Abstract:In New Orleans, LA prior to hurricane Katrina 20-30% of inner-city children had elevated blood Pb levels > or =10 microg/ dL and 10 census tracts had a median surface soil level of Pb >1000 mg/kg (2.5 times the U.S. standard). This project tests the feasibility of transporting and grading contaminated properties (n = 25) with 15 cm (6 in.) of clean Mississippi River alluvium from the Bonnet Carré Spillway (BCS) (median soil Pb content 4.7 mg/kg; range 1.7-22.8). The initial median surface soil Pb was 1051 mg/k… Show more
“…Zahran et al (2010) report on how natural processes did this same experiment, seeing substantially lower blood Pb levels for New Orleans children after Hurricane Katrina, due to the capping of much of the Pb-contaminated soil with flood-related sediments. Mielke et al (2006) observed that, over the course of several months after treatment, soil Pb levels in the treated sites began increasing. This increase was due to dust generated from soils from adjacent, untreated yards and neighborhoods that still had high soil Pb concentrations.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 98%
“…Most mitigation efforts for heavily-contaminated soils have involved soil removal and replacement, a disruptive and expensive option for controlling Pb sources in urban areas. Another approach was tested which was simply to cover the contaminated yard soils with about 15 cm of Pb-free soil, which in the case of New Orleans came from the nearby Mississippi levee (Mielke et al, 2006). At a fraction of the soil removal cost, this clean soil is simply graded over the old soil layer, hydroseeded, and left to grow a lawn.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 99%
“…This approach caps the Pb-contaminated soils, removing them from contact by children. The result of this approach has been a substantial reduction in the blood Pb levels of children living in the affected homes (Mielke et al, 2006). Zahran et al (2010) report on how natural processes did this same experiment, seeing substantially lower blood Pb levels for New Orleans children after Hurricane Katrina, due to the capping of much of the Pb-contaminated soil with flood-related sediments.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 99%
“…As indicated above, surface capping of Pb-contaminated soils is effective, especially if done on a neighborhood rather than individual property scale. Mielke et al (2006) calculated that the entire Pb-affected area of New Orleans could be remediated by capping for a total cost of less than $US 300M, compared to the $76M annual cost to New Orleans of Pb poisoning. Simply put, the national cost of doing nothing about soil Pb is staggering- Gould (2009) calculates that Pb poisoning costs the nation $US 30-146M in special education, $US 267M in attention deficit-hyperactivity disorder, and $US 1.7B in the direct cost of crime and recidivism.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
The past and future of cities are inextricably linked, a linkage that can be seen clearly in the long-term impacts of urban geochemical legacies. As loci of population as well as the means of employment and industry to support these populations, cities have a long history of co-locating contaminating practices and people, sometimes with negative implications for human health.
“…Zahran et al (2010) report on how natural processes did this same experiment, seeing substantially lower blood Pb levels for New Orleans children after Hurricane Katrina, due to the capping of much of the Pb-contaminated soil with flood-related sediments. Mielke et al (2006) observed that, over the course of several months after treatment, soil Pb levels in the treated sites began increasing. This increase was due to dust generated from soils from adjacent, untreated yards and neighborhoods that still had high soil Pb concentrations.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 98%
“…Most mitigation efforts for heavily-contaminated soils have involved soil removal and replacement, a disruptive and expensive option for controlling Pb sources in urban areas. Another approach was tested which was simply to cover the contaminated yard soils with about 15 cm of Pb-free soil, which in the case of New Orleans came from the nearby Mississippi levee (Mielke et al, 2006). At a fraction of the soil removal cost, this clean soil is simply graded over the old soil layer, hydroseeded, and left to grow a lawn.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 99%
“…This approach caps the Pb-contaminated soils, removing them from contact by children. The result of this approach has been a substantial reduction in the blood Pb levels of children living in the affected homes (Mielke et al, 2006). Zahran et al (2010) report on how natural processes did this same experiment, seeing substantially lower blood Pb levels for New Orleans children after Hurricane Katrina, due to the capping of much of the Pb-contaminated soil with flood-related sediments.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
confidence: 99%
“…As indicated above, surface capping of Pb-contaminated soils is effective, especially if done on a neighborhood rather than individual property scale. Mielke et al (2006) calculated that the entire Pb-affected area of New Orleans could be remediated by capping for a total cost of less than $US 300M, compared to the $76M annual cost to New Orleans of Pb poisoning. Simply put, the national cost of doing nothing about soil Pb is staggering- Gould (2009) calculates that Pb poisoning costs the nation $US 30-146M in special education, $US 267M in attention deficit-hyperactivity disorder, and $US 1.7B in the direct cost of crime and recidivism.…”
Section: New Views Of Lead Mitigation Approaches In Citiesmentioning
The past and future of cities are inextricably linked, a linkage that can be seen clearly in the long-term impacts of urban geochemical legacies. As loci of population as well as the means of employment and industry to support these populations, cities have a long history of co-locating contaminating practices and people, sometimes with negative implications for human health.
“…Capping lead contaminated urban soil with clean fill prevents contaminated soil from being resuspended as dust, thus reducing exposure through ingestion and inhalation of this resuspended soil dust, especially in summer months (Beniston and Lal, 2012;Filipelli and Laidlaw, 2010;Mielke et al, 2006;Mielke et al, 2011;Mielke et al, 2013;Wortman and Lovell, 2013). This approach is effective and financially feasible when a readily available, locally sourced fill is applied to exposed soils at the neighborhood scale (Filippelli et al, 2015).…”
Chronic low-level lead exposure among low-income minority children is an urgent environmental justice issue. Addressing this ubiquitous urban public health crisis requires a new transdisciplinary paradigm. The primary goals of this work are to inform best practices for urban gardeners working in lead contaminated soils and to reimagine urban organic waste management schemes to produce compost, which when covering or mixed with urban soil, could minimize lead exposure. We investigate bulk and bioaccessible lead from five types of compost used in urban gardens in Boston, MA. We categorized them by feedstock and measured bulk elemental concentrations and physical characteristics. Our results show that different feedstocks exhibit unique geochemical fingerprints. While bulk lead concentrations in compost are a fraction of what is typical for urban soils, the bioaccessible lead fraction in compost is greater than the default parameters for the Integrated Exposure Uptake Biokinetic (IEUBK) model. The lack of geochemical differences across feedstocks for lead sorption to carbon indicates a similar sorption mechanism for all compost. This suggests that municipal compost would be suitable for capping lead contaminated urban soils. Risk assessment models should consider lead bioaccessibility, to prevent the underprediction of exposure risk, and should include compost along with soils as urban matrices. Based on the observed bioaccessibility in our compost samples, 170 mg/kg total lead in compost will yield the same bioaccessible lead as the IEUBK model predicts for the 400 mg/kg EPA soil lead benchmark. Local logistical challenges remain for interdisciplinary teams of city planners, exposure scientists, and urban agricultural communities to design organic waste collection practices to produce compost that will support urban agriculture and primary lead exposure prevention.
While the presence of legacy lead (Pb) in urban soil is well documented, less is known about the bioaccessibility, transport, and exposure pathways of urban soil Pb. We study Pb bioaccessibility in Roxbury and Dorchester, MA, urban gardens to assess exposure risk and identify remediation strategies, applicable locally and in urban gardens across the country. We work in partnership with The Food Project, which brings the goals and perspectives of local farmers to the center of the research process and enables efficient local application of results to reduce Pb exposure. We measure changes in Pb bioaccessibility as a function of growing material, grain size, and Pb source. In comparison to soils, compost has lower total Pb concentrations, has lower Pb solubility in gastric fluid, and limits fine particle resuspension. The mean bioaccessible Pb concentration of compost is 265 mg/kg, nearly an order of magnitude lower than that of soils, and compost contains 14% higher carbon content than soils, which may account for the observed 19% lower Pb bioaccessibility in compost. For all matrices (soil, raised bed fill, and compost) grain sizes <37 μm contain a disproportionate fraction of the total pool of bioaccessible Pb. Furthermore, the isotopic composition of Pb in the size fractions linked with resuspension and elevated blood lead levels is indicative of leaded gasoline and leaded paint even decades removed from the primary deposition of these sources.
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