Public Health Implications of metals concentrations from prescribed burns: A study adjacent to the Perth Metropolitan Area.

J. Edwards
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Abstract

Ash is not a homogenous product. It is the solid residue of combustion and contains a complex mixture of chemical products. The ash residue resulting from fires varies and is dependent on its source, and burn characteristics such as the temperature of the fire. Ash comprises particles of carbon, soot and trace elements. Ash presents public health risk to people and communities, through direct and indirect ingestion and inhalation. The health effects of ash exposure are not limited to symptoms affecting the eyes, throat and lungs. They can contribute to chronic disease and increase the risk of cancer. The purpose of this study was to evaluate the public health implications of controlled burns in the Darling Escarpment, adjacent to Perth’s metropolitan area in Western Australia. Concentrations of metals in unburnt vegetative litter and ash (post burn), stratified by size fraction, were determined to assess the potential mobilisation of metals caused by prescribed burns and the potential public health implications associated with burns. These data can also be used in predictive modelling to ascertain the amount of metals likely to be released per hectare when authorities plan future burns in the area. Ash samples were collected immediately following the fire to capture fine material before it was blown away. The ash samples were separated into size fractions to investigate whether there are differences within each sub sample. Australia’s National Environmental Protection Measures were used to establish whether the metal concentrations were above designated thresholds for health and environmental investigation, these being the recognised levels above which metals are deemed to pose a risk to public (or environmental) health. Vegetation and ash samples were collected from three sites immediately after the prescribed burn. Samples were analysed for thirteen (13) metals with nine (9) showing statistically significant increases in concentrations in vegetation as compared to ash. The percentages of metals are higher in ash than in vegetative ground litter. The metals identified are Manganese Vegetation (158.3 ± 89.3 mg/kg), Ash (442.2 ± 462.6 mg/kg); Barium Vegetation (19.4 ± 25.3 mg/kg); Ash (41.8 ± 62.7 mg/kg); Zinc Vegetation (15.3 ± 9.7 mg/kg), Ash (25.6 ± 29.7 mg/kg); Vanadium Vegetation (31.0 mg/kg ± 76.3 mg/kg), Ash (32.2 mg/kg ± 51.0 mg/kg); Copper Vegetation (4.2 ± 1.5 mg/kg), Ash (10.9 ± 9.8 mg/kg); Chromium (Total) Vegetation (8.3 ± 15.6 mg/kg), Ash (9.6 ± 12.4 mg/kg); Lead Vegetation (6.1 ± 8.3 mg/kg), Ash (12.2 ± 8.5 mg/kg); Nickel Vegetation (2.2 ± 2.2 mg/kg), Ash (4.7 ± 4.4mg/kg) and Cadmium Vegetation (0.6 ± 0.9 mg/kg), Ash (0.6 ± 0.9 mg/kg). The ash samples were sieved through three aperture’s (2-4 mm, 1-2 mm, <1 mm) to stratify the samples by size fraction and concentrations in all but three of the metals increased as the ash size decreased. It was demonstrated that the level of metal present within the ash samples did not exceed health investigation levels and, with the exception of Manganese, and did not exceed environmental investigations levels. Metals were unlikely to pose a risk if left insitu. However, modelling estimated the volume of metal released and it was determined that metals can pose a subsequent risk if mobilised by wind or water. The likelihood of such mobilisation is high and this finding therefore has public health implications for surrounding communities that are subjected to increases in their exposure to metals, associated with bushfires. The findings from this study contribute to the management of prescribed burns by providing a better understanding of the composition of ash and the effects of potential distribution via aerial deposition or runoff. Data from this study can be used to do predictive modelling of heavy metal mobilisation that may result from burns of similar vegetation environments. This becomes particularly significant where burns are conducted in water catchment areas. Keywords-Smoke, Ash, Prescribed Burn, Heavy metal.
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规定烧伤金属浓度对公共健康的影响:珀斯大都会区附近的一项研究。
灰烬不是一种同质的产品。它是燃烧的固体残留物,含有复杂的化学产物混合物。火灾产生的灰烬残留物各不相同,取决于其来源和燃烧特性,如火灾温度。灰烬包括碳颗粒、烟灰和微量元素。灰烬通过直接和间接摄入和吸入给人们和社区带来公共健康风险。灰烬暴露对健康的影响不仅限于影响眼睛、喉咙和肺部的症状。它们可能导致慢性病,并增加患癌症的风险。本研究的目的是评估达令悬崖受控烧伤对公共健康的影响,达令悬崖毗邻西澳大利亚珀斯大都会区。测定未燃烧的植物垃圾和灰烬(烧伤后)中的金属浓度,按大小分数分层,以评估规定烧伤引起的金属的潜在运动以及与烧伤相关的潜在公共健康影响。这些数据也可用于预测建模,以确定当局计划该地区未来焚烧时每公顷可能释放的金属量。火灾发生后立即收集灰烬样本,以在被吹走之前捕获精细材料。将灰烬样品分为大小部分,以调查每个子样品中是否存在差异。澳大利亚的国家环境保护措施用于确定金属浓度是否高于健康和环境调查的指定阈值,这些阈值是公认的金属对公众(或环境)健康构成风险的水平。在规定的烧伤后立即从三个地点采集植被和灰烬样本。对样本中的十三(13)种金属进行了分析,其中九(9)种显示,与灰烬相比,植被中的浓度在统计上显著增加。灰烬中的金属百分比高于营养地面垃圾中的金属。鉴定的金属为锰植被(158.3±89.3 mg/kg)、灰烬(442.2±462.6 mg/kg);钡植被(19.4±25.3 mg/kg);灰分(41.8±62.7 mg/kg);锌植被(15.3±9.7 mg/kg),灰分(25.6±29.7 mg/kg);钒植被(31.0 mg/kg±76.3 mg/kg)、灰分(32.2 mg/kg±51.0 mg/kg);铜植被(4.2±1.5 mg/kg),灰烬(10.9±9.8 mg/kg);铬(总)植被(8.3±15.6 mg/kg)、灰分(9.6±12.4 mg/kg);铅植被(6.1±8.3 mg/kg),灰烬(12.2±8.5 mg/kg);镍植被(2.2±2.2 mg/kg)、灰分(4.7±4.4 mg/kg)和镉植被(0.6±0.9 mg/kg)、灰烬(0.6±0.9mg/kg)。通过三个孔径(2-4 mm、1-2 mm、<1 mm)对灰分样品进行筛分,以按粒度分数和除三种金属外的所有金属的浓度对样品进行分层。经证明,灰烬样本中的金属含量未超过健康调查水平,除锰外,也未超过环境调查水平。如果留在原地,金属不太可能构成风险。然而,建模估计了金属的释放量,并确定金属如果被风或水调动,可能会带来后续风险。这种动员的可能性很高,因此这一发现对周围社区的公共卫生有影响,这些社区暴露于与森林大火有关的金属的风险增加。这项研究的发现通过更好地了解灰烬的成分以及通过空气沉积或径流的潜在分布的影响,有助于管理规定的烧伤。这项研究的数据可用于对类似植被环境的烧伤可能导致的重金属迁移进行预测建模。在集水区进行焚烧的情况下,这一点尤为重要。关键词烟雾,灰烬,规定烧伤,重金属。
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