Widespread Pb contamination in urban backyard soils for >100 years identified in soil cores constrained by 210Pb and 137Cs

Contaminated soil in urban residential areas is often overlooked as a source of childhood exposure to toxic levels of lead (Pb). We document mean Pb concentrations of 1200 ± 1000 mg/kg, three times the now outdated EPA soil hazard standard of 400 mg/kg, for 370 surface soils collected from 76 homes...

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Veröffentlicht in:The Science of the total environment 2023-11, Vol.899, p.165407-165407, Article 165407
Hauptverfasser: Landes, Franziska C., Calcio, Margaret, Sobolewski, Jennifer M., Wallens-Logan, Kelcey, Ledeczi, Anna, Kiro, Yael, Bolge, Louise, Ross, James, Chillrud, Steven N., Mailloux, Brian J., van Geen, Alexander
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container_title The Science of the total environment
container_volume 899
creator Landes, Franziska C.
Calcio, Margaret
Sobolewski, Jennifer M.
Wallens-Logan, Kelcey
Ledeczi, Anna
Kiro, Yael
Bolge, Louise
Ross, James
Chillrud, Steven N.
Mailloux, Brian J.
van Geen, Alexander
description Contaminated soil in urban residential areas is often overlooked as a source of childhood exposure to toxic levels of lead (Pb). We document mean Pb concentrations of 1200 ± 1000 mg/kg, three times the now outdated EPA soil hazard standard of 400 mg/kg, for 370 surface soils collected from 76 homes in the boroughs of Brooklyn and Manhattan of New York City. The mean Pb content of 250 ± 290 mg/kg Pb for 571 surface soils collected from tree pits and public parks was much lower. A subset of 22 surface samples analyzed by EPA Method 1340 extracted 86 ± 21 % (±1SD) of total soil Pb, indicating that it the Pb was highly bioavailable. To investigate the origin of backyard contamination, 49 cores were collected to an average depth of 30 cm from a subset of 27 homes. Twelve soil cores were analyzed for 210Pb and 137Cs to constrain processes that impact contaminant distribution and inventories (particle focusing, soil accumulation, loss, and mixing). Concentrations of Pb declined with depth in 60 % of the cores but usually did not reach background. Mean uncorrected Pb inventories of 340 ± 210 g/m2 Pb (mean ± 1SD, n = 12) were more than five times higher than the radionuclide corrected inventory of 57 g/m2 from Central Park soil cores. Average inventories of 210Pbxs (3.5 ± 0.9 kBq/m2) and 137Cs (0.9 ± 0.6 kBq/m2) corresponded to 71 ± 19 % and 50 ± 30 % of the predicted atmospheric inventories. Elevated Pb concentrations were found both in the fine (1 mm) fractions, the latter suggesting a local non-atmospheric source. This was confirmed by individual grains containing up to 6 % Pb and visible pieces of coal, bricks, and ash. Regardless of the source of contamination in backyard soils, systematic testing is needed to identify contaminated areas and reduce child exposure. [Display omitted] •Backyards sampled in NYC average 1200 mg/kg in soil Pb, 3-times the EPA standard.•Soil from tree pits and public parks average 250 mg/kg Pb in the same study areas.•210Pbxs and 137Cs indicate Pb accumulation higher than regional atmospheric fallout.•Particles >1 mm with up to 6 % Pb suggest local source(s) other than paint.•Backyards in New York City should be tested for Pb, especially where children play.
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We document mean Pb concentrations of 1200 ± 1000 mg/kg, three times the now outdated EPA soil hazard standard of 400 mg/kg, for 370 surface soils collected from 76 homes in the boroughs of Brooklyn and Manhattan of New York City. The mean Pb content of 250 ± 290 mg/kg Pb for 571 surface soils collected from tree pits and public parks was much lower. A subset of 22 surface samples analyzed by EPA Method 1340 extracted 86 ± 21 % (±1SD) of total soil Pb, indicating that it the Pb was highly bioavailable. To investigate the origin of backyard contamination, 49 cores were collected to an average depth of 30 cm from a subset of 27 homes. Twelve soil cores were analyzed for 210Pb and 137Cs to constrain processes that impact contaminant distribution and inventories (particle focusing, soil accumulation, loss, and mixing). Concentrations of Pb declined with depth in 60 % of the cores but usually did not reach background. Mean uncorrected Pb inventories of 340 ± 210 g/m2 Pb (mean ± 1SD, n = 12) were more than five times higher than the radionuclide corrected inventory of 57 g/m2 from Central Park soil cores. Average inventories of 210Pbxs (3.5 ± 0.9 kBq/m2) and 137Cs (0.9 ± 0.6 kBq/m2) corresponded to 71 ± 19 % and 50 ± 30 % of the predicted atmospheric inventories. Elevated Pb concentrations were found both in the fine (&lt;1 mm) and coarse (&gt;1 mm) fractions, the latter suggesting a local non-atmospheric source. This was confirmed by individual grains containing up to 6 % Pb and visible pieces of coal, bricks, and ash. Regardless of the source of contamination in backyard soils, systematic testing is needed to identify contaminated areas and reduce child exposure. 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We document mean Pb concentrations of 1200 ± 1000 mg/kg, three times the now outdated EPA soil hazard standard of 400 mg/kg, for 370 surface soils collected from 76 homes in the boroughs of Brooklyn and Manhattan of New York City. The mean Pb content of 250 ± 290 mg/kg Pb for 571 surface soils collected from tree pits and public parks was much lower. A subset of 22 surface samples analyzed by EPA Method 1340 extracted 86 ± 21 % (±1SD) of total soil Pb, indicating that it the Pb was highly bioavailable. To investigate the origin of backyard contamination, 49 cores were collected to an average depth of 30 cm from a subset of 27 homes. Twelve soil cores were analyzed for 210Pb and 137Cs to constrain processes that impact contaminant distribution and inventories (particle focusing, soil accumulation, loss, and mixing). Concentrations of Pb declined with depth in 60 % of the cores but usually did not reach background. Mean uncorrected Pb inventories of 340 ± 210 g/m2 Pb (mean ± 1SD, n = 12) were more than five times higher than the radionuclide corrected inventory of 57 g/m2 from Central Park soil cores. Average inventories of 210Pbxs (3.5 ± 0.9 kBq/m2) and 137Cs (0.9 ± 0.6 kBq/m2) corresponded to 71 ± 19 % and 50 ± 30 % of the predicted atmospheric inventories. Elevated Pb concentrations were found both in the fine (&lt;1 mm) and coarse (&gt;1 mm) fractions, the latter suggesting a local non-atmospheric source. This was confirmed by individual grains containing up to 6 % Pb and visible pieces of coal, bricks, and ash. Regardless of the source of contamination in backyard soils, systematic testing is needed to identify contaminated areas and reduce child exposure. [Display omitted] •Backyards sampled in NYC average 1200 mg/kg in soil Pb, 3-times the EPA standard.•Soil from tree pits and public parks average 250 mg/kg Pb in the same study areas.•210Pbxs and 137Cs indicate Pb accumulation higher than regional atmospheric fallout.•Particles &gt;1 mm with up to 6 % Pb suggest local source(s) other than paint.•Backyards in New York City should be tested for Pb, especially where children play.</description><subject>Anthropogenic soils</subject><subject>Atmospheric radionuclides</subject><subject>Bioaccessibility</subject><subject>bioavailability</subject><subject>cesium radioisotopes</subject><subject>childhood</subject><subject>children</subject><subject>coal</subject><subject>environment</subject><subject>inventories</subject><subject>lead</subject><subject>Lead contamination</subject><subject>New York</subject><subject>polluted soils</subject><subject>Soil core profiles</subject><subject>toxicity</subject><subject>trees</subject><issn>0048-9697</issn><issn>1879-1026</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><recordid>eNqNkc2KFDEURoMo2I4-g1m6qfYmlUpSG2FodBQGdKG4DPm5BWm7kzZJDzS-jM_ik5mixa1mcxc537lcPkJeMtgyYPL1flt9bLlhethy4OOWyUmAekQ2TKt5YMDlY7IBEHqY5ayekme17qE_pdmG_PgaA9ZTQRvoJ0d9Ts0eY7It5kRjoufibKLO-m8XWwKtOR4qXXKhbxjAr58XtKXSrkgtLhHDGlmZLipYV11txcbUf9yFcgZ9h02BslHt6nPyZLGHii_-zBvy5d3bz7v3w_3Huw-72_vBjxLaEBy6sFjmOUgptLBCTIhsUiFYz8LitBXjEpzWYp7t4kaP0zhPPDiHcgY_3pBXV--p5O9nrM0cY_V4ONiE-VwN11pJrkY-_wcqBHQcREfVFfUl11pwMacSj7ZcDAOzNmP25m8zZm3GXJvpydtrEvvRDxHLymHyGGJB30zI8Z-O3wu2nV8</recordid><startdate>20231115</startdate><enddate>20231115</enddate><creator>Landes, Franziska C.</creator><creator>Calcio, Margaret</creator><creator>Sobolewski, Jennifer M.</creator><creator>Wallens-Logan, Kelcey</creator><creator>Ledeczi, Anna</creator><creator>Kiro, Yael</creator><creator>Bolge, Louise</creator><creator>Ross, James</creator><creator>Chillrud, Steven N.</creator><creator>Mailloux, Brian J.</creator><creator>van Geen, Alexander</creator><general>Elsevier B.V</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope><scope>7S9</scope><scope>L.6</scope></search><sort><creationdate>20231115</creationdate><title>Widespread Pb contamination in urban backyard soils for &gt;100 years identified in soil cores constrained by 210Pb and 137Cs</title><author>Landes, Franziska C. ; 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We document mean Pb concentrations of 1200 ± 1000 mg/kg, three times the now outdated EPA soil hazard standard of 400 mg/kg, for 370 surface soils collected from 76 homes in the boroughs of Brooklyn and Manhattan of New York City. The mean Pb content of 250 ± 290 mg/kg Pb for 571 surface soils collected from tree pits and public parks was much lower. A subset of 22 surface samples analyzed by EPA Method 1340 extracted 86 ± 21 % (±1SD) of total soil Pb, indicating that it the Pb was highly bioavailable. To investigate the origin of backyard contamination, 49 cores were collected to an average depth of 30 cm from a subset of 27 homes. Twelve soil cores were analyzed for 210Pb and 137Cs to constrain processes that impact contaminant distribution and inventories (particle focusing, soil accumulation, loss, and mixing). Concentrations of Pb declined with depth in 60 % of the cores but usually did not reach background. Mean uncorrected Pb inventories of 340 ± 210 g/m2 Pb (mean ± 1SD, n = 12) were more than five times higher than the radionuclide corrected inventory of 57 g/m2 from Central Park soil cores. Average inventories of 210Pbxs (3.5 ± 0.9 kBq/m2) and 137Cs (0.9 ± 0.6 kBq/m2) corresponded to 71 ± 19 % and 50 ± 30 % of the predicted atmospheric inventories. Elevated Pb concentrations were found both in the fine (&lt;1 mm) and coarse (&gt;1 mm) fractions, the latter suggesting a local non-atmospheric source. This was confirmed by individual grains containing up to 6 % Pb and visible pieces of coal, bricks, and ash. Regardless of the source of contamination in backyard soils, systematic testing is needed to identify contaminated areas and reduce child exposure. [Display omitted] •Backyards sampled in NYC average 1200 mg/kg in soil Pb, 3-times the EPA standard.•Soil from tree pits and public parks average 250 mg/kg Pb in the same study areas.•210Pbxs and 137Cs indicate Pb accumulation higher than regional atmospheric fallout.•Particles &gt;1 mm with up to 6 % Pb suggest local source(s) other than paint.•Backyards in New York City should be tested for Pb, especially where children play.</abstract><pub>Elsevier B.V</pub><doi>10.1016/j.scitotenv.2023.165407</doi><tpages>1</tpages><oa>free_for_read</oa></addata></record>
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source Elsevier ScienceDirect Journals
subjects Anthropogenic soils
Atmospheric radionuclides
Bioaccessibility
bioavailability
cesium radioisotopes
childhood
children
coal
environment
inventories
lead
Lead contamination
New York
polluted soils
Soil core profiles
toxicity
trees
title Widespread Pb contamination in urban backyard soils for >100 years identified in soil cores constrained by 210Pb and 137Cs
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