for respiratory illness, air pollution is also a possible contributing factor to development of cardiovascular illness, cancer and even Alzheimer’s disease (e.g. Calderon-Garciduenas et al., 2004; Morris et al., 1995). These links with adverse health effects have resulted in the introduction of ‘Air Quality Standards’ in many countries, with legal limits for the most significant and/or harmful pollution components.

Particulate matter below 10 µm in diameter (PM10), especially particles

below 0.1 µm (PM0.1), is considered to be

the most harmful air pollution component (Donaldson, 2003). It can be breathed deep into the respiratory system (figure 1), and there is no known minimum level at which adverse health effects do not occur (Bealey et al., 2007).

For example, living in an area with PM10

levels as low as 10 μg/m3 (i.e. less than

half the current European legal air quality standard) has been associated with an 8 % increase in the risk of lung cancer mortality (Elliot et al., 2007).

Figure 1: International organization for

standardization (ISO) respirable conventions (ISO IS 7708, 1995)

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Anthropogenic (man-made) PM10, containing potentially toxic metals such as

lead, zinc and iron (Al-Alawi et al., 2007), is produced in large quantities by fuel combustion in vehicle engines (Maricq et al., 1999) and in industrial processes. In Europe, with the introduction of legally binding emission reduction commitments, industrially-sourced PM10 is declining. However, vehicle use, especially short-journey

vehicle use (< 8 km), is increasing internationally (DfT 2007), thereby increasing human exposure to PM10.

High spatial resolution measurement of air pollution is thus becoming increasingly important - but is currently not always achieved. For example, if you live outside a big city like London, the likelihood is that the air quality of your whole town is measured by just one or two fixed monitoring stations. Additionally, to reduce the risk of vandalism, the inlets for many of these monitoring stations are situated at heights in excess of 3 metres. Recent research shows that traffic-derived PM10 is greatest at

approximately 0.3 metres (toddler head height), with values 50 % lower at 1.5 metres (adult head height). Thus, conventional fixed monitoring stations sampling at 3 metres are unlikely to provide representative data for human exposure (e.g. Maher et al., 2008; Matzka and Maher, 1999; Mitchell and Maher, subm). This problem of sparse and

possibly unrepresentative pollution measurement might be overcome by making use of ‘magnetic’ roadside trees.

Magnetic biomonitoring involves application of laboratory-generated magnetic fields to pollutant particles (PM10) collected passively by plants, including,

critically, by roadside tree leaves (figure 2). Close to the roadside, the magnetic properties of tree leaves change markedly, because the leaves act as pollution collectors and many of the pollutant particles they catch are strongly magnetic. When different

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Figure 3: Correlation between leaf

magnetic and co-located ambient PM10

values (R2 = 0.72, σ = 0.01, n = 22)

Figure 2: Sampling/ measurement procedure for magnetic biomonitoring; Leaves ‘catch’ pollutant particles

(as shown in the scanning electron microscopy (SEM) image). The roadside leaves are sampled and taken to the laboratory. Magnetic fields are applied and remanence values measured, giving detailed information regarding the leaf-surface pollutant particles.

magnetic fields are applied to leaf samples and their resultant magnetic remanences measured, information can rapidly be gained regarding the concentration, particle size and mineralogy of the leaf-collected pollution particles.

The leaf magnetic remanence values have been found to be strongly correlated with ambient particle concentrations, a finding independently tested by measurement of co-located pumped air samplers (figure 3). Thus, roadside leaf magnetic values can be used to calculate ambient PM10 levels at any tree location

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capability is critical in the context of health implications, given the serious adverse health effects associated with PM10 as outlined above and the current spatial scarcity of PM10

data.

Figure 4: SEM image of particulate matter deposited on a leaf sampled from a roadside tree in

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Magnetic remanence measurements on roadside lime tree (T. platyphyllos) leaves

located around Lancaster, UK, for example, corroborate the observed strong trend of increasing leaf magnetic remanence and PM10 values with increasing proximity to

heavily-trafficked roads. Analysis of mineralogy-specific magnetic parameters identifies that the dominant magnetic mineral present in the ambient particulate pollution is magnetite. Comparing the leaf magnetic properties with those of magnetites of known grain size, the dominant size of the leaf magnetite particles is between ~0.1 - 1 μm (Maher, 1988). This is in agreement with the particle sizes observed upon visual examination of the leaf and air filter samples with a scanning electron microscope (SEM), as in figure 4. This size fraction lies within the ‘high-risk respirable’ convention (figure 1); i.e. particles that can penetrate to the unciliated regions of the lung with potential significance in development of deep lung diseases such as pneumoconiosis (Colls, 2002).

The fine (<1 μm) pollution particles mainly comprise iron-rich ‘spherules’ (previously melted droplets) associated with fuel combustion. The larger particles are more angular and rich in aluminium and silica, consistent with particles from natural sources (e.g. from soil).

Lead, a significant neurotoxin even at low levels of exposure (Needleman and Landrigan, 2004), is strongly associated with the sub-micrometre, traffic-derived PM10

(Maher et al., 2008). Potential adverse health effects of lead exposure include liver and kidney damage, hearing impairment and retardation of cognitive development in children (e.g. Koller et al., 2004, Lanphear et al., 2000). Thus, biomagnetic monitoring can have a critical role in identifying and mapping areas with elevated traffic-derived PM10 levels,

crucial for targeting mitigation measures for exposure reduction. Further, magnetic biomonitoring can be used to combine not just monitoring of pollution but actual

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reduction of pollution exposure; trees can ‘filter’ out PM10 by up to ~ 20 % (e.g. Bealey

et al., 2007; Mitchell and Maher, subm). Targeted planting, and maintenance of low level

foliage, at locations with high PM10 levels can therefore provide significant protection

against exposure to PM10 at those areas shown by magnetic biomonitoring to be the worst

affected.

In addition to addressing traffic-derived pollution, magnetic biomonitoring can also be used for high-resolution monitoring of point source pollution, e.g. from an industry

chimney stack. As previously mentioned, traffic-sourced PM10 peaks at approximately

0.3 metres, and decreases with increased height from the ground. Thus, point source pollution (which tends to be more pervasive over a larger area) may be distinguished from more localised traffic-derived pollution by sampling leaves from above 1.5 metres height, and at distances exceeding tens of metres from the road.

Cheap and rapid high-resolution leaf magnetic sampling can be undertaken over a large area around the point source, and the results interpolated (values calculated using multiple nearby data points) to enable a PM10 value to be estimated for any location

within the study area (figure 5). These data can then be used to assist in identifying point pollution sources and the spatial distribution and loadings of their pollution ‘plumes’. Such information is required so that pollution reduction strategies and costs can be implemented and attributed. The biomagnetic data can also be used to assess the accuracy of the current generation of pollution plume models.

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Figure 5: Interpolated leaf calculated PM10levels around a point source in Oxfordshire, UK

(18/08/08) indicating proximal fixed monitoring stations (AURN sites), tree sample sites and point source (X) (Mitchell and Maher, in prep.).

X

Different tree species have different efficiencies for collection of PM10; leaves with

ridges or hairy surfaces have a greater ability to remove PM10 from the air than those with

shiny or waxy surfaces. Thus inter-species ‘calibration’ of magnetic and PM10 levels has

also been established (Mitchell and Maher, in prep) enabling maximum spatial coverage.

In conclusion, biomagnetic monitoring is a cheap, fast and robust method for collection of particulate pollution data at unprecedentedly high spatial resolution. Leaf magnetic remanence values can be used to: estimate PM10 levels; assess the dominant

particle size fractions; identify key ‘target’ areas for pollution reduction; and monitor the ‘filtering’ effect of roadside vegetation screening. Thus, ‘magnetic trees’ can be a key tool for decreasing urban pollution and enhancing human health.

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References:

Al-Alawi, M. T. M., Batarseh, M. I., Carreras, H., Alawi, M., Jiries, A. & Charlesworth, S. M., 2007. Aleppo Pine Bark as a Biomonitor of Atmospheric Pollution in the Arid Environment of Jordan. CLEAN - Soil, Air, Water.

Bealey, W. J., Mcdonald, A. G., Nemitz, E., Donovan, R., Dragosits, U., Duffy, T. R. & Fowler, D., 2007. Estimating the reduction of urban PM10 concentrations by trees

within an environmental information system for planners. Journal of Environmental Management, 85, 44-58.

Calderon-Garciduenas, L., Reed, W., Maronpot, R. R., Henriquez-Roldan, C., Delago-Chavez, R., Calderon-Garciduenas, A., Dragustinovis, I., Franco-Lira, M., Aragon-Flores, M., Solt, A. C., Altenburg, M., Torres-Jardon, R. & Swenburg, J. A., 2004. Brain Inflammation and Alzheimer's-Like Pathology in Individuals Exposed to Severe Air Pollution. Toxicologic Pathology, 32, 650-658.

Colls, J., 2002. Air pollution 2nd edition, London: SPON Press, 401.

Department for Transport, 2008. GB National Road Traffic Survey, AADF data accessed

Donaldson, K., 2003. The biological effects of coarse and fine particulate matter. Occupational and Environmental Medicine, 60, 313 - 314.

Elliott, P., Shaddick, G., Wakefield, J. C., De Hoogh, C., Briggs, D. J., 2007. Long-term associations of outdoor air pollution with mortality in Great Britain. Thorax, 62, 1088-1094.

Flanders, P. J., 1994. Collection, measurement, and analysis of airborne particulates from pollution in the environment. Journal of Applied Physics, 75, 5931-5936.

Koller, K., Brown, T., Spurgeon, A., Levy, L., 2004. Recent developments in low – level lead exposure and intellectual impairment in children. Environmental Health Perspectives, 112, 987 - 994.

Lanphear, B. P., Dietrich, K., Auinger, P., Cox, C., 2000. Deficits in cognitive and academic skills associated with lead exposure occurring at blood concentrations lower than 5 μg/dL. Public health report, 115, 530 – 531.

Maricq, M. M., Podsiadlik, D. H. & Chase, R. E., 1999. Gasoline Vehicle Particle Size Distributions: Comparison of Steady State, FTP, and US06 Measurements. Maher, B., 1988. Magnetic properties of some synthetic sub-micron magnetites.

Geophysical Journal, 94, 83-96.

Maher, B. A., Moore, C. & Matzka, J., 2008. Spatial variation in vehicle-derived metal pollution identified by magnetic and elemental analysis of roadside tree leaves. Atmospheric environment.

Matzka, J. & Maher, B. A., 1999. Magnetic biomonitoring of roadside tree leaves: identification of spatial and temporal variations in vehicle-derived particulates. Atmospheric Environment, 33, 4565-4569.

Mitchell, R. & Maher, B. A., (in review), Evaluation and application of biomagnetic monitoring of traffic-derived particulate pollution (Lancaster, U.K.). Atmospheric Environment.

Morris, W. A., Versteeg, J. K., Bryant, D. W., Legzdins, A. E., Mccarry, B. E. & Marvin, C. H., 1995. Preliminary comparisons between mutagenicity and magnetic susceptibility of respirable airborne particulate. Atmospheric Environment, 29,

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