Stable lead isotope profiles in smelter and general urban communities: a comparison of environmental and blood measures

High-precision lead isotope ratios and lead concentrations have been compared statistically and graphically in women of child-bearing age (n = 77) from two smelter communities and one general urban community to evaluate the relative contributions to blood lead of tissue lead stores and lead from the contemporaneous environment (soil, floor dust, indoor airborne dust, water, food). Blood lead (PbB) contents were generally low (e.g. <10 g dL^–1). Statistically significant isotopic differences in blood and environmental samples were observed between the three cities although isotopic differences in blood for individual subjects living in close proximity (200 m radius) was as large as the differences within a city. No single environmental measure dominated the biological isotope profile and in many cases the low levels of blood lead meant that their isotopic profiles could be easily perturbed by relatively small changes of environmental exposure. Apportioning of sources using lead isotopes is possibly not feasible, nor cost effective, when blood lead levels are <5 g dL^–1. Interpretations based on statistical analyses of city-wide data do not give the same conclusions as when the houses are considered individually. Aggregating data from multiple subjects in a study such as this obscures potentially useful information. Most of the measures employed in this study, and many other similar studies, are markers of only short-to-medium integration of lead exposure. Serial sampling of blood and longer sampling times, especially for household variables, should provide more meaningful information.     

Lead pollution in soils adjacent to homes in Tampa,Florida

In the United States, the study of lead pollution in soil has focused on older cities throughout the industrialised northern tier of states often referred to as the rust belt. Researchers have not studied the magnitude and extent of contamination in the newly developed portions of the sunbelt region of the south. In order to assess the significance of lead pollution in soils in these areas, an analysis of the lead content in 146 soil samples collected at a one km grid throughout residential portions of Tampa, Florida was undertaken. The results reveal that lead contaminated (>500 g g^–1) soil is present in the older portions of the city and near expressways. A comparison of the results with data collected in an older, northern city demonstrates that the magnitude and extent of the contamination in Tampa are less than found in the larger rust belt city. However, the presence of hazardous levels of lead in soil collected in Tampa is evidence that sunbelt cities must address lead pollution in the urban environment.     

The use of Monte Carlo simulation techniques to predict population blood lead levels

Effective management of the risks posed by lead depends on an understanding of the relationship between exposure (the presence and accessibility of lead in the environment) and dose (blood lead levels). Our paper begins by outlining the type of information most valuable to a decision maker addressing the lead problem. A useful exposure-dose characterisation must address multiple contamination sources simultaneously, provide estimates of the number of people with blood lead levels exceeding critical thresholds, and assess the influence of modifying factors (e.g. the soil and dust ingestion rate) on population blood lead variability. We describe a pilot effort to develop an urban setting lead exposure-dose model, and use this model to compare three approaches for generating model input quantities: (1) worst-case estimates, (2) central estimates and (3) Monte Carlo simulation. Using the criteria outlined above, we find that the Monte Carlo technique provides the most useful model output. We describe the population blood lead level distribution generated by the model, as well as the relative influence of environmental and behavioural factors on the variability of the population distribution. Finally, we assess the impact of parameter uncertainty on the model output, and contend this type of information can help identify areas in which further empirical study would be most valuable.     

Current uses of the EPA lead model to assess health risk and action levels for soil

The EPA lead model predicts mean blood lead levels and risk of elevated blood lead levels in children based on lead uptake from multiple sources. In the latest model versions, environmental data from individual homes within a community can be used to predict the overall blood lead distribution and percent risk of exceeding a specific blood lead level (i.e. 10 g dl^–1). Recent criteria used by the EPA to evaluate this information include no more than 5% of houses with a greater than 5% lead risk, and a community weighted-average risk below 5%. Environmental (primarily soil) and blood lead data from a residential community near a smelter were used to illustrate recent uses of the model. Scheduled remediation in the community will remove soil for approximately 60% of the houses (i.e. those with lead levels > 1000 mg kg^–1). After remediation, the model results indicate a relatively low community risk (0.5–1.9%), although the percentage of houses with lead risks above 5% ranged from 3 to as high as 13%, depending on the variation in blood lead and assuming the model's 7 g dl^–1 increase in blood lead with each 1000 mg kg^–1 increase in soil lead level. A comparison of the limited blood lead data with soil lead levels below 1000 mg kg^–1, however, indicated no apparent relationship. Given these uncertainties, less invasive actions than additional soil removal (e.g. exposure intervention, monitoring conditions, and follow-up as necessary) may be appropriate under the new EPA guidance for lead in soil.     

Identification and apportionment of sources of lead in human tissue

A brief review of the use of stable lead isotope ratio measurements to identify and apportion sources of lead in human tissue is followed by examples of the use of inductively coupled plasma source mass spectrometry for such studies. Inductively coupled plasma source mass spectrometry (ICP-MS) has only recently been used for measurements of coupled ratios in body tissues and fluids and in environmental sources of lead. Generally, the inaccuracy of these measurements is about −0.2% and the imprecision less than 0.5%. This analytical performance is sufficient to detect the much larger changes in²⁰⁶Pb:²⁰⁷Pb ratios of −2% or higher, seen in environmental lead exposure and in childhood lead poisoning. Measurements of lead isotope ratios by ICP-MS have been used to identify specific sources of childhood lead poisoning and to indicate the relative importance of environmental sources, such as drinking water and lead from petrol. Populations in the United Kingdom with low lead uptake usually have²⁰⁶:Pb²⁰⁷Pb ratios in body tissues within the range 1.13 ± 0.01. Significant deviations from this range have been seen in response to increased uptake from lead in: drinking water in parts of Scotland (source ratio ∼1.18 and petrol lead in inner London (source ratio ∼1.07). The dominant source for some Scottish subjects with high concentrations of lead in blood or in teeth was water, which contributed approximately 60% to body lead. Petrol lead was shown to be a significant contributor (30–40%) to the body lead of inner London children.     

珠三角地区POPs农药的污染现状及控制对策

概述了中国及国际社会对持久性有机污染物（Persistent Organic Pollutants,POPs）的关注情况。并通过对POPs农药在珠江三角洲地区（Pearl River Delta Area,PRD）使用情况的调查，以及对珠江三角洲地区POPs农药在各环境介质中的污染现状的文献综述，结合环境污染数据以及POPs农药污染调查工作中得到的数据和信息，对该地区POPs污染的可能原因和环境中可能存在的新近污染源进行了初步探讨。同时也指出了当前珠江三角洲地区在POPs农药削减与淘汰工作中所遭遇到的缺乏完善的管理体系等困难，并针对问题提出了包括加大科研投入，加强基础研究，掌握污染物来源和去向，加强替代药物的研究，建立和实施更严格的环境法规以及标准，加强环境监测能力建设，建立POPs农药污染的信息公开机制等一系列的控制对策。     

Bioaccessible lead in soils, slag, and mine wastes from an abandoned mining district in Brazil

We determined the amount of bioaccessible lead in samples of contaminated soils and in mining and refining wastes collected in the surroundings of a former smelter in a rural area in south-eastern Brazil. Previous studies showed that some resident children and adults had blood Pb levels above recommended limits, but the contamination route was not established. The incidental ingestion of contaminated soils and dusts is considered to be a major route of lead uptake by humans. Bioavailability of heavy metals like Pb depends on solubility during digestion. We used in vitro tests that simulate human gastrointestinal (GI) media to measure the amount of soluble Pb under such conditions. Pb in soil and solid waste samples ranged from 0.03 to 4.1% and 1.2 to 15%, respectively. On average, 70% of the lead content was soluble in three different simulated gastric solutions (pH 1.5 and 1.7). For the same samples, lead solubility decreased to 2–22% when the pH was raised to pH 7 to approximate conditions found in the small intestine. These results indicate that if soils and dusts of the area are ingested, most of the lead will dissolve in the stomach, and part of it will remain soluble in the duodenum, i.e., would be potentially available for absorption. These findings may explain the high blood Pb levels previously reported.     

Heavy metals in surface water and stream sediments in Jamaica

The levels of heavy metals in water and stream sediments in Jamaica are presented and compared to levels in soils and environmental standards. Heavy metals (cadmium, chromium, copper, mercury, nickel, lead and zinc) appear to be less of a problem to Jamaica's freshwater environment than might be expected given the concentrations in soils. This can be explained by taking into account the dynamics of the Jamaican water environment and the relative absence of anthropogenic sources. The dynamics of the freshwater system on the other hand, could pass any environmental threat to the coastal environment. Because the stream sediments are relatively coarse and contain little organic material the bio-availability of micropollutants such as heavy metals from the sediments can be expected to be relatively high.     

Contaminated lead environments of man: reviewing the lead isotopic evidence in sediments,peat, and soils for the temporal and spatial patterns of atmospheric lead pollution in Sweden

Clair Patterson and colleagues demonstrated already four decades ago that the lead cycle was greatly altered on a global scale by humans. Moreover, this change occurred long before the implementation of monitoring programs designed to study lead and other trace metals. Patterson and colleagues also developed stable lead isotope analyses as a tool to differentiate between natural and pollution-derived lead. Since then, stable isotope analyses of sediment, peat, herbaria collections, soils, and forest plants have given us new insights into lead biogeochemical cycling in space and time. Three important conclusions from our studies of lead in the Swedish environment conducted over the past 15 years, which are well supported by extensive results from elsewhere in Europe and in North America, are: (1) lead deposition rates at sites removed from major point sources during the twentieth century were about 1,000 times higher than natural background deposition rates a few thousand years ago (~10 mg Pb m^?2 year^?1 vs. 0.01 mg Pb m^?2 year^?1), and even today (~1 mg Pb m^?2 year^?1) are still almost 100 times greater than natural rates. This increase from natural background to maximum fluxes is similar to estimated changes in body burdens of lead from ancient times to the twentieth century. (2) Stable lead isotopes (²⁰⁶Pb/²⁰⁷Pb ratios shown in this paper) are an effective tool to distinguish anthropogenic lead from the natural lead present in sediments, peat, and soils for both the majority of sites receiving diffuse inputs from long range and regional sources and for sites in close proximity to point sources. In sediments >3,500 years and in the parent soil material of the C-horizon, ²⁰⁶Pb/²⁰⁷Pb ratios are higher, 1.3 to >2.0, whereas pollution sources and surface soils and peat have lower ratios that have been in the range 1.14–1.18. (3) Using stable lead isotopes, we have estimated that in southern Sweden the cumulative anthropogenic burden of atmospherically deposited lead is ~2–5 g Pb m^?2 and ~1 g Pb m^?2 in the “pristine” north. Half of this cumulative total was deposited before industrialization. (4) In the vicinity of the Rönnskär smelter in northern Sweden, a major point source during the twentieth century, there is an isotopic pattern that deviates from the general trends elsewhere, reflecting the particular history of ore usage at Rönnskär, which further demonstrates the chronological record of lead loading recorded in peat and in soil mor horizons.     

水环境中的微塑料及其生态效应

塑料在日常生活中无处不在,随意丢弃的塑料会在各种作用下最终进入江河、湖泊、近海、深海、以及大洋甚至极地地区。在外界条件(如高温、风化、紫外线)影响下,大型塑料结构的完整性易遭到破坏而被逐渐分解成微小的塑料碎片,当其粒径小于5 mm时即可被称为微塑料。塑料中的某些添加剂,如壬基苯酚、多溴联苯醚、邻苯二甲酸盐、双酚A等会在塑料降解为微塑料的过程中释放到水环境中,从而威胁到水生生态系统的安全。微塑料粒径小,易被浮游动物误食或沿着食物链传递,在生物体内累积转移,对机体产生不可逆转的毒害作用。此外,微塑料还能作为某些污染物富集的载体,产生较强的复合毒性。因此水环境正面临着微塑料污染的威胁,如何治理已成为全球性的环境问题。本文对水环境中微塑料的来源与分布、微塑料的迁移和转化以及微塑料对水环境的影响进行了综述,并对水环境中的微塑料污染问题提出了一些解决方案,期望能为微塑料及其在水环境中的生态效应研究提供理论基础和数据支持。     

Lead pollution in East Trinidad resulting from lead recycling and smelting activities

Several problems of acute lead poisoning in children have been identified over the past three years in Trinidad. In all cases investigated so far, continual exposure to lead from battery recycling or from lead-smelter wastes have been found responsible. In East Trinidad, illicit dumping of lead wastes from such sources has resulted in several sites becoming heavily contaminated. Some of these sites are in environmentally sensitive areas, including rivers and wetlands, and require urgent remedial action. Results of monitoring studies at several of these sites show lead levels as high as 75% by weight. The potential for surface and ground water contamination exists, as evidenced by leaching of lead into surrounding areas.     

Geologic materials and gamma radiation in the built environment

Human exposure to natural ionizing radiation is due to both internal sources such as ingestion and inhalation of radioactive isotopes, and external sources from cosmic radiation and primordial radionuclides present in the Earth crust. Primordial radionuclides are ⁴⁰K and radioisotopes of the decay series of ²³⁸U and ²³²Th, which emit gamma radiation at low doses. Gamma emission can occur both in outdoor, due to background geologic radiation, and in indoor spaces, due to the use of geologic materials in dwellings. This radiation has received less attention than man-made sources because it contributes less to the total doses that affect humans, on the average. However, there are geographical areas and rocks used as building materials that contain high concentrations of radionuclides, thus being a source of relatively high gamma dose exposures. Assessing exposure is difficult, especially in indoor situations where there are marked variations regarding materials application. Nonetheless, some measures and regulations to control such dose exposures on building materials have been suggested. This article reviews gamma radiation in geologic materials used for buildings. We discuss: (1) procedures that relate radionuclide contents in building materials to external gamma radiation, considering namely indoor applications and that are used for establishing restrictions on building materials commerce; (2) relation of rock radionuclide contents with their geologic history that can lead to listing of some geologic materials as potentially hazardous in terms of gamma radiation; and (3) the implications for the European regulation, which has an universal criteria that might be excessively restrictive for the commerce of geologic materials used in small amounts, and does not have provisions regarding existing structures where geologic materials are used in extended amounts.     

Habitat quality and heterogeneity influence distribution and behavior in African buffalo (Syncerus caffer)

Top-down effects of predators on prey behavior and population dynamics have been extensively studied. However, some populations of very large herbivores appear to be regulated primarily from the bottom up. Given the importance of food resources to these large herbivores, it is reasonable to expect that forage heterogeneity (variation in quality and quantity) affects individual and group behaviors as well as distribution on the landscape. Forage heterogeneity is often strongly driven by underlying soils, so substrate characteristics may indirectly drive herbivore behavior and distribution. Forage heterogeneity may further interact with predation risk to influence prey behavior and distribution. Here we examine differences in spatial distribution, home range size, and grouping behaviors of African buffalo as they relate to geologic substrate (granite and basalt) and variation in food quality and quantity. In this study, we use satellite imagery, forage quantity data, and three years of radio-tracking data to assess how forage quality, quantity, and heterogeneity affect the distribution and individual and herd behavior of African buffalo. We found that buffalo in an overall poorer foraging environment keyed-in on exceptionally high-quality areas, whereas those foraging in a more uniform, higher-quality area used areas of below-average quality. Buffalo foraging in the poorer-quality environment had smaller home range sizes, were in smaller groups, and tended to be farther from water sources than those foraging in the higher-quality environment. These differences may be due to buffalo creating or maintaining nutrient hotspots (small, high-quality foraging areas) in otherwise low-quality foraging areas, and the location of these hotspots may in part be determined by patterns of predation risk.     

全氟化合物同分异构体的环境行为及毒性效应研究进展

以全氟辛烷磺酸盐(PFOS)和全氟辛烷羧酸(PFOA)为代表的全氟化合物(PFASs)是一类新型持久性有机污染物,目前已经在全球自然环境、野生生物及人群中广泛检出,其环境与健康问题已引起人们的高度重视。传统的电氟化法生产工艺使PFASs产品存在碳链同分异构体。这些PFAS的同分异构体可能具有不同的环境行为和毒理效应。随着分析方法的逐渐成熟,目前,国外的学者已经在该研究领域进行了一些探索性的研究,并取得了一定的进展,而我国在该领域的研究相对较少。以PFOS和PFOA为例,在介绍了PFAS同分异构体的来源、命名和世界各地生产厂家的异构体组成等基本信息的基础上,还系统介绍了环境介质中PFAS同分异构体的分析方法、环境迁移转化差异及源分析研究;生物和人体的生物累积性及毒理学差异等;并对目前存在的问题进行了讨论,为今后PFAS同分异构体的环境问题研究提供相应的参考。     

Spatial relationships between lead sources and children’s blood lead levels in the urban center of Indianapolis (USA)

Urban children remain disproportionately at risk of having higher blood lead levels than their suburban counterparts. The Westside Cooperative Organization (WESCO), located in Marion County, Indianapolis, Indiana, has a history of children with high blood lead levels as well as high soil lead (Pb) values. This study aims at determining the spatial relationship between soil Pb sources and children’s blood lead levels. Soils have been identified as a source of chronic Pb exposure to children, but the spatial scale of the source–recipient relationship is not well characterized. Neighborhood-wide analysis of soil Pb distribution along with a furnace filter technique for sampling interior Pb accumulation for selected homes (n = 7) in the WESCO community was performed. Blood lead levels for children aged 0–5 years during the period 1999–2008 were collected. The study population’s mean blood lead levels were higher than national averages across all ages, race, and gender. Non-Hispanic blacks and those individuals in the Wishard advantage program had the highest proportion of elevated blood lead levels. The results show that while there is not a direct relationship between soil Pb and children’s blood lead levels at a spatial scale of ~100 m, resuspension of locally sourced soil is occurring based on the interior Pb accumulation. County-wide, the largest predictor of elevated blood lead levels is the location within the urban core. Variation in soil Pb and blood lead levels on the community level is high and not predicted by housing stock age or income. Race is a strong predictor for blood lead levels in the WESCO community.     

Distribution and mode of occurrence of selenium in US coals

Selenium excess and deficiency have been established as the cause of various health problems in man and animals. Combustion of fossil fuels, especially coal, may be a major source of the anthropogenic introduction of selenium in the environment. Coal is enriched in selenium relative to selenium's concentration in most other rocks and relative to selenium in the Earth's crust.Data from almost 9,000 coal samples have been used to determine the concentration and distribution of selenium in US coals. The geometric mean concentration of selenium in US coal is 1.7 ppm. The highest mean selenium value (geometric mean 4.7 ppm) is in the Texas Region. Atlantic Coast (Virginia and North Carolina) and Alaska coals have the lowest geometric means (0.2 and 0.42 ppm, respectively). All western coal regions have mean selenium concentrations of less than 2.0 ppm. In contrast, all coal basins east of the Rocky Mountains (except for several small basins in Rhode Island, Virginia, and North Carolina) have mean selenium values of 1.9 or greater.Generally, variations in selenium concentration do not correlate with variations in ash yield, pyritic sulphur, or organic sulphur concentrations. This may be the result of multiple sources of selenium; however, in some non-marine basins with restricted sources of selenium, selenium has positive correlations with other coal quality parameters.Selenium occurs in several forms in coal but appears to be chiefly associated with the organic fraction, probably substituting for organic sulphur. Other important forms of selenium in coal are selenium-bearing pyrite, selenium-bearing galena, and lead selenide (clausthalite). Water-soluble and ion-exchangeable selenium also have been reported.     

Lead redistribution in a mine soil treated with three manures and incubated at two different temperatures

The study of heavy metals’ redistribution between different fractions allows to know their bioavailability and mobility in soils. Soil samples were collected from a lead mine in Hamadan provinces, NW Iran. In a factorial experiment soil was treated with cow, sheep and poultry manures (20?g?kg^?1 soil) separately and incubated near field capacity at 10°C and 37°C. An untreated soil (as control) was also incubated at the same temperatures. After 0 and 120 days, a sequential extraction scheme was used to fractionate Pb of incubated samples into soluble-exchangeable (Sol-Exch), organic matter associated (AOM), carbonates associated (ACar), and residual (Res) forms. Soil Pb in Sol-Exch and AOM fractions were increased by manure application significantly. The AOM and ACar forms of Pb were higher in soils treated with the manures and incubated in lower temperature. In contrast, the Sol-Exch and Res chemical forms of Pb were higher in the soils incubated at 37°C. These results may be related to the higher calcium carbonate dissolution and organic matter decomposition because of better biological activity in the soils incubated in higher temperature. The increase of the Res fraction (stable form) in this condition may resulted in lower toxicity and mobility in soil environment.     

纳米颗粒与生物来源有机磷在水环境中的行为研究

随着纳米技术产业的快速发展,各种纳米颗粒(NPs)大规模生产,这不可避免地增加了NPs释放到环境、暴露于生态系统的可能性.有机磷是废水中磷的主要形式之一,是生物有效磷池和水体富营养化的重要组成部分.本文综述了近几年来NPs与生物来源有机磷在水环境中的反应机制、微观结构等方面的研究进展.文中按NPs的分类分别总结了NPs对常见的生物来源有机磷的吸附-解吸,溶解-沉淀等反应特性和微观机制.在水环境中,NPs因其物化特性受水化学条件(pH、天然有机质、温度)等影响,进而影响与有机磷的反应,从而表现出相应不同的环境效应.本文也对此方面的研究进行了讨论和总结.最后分析了目前纳米颗粒与有机磷在水环境研究中的瓶颈问题,并展望了未来需要开展的研究.     

工业废水毒性鉴定评价方法体系的建议及其应用示例

工业废水是自然环境中毒害污染物的主要来源,对其进行毒性鉴定和评价,是废水毒性管控的基础。我国目前仍缺乏规范的工业废水毒性鉴定和评价体系,本文针对这一状况,综述了美国环保局颁布的废水毒性鉴定评价（TIE）指南和欧盟采用的效应导向分析（EDA）方法,提出了结合TIE方法和EDA方法的优点建立工业废水毒性鉴定评价方法体系的建议,并选取珠三角地区电镀废水作为该体系的应用示例,采用发光菌和重组基因酵母菌进行快速毒性测试,并结合化学分析方法,确定电镀行业废水毒性主要来源于金属Cu和壬基酚聚氧乙烯醚类有机物。     

Understanding the role of nano-TiO2 on the toxicity of Pb on C. dubia through modeling–Is it additive or synergistic?

• A two-compartment model is able to quantify the effect of nano-TiO₂ on Pb toxicity. • Nano-TiO₂ reduces Pb tolerance level and increased the killing rate for C. dubia. • Thus, nano-TiO₂ synergistically enhances Pb toxicity. • Algae reduce Pb transfer rate to the body tissue and the killing rate. Nano-TiO₂ can remarkably increase lead (Pb) toxicity in aquatic organisms. However, the mechanism of this toxicity, additive or synergistic, is not well understood. To explore this mechanism, we inspected the role of nano-TiO₂ in the toxicity of Pb on Ceriodaphnia dubia (C. dubia), a model water flea species typically used for ecotoxicity studies. The effect of algae, a diet for aquatic organisms, on the effect of this binary mixture was also investigated. A two-compartment toxicokinetic (TK)-toxicodynamic (TD) modeling approach was used to quantify the Pb toxicity under these complex conditions and to develop critical parameters for understanding the mechanism of toxicity. This two-compartment modeling approach adequately described the Pb accumulation in the gut and in the rest of the body tissue under different nano-TiO₂ concentrations, with and without algae, and predicted the toxicity response of C. dubia. It indicated that increasing the nano-TiO₂ concentration reduced the Pb tolerance level and concurrently increased the killing rate constant of C. dubia. Therefore, nano-TiO₂ synergistically enhanced Pb toxicity. Algae remarkably reduced the toxicity of this binary mixture through reducing the Pb transfer rate to the body tissue and the killing rate, although it did not affect the Pb tolerance level. This two-compartment modeling approach is useful in understanding the role of nanoparticles when assessing the overall toxicity of nanoparticles and other toxic elements in the environment.